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HomeMy WebLinkAboutRA-5020_26571_CA_MRP_20230714 ENVIRONMENTAL | CIVIL | GEOTECHNICAL MONITORING REPORT FORMER UNION 76 GASOLINE STATION 2236 OLD US 1 HIGHWAY APEX, WAKE COUNTY, NC NCDEQ INCIDENT NO. 26571 RISK CLASSIFICATION: H0875D JULY 14, 2023 NCDEQ CONTRACT NO. N122019D TASK AUTHORIZATION NO. 04 CATLIN PROJECT NO. 220217 PREPARED FOR: MS. LINDA BLALOCK NCDEQ, DWM, UST SECTION 1646 MAIL SERVICE CENTER RALEIGH, NC 27699-1646 PREPARED BY: CATLIN ENGINEERS AND SCIENTISTS 220 OLD DAIRY ROAD WILMINGTON, NC 28405 (910) 452-5861 CORPORATE LICENSURE NO. FOR ENGINEERING SERVICES C-0585 CORPORATE LICENSURE NO. FOR GEOLOGY SERVICES C-118 NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 TABLE OF CONTENTS PAGE 1.0 SITE INFORMATION 1 2.0 EXECUTIVE SUMMARY 2 3.0 SCOPE OF SERVICES 3 4.0 SITE HISTORY AND CHARACTERIZATION 3 4.1 UST OWNER AND OPERATOR INFORMATION 3 4.2 UST INFORMATION 4 4.3 CONTAMINANT SOURCE INVENTORY 4 4.4 SITE CHARACTERISTICS 4 4.5 OWNERS AND OCCUPANTS OF ADJOINING/NEARBY PROPERTIES AND LAND USE 4 4.6 RECEPTOR INFORMATION 5 4.7 PREVIOUS INVESTIGATIONS AND REMEDIAL ACTIVITIES 5 5.0 REGIONAL AND SITE GEOLOGY AND HYDROGEOLOGY 7 5.1 SOIL AND BEDROCK 7 5.2 HYDROGEOLOGY 8 6.0 SITE ASSESSMENT INFORMATION 8 6.1 ENHANCED AFVR EVENT 8 6.2 GAUGING DATA 9 6.3 SAMPLING DATA 9 6.4 SUMMARY OF GROUNDWATER INFORMATION 10 6.5 EVALUATION OF ASSESSMENT INFORMATION 11 7.0 CONCLUSIONS AND RECOMMENDATIONS 12 8.0 LIMITATIONS 13 9.0 STATEMENTS AND CERTIFICATIONS 13 10.0 REFERENCES 14 NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 TABLES TABLE 1 SITE HISTORY – UST SYSTEM AND OTHER RELEASE INFORMATION TABLE 2 PUBLIC AND PRIVATE WATER SUPPLY WELLS AND OTHER RECEPTOR INFORMATION TABLE 3 WELL CONSTRUCTION AND HISTORICAL WATER LEVEL GAUGING DATA TABLE 4 SUMMARY OF GROUNDWATER LABORATORY RESULTS – STANDARD METHOD 6200B TABLE 5 SUMMARY OF HISTORICAL GROUNDWATER LABORATORY RESULTS – STANDARD METHOD 6200B FIGURES FIGURE 1 SITE VICINITY MAP FIGURE 2 POTENTIAL RECEPTOR MAP FIGURE 3 SITE MAP FIGURE 4 GROUNDWATER ELEVATION – MAY 10, 2023 FIGURE 5 MONITORING WELL GROUNDWATER SAMPLE ANALYTICAL RESULTS – MAY 10, 2023 APPENDICES APPENDIX A HISTORICAL DATA APPENDIX B SITE PHOTOGRAPHS APPENDIX C JOB HAZARD ANALYSES AND FIELD DATA SHEETS APPENDIX D ENHANCED AFVR EMISSIONS CALCULATIONS APPENDIX E DISPOSAL DOCUMENTS APPENDIX F LABORATORY ANALYTICAL REPORT AND CHAIN OF CUSTODY DOCUMENT NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 1 July 2023 1.0 SITE INFORMATION Site Identification Date: 07/14/2023 Site Risk/Priority Rank: H0875D UST Number: RA-5020 Incident Number: 26571 Site Name: Former Union 76 Gasoline Station Facility ID: Unknown Site Location: 2236 Old US 1 Highway Nearest City/Town: Apex County: Wake Description of Geographical Data Point: Former UST basin Location Method: Google Earth Latitude (decimal degrees): 35.69887° Longitude (decimal degrees): -78.89949° Contacts Information UST Owner: C.C. Tunstall (Deceased) Address: N/A Phone: N/A UST Operator: C.C. Tunstall (Deceased) Address: N/A Phone: N/A Property Owner: David Powell Address: 861 Bethlehem Church Rd., Youngsville, NC Phone: (919) 880-5987 Property Occupant: Unknown Address: 2236 Old US 1 Highway, Apex, NC Phone: Unknown Consultant: CATLIN Engineers and Scientists Address: 220 Old Dairy Rd., Wilmington, NC 28405 Phone: (910) 452-5861 Corporate Licensure No. For Engineering Services: C-0585 Corporate Geology License No.: C-118 Analytical Laboratory: Con-Test Analytical Laboratory State Certification: NC 652, NC-DW 25703 Address: 39 Spruce St., E. Longmeadow, MA 01028 Phone: (413) 525-2332 Release Information Date Discovered: 03/17/2004 Estimated Quantity of Release: Unknown Cause of Release: Leak in the UST system Source of Release: UST system or associated fitting(s) Sizes and contents of UST system(s) from which the release occurred: • One 550-gallon gasoline UST • One 1,000-gallon gasoline UST NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 2 July 2023 2.0 EXECUTIVE SUMMARY The Former Union 76 Gasoline Station Site is located at 2236 Old US 1 Highway, Apex, Wake County, North Carolina. This site operated as a retail gasoline fueling station from the early 1940s until 1982 by Mr. C.C. Tunstall, and subsequently his son Edward Tunstall. The former underground storage tank (UST) system was installed in the early 1940s and consisted of one 550-gallon gasoline and one 1,000-gallon gasoline UST. The USTs were removed on March 17, 2004, and in the removal process, soil contaminated with petroleum constituents were discovered below one of the tanks, and later in the on-site water supply well (WSW) that supplied potable water to the store building. The former UST owner is deceased. Currently, the property is owned by David Powell and consists of a rental house and a church building. The purpose of this report is to document the latest remediation efforts and groundwater sampling activities. On April 11, 2023, CATLIN Engineers and Scientists (CATLIN) coordinated with Eastern Environmental Management, LLC (EEM) to conduct an enhanced aggressive fluid vapor recovery (AFVR) event with air sparging. Monitoring wells MW-1, MW-2, and MW-3R were used as extraction points, and air sparging was performed through monitoring well DW-1. The event lasted eight hours and resulted in the recovery of 517 gallons of impacted groundwater and a calculated 1.34 pounds of petroleum vapors (equivalent to 0.21 gallons of petroleum) were removed. CATLIN returned to the site on May 10, 2023, to conduct gauging and sampling activities. CATLIN personnel gauged all accessible wells for depth to water. Depth to water in the shallow (Type II) wells was an average of 14.5 feet below top of casing (BTOC). Depth to water in the deep (Type III) well (DW-1) was 15.59 feet BTOC. Samples were collected from eight monitoring wells (MW-1, MW-2, MW-3R, MW-4R, MW-5, MW-6, MW-7, and DW-1) and submitted for volatile organic compounds (VOCs) analysis per Standard Method (SM) 6200B [plus ethylene dibromide (EDB), methyl tert-butyl ether (MTBE), and diisopropyl ether (DIPE)]. Laboratory results did not indicate any dissolved petroleum constituents above their respective laboratory method detection limits in the samples from monitoring wells MW-5, MW-6, and MW-7. One or more VOCs were detected in the MW-1, MW-2, MW-3R, MW-4R, and DW-1 samples at concentrations greater than those established in Title 15A of the North Carolina Administrative Code, Subchapter 2L, Section .0202 Groundwater Quality Standards (2L GWQS), but below the Gross Contaminant Levels (GCLs). Contaminant concentrations appear to have generally decreased in samples from monitoring wells MW-2, MW-3R, and DW-1 since the previous sampling event in March 2023, while those in MW-1 and MW-4R have increased. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 3 July 2023 As detailed in the previous monitoring report, the subject site and surrounding properties are likely to be sold and developed. During development activities, water supply wells WSW-1, WSW-2, WSW-4, WSW-10 WSW-12 and WSW-13 would be abandoned. In addition, there is the potential for redevelopment (by a different firm) across Old US 1 Highway, which would result in the abandonment of the majority of water supply wells within 1,000 feet of the subject site. The proposed redevelopment in the area may allow for a risk reduction for the subject site and another site located across Old US 1 Highway (McNeil’s Grocery Site - Incident Number 6891) from high risk to low risk classification. Based on the current laboratory data and the potential sale and redevelopment of the property, CATLIN recommends the following: • Collect one additional sample from MW-3R and abandon all on-site monitoring wells immediately before the start of site development. 3.0 SCOPE OF SERVICES The scope of services for this report was performed in general accordance with CATLIN proposal number 220217.04P, dated March 24, 2023. Services were authorized by the North Carolina Environmental Quality (NCDEQ) Task Authorization (TA) #04, accepted March 24, 2023, and Contract Number N122019D. The approved scope of services for this Task Authorization included: • Coordinate and oversee an enhanced AFVR event; • Approximately 30 days after the event, collect samples from eight monitoring wells (MW-1, MW-2, MW-3R, MW-4R, MW-5, MW-6, MW-7, and DW-1); • Analyze 10 water samples (eight monitoring wells, one equipment blank, and one laboratory-provided trip blank) per SM 6200B (plus EDB, MTBE, and DIPE); and • Prepare and submit a monitoring report summarizing the findings. The scope of services was conducted in general accordance with the approved TA. 4.0 SITE HISTORY AND CHARACTERIZATION The Former Union 76 Gasoline Station site is located at 2236 Old US 1 Highway, Apex, Wake County, North Carolina (Figures 1, 2, and 3). Summarized available historical sampling and gauging data from previous consultants are provided in Appendix A. Site photographs are presented in Appendix B. 4.1 UST OWNER AND OPERATOR INFORMATION According to previous reports, the USTs were owned and operated by C. Tunstall (now deceased). C. Tunstall, and subsequently his son Ed Tunstall, operated the site beginning in the early 1940s until 1993. However, the UST NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 4 July 2023 system was not in operation after 1982. In 1993, the property was sold to David Powell who currently owns the site. Available information regarding UST owners/operators is presented on Table 1. 4.2 UST INFORMATION The former UST system reportedly consisted of dispensing pumps, one 550- gallon gasoline UST, and one 1,000-gallon gasoline UST. The USTs and pumps were removed from the site on March 17, 2004. The 1,000-gallon UST was in fair condition, showing minor signs of corrosion. However, the 550-gallon tank was reported to be in poor condition and was structurally weak and corroded. Available UST system information is presented in Table 1 and the approximate former UST system locations are illustrated on Figure 3. 4.3 CONTAMINANT SOURCE INVENTORY On March 17, 2004, six soil samples were collected from beneath the former tanks and pump island during UST removal activities. The laboratory analytical results indicated that concentrations of total petroleum hydrocarbons (TPH) gasoline range organics (GRO) were detected above State Action Levels (S&ME, 2020). The volume of product released from the associated USTs is unknown. 4.4 SITE CHARACTERISTICS The site is currently owned by Mr. David Powell. The site consists of two buildings: the former Union 76 building (currently being used as Evolution Empowerment Ministry) and an occupied residential home to the northeast of the building. The site has gravel driveways and parking along Old US 1 Highway, grassy space behind the buildings, and the northern and eastern borders of the property are heavily vegetated. There is a pond located on the property northeast of the release. The locations of the pump island and former UST basin are illustrated on Figure 3. 4.5 OWNERS AND OCCUPANTS OF ADJOINING/NEARBY PROPERTIES AND LAND USE The adjoining properties to the site are a combination of private residences, agricultural fields, commercial business, and undeveloped land. Residences are located to the northwest and east. The McNeil’s Grocery site (UST NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 5 July 2023 Incident No. 6891) is located to the south across Old US 1 Highway and currently houses two businesses. 4.6 RECEPTOR INFORMATION Conducting a receptor survey was outside the scope of this monitoring event. A review of historical files available on the NCDEQ Waste Management Online Database (aka Laserfiche) indicates that the last receptor survey update for the Former Union 76 Gasoline Station site was conducted in 2020 by S&ME, Inc. (S&ME). S&ME identified six potable and three inactive water supply wells within 500 feet of the site. Five additional potable water supply wells were identified between 500 and 1,000 feet of the site. S&ME indicated municipal water is available to the properties within 500 feet of the source; however, municipal water is not available between 500 and 1,000 feet from the site. Two ponds are located within 1,000 feet of the site. The closest pond is located on-site approximately 150 northeast of the former USTs. Potential receptors are illustrated on Figure 2 and receptor information obtained from S&ME (2020) is shown on Table 2. 4.7 PREVIOUS INVESTIGATIONS AND REMEDIAL ACTIVITIES Two USTs were removed from the site on March 17, 2004. During the removal, 5.7 cubic yards of contaminated soil was removed from the excavation and six soil samples were collected from beneath the former UST locations and pump island. Analytical results of the soil samples revealed concentrations of TPH GRO above the State Action Levels. In July 2004, Withers and Ravenel (W&R) installed one monitoring well (MW-1) and collected nine additional soil samples in the vicinity of the former tank basin. Soil analytical results revealed petroleum constituents above soil-to-groundwater (STGW) maximum soil contaminant concentrations (MSCCs) and/or the Residential MSCCs in all soil samples collected. The groundwater sample collected from MW-1 contained several contaminant concentrations above the 2L GWQS. 1,2-Dibromoethane and 1,2-DCA concentrations were above their respective GCLs. W&R also collected samples from the two on-site water supply wells identified during their investigation. Laboratory analytical results from the water supply well that supplies potable water to the building revealed benzene and ethylene dichloride concentrations above the 2L GWQS. W&R summarized their findings in a Limited Site Assessment Report, dated August 18, 2004. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 6 July 2023 Monitoring wells MW-2, MW-3, MW-4, and DW-1 were installed between 2004 and 2005. In 2013, MW-1, MW-2, MW-3, DW-1, and on-site water supply well WSW-9 were sampled. All four monitoring wells were found to have 2L GWQS exceedances and WSW-9 was found to have no detectable compounds. On April 25, 2019, it was discovered that MW-3 and MW-4 were damaged, likely due to road widening activities. On June 5, 2020, S&ME abandoned MW-3 and MW-4 and installed replacement wells MW-3R and MW-4R. Periodic groundwater monitoring events were conducted at the site between 2004 and 2020. Analytical results of the groundwater samples indicated the persistence of several petroleum constituents above the 2L GWQS. Light non-aqueous phase liquids (LNAPL; aka free-phase product) were measured in monitoring well MW-4 in June 2010 (approximately 0.5 inches thick); however, it has not been measured since that time. CATLIN conducted a groundwater monitoring event in February 2021. Multiple petroleum constituents were detected in the samples collected from MW-1, MW-2, MW-3R, MW-4R, and DW-1 at concentrations above 2L GWQS; however, none were above their respective GCL (CATLIN, 2021). In May 2022, CATLIN installed three Type II monitoring wells (MW-5, MW-6, and MW-7) to 20 feet below land surface (BLS). One soil sample was collected from each boring and analyzed for VOCs and semi-VOCs per Environmental Protection Agency (EPA) Methods 8260D & 8270E, and volatile petroleum hydrocarbons (VPH) and extractable petroleum hydrocarbons (EPH) per Massachusetts Department of Environmental Protection (MADEP) methods. No EPA 8260D or EPA 8270E analytes were above the laboratory method detection limits. Estimated concentrations (“J”- value) of VPH C9-C10 aromatics were detected in the samples from MW-5 and MW-6 (obtained from approximately 10 to 12 feet BLS), but they were well below the lowest MSCC (CATLIN, 2022). CATLIN returned in June and July 2022 to sample all eight accessible monitoring wells as well as water supply wells WSW-1, WSW-4, and WSW-10. Multiple petroleum constituents persisted at concentrations above 2L GWQS in the samples from MW-1, MW-2, MW-3R, MW-4R, and DW-1. In addition, EDB was reported above its GCL in the MW-3R sample. No targeted analytes were detected in the WSW-4 sample. A low concentration of MTBE was reported in the WSW-10 sample but was below the 2L GWQS. In the WSW-1 sample, 1,2-DCA was above its 2L GWQS (but below GCL) and an estimated concentration (“J”-value) of benzene was detected but was below 2L GWQS (CATLIN, 2022). Slug tests were performed on monitoring wells MW-1 and MW-4R during the June 2022 event. The analyses resulted in hydraulic conductivities of NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 7 July 2023 0.00005366 centimeter per second (cm/sec) and 0.00008826 cm/sec at MW-1 and MW-4R, respectively, and an average groundwater velocity of 14.4 feet per year across the site. Groundwater modeling determined that non-compliant benzene concentrations would migrate approximately 240 feet downgradient, potentially impacting the on-site water supply well (WSW-1) located 200 feet northeast from the source area (CATLIN, 2022). CATLIN coordinated an enhanced AFVR event in February 2023. The event lasted for a duration of eight hours utilizing monitoring wells MW-1, MW-2, MW-3R, and MW-4R as extraction points, and air sparging was performed through monitoring well DW-1. A total of 525 gallons of impacted groundwater were recovered and a calculated 7.29 pounds of petroleum vapors (equivalent to 1.17 gallons of petroleum) were emitted (CATLIN, 2023). In March 2023, CATLIN sampled eight monitoring wells (MW-1, MW-2, MW-3R, MW-4R, MW-5, MW-6, MW-7, and DW-1) and three water supply wells (WSW-1, WSW-4, and WSW-10). One or more VOCs were reported above their 2L GWQS in the MW-1, MW-2, MW-3R, MW-4R, and DW-1 samples; however, all were below GCL. The petroleum constituent concentrations had generally decreased in monitoring well samples since the June 2022 sampling event. No targeted analytes were above the method detection limit in the WSW-4 sample. A low concentration (below 2L GWQS) of MTBE was detected in the WSW-10 sample. 1,2-DCA was above its 2L GWQS in the WSW-1 sample, although the concentration had decreased since June 2022 (CATLIN, 2023). A summary of historical data from reports prepared by other consultants is included in Appendix A. 5.0 REGIONAL AND SITE GEOLOGY AND HYDROGEOLOGY 5.1 SOIL AND BEDROCK As defined in the Geologic Map of North Carolina, published by the North Carolina Department of Natural Resources and Community Development (1985), the site lies within the Piedmont physiographic province. The site is underlain by the Triassic Basins, and consists of conglomerate, fanglomerate, sandstone, and mudstone (Rhodes et al., 1985). Based on the well construction records from CATLIN (2022), the site is immediately underlain (up to approximately 5 feet BLS) by light to dark brown clay (with traces of sand). From a depth of 5 to 20 feet BLS (boring termination), light brown to dark brown silty clay with some clayey silt lenses were encountered. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 8 July 2023 5.2 HYDROGEOLOGY Groundwater - The 2020 Visual Hydrogeologic Framework (VHF) – North Carolina Hydrogeological Database did not identify sufficient boreholes near the site to draw a cross-section. CATLIN performed slug tests on monitoring wells MW-1 and MW-4R in June 2022. The analyses resulted in hydraulic conductivities of 0.00005366 cm/sec and 0.00008826 cm/sec at MW-1 and MW-4R, respectively, and an average groundwater velocity of 14.4 feet per year across the site (CATLIN, 2022). Surface Water – Two ponds are located within 1,000 feet of the site. The closest pond is located on-site approximately 150 northeast of the former USTs. 6.0 SITE ASSESSMENT INFORMATION CATLIN conducted field activities in general accordance with the approved TA and pre-prepared Health and Safety Plan (HASP). Upon arrival at the site, potential hazards were evaluated before beginning field work and are documented on electronic Job Hazard Analysis (JHA) forms. The JHA forms are included in Appendix C. Photographs from the site visits are included in Appendix B. 6.1 ENHANCED AFVR EVENT On April 11, 2023, CATLIN mobilized to the site to supervise an enhanced AFVR event conducted by EEM. The event was conducted for a duration of eight hours utilizing monitoring wells MW-1, MW-2, and MW-3R as extraction points, and air sparging was performed through DW-1. Prior to the event, CATLIN personnel gauged the shallow wells MW-1, MW-2, and MW-3R at an average of approximately 16.5 feet BTOC. LNAPL was not measured in any of the monitoring wells. The April 2023 enhanced AFVR event resulted in the removal of 517 gallons of impacted groundwater from the subsurface. A calculated 1.34 pounds of petroleum vapors were recovered (and released), equivalent to approximately 0.21 gallons of petroleum. Gauging results are included in Table 3. The AFVR field data sheets and emissions calculations are provided in Appendix D. The waste manifest is provided in Appendix E. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 9 July 2023 6.2 GAUGING DATA Historically, depth to water has ranged from 9.43 feet BTOC (MW-4) to 19.02 feet BTOC (MW-2). LNAPL was measured in monitoring well MW-4 (0.5 inches thick) in 2010 but has not been measured since. Groundwater flow direction has been previously illustrated towards the north and east (S&ME, 2020; CATLIN, 2023). During the May 2023 event, CATLIN personnel measured depth to water in eight monitoring wells using an electronic water interface probe. To prevent cross contamination, the probe and cabling were decontaminated according to manufacturer’s instructions and rinsed with distilled water between use in each well. Gauging data were recorded on an electronic groundwater sampling form using a tablet device. Gauging procedures were performed in general accordance with NCDEQ Guidelines and EPA Region 4 Operating Procedures. Depth to water in the shallow (Type II) wells ranged from 12.29 feet BTOC (MW-6) to 15.44 feet BTOC (MW-2). Depth to water in the deep (Type III) well (DW-1) was 15.59 feet BTOC. Groundwater flow direction at the site was calculated to have both east and north-northeast components. Gauging results for events conducted by CATLIN are presented in Table 3 and the groundwater sampling forms are provided in Appendix C. Groundwater elevations and groundwater contours are shown on Figure 4. 6.3 SAMPLING DATA Following gauging, the monitoring wells were sampled in general accordance with NCDEQ Guidelines and U.S. EPA Region 4 Operating Procedures. Prior to obtaining representative groundwater samples, each well was purged by removing a minimum of three well volumes using a new, disposable bailer. Groundwater field parameter data were measured at one-minute intervals using an In-Situ Aqua TROLL 600 Multiparameter Sonde (Aqua TROLL). The Aqua TROLL measured specific conductivity, pH, oxidation-reduction potential (ORP), dissolved oxygen, and temperature, which were recorded utilizing the VuSitu mobile application (version 1.17.12). Groundwater parameter data were transferred from the VuSitu mobile application to the electronic groundwater sampling forms. Copies of the groundwater sampling forms are available in Appendix C. After the well was purged a minimum of three well volumes (or the well was purged dry), a groundwater sample was collected from each well from the disposable bailer and poured directly into appropriate, pre-preserved, laboratory provided glassware, labeled, and placed on ice in an insulated cooler. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 10 July 2023 To verify that sampling equipment was decontaminated sufficiently between wells, an equipment rinsate blank sample was collected from the electronic probe. Clean distilled water was allowed to cascade down the electronic probe and into appropriate laboratory-provided, pre-preserved glassware. The glassware was labeled and placed on ice in an insulated cooler. A laboratory-provided trip blank was maintained in the cooler for the duration of the event. The groundwater samples, equipment rinsate blank, and laboratory-provided trip blank were submitted to Con-Test Analytical Laboratory (Certification NC 652 and NC-DW 25703) in East Longmeadow, Massachusetts, under proper chain of custody (COC) protocol for analysis per SM 6200B (including EDB, MTBE, and DIPE). The laboratory analytical data and COC are included in Appendix F. 6.4 SUMMARY OF GROUNDWATER INFORMATION Historically, all monitoring wells on-site have been impacted by petroleum contaminants. LNAPL was previously measured in monitoring well MW-4 in June 2010; however, it has not been measured since that time. During past events, GCL exceedances of benzene, 1,2-DCA, and/or 1,2-dibromoethane have been detected in MW-1, MW-2, MW-3, and MW-4. Historical information from previous consultants is included in Appendix A. The latest groundwater sampling laboratory results for SM 6200B analysis are summarized in Table 4. Historical results for events conducted by CATLIN are in Table 5. Monitoring well sample analytical results are summarized on Figure 5. A copy of the complete laboratory report and COC documentation are in Appendix F. Monitoring Wells During the May 2023 monitoring event, eight monitoring well groundwater samples (MW-1, MW-2, MW-3R, MW-4R, MW-5, MW-6, MW-7, and DW-1) were collected and submitted for analysis via SM 6200B (including EDB, MTBE, and DIPE). Laboratory analysis did not detect any constituents above their respective laboratory reporting limits in the samples from MW-5, MW-6, and MW-7. No analyte concentrations were detected above GCL. Analytical results indicated the following constituents at concentrations above their 2L GWQS in samples MW-1, MW-2, MW-3R, MW-4R, and DW-1: • MW-1: benzene, naphthalene, toluene, and total xylenes; • MW-2: 1,2-DCA; • MW-3R: benzene, EDB, 1,2-dichloroethane, and naphthalene; NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 11 July 2023 • MW-4R: benzene, ethylbenzene, isopropylbenzene, naphthalene, n-propylbenzene, toluene, 1,2,4-trimethylbenzene, 1,3,5- trimethylbenzene, and total xylenes; and • DW-1: 1,2-DCA. Equipment Rinsate Blank and Trip Blank One equipment rinsate blank and one laboratory-provided trip blank were submitted for analysis per SM 6200B (including EDB, MTBE, and DIPE). Estimated concentrations (“J”-value) of acetone (a common laboratory artifact) were detected in the trip blank and equipment rinsate blank; however, they were well below 2L GWQS. No other targeted analytes were detected. 6.5 EVALUATION OF ASSESSMENT INFORMATION Extent of contamination Groundwater samples from all monitoring wells MW-1, MW-2, MW-3R, MW-4R, and DW-1 contained concentrations of several constituents above their respective 2L GWQS; however, none were above GCL. The overall estimated extent of groundwater contamination is shown on Figure 5. The groundwater plume is not delineated to the north or south, nor is it vertically delineated below 40 feet. The highest dissolved phase concentration benzene, toluene, ethylbenzene, and total xylenes (BTEX) compounds has historically been reported in samples from MW-3R. The BTEX concentrations in samples obtained from MW-2, MW-3R, and DW-1 have generally decreased since the March 2023 monitoring event. However, the concentrations in samples from MW-1 and MW-4R have increased. Cleanup levels achieved Soil – According to a 2004 LSA report prepared by W&R, contaminated soils are present in the vicinity of the former UST basin. Contaminant concentrations were detected above STGW and/or Residential MSCCs from approximately 3 to 20 feet below land surface (W&R, 2004). However, no contamination was present in the soil samples obtained in 2022 (CATLIN, 2022). Groundwater – Groundwater contaminant concentrations are above 2L GWQS in multiple monitoring well samples. As of March 2023, 1,2-DCA was above its 2L GWQS in water supply well WSW-1. LNAPL – LNAPL was not measured during this monitoring event. LNAPL has not been observed at this site since 2010. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 12 July 2023 7.0 CONCLUSIONS AND RECOMMENDATIONS Conclusions Groundwater findings from the remediation and monitoring activities are summarized below: • An enhanced AFVR event was conducted utilizing MW-1, MW-2, and MW-3R as extraction points and air sparging through DW-1. Approximately 517 gallons of impacted groundwater were removed. A calculated 1.34 pounds of petroleum vapors were collected (and released), equivalent to 0.21 gallons of petroleum. • The groundwater gauging data indicates an apparent groundwater flow components towards both the east and north-northeast. • Monitoring well laboratory results revealed multiple petroleum constituents above their respective 2L GWQS in the samples collected from MW-1, MW-2, MW-3R, MW-4R, and DW-1. • The BTEX concentrations in MW-2, MW-3R, and DW-1 have generally decreased since the previous monitoring event in March 2023. However, the concentrations in MW-1 and MW-4R have increased. • The groundwater plume is currently not horizontally delineated in any direction, nor is it vertically delineated below 40 feet. As detailed in the previous monitoring report, the subject site and surrounding properties are likely to be sold and developed. During development activities, water supply wells WSW-1, WSW-2, WSW-4, WSW-10 WSW-12 and WSW-13 would be abandoned. In addition, there is the potential for redevelopment (by a different firm) across Old US 1 Highway, which would result in the abandonment of the majority of water supply wells within 1,000 feet of the subject site. The proposed redevelopment in the area may allow for a risk reduction for the subject site and another site located across Old US 1 Highway (McNeil’s Grocery Site - Incident Number 6891) from high risk to low risk classification. Recommendations Based on the current laboratory data and the potential sale and redevelopment of the property, CATLIN recommends the following: • Collect one additional sample from MW-3R and abandon all on-site monitoring wells immediately before the start of site development. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 13 July 2023 8.0 LIMITATIONS The groundwater samples analyzed as part of this investigation only provide isolated data points and may not represent conditions at every location in the project area. Analyses and conclusions of this report, being based on interpolation between data points at the project area, may not be completely representative of all site conditions. Conclusions and recommendations of this investigation and report are based on the best available data in an effort to comply with current regulatory requirements. 9.0 STATEMENTS AND CERTIFICATIONS 1 Enter the date the monitoring report was due. July 14, 2023 Will this report be submitted after the established due date? NO 2 Was any required information from the above template missing from this report? YES No cross sections are provided. Adequate subsurface information is not available. 3 If applicable, will any of the proposed attenuation milestones under the schedule approved in the Corrective Action Plan not be met? NA No CAP has been submitted for this site. 4 Does any known or suspected source zone soil contamination or free product remain outside of the assessed area that could be inhibiting natural attenuation? NO 5 Has there been an unexpected increase in contaminant mass sufficient to suggest a potential new release from a separate onsite or offsite source? NO 6 Certification: I, Sean J. O’Neil, a Licensed Engineer for CATLIN Engineers and Scientists, do certify that the information contained in this report is correct and accurate to the best of my knowledge. CATLIN Engineers and Scientists is licensed to practice engineering in North Carolina. The certification number of the company or corporation is C-0585. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 14 July 2023 10.0 REFERENCES CATLIN Engineers & Scientists, Monitoring Report, Former Union 76 Gasoline Station, 2236 Old US 1 Highway, Apex, Wake County, North Carolina, NCDEQ Incident No. 26571, Risk Classification: H0875D, March 5, 2021. CATLIN Engineers & Scientists, Monitoring Report, Former Union 76 Gasoline Station, 2236 Old US 1 Highway, Apex, Wake County, North Carolina, NCDEQ Incident No. 26571, Risk Classification: H0875D, August 19, 2022. CATLIN Engineers & Scientists, Monitoring Report, Former Union 76 Gasoline Station, 2236 Old US 1 Highway, Apex, Wake County, North Carolina, NCDEQ Incident No. 26571, Risk Classification: H0875D, March 27, 2023. Crawford Environmental Services, Monitoring Letter/Report, Union 76 Gas Station, Incident No. 26571, Apex, Wake County, North Carolina, Contract Number: 4351-4F, August 23, 2013. NCDEQ, UST Section, North Carolina Department of Environment Quality, Division of Waste Management, Guidelines for Site Checks, Tank Closure, and Initial Response and Abatement for Petroleum and Hazardous Substance UST Releases, Petroleum Non-UST Releases, January 19, 2021. NCDEQ, UST Section, North Carolina Department of Environmental Quality, Division of Waste Management, Guidelines for Sampling, UST Section, North Carolina Department of Environment and Natural Resources, December 1, 2013. NCDEQ, UST Section, North Carolina Department of Environmental Quality, Division of Waste Management, UST Section Assessment Guidelines, Petroleum and Hazardous Substance UST Releases, Petroleum Non-UST Releases, January 19, 2021 NCDEQ, UST Section, North Carolina Department of Environmental Quality, Division of Waste Management, UST Section Corrective Action Guidelines, Petroleum and Hazardous Substance UST Releases, Petroleum Non-UST Releases, January 19, 2021. Rhodes, Thomas S., and Conrad, Stephen G., 1985, Geologic Map of North Carolina: Department of Natural Resources and Community Development, Division of Land Resources, and the NC Geological Survey, compiled by Brown, Philip M., et al, and Parker, John M. III, and in association with the State Geologic Map Advisory Committee, scale 1:500,000. S&ME, Inc., Groundwater Monitoring Report, Former Union 76, Incident No. 26571, Apex, Wake County, North Carolina, S&ME Project #4305-19-052, June 25, 2019. S&ME, Inc., Monitor Well Installation and Groundwater Monitoring Report, Former Union 76, TF-26571, RA-5020, 2236 Old US Highway 1, Apex, Wake County, NC, S&ME Project No. 4305-19-052A, July 1, 2020. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 15 July 2023 U.S. EPA, Region 4, U.S. Environmental Protection Agency, Science and Ecosystem Support Division, Athens Georgia, Operating Procedure – Field Equipment Cleaning and Decontamination at the FEC, Striggow, B., U.S. EPA Report No. SESDPROC-206-R3, Effective Date December 18, 2015. U.S. EPA, Region 4, U.S. Environmental Protection Agency, Science and Ecosystem Support Division, Athens Georgia, Operating Procedure – Groundwater Level and Well Depth Measurement, Striggow, B., U.S. EPA Report No. SESDPROC-105-R3, Effective Date November 3, 2016. U.S. EPA, Region 4, U.S. Environmental Protection Agency, Science and Ecosystem Support Division, Athens Georgia, Operating Procedure – Groundwater Sampling, Striggow, B., U.S. EPA Report No. SESDPROC-301-R4, Effective Date April 26, 2017. U.S. EPA, Region 4, U.S. Environmental Protection Agency, Science and Ecosystem Support Division, Athens Georgia, Operating Procedure – In Situ Water Quality Monitoring, Chief, Field Services Branch, U.S. EPA Report No. SESDPROC-111-R4, Effective Date March 14, 2018. Withers & Ravenel, Underground Storage Tank Closure Report, Union 76 Gasoline Station, Incident No. 26571, Apex, Wake County, North Carolina, W&R Job NO. 204086.0, April 12, 2004. Withers & Ravenel, Phase 1 Limited Site Assessment, Former Union 76 Gasoline Station, Incident No. 26571, Apex, Wake County, North Carolina, W&R Job NO. 204086.0, August 18, 2004. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 TABLES Page 1 of 1 TABLE 1 SITE HISTORY — UST SYSTEM AND OTHER RELEASE INFORMATION Incident Name and No.: Former Union 76 Gas Station - 26571 UST ID Number Name of Owner/ Operator Last Contents Previous Contents Capacity (gal) Construction Details Tank Dimensions (feet) Installation Date Date Removed (mm/dd/yy) T1 Gasoline Unknown 550 Unknown 3.5 x 7.5 Unknown 03/17/04 T2 Gasoline Unknown 1,000 Unknown 4.2 x 10 Unknown 03/17/04 Incident Number Material Released Date Release Discovered (mm/dd/yy) 26571 Gasoline 03/17/04 Information obtained from W&R (2004). gal = gallons Description of the Release TPH discovered in soils during UST excavation on March 17, 2004. C.C. Tunstall (Decased), Ed & Ruth Tunstall Dates of Ownership/ Operation Early 1940s to 1982 NCDEQ; 26571_Former Union 76 Gas Station; T1_Site History CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 Page 1 of 2 TABLE 2 PUBLIC AND PRIVATE WATER SUPPLY WELLS WITH OTHER RECEPTOR INFORMATION Incident Name and No.: Former Union 76 Gas Station - 26571 Well ID Property Address Parcel Identification Number (PID) Owner Name Owner Mailing Address Well Use Distance / Direction from Source Area (feet) Comment WSW-1 Active 200 / NW WSW-2 Inactive 150 / N Hand-dug well formerly labeled as WSW-HD. WSW-3 2237 Old US Highway 1, Apex, NC 0720999210 Miller Land Group LLC (Vicious Fishes Brewery) 1922 Napoli Drive, Apex, NC Inactive 250 / SE Well is inactive - site is connected with municipal water - located at McNeil's Grocery Site - TF-6891 WSW-4 7528 Humie Olive Road, Apex, NC 720992587 Shelba Clem & Diane Williams 3007 Buckingham Way, Apex, NC Active 400 / NW WSW-5 500 / SE WSW-6 520 / SE WSW-7 3113 Holland Road, Apex, NC 0730097826 Walter McClamb PO Box 243, Apex, NC Active 950 / NE WSW-8 7629 Vaudry Court, Apex, NC 0720988751 Active 500 / SW WSW-9 2309 Old US Highway 1, Apex, NC 0720985958 Active 400 / SW WSW-10 1001 Red Cardinal Lane, Apex, NC 0730091779 Johnny & Carolyn Pendergraft 2212 Old US 1 Highway South, Apex, NC Active 480 / NE Downtown Friendship LLC 2301 Old US 1 Highway, Apex, NC Unknown During a telephone conversation, owner was unable to successfully describe which well was the active one. To be conservative, WSW-5 was designated as active. 0730093122 2217 Old US 1 Highway, Apex, NC David Ray Powell 861 Bethlemhem Church Road, Youngsville, NC 2236 Old US Highway 1, Apex, NC 0720998487 Joyce Kelly 2217 Old US 1 Highway, Apex, NC NCDEQ; 26571_Former Union 76 Gas Station; T2_Receptor & WSW Info CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 Page 2 of 2 TABLE 2 PUBLIC AND PRIVATE WATER SUPPLY WELLS WITH OTHER RECEPTOR INFORMATION Incident Name and No.: Former Union 76 Gas Station - 26571 Well ID Property Address Parcel Identification Number (PID) Owner Name Owner Mailing Address Well Use Distance / Direction from Source Area (feet) Comment WSW-12 1005 Red Cardnial Lane, Apex, NC 0731001087 Joanne Pendergraft Hearn Heirs, Bonnie Wood 1115 Dycus Road, Sanford, NC Active 900 / NE WSW-13 3116 Holland Road, Apex, NC 0730095707 Frances Bullock ETAL & Pamela Purefoy 3116 Holland Road, Apex, NC Active 1,100 / NE WSW-15 3000 Friendship Road, Apex, NC 0730096271 Downtown Friendship LLC 2301 Old US 1 Highway, Apex, NC Inactive 900 / E WSW-17 2124 Old US 1 Highway, Apex, NC 0730098773 Walter McClamb PO Box 243, Apex, NC Active 950 / NE Receptor ID Location Contact Distance/ Direction from Source Area (feet) Pond 1 2236 Old US Highway 1, Apex, NC 919-387-0848 180 / NE Pond 2 2217 Old US Highway 1, Apex, NC 919-387-0848 415 / SE Information obtained from S&ME, Inc. (2020) and Wake County iMaps (accessed March 20, 2023). Description Surface water feature located on adjacent parcel to the southeast. Surface water feature located on Former Union 76 parcel to the north. NCDEQ; 26571_Former Union 76 Gas Station; T2_Receptor & WSW Info CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 Page 1 of 3 TABLE 3 Incident Name and No.: Former Union 76 Gas Station - 26571 Well ID Date Installed (mm/dd/yy)* Date Water Level Measured (mm/dd/yy) Well Diameter (inches) Well Casing Depth (ft. BLS)* Screened Interval (x to y ft. BLS)* Bottom of Well (ft. BLS)* Top of Casing Elevation* (ft.) Free-Phase Product Thickness (ft.) Depth to Water from Top of Casing (ft.) Ground Water Elevation (ft.) Comments 02/16/20 NMT 9.60 90.34 06/16/22 NMT 15.24 84.70 02/09/23 NMT 18.42 81.52 Pre-AFVR 02/09/23 NMT 19.45 80.49 Post-AFVR 03/07/23 NMT 17.15 82.79 04/11/23 NMT 16.28 83.66 Pre-AFVR 04/11/23 NMT 19.80 80.14 Post-AFVR 05/10/23 NMT 14.97 84.97 02/16/20 NMT 10.36 89.64 06/16/22 NMT 15.99 84.01 02/09/23 NMT 19.02 80.98 Pre-AFVR 02/09/23 NMT 19.60 80.40 Post-AFVR 03/07/23 NMT 17.69 82.31 04/11/23 NMT 16.86 83.14 Pre-AFVR 04/11/23 NMT 14.25 85.75 Post-AFVR 05/10/23 NMT 15.44 84.56 02/16/20 NMT 10.21 89.63 06/16/22 NMT 15.65 84.19 02/09/23 NMT 18.57 81.27 Pre-AFVR 02/09/23 Post-AFVR 03/07/23 NMT 17.29 82.55 04/11/23 NMT 16.47 83.37 Pre-AFVR 04/11/23 NMT 19.80 80.04 Post-AFVR 05/10/23 NMT 15.04 84.80 2010-20 2.0 5 5-20 20 100.00 Dry MW-2 99.94205-205 99.84 WELL CONSTRUCTION AND HISTORICAL WATER LEVEL GAUGING DATA 07/21/04MW-1 102.0 2.0 MW-3R 06/05/20 05/24/05 NCDEQ; 26571_Former Union 76 Gas Station; T3_Well Construction & Gauging CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 Page 2 of 3 TABLE 3 Incident Name and No.: Former Union 76 Gas Station - 26571 Well ID Date Installed (mm/dd/yy)* Date Water Level Measured (mm/dd/yy) Well Diameter (inches) Well Casing Depth (ft. BLS)* Screened Interval (x to y ft. BLS)* Bottom of Well (ft. BLS)* Top of Casing Elevation* (ft.) Free-Phase Product Thickness (ft.) Depth to Water from Top of Casing (ft.) Ground Water Elevation (ft.) Comments WELL CONSTRUCTION AND HISTORICAL WATER LEVEL GAUGING DATA 02/16/20 NMT 10.44 89.00 06/16/22 NMT 14.62 84.82 02/09/23 NMT 18.00 81.44 Pre-AFVR 02/09/23 NMT 19.95 79.49 Post-AFVR 03/07/23 NMT 16.85 82.59 05/10/23 NMT 14.67 84.77 06/16/22 NMT 14.24 83.99 05/10/23 NMT 15.28 82.95 NMT 13.31 84.92 06/16/22 97.72 NMT 12.47 85.25 03/07/23 NMT 13.84 NM Casing moved 05/10/23 NMT 12.29 NM 06/16/22 NMT 16.31 83.83 03/07/23 NMT 17.92 82.22 05/10/23 NMT 15.43 84.71 NM 98.23 99.44 100.1405/17/22 05/17/22 05/17/22 06/05/20 20 20 20 2010-20 10-20 10-20 10-20MW-4R MW-7 MW-6 MW-5 10 10 2.0 2.0 2.0 2.0 10 10 NCDEQ; 26571_Former Union 76 Gas Station; T3_Well Construction & Gauging CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 Page 3 of 3 TABLE 3 Incident Name and No.: Former Union 76 Gas Station - 26571 Well ID Date Installed (mm/dd/yy)* Date Water Level Measured (mm/dd/yy) Well Diameter (inches) Well Casing Depth (ft. BLS)* Screened Interval (x to y ft. BLS)* Bottom of Well (ft. BLS)* Top of Casing Elevation* (ft.) Free-Phase Product Thickness (ft.) Depth to Water from Top of Casing (ft.) Ground Water Elevation (ft.) Comments WELL CONSTRUCTION AND HISTORICAL WATER LEVEL GAUGING DATA 02/16/20 NMT 10.47 89.73 Type III; Ɨ 06/16/22 NMT 16.30 83.90 Type III; Ɨ 02/09/23 NMT 19.23 80.97 Type III; Pre-AFVR; Ɨ 02/09/23 NMT 22.67 77.53 Type III; Post-AFVR; Ɨ 03/07/23 NMT 17.93 82.27 Type III; Ɨ 04/11/23 NMT 17.05 83.15 Type III; Pre-AFVR; Ɨ 04/11/23 NMT 30.70 69.50 Type III; Post-AFVR; Ɨ 05/10/23 NMT 15.59 84.61 Type III; Ɨ Ɨ = Depth to water was measured above the screened interval. NM = Not Measured NMT = No Measureable Thickness AFVR = Aggressive Fluid Vapor Recovery * = Construction data for wells installed prior to 2022 were obtained from S&ME (2020). 35 ft. BLS = feet Below Land Surface 100.2035-40 40DW-1 05/26/05 2.0/6.0 NCDEQ; 26571_Former Union 76 Gas Station; T3_Well Construction & Gauging CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 Page 1 of 1 TABLE 4 SUMMARY OF GROUNDWATER LABORATORY RESULTS — STANDARD METHOD 6200B Incident Name and No.: Former Union 76 Gas Station - 26571 Date Collected (mm/dd/yy) 05/10/23 59 J 1,400 51 J 3.0 J <2.5 <3.2 ƚ <6.1 ƚ 8.0 J 150 <24 8.6 J 3.6 J <26 28 9.4 J 1,400 130 57 1,130 BMDL 05/10/23 2.6 J <0.18 <1.7 <0.15 <0.13 <0.16 ƚ 2.1 <0.20 <0.22 <1.2 <0.15 <0.13 <1.3 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73 BMDL 05/10/23 <8.0 290 <6.7 1.7 J 0.92 J 8.5 45 1.6 J 23 17 J 2.3 1.5 J 10 J 23 2.1 49 130 81 480 BMDL 05/10/23 230 J 840 290 J 47 J <13 <16 ƚ <30 ƚ <20 1,800 <120 ƚ 99 <13 <130 ƚ 430 230 9,900 2,000 620 11,900 BMDL 05/10/23 2.7 J <0.18 <1.7 <0.15 <0.13 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <1.3 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73 BMDL 05/10/23 <2.0 <0.18 <1.7 <0.15 <0.13 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <1.3 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73 BMDL 05/10/23 2.9 J <0.18 <1.7 <0.15 <0.13 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <1.3 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73 BMDL 05/10/23 3.4 J <0.18 <1.7 <0.15 <0.13 <0.16 ƚ 0.82 <0.20 <0.22 <1.2 <0.15 0.34 J <1.3 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73 BMDL 05/10/23 9.6 J <0.18 <1.7 <0.15 <0.13 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <1.3 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73 BMDL 05/10/23 2.9 J <0.18 <1.7 <0.15 <0.13 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <1.3 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73 BMDL All results in micrograms per liter (µg/L). BMDL = Below Method Detection Limit (refer to analytical report for a complete list of analytes and detection limits) Eq. = Equipment 2L GWQS = NCAC T15A:02L Groundwater Quality Standards Bold results indicate concentrations above 2L GWQS. GCL = Gross Contaminant Level < = Less than method detection limit ƚ = The method detection limit is above the 2L GWQS. J = Detected but below the Reporting Limit (lowest calibration standard); therefore, result is an estimated concentration (CLP J-Flag).1,2-Dibromoethane (EDB)Diisopropyl Ether (DIPE)1,2-Dichloroethane Eq. Rinse Contaminant of Concern Acetone5,900 70n-Butylbenzene5,000 1 400 0.4 70,000 70 Trip Blank GCL (µg/L) 2L GWQS (µg/L) 6,000,000 6,000 50 0.02 30,500 70 40,000 40 1,3,5-TrimethylbenzeneTotal XylenesToluene p-Isopropyltoluene (p-Cymene)100,000 100 11,700 25Isopropylbenzene (Cumene)Naphthalene n-Propylbenzene2-Hexanone (MBK)4-Methyl-2-pentanone (MIBK)All Other SM 6200B AnalytesVaries Varies 6,000 6 26,100 70 260,000 600 28,500 400 24,100 400 50,000 5001,2,4-Trimethylbenzene80,000 600 8,800 70sec-Butylbenzene MW-3R MW-2 MW-1 Well/ Sample ID DW-1 MW-7 MW-6 MW-5 MW-4R 2-Butanone (MEK)4,000,000 4,000 EthylbenzeneBenzene NCDEQ; 26571_Former Union 76 Gas Station; T4_GW Results (SM 6200B) CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 Page 1 of 1 TABLE 5 SUMMARY OF HISTORICAL GROUNDWATER LABORATORY RESULTS — STANDARD METHOD 6200B Incident Name and No.: Former Union 76 Gas Station - 26571 Well Type Well/ Sample ID Date Collected 02/16/21 BMDL 650 <38 4.2 J <2.0 <1.8 23 71 <3.0 270 <28 20 3.8 J <3.4 <32 74 26 3.8 J 2,100 390 190 2,600 BMDL 06/16/22 35 J 1,600 BMDL 5.7 1.8 J BMDL <1.7 ƚ <3.1 ƚ 6.7 200 <11 12 1.7 J 3.4 J <13 23 L 12 BMDL 1,700 200 100 1,640 BMDL 03/07/23 50 J 890 18 J 3.1 J <1.3 <1.4 <1.6 ƚ <3.0 ƚ 3.9 J 86 <12 4.5 J <1.3 <1.7 <13 21 5.5 <1.5 510 44 33 520 BMDL 05/10/23 59 J 1,400 51 J 3.0 J <2.5 <2.8 <3.2 ƚ <6.1 ƚ 8.0 J 150 <24 8.6 J 3.6 J <3.4 <26 28 9.4 J <3.0 1,400 130 57 1,130 BMDL 02/16/21 BMDL 560 <19 1.4 J <1.0 <0.90 <1.5 ƚ 100 4.2 J 60 <14 8.4 2.6 J 7.4 <16 37 5.4 <0.80 3.5 J 2.7 J 5.6 11.3 J BMDL 06/16/22 <20 1,400 BMDL 1.8 J 1.5 J BMDL 5.6 <3.1 ƚ 9.0 230 <11 15 3.3 J 15 <13 77 L 17 BMDL 21 2.8 J 5.0 85.8 J BMDL 03/07/23 8.6 J 1.0 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ 4.6 0.26 J 0.24 J <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 05/10/23 2.6 J <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ 2.1 <0.20 <0.22 <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 02/16/21 BMDL 280 14 J 9.5 5.6 1.4 J 19 74 2.2 J 110 21 J 17 5.4 2.3 J 10 J 22 30 1.0 J 470 330 130 800 BMDL 06/16/22 160 J 3,500 BMDL 13 J <5.5 BMDL 76 <15 ƚ <6.4 580 190 J 38 5.5 J <8.6 82 J 110 L 49 BMDL 6,600 520 190 4,100 BMDL 03/07/23 41 J 570 35 J 6.1 <1.3 <1.4 9.5 <3.0 ƚ <2.0 49 14 J 6.1 2.5 J <1.7 <13 19 5.7 <1.5 480 66 61 800 BMDL 05/10/23 <8.0 290 <6.7 1.7 J 0.92 J <0.57 8.5 45 1.6 J 23 17 J 2.3 1.5 J <0.68 10 J 23 2.1 <0.60 49 130 81 480 BMDL 02/16/21 BMDL 1,200 <190 41 J 22 J <9.0 41 J <32 ƚ <15 2,000 <140 120 12 J <17 <160 ƚ 690 320 <8.0 11,000 2,300 840 11,900 BMDL 06/16/22 <100 380 BMDL 70 22 J BMDL <8.5 ƚ <15 ƚ <6.4 1,900 <56 ƚ 120 15 J <8.6 <64 450 L 320 BMDL 7,200 2,400 810 11,900 BMDL 03/07/23 <200 510 <170 43 J <13 <14 <16 ƚ <30 ƚ <20 1,700 <120 ƚ 100 <13 <17 <130 ƚ 380 250 <15 6,100 620 <15 10,100 BMDL 05/10/23 230 J 840 290 J 47 J <13 <14 <16 ƚ <30 ƚ <20 1,800 <120 ƚ 99 <13 <17 <130 ƚ 430 230 <15 9,900 2,000 620 11,900 BMDL 06/16/22 <2.0 <0.20 BMDL <0.15 <0.11 BMDL <0.17 ƚ <0.31 <0.13 <0.21 <1.1 <0.11 <0.097 <0.17 <1.3 <0.24 <0.086 BMDL <0.22 <0.20 <0.11 <0.69 BMDL 03/07/23 <2.0 <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 05/10/23 2.7 J <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 06/16/22 <2.0 <0.20 BMDL <0.15 <0.11 BMDL <0.17 ƚ <0.31 <0.13 <0.21 <1.1 <0.11 <0.097 <0.17 <1.3 <0.24 <0.086 BMDL <0.22 <0.20 <0.11 <0.69 BMDL 03/07/23 <2.0 <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 05/10/23 <2.0 <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 06/16/22 <2.0 <0.20 BMDL <0.15 <0.11 BMDL <0.17 ƚ <0.31 <0.13 <0.21 <1.1 <0.11 <0.097 <0.17 <1.3 <0.24 <0.086 BMDL <0.22 <0.20 <0.11 <0.69 BMDL 03/07/23 <2.0 <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 05/10/23 2.9 J <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 02/16/21 BMDL 1.2 <1.9 <0.14 <0.10 <0.090 <0.15 ƚ 1.4 <0.15 <0.090 <1.4 <0.10 <0.090 <0.17 <1.6 0.25 J <0.080 <0.080 <0.11 0.12 J <0.10 1.06 J BMDL 06/16/22 <2.0 6.1 BMDL <0.15 <0.11 BMDL <0.17 ƚ 6.6 <0.13 <0.21 <1.1 0.99 <0.097 <0.17 <1.3 1.8 L <0.086 BMDL <0.22 0.8 <0.11 5.6 BMDL 03/07/23 <2.0 0.80 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ 1.5 <0.20 <0.22 <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.92 J*BMDL 05/10/23 3.4 J <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ 0.82 <0.20 <0.22 <1.2 <0.15 0.34 J <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 07/26/22 <2.0 0.35 J BMDL <0.15 <0.11 BMDL <0.17 ƚ 2.2 <0.13 <0.21 <1.1 <0.11 <0.097 <0.17 <1.3 <0.24 <0.086 BMDL <0.22 <0.20 <0.11 <0.69 BMDL 03/07/23 <2.0 <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ 0.82 <0.20 <0.22 <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 06/16/22 <2.0 <0.20 BMDL <0.15 <0.11 BMDL <0.17 ƚ <0.31 <0.13 <0.21 <1.1 <0.11 <0.097 <0.17 <1.3 <0.24 <0.086 BMDL <0.22 <0.20 <0.11 <0.69 BMDL 03/07/23 <2.0 <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 <0.17 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL 06/16/22 <2.0 <0.20 BMDL <0.15 <0.11 BMDL <0.17 ƚ <0.31 <0.13 <0.21 <1.1 <0.11 <0.097 0.66 <1.3 <0.24 <0.086 BMDL <0.22 <0.20 <0.11 <0.69 BMDL 03/07/23 <2.0 <0.18 <1.7 <0.15 <0.13 <0.14 <0.16 ƚ <0.30 <0.20 <0.22 <1.2 <0.15 <0.13 0.69 <1.3 <0.38 <0.12 <0.15 <0.22 <0.20 <0.15 <0.73 BMDL All results in micrograms per liter (µg/L).J = Detected but below the Reporting Limit (lowest calibration standard); therefore, result is an estimated concentration (CLP J-Flag). SM = Standard Method L = Laboratory fortified blank/laboratory control sample recovery and duplicate recovery are outside of control limits. Reported value for this compound is likely to be biased on the low side (L-04 Flag). 2L GWQS = NCAC T15A:02L Groundwater Quality Standards < = Less than method detection limit Bold results indicate concentrations above 2L GWQS.BMDL = Below Method Detection Limit (refer to analytical report for a complete list of analytes and detection limits) Shaded results indicate concentrations above GCL.* = The value represents the sum of the reported practical quantitation limit of one analyte and the detected concentration of the other analyte. GCL = Gross Contaminant Level ƚ = The method detection limit is above the 2L GWQS.2-Hexanone (MBK)Contaminant of Concern AcetoneBenzene 2-Butanone (MEK)n-Butylbenzenesec-Butylbenzene tert-Butylbenzene 1,2-Dibromoethane (EDB)1,2-Dichloroethane Diisopropyl Ether (DIPE)EthylbenzeneAll Other SM 6200B AnalytesIsopropylbenzene (Cumene)p-Isopropyltoluene (p-Cymene)Methyl tert-Butyl Ether (MTBE)4-Methyl-2-pentanone (MIBK)Naphthalene n-PropylbenzeneStyrene Toluene 1,2,4-Trimethylbenzene1,3,5-TrimethylbenzeneTotal Xylenes6,000,000 6,000MonitoringMW-1 MW-2 MW-3R MW-4R MW-5 MW-6 MW-7 DW-1 Water SupplyWSW-1 WSW-4 WSW-10 GCL (µg/L) 2L GWQS (µg/L) 11,700 25 5,000 1 4,000,000 4,000 5,900 70 8,800 70 14,750 70 50 0.02 400 0.4 70,000 70 80,000 600 40,000 40 30,500 70 28,500 400 24,100 400 50,000 500 Varies Varies 20,000 20 100,000 100 6,000 6 26,100 70 70,000 70 260,000 600 NCDEQ; 26571_Former Union 76 Gas Station; T5_Historical GW (SM 6200B) CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 FIGURES FIGUREPROJECTTITLE 1SITE VICINITY MAP SITE LOCATION OLD US 1 HW YHUMIE OLIVE RD US HW Y 1Copyright:© 2013 National Geographic Society, i-cubed 2,000 0 2,000 4,0001,000 Feet ³ UNION 76 GASOLINE STATION 2236 OLD US 1 HWYAPEX, NC INCIDENT NO.JOB NO.DATE SCALE DRAWN BY/CHECKED BY26571220217JULY 2023 AS SHOWN KMC/SJO FIGUREPROJECTTITLE 2 UNION 76 GASOLINE STATION 2236 OLD US 1 HWYAPEX, NC POTENTIAL RECEPTOR MAP !(P !(W !(W !(P !(P !(P !(P !(P !(P !(P !(P !(P !(W !(P SITE LOCATION OLD US 1 HW YHUMIE OLIVE RD 1 ,5 0 0 F EET RADIUS 500F E E T RADIUS POND 2 POND 1 WSW-6*WSW-5* WSW-8 WSW-9 WSW-4 WSW-1 WSW-3 WSW-2 WSW-7 WSW-15 WSW-10 WSW-12 WSW-17WSW-13 Source: Esri, Maxar, Earthstar Geographics, and the GIS User Community 500 0 500 1,000250 Feet ³ NOTES: 1. Well locations were obtained from previous reports prepared by other consultants and are approximate.2. * = Unable to determine which well (WSW-5 or WSW-6) wasactive; to be conservative, WSW-5 was designated as active. LEGEND !(P Active PotableWater Supply Well !(P Inactive PotableWater Supply Well INCIDENT NO.JOB NO.DATE SCALE DRAWN BY/CHECKED BY26571220217JULY 2023 AS SHOWN KMC/SJO !(W Inactive Non-PotableWater Supply Well FIGUREPROJECTTITLE 3 UNION 76 GASOLINE STATION 2236 OLD US 1 HWYAPEX, NC SITE MAP !(P !(W !(W !(P !> !>!> !>!(> !> !>!(P!(P!(P!(P!(P !(P !(P !(P !(W !(P !> !> !> O L D U S 1 H W Y WSW-2 MW-2DW-1 MW-3R MW-1MW-4R MW-7 MW-5 MW-6 MW-4 MW-3 Source: Esri, Maxar, Earthstar Geographics, and the GIS User Community 20 0 20 4010 Feet ³ NOTE: Well and tank locations were obtained from previous reports prepared by other consultants and are approximate. Parcel Boundary Approximate Location of Former USTs Monitoring Well (Type II)!> LEGEND !(W Inactive Non-Potable Water Supply Well Monitoring Well(Type III)!(> INCIDENT NO.JOB NO.DATE SCALE DRAWN BY/CHECKED BY26571220217JULY 2023 AS SHOWN KMC/SJO Destroyed Monitoring Well (Type II)!> FIGUREPROJECTTITLE 4 UNION 76 GASOLINE STATION2236 OLD US 1 HWYAPEX, NC GROUNDWATER ELEVATION –MAY 10, 2023 !(P !(W !(W !(P !>!> !>!(> !> !(P!(P!(P!(P!(P !(P !(P !(P !(W !(P !> !> !><O L D U S 1 H W Y WSW-2 MW-2(84.56) DW-1*(84.61)MW-3R(84.80) MW-1(84.97) MW-4R(84.77) MW-7(84.71)MW-5(84.92) MW-6[12.29] 8 4 .7 0 8 4 .8 0 8 4 .9 0 8 4 .6 0 84.8084.90Source: Esri, Maxar, Earthstar Geographics, and the GIS User Community 20 0 20 4010 Feet ³ Parcel Boundary Approximate Location of Former USTs Monitoring Well(Type II)!> LEGEND !(W Inactive Non-PotableWater Supply Well INCIDENT NO.JOB NO.DATE SCALE DRAWN BY/CHECKED BY26571220217JULY 2023 AS SHOWN KMC/SJO Gauged Monitoring Well (Type II)!> Gauged Monitoring Well (Type III)!(> NOTES: 1. Well and tank locations were obtained from previous reportsprepared by other consultants and are approximate.2. BTOC = Below Top of Casing3. * = Deep well; elevation not used for contouring purposes.4. The groundwater elevation contour interval is 0.10 feet. Groundwater FlowDirection Groundwater Contour<Groundwater Elevation (Feet)(##) Depth to Groundwater(Feet BTOC)[##] FIGUREPROJECTTITLE 5 UNION 76 GASOLINE STATION2236 OLD US 1 HWYAPEX, NC MONITORING WELLGROUNDWATER SAMPLEANALYTICAL RESULTS –MAY 10, 2023 !(P !(W !(W !(P !>!> !>!(> !> !(P!(P!(P!(P!(P !(P !(P !(P !(W !(P !> !> !> O L D U S 1 H W Y WSW-2 MW-2DW-1* MW-3R MW-1MW-4R MW-7MW-5 MW-6 ESTIMATED HORIZONTALEXTENT OF 2L GWQSEXCEEDANCES? ? Source: Esri, Maxar, Earthstar Geographics, and the GIS User Community 20 0 20 4010 Feet ³ Parcel Boundary Approximate Location of Former USTs LEGEND !(W Inactive Non-PotableWater Supply Well INCIDENT NO.JOB NO.DATE SCALE DRAWN BY/CHECKED BY26571220217JULY 2023 AS SHOWN KMC/SJO Sampled Monitoring Well (Type II)!> Sampled Monitoring Well (Type III)!(> NOTES: 1. Well and tank locations were obtained from previous reportsprepared by other consultants and are approximate.2. * = Deep well; analytical results not used for contouring purposes. SUMMARY OF GROUNDWATER LABORATORY RESULTS - STANDARD METHOD 6200BIncident Name and No.: Former Union 76 Gas Station - 26571 Well/ Sample ID DateCollected MW-1 05/10/23 1,400 <3.2 ƚ <6.1 ƚ 150 8.6 J 28 9.4 J 1,400 130 57 1,130MW-2 05/10/23 <0.18 <0.16 ƚ 2.1 <0.22 <0.15 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73MW-3R 05/10/23 290 8.5 45 23 2.3 23 2.1 49 130 81 480MW-4R 05/10/23 840 <16 ƚ <30 ƚ 1,800 99 430 230 9,900 2,000 620 11,900MW-5 05/10/23 <0.18 <0.16 ƚ <0.30 <0.22 <0.15 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73MW-6 05/10/23 <0.18 <0.16 ƚ <0.30 <0.22 <0.15 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73MW-7 05/10/23 <0.18 <0.16 ƚ <0.30 <0.22 <0.15 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73DW-1 05/10/23 <0.18 <0.16 ƚ 0.82 <0.22 <0.15 <0.38 <0.12 <0.22 <0.20 <0.15 <0.73 All results in micrograms per liter (µg/L).Bold results are above 2L GWQS.Refer to Table 4 for all other results and notes.Total Xylenes6,0006 26,10070 260,000600500.02 80,000600 30,50070 28,500400 50,0005004000.41,2-Dichloroethane Naphthalene n-PropylbenzeneToluene 1,2,4-TrimethylbenzeneEthylbenzene1,3,5-Trimethylbenzene24,100400Isopropylbenzene (Cumene)2L GWQS (µg/L) 5,0001GCL (µg/L)Benzene Contaminant of Concern 1,2-Dibromoethane (EDB) NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 APPENDICES NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 APPENDIX A HISTORICAL DATA • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • Sample ID B-101 B-102 B-103 Sample Depth in Feet (8-10) (8-10) (7-9) Aliphatics & Aromatics Method C5-C8 Aliphatics, mg/kg VPH 163 38.8 19.5 C9-C 12 Aliphatics, mg/kg VPH 110 18.4 40.4 C9-C10 Aromatics, mg/kg VPH 43.6 ND ND olatile Organics Acetone, mg/kg 8260 0.0925 0.226 ND Benzene, mg/kg 8260 3.08 1.72 0.0223 n-butylbenzene, mg/kg 8260 ND ND ND sec-butylbenzene, mg/kg 8260 0.00266 0.0397 0.00378 tert-butylbenzene, mg/kg 8260 ND 0.0073 ND carbon disulfide, mg/kg 8260 ND ND ND cis-1,2-Dichloroethene, mg/kg 8260 ND ND ND Chloroform, mg/kg 8260 ND ND ND 1,2-Dibromoethane, mg/kg 8260 0.113 ND 1,2-Dichloroethane, mg/kg 8260 0.308 0.177 0.0049 Ethylbenzene, mg/kg 8260 6.5 0.631 0.0272 Hexachlorobutadiene, mg/kg 8260 ND ND ND 2-Hexanone, mg/kg 8260 ND ND ND lsopropylbenzene, mg/kg 8260 0.0132 0.124 0.00757 4-lsopropyltoluene, mg/kg 8260 ND 0.0474 0.00597 Naphthalene, mg/kg 8260 0.0853 0.509 0.0467 4-Methyl-2-pentanone, mg/kg 8260 ND ND ND Methylene Chloride, mg/kg 8260 ND ND ND n-Propylbenzene, mg/kg 8260 0.0321 0.266 0.0162 Styrene, mg/kg 8260 ND ND ND 1,2,4-Trichlorobenzene, mg/kg 8260 ND ND ND Toluene, mg/kg 8260 16.4 3.48 0.0762 1,2,4 Trimethylbenzene, mg/kg 8260 0.204 1.69 0.121 1,3,5 Trimethylbenzene, mg/kg 8260 0.0634 0.674 0.0497 Total Xylenes. mg/kg 8260 31.2 3.49 0.167 Notes: ND -Not detected NT -Not tested NS -No standard • -interim standard Concentration in bold and -shaded exceeds state residential standards Concentration in bold and shaded exceeds state industrial/commercial standards Concentration in Bold exceeds state Soil to GW standards B-104 (9-11) ND ND ND ND 0.0065 ND ND ND ND ND ND ND ND 0.0033 ND ND ND ND 0.00752 ND ND ND ND ND 0.0133 ND 0.00863 0.0195 TABLE3 SUMMARY OF SOIL ANAi. YTICAI. RESULTS Former 76 Service Station 2236 Old US Highway 1 Apex, North Carolina B-105 B-106 B-107 B-108 B-109 (7-9) (9-11) (9-11) (7-9) (7-9) MW-1 (6-8) MW-1 (10-11) State Standards (mg/kg) Residential Industrial/Commercial Soil to GW 380 14.7 ND 265 ND 1,010 ND ND 390 ND ND ND ND -. --939 24,528 72 9,386 245,280 3,255 469 12,264 34 • l 0.253 ND ND 0.0956 ND 0.166 0.576 0.308 0.318 0.0031 ND ND ND ND ND 0.1 14 0.00955 0.00304 0.128 ND 0.023 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND 0.0439 0.0441 0.0377 ND ND 1.66 1,564 40,880 3 20.1 12.3 22 200 0.0056 56.4 ND 156 4,088 4 11.6 0.169 ,56 4,088 3 ND ND 156 4,088 3 ND ND 1,564 40,880 4 ND ND 156 4,000 0.35 ND ND 100 938 0.001 ND ND 0.0075 0.067 0.00000197 ND ND 7 63.000 0.0018 3.62 0.21 0.0568 4.9 ND ND ND ND ND ND ND ND ND ND ND 2.1 0.0296 0.00677 1.66 ND 0.193 0.0113 0.00739 0.088 ND 172 127 1,560 40,000 0.24 ND ND 3 73 0.26 ND ND 625 16,352 1.9 22.9 19.8 1,564 40,880 2 7.39 0.134 NS NS NS 7.63 0.108 0.0489 6.15 ND ND ND ND ND ND 60.6 63 1,635 0.58 ND ND NS NS NS ND ND ND ND ND 4.71 0.0605 0.0112 7.3 ND ND ND ND ND ND ND ND ND ND ND 4.18 1.31 0.4 5.94 0.0121 34.2 0.631 0.208 39.2 ND 13.8 0.145 0.0981 13.5 ND 25.3 1.39 0.561 30.8 0.005 ND ND 85 763 0.02 90.2 74.3 156 4,088 2 ND ND 3128 81 ,760 2.24 ND ND 156 4,088 2.6 343 212 3,200 82,000 7 427 359 782 20,440 8 163 149 782 20,440 7 841 642 32,000 200,000 5 APPENDIX A HISTORICAL DATA NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 NOTE: 1. 2. SOIL SAMPLES COLLECTED FROM BORINGS AT DEPTHS RANGING FROM 7 TO 11 FEET BLS. DEPTH TO GROUNDWATER IN MW-1 WAS APPROXIMATELY 14.01 FEET BLS. HUMIE OLIVE ROAD OVERHA f--- 2236 OLD US HIGHWAY 1 - r-- SHED >- ,- NG --= ---- -- - - - - WSW-HD ~ SAMPLED ON MARCH 17, 2004. J ~ RESULTS INDICATE ANALYTES Q BELOW METHOD DETECTION LIMITS. HAND DUG WATER SUPPLY WELL APPROXIMATE EXTENT OF UST EXCAVATION 1.3.0' x 7.0' x 6.0' DEEP) r-·--·--·--·, .rw, I < MSCCs 8-109 ! I I j I I ;""'~I "", ----APPROXIMATE LOCATION FORMER PUMP ISLAND ------------------~ 1 1 OF FORMER 1,000-GALLON ( ~ ~ ) i I I I GASOLINE UST APPROXIMATE EXTENT OF UST EXCAVATION ( ~ 9.0' x 5.0' x 6.0' DEEP) 8-108 e .._, -------l L'-_j ! UST #2 • I • L. __________ J 8-104 > MSCCs -·--=·--·, e 8-1 03 •8-107 > MSCCs LEGEND : ~ MW-1 MONITORING WELL LOCATION • SOIL BORING LOCATION B-101 > MSCCs < MSCCs > MSCCs UST CLOSURE SAMPLES EXCEEDS SOIL TO GROUNDWATER MAXIMUM SOIL CONTAMINANT CONCENTRATIONS {MSCCs) LESS THAN SOIL TO GROUNDWATER MSCCs CONCENTRATION IN SOIL EXCEEDS RESIDENTIAL MSCCs CONCENTRATION IN SOIL EXCEEDS INDUSTRIAL/ COMMERCIAL MSCCs LAKE ____.,, APPROXIMATELY 150 FEET FROM PUMP ISLAND WSW-1 APPROXIMATELY 150 FEET ---~- FROM SOURCE AREA SAMPLED ON MARCH 17, 2004 . RESULTS INDICATE PETROLEUM CONSTITUENTS EXCEED 15A NCAC SUBCHAPTER 2L FOR BENZENE (1 2.3 ug/L) AND 1,2-DICHLORO- ETHANE (8.9 ug/L). APPROXIMATE LOCATION OF UNDERGROUND LINES ~ • 8-105 ~ !~w~i > MSCCs L._ __ ---=--~_r-~-------------------APPROXIMATE LOCATION OF FORMER 550-GALLON GASOLINE UST ------- ~8-102• . ~ 8-106~ ............................ -..... -...................................................................................................... . e 8-101 ~ ................................... -.... -................ -....................................................................................... . -.__ .... ·-· -~-·.· ·.· ._ .. _ ... ·.· ·.· ............... :.: ._ .. _ .... :.:. : .. : .. : .. : .. :.:.:. : .. : .. : .. : ... :.:. _. ._ .. _ .... :.: ._ .. _ .... :.: ._ .. _ .... :.: ._ .. _ .... :.: ._ .. _ .... :.:. : .. ,; .. : ... : .. :.:.: .. : ... :.~.: .. :.:.: ._ .. _ .. - ........................................................................................................................................ -......... . OLD US HIGHWAY 1 . . . . . . . . . -........................................................................................................................................ . WITHERS & RAVENEL ENSINEEIS I PLANNERS I SURVEYORS 111 MoeKenari M,e Cay, North c«tiino 27511 nw.wilhennM,nelcom tel: 919-460-6006 fax: 919-5JS-.4545 Revisiona No. Description Dato By FORMER UNION 76 SERVICE STATION 2 2 36 OLD US HIGHWAY 1 APEX NORTH CAROLINA I SAMPLE LOCATION MAP UST #1 I o..wne, Scalo KTC 1 ·s:::1 o· ~"" Dato KTC 4/12/04 Joi> No. 204086.0 -No. 3 APPENDIX A HISTORICAL DATA Well ID Date Installed Well Casing Depth (ft-bgs) Screened Interval (ft- bgs) Well Material Well Diameter (inches) Total Well Depth from Top of Casing (ft.) Top of Casing Elevation (ft-rel) Date of Measurement Depth to Water (ft-btoc) Groundwater Elevation (ft-rel) 7/21/2004 14.01 85.93 6/14/2005 13.61 86.33 6/28/2006 14.90 85.04 3/24/2015 10.47 89.47 4/25/2019 10.15 89.79 6/8/2020 14.23 85.71 6/14/2005 14.02 85.98 6/28/2006 15.00 85.00 3/24/2015 10.58 89.42 4/25/2019 6/8/2020 14.89 85.11 6/14/2005 13.03 86.07 6/28/2006 14.00 85.10 3/24/2015 9.66 89.44 4/25/2019 MW-3R 6/5/2020 0.0-10.0 10.0-20.0 PVC 2 20.0 99.84 6/8/2020 14.54 85.30 6/14/2005 12.05 86.63 6/28/2006 13.65 85.03 3/24/2015 9.43 89.25 4/25/2019 MW-4R 6/5/2020 0.0-10.0 10.0-20.0 PVC 2 20.0 99.44 6/8/2020 13.66 85.78 6/14/2005 14.45 85.75 6/28/2006 15.24 84.96 3/24/2015 10.74 89.46 4/25/2019 10.82 89.38 6/8/2020 15.13 85.07 Notes: ft-bgs: Feet below ground surface ft-rel: Feet relative elevation ft-btoc: feet below top of casing Groundwater samples were collected by Terraquest Environmental Consultants on 6/24/2010, however, no groundwater measurements were included in the Letter Report. Approximately 0.5 inches of free product was reportedly measured in monitor well MW-4 on 6/24/2010. Groundwater samples were collected by Crawford Environmental Services on 6/10/13 however, no groundwater measurements were included in the Letter Report. S&ME Project No. 4305-19-052A Not Measured Well Damaged - Not Measured 2 20.0 99.94 MW-2 20.0 100.00 MW-1 TABLE 3 Monitor Well Construction Details and Groundwater Elevation Data Former Union 76 (Incident No. 26571, UST No. RA-5020) 2236 Old US Highway 1 Apex, Wake County, North Carolina Well Damaged - Not Measured 0.0 - 5.05/26/2005MW-4 99.105/25/2005MW-3 98.6820.02PVC5.0 - 20.0 20.02PVC5.0 - 20.0 7/21/2004 0.0 - 5.0 5.0 - 20.0 PVC 5/24/2005 0.0 - 5.0 5.0 - 20.0 PVC 2 2 40.0 100.20DW-1 5/26/2005 0.0 - 35.0 35.0 - 40.0 PVC 0.0 - 5.0 APPENDIX A HISTORICAL DATA NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 Sample ID Date Collected 7/22/2004 BDL 4,950 BDL 36 230 936 688 54 8.2 BDL BDL 69 238 27 7 109 BDL NA NA 600 188 6,600 3,780 6/14/2005 BDL 3,300 BDL BDL 70 BDL 2,070 116 BDL BDL BDL 29 840 BDL BDL 242 BDL NA NA 2,720 790 11,600 15,750 6/29/2006 BDL 7,360 BDL BDL 38 BDL 820 BDL BDL BDL BDL BDL 357 BDL BDL BDL BDL NA NA 1,460 570 8,660 8,940 6/9/2010 BDL 5,740 BDL 36 47 773 1,060 60 BDL BDL BDL 107 404 BDL BDL 68 BDL NA NA 947 340 9,320 8,120 6/10/2013 BDL 4,100 BDL BDL 110 710 440 26 BDL BDL BDL 50 740 30 BDL 48 BDL NA NA 520 240 5,400 4,300 3/24/2015* BDL 7,330 BDL 28 BDL 800 755 41 BDL BDL BDL 31 342 BDL BDL 63 BDL NA NA 755 304 6,830 4,780 4/25/2019* BDL 3,400 BDL BDL BDL BDL 420 BDL BDL BDL BDL BDL 160 BDL BDL BDL BDL NA NA 370 160 4,600 3,100 6/8/2020* BDL 990 BDL BDL 11 J 84 210 42 J BDL BDL BDL BDL 160 BDL BDL 34 BDL BDL BDL 230 130 1,800 2,010 6/14/2005 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL NA NA BDL BDL BDL BDL 6/29/2006 BDL 3,720 BDL BDL 91 BDL 568 BDL BDL BDL BDL BDL BDL BDL BDL BB BDL NA NA 428 BDL 4,740 3,170 6/9/2010 BDL 86 BDL 4.6 7.7 94 18 0.97 BDL BDL BDL 16 11 BDL BDL 0.67 BDL NA NA BDL 3.7 4.4 8.3 6/10/2013 BDL 8.8 BDL 1.0 0.24 13 0.14 BDL BDL BDL BDL 2.2 BDL BDL BDL BDL BDL NA NA 0.24 0.38 0.72 2.2 3/24/2015* BDL 832 BDL BDL BDL 108 76 11 BDL 32 BDL 14 83 BDL BDL 6.9 BDL NA NA BDL BDL BDL BDL 4/25/2019 6/8/2020* BDL 670 BDL 4.4 8.3 97 37 8.2 J BDL BDL BDL 12 60 BDL BDL 5.5 BDL BDL BDL 4.2 J 11 11 25.4 6/14/2005 BDL 7,150 BDL BDL 407 BDL 1,340 81 BDL BDL BDL BDL 478 BDL BDL 96 BDL 72,000 367 1,250 491 12,100 7,380 6/29/2006 BDL 7,080 BDL BDL 370 BDL 1,200 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL NA NA 1,040 BDL 11,300 6,740 6/9/2010 BDL 3,170 BDL 4.8 113 239 50 BDL BDL BDL BDL 8.6 157 59 BDL BDL 6.5 NA NA 692 227 5,190 4,110 6/10/2013 500 2,900 16 BDL 75 BDL 560 36 BDL BDL 370 BDL BDL 16 BDL 56 BDL NA NA 530 200 5,000 3,800 3/24/2015* BDL 1,220 BDL BDL 18 62 200 14 BDL 48 BDL BDL 55 19 BDL BDL BDL NA NA 176 55 275 713 4/25/2019 MW-3R 6/8/2020*300 2,500 BDL BDL 58 190 580 97 J BDL BDL 170 J 16 J 340 33 BDL 100 BDL BDL BDL 730 260 4,300 3,700 6/14/2005 BDL 8,950 BDL BDL 494 BDL 3,300 134 BDL BDL BDL 126 1,070 BDL BDL 362 BDL 153,000 BDL 2,870 834 33,500 18,190 6/29/2006 BDL 8,960 BDL BDL 362 BDL 2,840 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL NA NA 2,400 BDL 30,800 16,420 6/9/2010 6/10/2013 3/24/2015* BDL 3,390 BDL BDL 530 257 783 62.3 BDL BDL BDL BDL 1,040 133 BDL BDL 11.6 NA NA 2,850 827 11,300 15,030 4/25/2019 MW-4R 6/8/2020* BDL 2,000 BDL BDL BDL BDL 2,400 370 J BDL BDL BDL BDL 1,300 98 BDL 480 BDL BDL BDL 3,000 1,100 14,000 15,800 6/14/2005 BDL 8.5 BDL 0.6 6.8 29 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 934 BDL 0.84 BDL 2.3 4.7 6/29/2006 BDL 353 BDL BDL 362 BDL 18 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL NA NA BDL BDL BDL 22 6/9/2010 BDL 5.6 BDL 0.51 BDL 18.7 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL NA NA BDL BDL BDL BDL 6/10/2013 BDL 2 BDL 0.41 BDL 15 0.11 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL NA NA 0.24 BDL 0.87 0.9 3/24/2015* BDL 2.3 BDL BDL BDL 3 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL NA NA BDL BDL BDL 0.96 4/25/2019 BDL 1.5 BDL BDL BDL 1.7 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL NA NA BDL BDL BDL 1.19 J 6/8/2020 BDL 7.8 BDL BDL BDL 5.1 BDL 1.8 J BDL BDL BDL BDL 5.7 BDL BDL BDL BDL BDL BDL 1.1 BDL BDL 8.4 6,000 1 70 70 0.02 0.40 600 70 25 5 4,000 20 6 70 70 70 70 40 128 400 400 600 500 60,000,000 5,000 70,000 70,000 50 400 84,500 25,000 11,700 5,000 4,000,000 20,000 6,000 6,900 8,500 30,000 70,000 40,000 12,800 28,500 25,000 260,000 85,500 * Indicates samples analyzed at dilution 2L Standards: 15A NCAC 2L Groundwater Standards.BDL: Below Detection Limits Only detected constituents are shown for the method.NA - Not Analized Constituents in BOLD were reported at concentrations above the laboratory analytical method detection limits. Constituents in BOLD and shaded were reported at concentrations above the North Carolina 2L Standards. Constituents in BOLD, shaded and underlined were reported at concentrations above the Gross Contamination Levels. Monitor Well Obstructed - Not Sampled S&ME Project No. 4305-19-052A chloroformVolatile Organic Compounds by EPA 6200B or Equivalent (µg/l)styrenetotal xylenesisopropylbenzenemethyl tert-butyl ethernaphthalenen-butylbenzenetoluenetert-amyl alcoholConstituent of Concern tert-amyl methyl ethern-propylbenzeneTABLE 4 Summary of Groundwater Analytical Results Former Union 76 (Incident No. 26571, UST No. RA-5020) 2236 Old US Highway 1Apex, Wake County, North Carolina 1,3,5-trimethylbenzenebenzeneacetone1,2,4-rimethylbenzenedi-isopropyl etherethylbenzenesec-butylbenzene4-isopropyltoluenemethylene chloridemethyl ethyl ketone1,2-dibromoethane 1,2-dichloroethaneAnalytical Method 2L Standards MW-3 MW-4 MW-1 MW-2 Monitor Well Damaged - Not Sampled Monitor Well Damaged - Not Sampled µg/L = micrograms per liter. Gross Contamination Levels NOTES: Monitor Well Not Sampled - Approximately 0.5 inches of Free Product Monitor Well Not Sampled DW-1 APPENDIX A HISTORICAL DATA NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 Sample ID Date Collected 3/17/2004 12.3 8.9 BDL 1.4 BDL 4 BDL 0.8 BDL 2.9 6/14/2005 31 BDL BDL BDL BDL 4.6 0.87 3.3 BDL 5.6 6/29/2006 39 10 BDL BDL BDL 7.8 BDL BDL BDL 18 6/9/2010 24.7 14 0.57 BDL BDL 6 BDL 2.5 BDL 8.6 3/24/2015 5.9 3.1 BDL BDL BDL BDL BDL BDL BDL BDL 4/25/2019 6/14/2005 5.9 BDL BDL 1.3 BDL 1.7 0.68 2.9 0.66 5.6 4/25/2019 6/14/2005 1.7 BDL BDL BDL 8.7 BDL BDL BDL BDL BDL 6/29/2006 4.7 BDL BDL 31 BDL 1.7 BDL BDL BDL 4.3 4/25/2019 6/14/2005 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 6/29/2005 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 4/25/2019 6/14/2005 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 4/25/2019 6/14/2005 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 4/25/2019 6/14/2005 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 6/28/2006 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 4/25/2019 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 6/14/2005 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 6/28/2006 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 3/24/2015 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 4/25/2019 6/14/2005 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 6/28/2006 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 6/10/2013 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 3/24/2015 BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL 4/25/2019 1 0.4 70 70 20 6 600 400 400 500 5,000 400 70,000 25,000 20,000 6,000 260,000 28,500 25,000 85,500 NOTES: Water supply wells WSW-1, WSW-2, and WSW-3 are inactive. 2L Standards: 15A NCAC 2L Groundwater Standards. Only detected constituents are shown for the method. Constituents in BOLD were reported at concentrations above the laboratory analytical method detection limits. Constituents in BOLD and shaded were reported at concentrations above the North Carolina 2L Standards. Constituents in BOLD, shaded and underlined were reported at concentrations above the Gross Contamination Levels. BDL: Below Detection Limit Not Sampled Not Sampled Not Sampled Not Sampled Not Sampled Not Sampled Not Sampled Not Sampled Constituent of Concern µg/L = micrograms per liter. S&ME Project No. 4305-19-052A 2L Standards isopropylbenzeneWSW-5 WSW-6 WSW-7 WSW-8 WSW-9 WSW-1 WSW-2 WSW-3 WSW-4 Gross Contamination Levels Analytical Method benzene1,2-dichloroethaneVolatile Organic Compounds by EPA Method 6200B (µg/l)1,3,5-trimethylbenzenemethyl tert-butyl ethernaphthalene1,2,4-trimethylbenzenetotal xylenesdi-isopropyl ethertolueneTABLE 5 Summary of Water Supply Well Analytical Results Former Union 76 (Incident No. 26571, UST No. RA-5020) 2236 Old US Highway 1 Apex, Wake County, North Carolina APPENDIX A HISTORICAL DATA NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 Adjacent Property Owners Page 1 of 1 Map ID Parcel Number Location Usage Distance from source area of release (feet) Site 720998487 2236 Old US Highway 1, Apex, NC Residential SITE 1 730091779 1001 Red Cardinal Lane, Apex, NC Residential 300' N 2 720993901 0 Humie Olive Road, Apex, NC Vacant 400' NW 3 720992587 7528 Humie Olive Rd., Apex, NC Residential 200' SW 4 720993254 0 Humie Olive Road, Apex, NC Vacant 190' SW 5 720995061 2300 Old US Highway 1, Apex, NC Residential 200' SW 6 720988751 7628 Vaudry Court, Apex, NC Residential 130' S 7 720999210 2237 Old US Highway 1, Apex, NC Commercial 120' S 8 730009122 2217 Old US Highway 1, Apex, NC Residential 300' SE Public and Private Water Supply Wells within 500 Feet of Property Boundary Map ID /Well ID Parcel Number Well Owner Property Address Owner Address Phone Number Well Use Well Depth (ft bgs) Well Casing Depth (ft. bgs) Well Screen Interval Distance from source area of release (feet) Comment WSW-1 730009122 David Ray Powell 2236 Old US Highway 1 524 Lapis Lane, Cary, NC 919-387-0848 Inactive 300 44 Unknown 150 Feet N Inactive water supply well WSW-2 730009122 David Ray Powell 2236 Old US Highway 1 524 Lapis Lane, Cary, NC 919-387-0848 Inactive Unknown Unknown Unknown 200 Feet NW Hand-dug well formerly labled as WSW-HD. WSW-3 720999210 Miller Land Group LLC (Vicious Fishes Brewery) 2237 Old US Highway 1 1922 Napoli Dr, Apex, NC 919-362-8972 Inactive Unknown Unknown Unknown 250 Feet SE Well is inactive - site is connected with municipal water - located at McNeil's Grocery Site - TF-6891 WSW-4 720992587 Shelba Clem 7528 Humie Olive Rd., Apex, NC 7528 Humie Olive Rd., Apex, NC 919-328-4812 Active Unknown Unknown Unknown 400 Feet NW WSW-5 730009122 Joyce Kelly 2217 Old US Highway 1, Apex, NC 2217 Old US Highway 1, Apex, NC 919-387-8543 Active Unknown Unknown Unknown 480 Feet SE WSW-6 730009122 Joyce Kelly 2217 Old US Highway 1, Apex, NC 2217 Old US Highway 1, Apex, NC 919-387-8543 Active Unknown Unknown Unknown 500 Feet SE WSW-7 730095707 Frances Bullock 3116 Holland Road, Apex, NC 3116 Holland Road, Apex, NC 919-362-8313 Active Unknown Unknown Unknown 950 Feet NE WSW-8 720995061 Richere Levert 2300 Old US Highway 1, Apex, NC 7628 Vaudry Court, Apex, NC 919-363-8906 Active Unknown Unknown Unknown 500 Feet SW WSW-9 720988751 Richere Levert 7628 Vaudry Court, Apex, NC 7628 Vaudry Court, Apex, NC 919-363-8906 Active Unknown Unknown Unknown 400 Feet SW WSW-10 730091779 Johnny Pendergraft 1001 Red Cardinal Lane, Apex, NC 2212 Old US Highway 1, Apex, NC 919-362-7487 Active Unknown Unknown Unknown 480 Feet NE WSW-12 731001087 Joanne Hearn 1005 Red Cardnial Lane, Apex, NC 1115 Dycus Road, Sanford, NC 919-775-5391 Active Unknown Unknown Unknown 900 Feet NE WSW-13 730097826 Walter McClamb 3113 Holland Road, Apex, NC P.O. Box 243, Apex, NC 919-362-7313 Active Unknown Unknown Unknown 1,100 Feet NE WSW-15 730096271 Johnny and Penny Roberts 3000 Friendship Road, Apex, NC 3000 Friendship Road, Apex, NC 919-303-8535 Active Unknown Unknown Unknown 900 Feet E WSW-17 730098773 Walter McClamb 3113 Holland Road, Apex, NC 2124 Old US Highway 1, Apex, NC 919-362-7313 Active Unknown Unknown Unknown 950 Feet NE P-1 730009122 David Ray Powell 2236 Old US Highway 1 524 Lapis Lane, Cary, NC 919-387-0848 210 Feet SE Surface water feature located on adjacent parcel to SE P-2 730009122 Joyce Kelly 2217 Old US Highway 1, Apex, NC 2217 Old US Highway 1, Apex, NC 919-387-0848 150 Feet N Surface water feature located on Former Union 76 Site to the north. Notes: ft. bgs - Feet Below Ground Surface Refer to Figure 3 for Adjacent Property Owner and Water Supply Well Location Map. Property address information obtained from the Wake County GIS website on April 16, 2015. Water Supply Well information is taken from previous reports prepared by Groundwater Management Associates (GMA), dated August 16, 2006, and Crawford Environmental Services, dated August 23, 2013. Vacant property to the southwest Residential property to the southwest Adjacent proprety to the south - TF-XXX McNeil's Grocery Site Adjacent property to the south/southwest Residential property to the southwest TABLE 6 Receptor Information and Adjacent Property Owners Former Union 76 (Incident No. 26571, RA-5020) 2236 Old US Highway 1, Apex, Wake County, North Carolina S&ME Project No. 4305-19-052A Description Contact/Telephone Number Comment Former Union 76 Property (TF-26571) and occupied house David Ray Powell / 919-387-0848 SITE Vicious Fishes Brewery Miller Land Group, LLC / 919-362-8972 Residential Johnny Pendergraft / 919-362-7487 Adjoining residential property to the north and east Vacant - Undeveloped NDJ Ventures, LLC / 919-362-9285 Ajoining residential property to the west Residential Richere Levert / 919-363-8906 Residential David Clem / 919-328-4812 Vacant - Undeveloped David Ray Powell / 919-387-0848 Residential Richere Levert / 919-363-8906 Residential Joyce Kelly / 919-387-8543 Adjacent proprety to the southeast Not Applicable Not Applicable APPENDIX A HISTORICAL DATA NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 APPENDIX B SITE PHOTOGRAPHS APPENDIX B SITE PHOTOGRAPHS – APRIL 11, 2023 NCDEQ; 26571_Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 View of site, facing northwest. View of AFVR Set-up, facing northwest. APPENDIX B SITE PHOTOGRAPHS – APRIL 11, 2023 NCDEQ; 26571_Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 View of vacuum truck, facing north. View of MW-1, facing west-southwest. APPENDIX B SITE PHOTOGRAPHS – APRIL 11, 2023 NCDEQ; 26571_Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 View of MW-2, facing northwest. View of MW-3R, facing northwest. APPENDIX B SITE PHOTOGRAPHS – APRIL 11, 2023 NCDEQ; 26571_Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 View of DW-1, facing northwest. APPENDIX B SITE PHOTOGRAPHS – MAY 10, 2023 NCDEQ; 26571_Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 View of the site, facing northeast. View of MW-1, facing northwest. APPENDIX B SITE PHOTOGRAPHS – MAY 10, 2023 NCDEQ; 26571_Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 View of MW-2, facing north. View of MW-3R, facing northwest. APPENDIX B SITE PHOTOGRAPHS – MAY 10, 2023 NCDEQ; 26571_Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 View of MW-4R, facing northeast. View of MW-5, facing northeast. APPENDIX B SITE PHOTOGRAPHS – MAY 10, 2023 NCDEQ; 26571_Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 View of MW-6, facing west. View of MW-7, facing north-northeast. APPENDIX B SITE PHOTOGRAPHS – MAY 10, 2023 NCDEQ; 26571_Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 View of DW-1, facing north. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 APPENDIX C JOB HAZARD ANALYSES AND FIELD DATA SHEETS Source Exposure Limit Groundwater and/or soil vapor 0.5 ppm TLV-TWA ACGIH Groundwater and/or soil vapor 100 ppm TLV-TWA ACGIH Groundwater and/or soil vapor 20 ppm TLV-TWA ACGIH Groundwater and/or soil vapor 100 ppm TLV-TWA ACGIH Groundwater and/or soil vapor 50 ppm TLV-TWA ACGIH Groundwater and/or soil vapor 10 ppm TLV-TWA ACGIH Source Exposure Limit atmosphere N/A atmosphere N/A surroundings N/A Vacuum Truck 85 dBA TWA ACGIH Exposure Potential Likely Unlikely Unlikely Start Stop 6:30 6:45 6:45 7:00 7:00 16:45 16:45 17:45 Date and Time: 4/11/23 @ 07:00 Site-Specific Job Hazard Analysis Operational Phase Task/Operation Location Where Task/Operation Performed Monitoring Enhanced Aggressive Fluid and Vapor Recovery (AFVR)Former Union 76 Gasoline Station, Apex, NC ETHYL BENZENE ppm Date(s) this JHA Conducted: 4-11-2023 Employee Certifying this JHA Print Name: Sean O'Neil, PE Signature: Weather:Sunny, low 40s-mid 70s Chemical Hazards Potential Chemicals Concentration BENZENE ppm TOLUENE ppm XYLENE, ALL ISOMERS ppm METHYL TERT-BUTYL ETHER ppm NAPHTHALENE ppm * Gas and/or Diesel Physical Hazards Name of Physical Hazard Exposure Level/ Potential Insect bites and stings surroundings Cold Weather Operations Unlikely Heat (ambient)Unlikely Slips/Trips/Falls Likely Noise Likely Biological Hazards Name of Biological Hazard Source On-site health and safety briefing. Watch for cars in driveway and going down the road. Wear safety vest when near road. Watch for ants and spiders when in and around wells. Wear hearing protection and be careful on and around vacuum truck to avoid slips, trips, and falls. Snakes surroundings Poison Plants (Ivy, Oak, and/or Sumac)surroundings DAILY TASK Truck #55 Mileage:Start: End: Mob and travel to site. Opened and gauged wells; assisted with set-up of extraction points. Used MW-1, -2, -3R, and DW-1 (sparge). Supervise AFVR. Assist with break down connections, gauge wells, close up covers, take pictures. Needed to wait until air quit escaping from DW-1 so the cap would stay on the well. Travel to Apex and demob PERSONNEL ONSITE Name and Company (Print)Signature Sandra Miller / CATLIN Equipment Used:PPE D/Oil-Water Interface Probe/PID Meter Source Exposure Limit Groundwater and/or soil vapor 0.5 ppm TLV-TWA ACGIH Groundwater and/or soil vapor 100 ppm TLV-TWA ACGIH Groundwater and/or soil vapor 20 ppm TLV-TWA ACGIH Groundwater and/or soil vapor 100 ppm TLV-TWA ACGIH Groundwater and/or soil vapor 50 ppm TLV-TWA ACGIH Groundwater and/or soil vapor 10 ppm TLV-TWA ACGIH Source Exposure Limit atmosphere N/A atmosphere N/A surroundings N/A Roads N/A Exposure Potential Likely Likely Unlikely Start Stop 10:30 10:45 10:45 14:45 14:45 16:15 Date and Time: 5/10/23 @ 10:45 Employee Certifying this JHA Print Name: Sean O'Neil, P.E.Signature: Operational Phase Monitoring Date(s) this JHA Conducted: 5/10/2023 Site-Specific Job Hazard Analysis Location Where Task/Operation Performed Union 76 Gasoline Station, Apex, NC Task/Operation Gauge & Sample Monitoring Wells METHYL TERT-BUTYL ETHER ppm Traffic Likely 80s SunnyWeather: ETHYL BENZENE NAPHTHALENE ppm Physical Hazards Name of Physical Hazard Exposure Level/ Potential * Gas and/or Diesel ppm TOLUENE ppm XYLENE, ALL ISOMERS ppm Chemical Hazards Potential Chemicals Concentration BENZENE ppm Nate Newman / CATLIN Safety Meeting on site. Watch for insects, spiders and snakes. Practice safe housekeeping to avoid slips, trips and falls. Wear PPE including safety vest when in and around parking lot and road. Biological Hazards Name of Biological Hazard Source Poison Plants (Ivy, Oak, and/or Sumac)surroundings Insect bites and stings surroundings Snakes surroundings End: DAILY TASK PERSONNEL ONSITE Name and Company (Print)Signature Equipment Used:PPE D/Interface Probe/Sampling Supplies/Aqua Troll 600/Bailers Opened, gauged, photographed, and sampled MW-1, MW-2, MW-3R, MW-4R, MW-5, and MW-6. Closed up wells and cleaned up equipment. DTW in MW-6 may not be accurate due to PVC sinking. Cold Weather Operations Unlikely Heat (ambient)Likely Slips/Trips/Falls Likely Van #59 Mileage: completed COC, obtained PO#, traveled to Pace to drop off prior and current samples, return to Raleigh office, demob Start: P:\2020\220217 DEQ SLP - Union 76 Gasoline Station (Former)\Field Notes\TA04\Sampling\Union 76_GW_Sampling_Sheets CATLIN PROJECT:SAMPLED BY: CATLIN PROJECT # :DATE SAMPLED: CLIENT'S NAME: MW-1 5.03 14.97 0.821 NMT 2.463 20 4.104 2 Method:Bailer Purge Start Time:13:38 Required Bails for 3 Well Volumes:11 Purge Stop Time:13:40 Required Bails for 5 Well Volumes:18 Was Well Purged Dry?YES Number of Bails Removed:3.25 Sample Time:13:48 Groundwater Removed (gal):0.8 Equipment Used: Time Specific Cond. (µS/cm) Dissolved Oxygen (mg/L) pH (Standard Units) ORP (mV) Temperature (Co) Laboratory:Con-Test Analysis:6200B Cloudy. Not enough water for VuSitu readings. Well Data Well ID N. Newman 5/10/2023 Depth to Product (ft below TOC) Total Well Depth (ft) Purging Information Information Laboratory Analysis Information GROUNDWATER SAMPLING FORM Water Column (ft below TOC) One Well Volume (gal) Three Well Volumes (gal) Five Well Volumes (gal) Volume of Groundwater in Well Aqua Troll 600 Turbidity and Additional Sampling Notes Well Diameter (inches) Monitoring Well Information Geochemical Parameters Depth to Water (ft below TOC) NCDEQ-SLP, Linda Blalock Former Union 76 Gas Station 220217 NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 P:\2020\220217 DEQ SLP - Union 76 Gasoline Station (Former)\Field Notes\TA04\Sampling\Union 76_GW_Sampling_Sheets CATLIN PROJECT:SAMPLED BY: CATLIN PROJECT # :DATE SAMPLED: CLIENT'S NAME: MW-2 4.56 15.44 0.744 NMT 2.233 20 3.721 2 Method:Bailer Purge Start Time:11:33 Required Bails for 3 Well Volumes:10 Purge Stop Time:11:40 Required Bails for 5 Well Volumes:16 Was Well Purged Dry?YES Number of Bails Removed:8 Sample Time:11:44 Groundwater Removed (gal):1.9 Equipment Used: Time Specific Cond. (µS/cm) Dissolved Oxygen (mg/L) pH (Standard Units) ORP (mV) Temperature (Co) 11:34 79.33 6.40 6.00 313.78 19.56 11:35 66.33 5.01 5.24 367.49 19.49 11:36 65.17 5.01 5.12 375.27 19.43 11:37 64.64 5.08 5.08 380.51 19.41 11:38 63.46 5.13 5.05 382.77 19.39 11:39 61.52 5.25 5.12 380.11 19.37 11:40 0.06 7.91 5.33 372.97 19.31 Laboratory:Con-Test Analysis:6200B GROUNDWATER SAMPLING FORM Monitoring Well Information Well Data Volume of Groundwater in Well Well ID Water Column (ft below TOC) N. Newman 5/10/2023 NCDEQ-SLP, Linda Blalock Former Union 76 Gas Station 220217 Depth to Water (ft below TOC)One Well Volume (gal) Depth to Product (ft below TOC)Three Well Volumes (gal) Total Well Depth (ft)Five Well Volumes (gal) Laboratory Analysis Information Well Diameter (inches) Purging Information Information Geochemical Parameters Aqua Troll 600 Turbidity and Additional Sampling Notes high turbidity to start light brown low turbidity at sample. entire well shield was an ant nest NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 P:\2020\220217 DEQ SLP - Union 76 Gasoline Station (Former)\Field Notes\TA04\Sampling\Union 76_GW_Sampling_Sheets CATLIN PROJECT:SAMPLED BY: CATLIN PROJECT # :DATE SAMPLED: CLIENT'S NAME: MW-3R 4.96 15.04 0.809 NMT 2.428 20 4.047 2 Method:Bailer Purge Start Time:14:08 Required Bails for 3 Well Volumes:11 Purge Stop Time:14:12 Required Bails for 5 Well Volumes:17 Was Well Purged Dry?YES Number of Bails Removed:3 Sample Time:14:20 Groundwater Removed (gal):0.7 Equipment Used: Time Specific Cond. (µS/cm) Dissolved Oxygen (mg/L) pH (Standard Units) ORP (mV) Temperature (Co) Laboratory:Con-Test Analysis:6200B GROUNDWATER SAMPLING FORM Monitoring Well Information Well Data Volume of Groundwater in Well Well ID Water Column (ft below TOC) N. Newman 5/10/2023 NCDEQ-SLP, Linda Blalock Former Union 76 Gas Station 220217 Depth to Water (ft below TOC)One Well Volume (gal) Depth to Product (ft below TOC)Three Well Volumes (gal) Total Well Depth (ft)Five Well Volumes (gal) Laboratory Analysis Information Well Diameter (inches) Purging Information Information Geochemical Parameters Aqua Troll 600 Turbidity and Additional Sampling Notes Cloudy. Not enough water for VuSitu readings. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 P:\2020\220217 DEQ SLP - Union 76 Gasoline Station (Former)\Field Notes\TA04\Sampling\Union 76_GW_Sampling_Sheets CATLIN PROJECT:SAMPLED BY: CATLIN PROJECT # :DATE SAMPLED: CLIENT'S NAME: MW-4R 5.33 14.67 0.870 NMT 2.610 20 4.349 2 Method:Bailer Purge Start Time:13:30 Required Bails for 3 Well Volumes:11 Purge Stop Time:13:33 Required Bails for 5 Well Volumes:19 Was Well Purged Dry?YES Number of Bails Removed:4.25 Sample Time:13:44 Groundwater Removed (gal):1.0 Equipment Used: Time Specific Cond. (µS/cm) Dissolved Oxygen (mg/L) pH (Standard Units) ORP (mV) Temperature (Co) 13:30 0.06 8.03 4.56 403.35 20.45 13:31 73.61 6.24 5.20 393.60 20.61 13:32 77.69 3.26 5.02 398.98 20.52 13:33 77.70 3.12 4.96 400.53 20.54 13:34 0.06 5.12 5.11 395.80 20.50 Laboratory:Con-Test Analysis:6200B GROUNDWATER SAMPLING FORM Monitoring Well Information Well Data Volume of Groundwater in Well Well ID Water Column (ft below TOC) N. Newman 5/10/2023 NCDEQ-SLP, Linda Blalock Former Union 76 Gas Station 220217 Depth to Water (ft below TOC)One Well Volume (gal) Depth to Product (ft below TOC)Three Well Volumes (gal) Total Well Depth (ft)Five Well Volumes (gal) Laboratory Analysis Information Well Diameter (inches) Purging Information Information Geochemical Parameters Aqua Troll 600 Turbidity and Additional Sampling Notes Very turbid; red/brown. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 P:\2020\220217 DEQ SLP - Union 76 Gasoline Station (Former)\Field Notes\TA04\Sampling\Union 76_GW_Sampling_Sheets CATLIN PROJECT:SAMPLED BY: CATLIN PROJECT # :DATE SAMPLED: CLIENT'S NAME: MW-5 6.69 13.31 1.092 NMT 3.275 20 5.459 2 Method:Bailer Purge Start Time:13:00 Required Bails for 3 Well Volumes:14 Purge Stop Time:13:05 Required Bails for 5 Well Volumes:23 Was Well Purged Dry?No Number of Bails Removed:14 Sample Time:13:06 Groundwater Removed (gal):3.4 Equipment Used: Time Specific Cond. (µS/cm) Dissolved Oxygen (mg/L) pH (Standard Units) ORP (mV) Temperature (Co) 13:00 0.00 6.98 4.91 418.05 29.93 13:01 392.61 7.21 4.82 356.44 24.08 13:02 609.97 5.40 4.63 380.90 19.90 13:03 635.59 5.46 4.42 399.16 19.17 13:04 655.09 5.49 4.37 406.07 18.82 Laboratory:Con-Test Analysis:6200B GROUNDWATER SAMPLING FORM Monitoring Well Information Well Data Volume of Groundwater in Well Well ID Water Column (ft below TOC) N. Newman 5/10/2023 NCDEQ-SLP, Linda Blalock Former Union 76 Gas Station 220217 Depth to Water (ft below TOC)One Well Volume (gal) Depth to Product (ft below TOC)Three Well Volumes (gal) Total Well Depth (ft)Five Well Volumes (gal) Laboratory Analysis Information Well Diameter (inches) Purging Information Information Geochemical Parameters Aqua Troll 600 Turbidity and Additional Sampling Notes Moderate turbidity; light red- brown. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 P:\2020\220217 DEQ SLP - Union 76 Gasoline Station (Former)\Field Notes\TA04\Sampling\Union 76_GW_Sampling_Sheets CATLIN PROJECT:SAMPLED BY: CATLIN PROJECT # :DATE SAMPLED: CLIENT'S NAME: MW-6 7.71 12.29 1.258 NMT 3.775 20 6.291 2 Method:Bailer Purge Start Time:13:12 Required Bails for 3 Well Volumes:16 Purge Stop Time:13:18 Required Bails for 5 Well Volumes:27 Was Well Purged Dry?No Number of Bails Removed:16 Sample Time:13:19 Groundwater Removed (gal):3.8 Equipment Used: Time Specific Cond. (µS/cm) Dissolved Oxygen (mg/L) pH (Standard Units) ORP (mV) Temperature (Co) 13:11 1.20 8.08 3.90 420.22 19.75 13:12 0.06 7.95 5.11 375.14 19.84 13:13 85.64 5.45 5.23 372.90 19.25 13:14 84.11 5.42 5.20 376.52 19.03 13:15 78.07 5.68 5.15 381.08 19.02 13:16 77.01 5.87 5.15 383.41 19.04 Laboratory:Con-Test Analysis:6200B GROUNDWATER SAMPLING FORM Monitoring Well Information Well Data Volume of Groundwater in Well Well ID Water Column (ft below TOC) N. Newman 5/10/2023 NCDEQ-SLP, Linda Blalock Former Union 76 Gas Station 220217 Depth to Water (ft below TOC)One Well Volume (gal) Depth to Product (ft below TOC)Three Well Volumes (gal) Total Well Depth (ft)Five Well Volumes (gal) Laboratory Analysis Information Well Diameter (inches) Purging Information Information Geochemical Parameters Aqua Troll 600 Turbidity and Additional Sampling Notes Moderate turbidity; light brown. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 P:\2020\220217 DEQ SLP - Union 76 Gasoline Station (Former)\Field Notes\TA04\Sampling\Union 76_GW_Sampling_Sheets CATLIN PROJECT:SAMPLED BY: CATLIN PROJECT # :DATE SAMPLED: CLIENT'S NAME: MW-7 4.57 15.43 0.746 NMT 2.237 20 3.729 2 Method:Bailer Purge Start Time:13:54 Required Bails for 3 Well Volumes:10 Purge Stop Time:14:02 Required Bails for 5 Well Volumes:16 Was Well Purged Dry?No Number of bails removed 10 Sample Time:14:04 Groundwater Removed (gal):2.4 Equipment Used: Time Specific Cond. (µS/cm) Dissolved Oxygen (mg/L) pH (Standard Units) ORP (mV) Temperature (Co) 13:55 62.18 6.49 5.58 323.10 21.34 13:56 61.30 5.11 4.96 363.45 20.16 13:57 59.79 5.07 4.70 384.11 19.95 13:58 60.35 5.07 4.57 392.75 19.90 13:59 60.40 5.08 4.50 396.59 19.94 14:00 60.44 5.09 4.49 399.61 19.95 14:01 59.86 5.11 4.48 404.08 19.98 Laboratory:Con-Test Analysis:6200B GROUNDWATER SAMPLING FORM Monitoring Well Information Well Data Volume of Groundwater in Well Well ID Water Column (ft below TOC) N. Newman 5/10/2023 NCDEQ-SLP, Linda Blalock Former Union 76 Gas Station 220217 Depth to Water (ft below TOC)One Well Volume (gal) Depth to Product (ft below TOC)Three Well Volumes (gal) Total Well Depth (ft)Five Well Volumes (gal) Laboratory Analysis Information Well Diameter (inches) Purging Information Information Geochemical Parameters Aqua Troll 600 Turbidity and Additional Sampling Notes Turbid; light brown. NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 P:\2020\220217 DEQ SLP - Union 76 Gasoline Station (Former)\Field Notes\TA04\Sampling\Union 76_GW_Sampling_Sheets CATLIN PROJECT:SAMPLED BY: CATLIN PROJECT # :DATE SAMPLED: CLIENT'S NAME: DW-1 24.41 15.59 3.984 NMT 11.951 40 19.918 2 Method:Bailer Purge Start Time:10:58 Required Bails for 3 Well Volumes:49 Purge Stop Time:11:20 Required Bails for 5 Well Volumes:83 Was Well Purged Dry?No Number of Bails Removed:49 Sample Time:11:20 Groundwater Removed (gal):11.8 Equipment Used: Time Specific Cond. (µS/cm) Dissolved Oxygen (mg/L) pH (Standard Units) ORP (mV) Temperature (Co) 11:00 382.21 3.20 8.51 107.25 20.35 11:01 384.36 3.14 8.70 91.55 20.15 11:02 368.95 3.18 8.79 97.58 20.14 11:03 369.34 3.24 8.85 108.65 20.12 11:04 370.34 3.26 8.86 117.49 19.98 11:05 346.43 3.36 8.71 124.41 19.90 11:06 315.12 3.80 8.30 139.35 19.84 11:07 302.93 3.96 8.01 154.91 19.80 11:08 277.33 4.08 7.78 166.01 19.76 11:09 262.04 4.25 7.56 177.09 19.74 11:10 214.79 4.54 7.32 189.48 19.73 11:11 191.14 4.67 7.17 200.76 19.67 11:12 175.16 4.73 7.06 210.59 19.67 11:13 183.31 4.78 6.97 219.09 19.64 11:14 175.63 4.84 6.89 227.44 19.61 11:15 168.69 4.83 6.82 235.33 19.60 11:16 163.64 4.83 6.76 242.90 19.59 11:17 156.04 4.85 6.71 249.30 19.58 11:18 150.19 4.88 6.66 255.37 19.59 Laboratory:Con-Test Analysis:6200B GROUNDWATER SAMPLING FORM Monitoring Well Information Well Data Volume of Groundwater in Well Well ID Water Column (ft below TOC) N. Newman 5/10/2023 NCDEQ-SLP, Linda Blalock Former Union 76 Gas Station 220217 Depth to Water (ft below TOC)One Well Volume (gal) Depth to Product (ft below TOC)Three Well Volumes (gal) Total Well Depth (ft)Five Well Volumes (gal) Laboratory Analysis Information Well Diameter (inches) Purging Information Information Geochemical Parameters Aqua Troll 600 Turbidity and Additional Sampling Notes mild turbidity light brown NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Project No. 220217 CATLIN Engineers and Scientists July 2023 NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 APPENDIX D ENHANCED AFVR EMISSIONS CALCULATIONS Page 1 of 2 DESCRIBE SOIL IN THE SATURATED ZONE: Unknown IDENTIFY THE WELL AND THE I.D. OF EACH WELL USED FOR AFVR: MW-1, MW-2, MW-3R, and DW-1 (used for air sparging) PROVIDE BLOWER SPECIFICATIONS OF THE VACUUM TRUCK (cfm @ in Hg): 20" Hg COORDINATES USED FOR HUMIDITY RATIO CALCUALTIONS (Bwsw) (Lat, Long, Elev): 35.698863° Lat, -78.899473° Long, 390 Feet Elev. DRY STANDARD CUBIC FEET PER MINUTE (DSCFM) AIR FLOW CALCULATIONS (Qstd) Time Meas. Vacuum AVP Velocity Pipe ID Temp.RH Bwsw Bws Qstd flow (in Hg)(in Hg)(ft/min)(in)(°F)(%)(grainsH2O/lbAir)(% v/v)(DSCFM) 7:45 20 9.92 89 6 56 87 58.82898433 0.990 0.1888:00 20 9.92 114 6 59 100 75.62132604 0.992 0.1868:15 20 9.92 155 6 60 100 78.41939209 0.992 0.2448:30 20 9.92 244 6 96 100 268.5184185 0.998 0.106 8:45 20 9.92 188 6 104 100 347.4820822 0.998 0.062 9:00 20 9.92 168 6 107 100 382.3877694 0.998 0.050 9:15 20 9.92 173 6 108 100 394.7476079 0.998 0.050 9:30 20 9.92 192 6 122 100 614.1798478 0.999 0.0359:45 21 8.92 187 6 127 100 718.8416614 0.999 0.02910:15 21 8.92 144 6 132 100 841.718831 0.999 0.01910:45 21 8.92 201 6 141 100 1121.537327 0.999 0.019 11:15 21 8.92 227 6 143 100 1196.397238 0.999 0.020 11:45 21 8.92 219 6 146 100 1319.204808 1.000 0.018 12:15 20 9.92 183 6 149 100 1456.265729 1.000 0.013 12:45 20 9.92 142 6 155 100 1782.305939 1.000 0.00813:15 20 9.92 174 6 156 100 1844.596821 1.000 0.01013:45 20 9.92 157 6 158 100 1977.146455 1.000 0.00814:15 20 9.92 142 6 159 100 2047.710242 1.000 0.007 14:45 20 9.92 254 6 158 100 1977.146455 1.000 0.013 15:15 20 9.92 201 6 114 100 477.3692697 0.999 0.047 15:45 20 9.92 187 6 160 100 2121.356476 1.000 0.009 NOTESAVP = Absolute Vacuum Pressure Qstd = Flow at DSCFM Measured Vacuum = The level of vacuum being applied (should be recorded from the vacuum truck tank in inches of Hg) Velocity = The rate at which air flow is measured at the blower discharge piping (anemometer or pitot tube) Pipe ID = The inside diameter of the blower discharge piping (from the vacuum truck) Temperature = The temperature of the air stream exiting the blower discharge piping (dry bulb temp., in °F) RH = The % relative humidity of the air stream exiting the blower discharge piping Bwsw = Humidity Ratio (i.e. grains of water per lb of dry air, derived from the Psychrometric chart or calculator (dry bulb temp. vs. RH) Bws = water vapor % by volume EQUATIONS AVP = Standard Pressure (29.92 in Hg) - Measured Vacuum Bws = (Bwsw/18 lb-mole H2O)/[(1/28.84 lb-mole dry air) + (Bwsw/18 lb-mole H2O)] Qstd = (1-Water Vapor) * velocity * [PI * (diameter/24)2] * [528°R/(Temp + 460)] * (AVP/29.92) INDICATE AVERAGE HYDRAULIC CONDUCTIVITY (if known): Unknown AGGRESSIVE FLUID VAPOR RECOVERY (AFVR) SITE NAME: Former Union 76 Gasoline Station INCIDENT NUMBER: 26571 AVERAGE DEPTH TO GROUNDWATER: 16.7' Below Top of Casing SDC Group, Inc.; AFVR_field calc_4-11-23\Calc AFVR Calculations CATLIN Engineers and Scientists July 2023 Page 2 of 2 EMISSION CALCULATIONS Elapsed QstdTimeFlow PPMmeasured PPMwet PPMdry K PPMconc Cc:m Cc PMRc PMRg PMR (min)(DSCFM)(ppm)(#C - gas)(mg/dsm3)(lb/dscf)(lb/hr)(lb/hr)(lb) 0 0.188 3209 3209 305680 4 1222720 610090 0.038 0.429 0.496 0.000 15 0.186 1117 1117 136455 4 545821 272343 0.017 0.190 0.220 0.055 30 0.244 919 919 116387 4 465548 232291 0.015 0.212 0.246 0.061 45 0.106 647 647 279003 4 1116013 556848 0.035 0.220 0.255 0.064 60 0.062 747 747 416634 4 1666538 831538 0.052 0.193 0.223 0.056750.050 765 765 469458 4 1877831 936965 0.058 0.176 0.203 0.051900.050 761 761 482073 4 1928293 962144 0.060 0.180 0.208 0.052 105 0.035 1035 1035 1019529 4 4078118 2034823 0.127 0.265 0.306 0.153 120 0.029 733 733 844961 4 3379846 1686412 0.105 0.181 0.209 0.052 150 0.019 577 577 778731 4 3114924 1554227 0.097 0.109 0.126 0.094 180 0.019 569 569 1023035 4 4092139 2041819 0.127 0.147 0.171 0.085 210 0.020 433 433 830448 4 3321793 1657446 0.103 0.126 0.146 0.0732400.018 381 381 805685 4 3222741 1608023 0.100 0.107 0.124 0.0622700.013 379 379 884685 4 3538740 1765695 0.110 0.088 0.102 0.051 300 0.008 390 390 1114094 4 4456374 2223559 0.139 0.070 0.081 0.081 330 0.010 405 405 1197364 4 4789456 2389753 0.149 0.089 0.103 0.051 360 0.008 433 433 1372103 4 5488410 2738505 0.171 0.085 0.099 0.049 390 0.007 437 437 1434185 4 5736738 2862411 0.179 0.078 0.090 0.045 420 0.013 418 418 1324570 4 5298280 2643637 0.165 0.133 0.154 0.0774500.047 424 424 324721 4 1298884 648093 0.040 0.115 0.133 0.0674800.009 410 410 1393953 4 5575811 2782114 0.174 0.096 0.111 0.055 Total emissions in pounds = 1.335 Total emissions in gallons = 0.214 NOTES PPMmeasured = Actual measurements (ppm) taken with a OVA, PID, or TVA at the blower discharge piping PPMwet = "wet" concentration PPMdry = "dry" concentration K = Number of carbons in calibration gas: (Methane K = 1, or Propane K = 3, or Isobutene K = 4, or Hexane K = 6) PPMc= PPMv, Volumetric concentration of VOC emissions as carbon, dry basis at STP Cc:m = mg/dsm3, mass concentration of VOC emissions as carbon Mc = 12.01 mg/mg-mole, molecular weight of carbon K3 = 24.07 dsm3/106 mg-mole, mass to volume conversion factor at STP Cc = lb/dcsf, mass concentration of VOC emissions as carbon, dry basis at STP PMRc = lb/hr, pollutant mass removal rate of VOCs as carbon PMRg = lb/hr, pollutant mass removal rate of VOCs as gasoline PMR = lb, pollutant mass removal of VOCs as gasoline EQUATIONS PPMwet = PPMmeasured PPMdry = (PPMwet)/(1-Bws) PPMconc = (PPMdry)(K) Cc:m = (PPMconc)(Mc / K3) Cc = (Cc:m)(62.43x10-9 lb-m3/mg-ft3) PMRc = (Cc)(Qstd)(60 min/hr) PMRg = (PMRc)(Mg/Mcg) PMR = (PMRg)(#minutes/60) SDC Group, Inc.; AFVR_field calc_4-11-23\Calc AFVR Calculations CATLIN Engineers and Scientists July 2023 NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 APPENDIX E DISPOSAL DOCUMENTS NCDEQ; 26571_Former Union 76 Gasoline Station CATLIN Engineers and Scientists CATLIN Project No. 220217 July 2023 APPENDIX F LABORATORY ANALYTICAL REPORT AND CHAIN OF CUSTODY DOCUMENT 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 May 22, 2023 Sean O’Neil CATLIN Engineers & Scientists 1044 Washington Street Raleigh, NC 27605 Project Location: Apex, NC Client Job Number: Project Number: 220217.04 Laboratory Work Order Number: 23E1563 Enclosed are results of analyses for samples as received by the laboratory on May 11, 2023. If you have any questions concerning this report, please feel free to contact me. Sincerely, Kaitlyn A. Feliciano Project Manager Table of Contents Sample Summary 3 Hits Only Report 4 Case Narrative 7 Sample Results 8 23E1563-01 8 23E1563-02 10 23E1563-03 12 23E1563-04 14 23E1563-05 16 23E1563-06 18 23E1563-07 20 23E1563-08 22 23E1563-09 24 23E1563-10 26 Sample Preparation Information 28 QC Data 29 Volatile Organic Compounds by GC/MS 29 B340215 29 B340343 33 B340602 37 Flag/Qualifier Summary 41 Certifications 42 Chain of Custody/Sample Receipt 44 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 ANALYTICAL SUMMARY 5/22/2023 CATLIN Engineers & Scientists 1044 Washington Street Raleigh, NC 27605 ATTN: Sean O’Neil 220217.04 23E1563 The results of analyses performed on the following samples submitted to the CON-TEST Analytical Laboratory are found in this report. PROJECT LOCATION: PURCHASE ORDER NUMBER: PROJECT NUMBER: REPORT DATE: WORK ORDER NUMBER: FIELD SAMPLE #LAB ID:MATRIX TESTSAMPLE DESCRIPTION SUB LAB Apex, NC 230510-7 MW-1 23E1563-01 Ground Water SM21-23 6200B MW-2 23E1563-02 Ground Water SM21-23 6200B MW-3R 23E1563-03 Ground Water SM21-23 6200B MW-4R 23E1563-04 Ground Water SM21-23 6200B MW-5 23E1563-05 Ground Water SM21-23 6200B MW-6 23E1563-06 Ground Water SM21-23 6200B MW-7 23E1563-07 Ground Water SM21-23 6200B DW-1 23E1563-08 Ground Water SM21-23 6200B Eq. Rinse 23E1563-09 Ground Water SM21-23 6200B Trip Blank 23E1563-10 Trip Blank Water SM21-23 6200B [TOC_1]Sample Summary[TOC] 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 [TOC_1]Hits Only Report[TOC]EXECUTIVE SUMMARY Client ID:Lab ID:23E1563-06MW-6 No Results Detected Con-Test does not accept liability for the consequences of any actions taken solely on the basis of the information provided in the Executive Summary section of this report. Users must review this report in its entirety to determine data usability and assessment. 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 EXECUTIVE SUMMARY Client ID:Lab ID: Analyte Results/Qual RL Units Method 23E1563-01MW-1 DL 1,2,4-Trimethylbenzene 130 10 g/L SM21-23 6200B4.0 1,3,5-Trimethylbenzene 57 10 g/L SM21-23 6200B3.0 2-Butanone (MEK)51 100 g/L SM21-23 6200BJ34 Acetone 59 1000 g/L SM21-23 6200BJ40 Benzene 1400 10 g/L SM21-23 6200B3.7 Diisopropyl Ether (DIPE)8.0 10 g/L SM21-23 6200BJ4.0 Ethylbenzene 150 10 g/L SM21-23 6200B4.4 Isopropylbenzene (Cumene)8.6 10 g/L SM21-23 6200BJ3.0 m+p Xylene 750 20 g/L SM21-23 6200B9.8 Naphthalene 28 10 g/L SM21-23 6200B7.6 n-Butylbenzene 3.0 10 g/L SM21-23 6200BJ3.0 n-Propylbenzene 9.4 10 g/L SM21-23 6200BJ2.5 o-Xylene 380 10 g/L SM21-23 6200B4.9 p-Isopropyltoluene (p-Cymene)3.6 10 g/L SM21-23 6200BJ2.5 Toluene 1400 10 g/L SM21-23 6200B4.5 Client ID:Lab ID: Analyte Results/Qual RL Units Method 23E1563-02MW-2 DL 1,2-Dichloroethane 2.1 0.50 g/L SM21-23 6200B0.30 Acetone 2.6 50 g/L SM21-23 6200BJ2.0 Client ID:Lab ID: Analyte Results/Qual RL Units Method 23E1563-03MW-3R DL 1,2,4-Trimethylbenzene 130 2.0 g/L SM21-23 6200B0.80 1,2-Dibromoethane (EDB)8.5 2.0 g/L SM21-23 6200B0.64 1,2-Dichloroethane 45 4.0 g/L SM21-23 6200B1.2 1,3,5-Trimethylbenzene 81 2.0 g/L SM21-23 6200B0.60 2-Hexanone (MBK)17 20 g/L SM21-23 6200BJ4.8 4-Methyl-2-pentanone (MIBK)10 20 g/L SM21-23 6200BJ5.3 Benzene 290 2.0 g/L SM21-23 6200B0.74 Diisopropyl Ether (DIPE)1.6 2.0 g/L SM21-23 6200BJ0.81 Ethylbenzene 23 2.0 g/L SM21-23 6200B0.88 Isopropylbenzene (Cumene)2.3 2.0 g/L SM21-23 6200B0.60 m+p Xylene 250 4.0 g/L SM21-23 6200B2.0 Naphthalene 23 2.0 g/L SM21-23 6200B1.5 n-Butylbenzene 1.7 2.0 g/L SM21-23 6200BJ0.60 n-Propylbenzene 2.1 2.0 g/L SM21-23 6200B0.50 o-Xylene 230 2.0 g/L SM21-23 6200B0.97 p-Isopropyltoluene (p-Cymene)1.5 2.0 g/L SM21-23 6200BJ0.51 sec-Butylbenzene 0.92 2.0 g/L SM21-23 6200BJ0.51 Toluene 49 2.0 g/L SM21-23 6200B0.89 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Client ID:Lab ID: Analyte Results/Qual RL Units Method 23E1563-04MW-4R DL 1,2,4-Trimethylbenzene 2000 50 g/L SM21-23 6200B20 1,3,5-Trimethylbenzene 620 50 g/L SM21-23 6200B15 2-Butanone (MEK)290 500 g/L SM21-23 6200BJ170 Acetone 230 5000 g/L SM21-23 6200BJ200 Benzene 840 50 g/L SM21-23 6200B18 Ethylbenzene 1800 50 g/L SM21-23 6200B22 Isopropylbenzene (Cumene)99 50 g/L SM21-23 6200B15 m+p Xylene 7700 100 g/L SM21-23 6200B49 Naphthalene 430 50 g/L SM21-23 6200B38 n-Butylbenzene 47 50 g/L SM21-23 6200BJ15 n-Propylbenzene 230 50 g/L SM21-23 6200B12 o-Xylene 4200 50 g/L SM21-23 6200B24 Toluene 9900 50 g/L SM21-23 6200B22 Client ID:Lab ID: Analyte Results/Qual RL Units Method 23E1563-05MW-5 DL Acetone 2.7 50 g/L SM21-23 6200BJ2.0 Client ID:Lab ID: Analyte Results/Qual RL Units Method 23E1563-07MW-7 DL Acetone 2.9 50 g/L SM21-23 6200BJ2.0 Client ID:Lab ID: Analyte Results/Qual RL Units Method 23E1563-08DW-1 DL 1,2-Dichloroethane 0.82 0.50 g/L SM21-23 6200B0.30 Acetone 3.4 50 g/L SM21-23 6200BJ2.0 p-Isopropyltoluene (p-Cymene)0.34 0.50 g/L SM21-23 6200BJ0.13 Client ID:Lab ID: Analyte Results/Qual RL Units Method 23E1563-09Eq. Rinse DL Acetone 9.6 50 g/L SM21-23 6200BJ2.0 Client ID:Lab ID: Analyte Results/Qual RL Units Method 23E1563-10Trip Blank DL Acetone 2.9 50 g/L SM21-23 6200BJ2.0 Con-Test does not accept liability for the consequences of any actions taken solely on the basis of the information provided in the Executive Summary section of this report. Users must review this report in its entirety to determine data usability and assessment. 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 CASE NARRATIVE SUMMARY All reported results are within defined laboratory quality control objectives unless listed below or otherwise qualified in this report. For method 6200B elevated reporting limits for samples 23E1563-01,03+04 due to high concentrations of target compounds. [TOC_1]Case Narrative[TOC] SM21-23 6200B Qualifications: Laboratory fortified blank duplicate RPD is outside of control limits. Reduced precision is anticipated for any reported value for this compound. Analyte & Samples(s) Qualified: R-05 1,2,3-Trichloropropane 23E1563-01[MW-1], 23E1563-04[MW-4R], 23E1563-05[MW-5], 23E1563-06[MW-6], 23E1563-07[MW-7], 23E1563-08[DW-1], 23E1563-09[Eq. Rinse], 23E1563-10[Trip Blank], B340215-BLK1, B340215-BS1, B340215-BSD1, S087472-CCV1 Elevated reporting limit due to high concentration of target compounds. Analyte & Samples(s) Qualified: RL-11 23E1563-01[MW-1], 23E1563-03[MW-3R], 23E1563-04[MW-4R] The results of analyses reported only relate to samples submitted to the Con-Test Analytical Laboratory for testing. I certify that the analyses listed above, unless specifically listed as subcontracted, if any, were performed under my direction according to the approved methodologies listed in this document, and that based upon my inquiry of those individuals immediately responsible for obtaining the information, the material contained in this report is, to the best of my knowledge and belief, accurate and complete. Meghan E. Kelley Reporting Specialist 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-01 Field Sample #: MW-1 Sample Matrix: Ground Water Sampled: 5/10/2023 13:48 [TOC_2]23E1563-01[TOC] AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Sample Flags: RL-11 Volatile Organic Compounds by GC/MS 59 1000 5/16/23 3:49 MFFg/L40 5/15/23SM21-23 6200B20JAcetone 1400 10 5/16/23 3:49 MFFg/L3.7 5/15/23SM21-23 6200B20Benzene ND 10 5/16/23 3:49 MFFg/L3.0 5/15/23SM21-23 6200B20Bromobenzene ND 10 5/16/23 3:49 MFFg/L5.7 5/15/23SM21-23 6200B20Bromochloromethane ND 10 5/16/23 3:49 MFFg/L3.2 5/15/23SM21-23 6200B20Bromodichloromethane ND 10 5/16/23 3:49 MFFg/L8.2 5/15/23SM21-23 6200B20Bromoform ND 40 5/16/23 3:49 MFFg/L26 5/15/23SM21-23 6200B20Bromomethane 51 100 5/16/23 3:49 MFFg/L34 5/15/23SM21-23 6200B20J2-Butanone (MEK) 3.0 10 5/16/23 3:49 MFFg/L3.0 5/15/23SM21-23 6200B20Jn-Butylbenzene ND 10 5/16/23 3:49 MFFg/L2.5 5/15/23SM21-23 6200B20sec-Butylbenzene ND 10 5/16/23 3:49 MFFg/L2.8 5/15/23SM21-23 6200B20tert-Butylbenzene ND 10 5/16/23 3:49 MFFg/L3.3 5/15/23SM21-23 6200B20Carbon Tetrachloride ND 10 5/16/23 3:49 MFFg/L2.4 5/15/23SM21-23 6200B20Chlorobenzene ND 1000 5/16/23 3:49 MFFg/L410 5/15/23SM21-23 6200B20Ethanol ND 10 5/16/23 3:49 MFFg/L4.0 5/15/23SM21-23 6200B20Chlorodibromomethane ND 10 5/16/23 3:49 MFFg/L6.8 5/15/23SM21-23 6200B20Chloroethane ND 10 5/16/23 3:49 MFFg/L2.8 5/15/23SM21-23 6200B20Chloroform ND 12 5/16/23 3:49 MFFg/L10 5/15/23SM21-23 6200B20Chloromethane ND 10 5/16/23 3:49 MFFg/L3.1 5/15/23SM21-23 6200B202-Chlorotoluene ND 10 5/16/23 3:49 MFFg/L3.1 5/15/23SM21-23 6200B204-Chlorotoluene ND 10 5/16/23 3:49 MFFg/L3.2 5/15/23SM21-23 6200B201,2-Dibromoethane (EDB) ND 10 5/16/23 3:49 MFFg/L2.6 5/15/23SM21-23 6200B201,2-Dichlorobenzene ND 10 5/16/23 3:49 MFFg/L2.7 5/15/23SM21-23 6200B201,3-Dichlorobenzene ND 10 5/16/23 3:49 MFFg/L2.6 5/15/23SM21-23 6200B201,4-Dichlorobenzene ND 10 5/16/23 3:49 MFFg/L3.2 5/15/23SM21-23 6200B20Dichlorodifluoromethane (Freon 12) ND 10 5/16/23 3:49 MFFg/L2.7 5/15/23SM21-23 6200B201,1-Dichloroethane ND 10 5/16/23 3:49 MFFg/L6.1 5/15/23SM21-23 6200B201,2-Dichloroethane ND 10 5/16/23 3:49 MFFg/L2.8 5/15/23SM21-23 6200B201,1-Dichloroethylene ND 10 5/16/23 3:49 MFFg/L2.8 5/15/23SM21-23 6200B20cis-1,2-Dichloroethylene ND 10 5/16/23 3:49 MFFg/L3.4 5/15/23SM21-23 6200B20trans-1,2-Dichloroethylene ND 10 5/16/23 3:49 MFFg/L3.9 5/15/23SM21-23 6200B201,2-Dichloropropane ND 10 5/16/23 3:49 MFFg/L2.3 5/15/23SM21-23 6200B201,3-Dichloropropane ND 10 5/16/23 3:49 MFFg/L7.0 5/15/23SM21-23 6200B202,2-Dichloropropane ND 10 5/16/23 3:49 MFFg/L3.0 5/15/23SM21-23 6200B201,1-Dichloropropene ND 10 5/16/23 3:49 MFFg/L3.3 5/15/23SM21-23 6200B20cis-1,3-Dichloropropene ND 10 5/16/23 3:49 MFFg/L2.8 5/15/23SM21-23 6200B20trans-1,3-Dichloropropene 8.0 10 5/16/23 3:49 MFFg/L4.0 5/15/23SM21-23 6200B20JDiisopropyl Ether (DIPE) 150 10 5/16/23 3:49 MFFg/L4.4 5/15/23SM21-23 6200B20Ethylbenzene ND 100 5/16/23 3:49 MFFg/L24 5/15/23SM21-23 6200B202-Hexanone (MBK) 8.6 10 5/16/23 3:49 MFFg/L3.0 5/15/23SM21-23 6200B20JIsopropylbenzene (Cumene) 3.6 10 5/16/23 3:49 MFFg/L2.5 5/15/23SM21-23 6200B20Jp-Isopropyltoluene (p-Cymene) ND 10 5/16/23 3:49 MFFg/L3.4 5/15/23SM21-23 6200B20Methyl tert-Butyl Ether (MTBE) ND 100 5/16/23 3:49 MFFg/L3.5 5/15/23SM21-23 6200B20Methylene Chloride ND 100 5/16/23 3:49 MFFg/L26 5/15/23SM21-23 6200B204-Methyl-2-pentanone (MIBK) [TOC_1]Sample Results[TOC] 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-01 Field Sample #: MW-1 Sample Matrix: Ground Water Sampled: 5/10/2023 13:48 AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Sample Flags: RL-11 Volatile Organic Compounds by GC/MS 28 10 5/16/23 3:49 MFFg/L7.6 5/15/23SM21-23 6200B20Naphthalene 9.4 10 5/16/23 3:49 MFFg/L2.5 5/15/23SM21-23 6200B20Jn-Propylbenzene ND 10 5/16/23 3:49 MFFg/L3.0 5/15/23SM21-23 6200B20Styrene ND 10 5/16/23 3:49 MFFg/L2.7 5/15/23SM21-23 6200B201,1,2,2-Tetrachloroethane ND 10 5/16/23 3:49 MFFg/L3.4 5/15/23SM21-23 6200B20Tetrachloroethylene 1400 10 5/16/23 3:49 MFFg/L4.5 5/15/23SM21-23 6200B20Toluene ND 20 5/16/23 3:49 MFFg/L6.8 5/15/23SM21-23 6200B201,2,3-Trichlorobenzene ND 20 5/16/23 3:49 MFFg/L6.0 5/15/23SM21-23 6200B201,2,4-Trichlorobenzene ND 10 5/16/23 3:49 MFFg/L3.0 5/15/23SM21-23 6200B201,1,1-Trichloroethane ND 10 5/16/23 3:49 MFFg/L3.8 5/15/23SM21-23 6200B201,1,2-Trichloroethane ND 10 5/16/23 3:49 MFFg/L3.5 5/15/23SM21-23 6200B20Trichloroethylene ND 10 5/16/23 3:49 MFFg/L3.1 5/15/23SM21-23 6200B20Trichlorofluoromethane (Freon 11) ND 10 5/16/23 3:49 MFFg/L5.5 5/15/23SM21-23 6200B20R-051,2,3-Trichloropropane 130 10 5/16/23 3:49 MFFg/L4.0 5/15/23SM21-23 6200B201,2,4-Trimethylbenzene 57 10 5/16/23 3:49 MFFg/L3.0 5/15/23SM21-23 6200B201,3,5-Trimethylbenzene ND 400 5/16/23 3:49 MFFg/L33 5/15/23SM21-23 6200B20Vinyl Acetate ND 10 5/16/23 3:49 MFFg/L4.7 5/15/23SM21-23 6200B20Vinyl Chloride 750 20 5/16/23 3:49 MFFg/L9.8 5/15/23SM21-23 6200B20m+p Xylene 380 10 5/16/23 3:49 MFFg/L4.9 5/15/23SM21-23 6200B20o-Xylene Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 89.6 5/16/23 3:4970-130 Toluene-d8 97.1 5/16/23 3:4970-130 4-Bromofluorobenzene 94.7 5/16/23 3:4970-130 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-02 Field Sample #: MW-2 Sample Matrix: Ground Water Sampled: 5/10/2023 11:44 [TOC_2]23E1563-02[TOC] AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS 2.6 50 5/19/23 0:16 MFFg/L2.0 5/18/23SM21-23 6200B1JAcetone ND 0.50 5/19/23 0:16 MFFg/L0.18 5/18/23SM21-23 6200B1Benzene ND 0.50 5/19/23 0:16 MFFg/L0.15 5/18/23SM21-23 6200B1Bromobenzene ND 0.50 5/19/23 0:16 MFFg/L0.28 5/18/23SM21-23 6200B1Bromochloromethane ND 0.50 5/19/23 0:16 MFFg/L0.16 5/18/23SM21-23 6200B1Bromodichloromethane ND 0.50 5/19/23 0:16 MFFg/L0.41 5/18/23SM21-23 6200B1Bromoform ND 2.0 5/19/23 0:16 MFFg/L1.3 5/18/23SM21-23 6200B1Bromomethane ND 5.0 5/19/23 0:16 MFFg/L1.7 5/18/23SM21-23 6200B12-Butanone (MEK) ND 0.50 5/19/23 0:16 MFFg/L0.15 5/18/23SM21-23 6200B1n-Butylbenzene ND 0.50 5/19/23 0:16 MFFg/L0.13 5/18/23SM21-23 6200B1sec-Butylbenzene ND 0.50 5/19/23 0:16 MFFg/L0.14 5/18/23SM21-23 6200B1tert-Butylbenzene ND 0.50 5/19/23 0:16 MFFg/L0.16 5/18/23SM21-23 6200B1Carbon Tetrachloride ND 0.50 5/19/23 0:16 MFFg/L0.12 5/18/23SM21-23 6200B1Chlorobenzene ND 50 5/19/23 0:16 MFFg/L20 5/18/23SM21-23 6200B1Ethanol ND 0.50 5/19/23 0:16 MFFg/L0.20 5/18/23SM21-23 6200B1Chlorodibromomethane ND 0.50 5/19/23 0:16 MFFg/L0.34 5/18/23SM21-23 6200B1Chloroethane ND 0.50 5/19/23 0:16 MFFg/L0.14 5/18/23SM21-23 6200B1Chloroform ND 0.60 5/19/23 0:16 MFFg/L0.50 5/18/23SM21-23 6200B1Chloromethane ND 0.50 5/19/23 0:16 MFFg/L0.15 5/18/23SM21-23 6200B12-Chlorotoluene ND 0.50 5/19/23 0:16 MFFg/L0.15 5/18/23SM21-23 6200B14-Chlorotoluene ND 0.50 5/19/23 0:16 MFFg/L0.16 5/18/23SM21-23 6200B11,2-Dibromoethane (EDB) ND 0.50 5/19/23 0:16 MFFg/L0.13 5/18/23SM21-23 6200B11,2-Dichlorobenzene ND 0.50 5/19/23 0:16 MFFg/L0.14 5/18/23SM21-23 6200B11,3-Dichlorobenzene ND 0.50 5/19/23 0:16 MFFg/L0.13 5/18/23SM21-23 6200B11,4-Dichlorobenzene ND 0.50 5/19/23 0:16 MFFg/L0.16 5/18/23SM21-23 6200B1Dichlorodifluoromethane (Freon 12) ND 0.50 5/19/23 0:16 MFFg/L0.14 5/18/23SM21-23 6200B11,1-Dichloroethane 2.1 0.50 5/19/23 0:16 MFFg/L0.30 5/18/23SM21-23 6200B11,2-Dichloroethane ND 0.50 5/19/23 0:16 MFFg/L0.14 5/18/23SM21-23 6200B11,1-Dichloroethylene ND 0.50 5/19/23 0:16 MFFg/L0.14 5/18/23SM21-23 6200B1cis-1,2-Dichloroethylene ND 0.50 5/19/23 0:16 MFFg/L0.17 5/18/23SM21-23 6200B1trans-1,2-Dichloroethylene ND 0.50 5/19/23 0:16 MFFg/L0.19 5/18/23SM21-23 6200B11,2-Dichloropropane ND 0.50 5/19/23 0:16 MFFg/L0.12 5/18/23SM21-23 6200B11,3-Dichloropropane ND 0.50 5/19/23 0:16 MFFg/L0.35 5/18/23SM21-23 6200B12,2-Dichloropropane ND 0.50 5/19/23 0:16 MFFg/L0.15 5/18/23SM21-23 6200B11,1-Dichloropropene ND 0.50 5/19/23 0:16 MFFg/L0.16 5/18/23SM21-23 6200B1cis-1,3-Dichloropropene ND 0.50 5/19/23 0:16 MFFg/L0.14 5/18/23SM21-23 6200B1trans-1,3-Dichloropropene ND 0.50 5/19/23 0:16 MFFg/L0.20 5/18/23SM21-23 6200B1Diisopropyl Ether (DIPE) ND 0.50 5/19/23 0:16 MFFg/L0.22 5/18/23SM21-23 6200B1Ethylbenzene ND 5.0 5/19/23 0:16 MFFg/L1.2 5/18/23SM21-23 6200B12-Hexanone (MBK) ND 0.50 5/19/23 0:16 MFFg/L0.15 5/18/23SM21-23 6200B1Isopropylbenzene (Cumene) ND 0.50 5/19/23 0:16 MFFg/L0.13 5/18/23SM21-23 6200B1p-Isopropyltoluene (p-Cymene) ND 0.50 5/19/23 0:16 MFFg/L0.17 5/18/23SM21-23 6200B1Methyl tert-Butyl Ether (MTBE) ND 5.0 5/19/23 0:16 MFFg/L0.18 5/18/23SM21-23 6200B1Methylene Chloride ND 5.0 5/19/23 0:16 MFFg/L1.3 5/18/23SM21-23 6200B14-Methyl-2-pentanone (MIBK) 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-02 Field Sample #: MW-2 Sample Matrix: Ground Water Sampled: 5/10/2023 11:44 AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS ND 0.50 5/19/23 0:16 MFFg/L0.38 5/18/23SM21-23 6200B1Naphthalene ND 0.50 5/19/23 0:16 MFFg/L0.12 5/18/23SM21-23 6200B1n-Propylbenzene ND 0.50 5/19/23 0:16 MFFg/L0.15 5/18/23SM21-23 6200B1Styrene ND 0.50 5/19/23 0:16 MFFg/L0.14 5/18/23SM21-23 6200B11,1,2,2-Tetrachloroethane ND 0.50 5/19/23 0:16 MFFg/L0.17 5/18/23SM21-23 6200B1Tetrachloroethylene ND 0.50 5/19/23 0:16 MFFg/L0.22 5/18/23SM21-23 6200B1Toluene ND 1.0 5/19/23 0:16 MFFg/L0.34 5/18/23SM21-23 6200B11,2,3-Trichlorobenzene ND 1.0 5/19/23 0:16 MFFg/L0.30 5/18/23SM21-23 6200B11,2,4-Trichlorobenzene ND 0.50 5/19/23 0:16 MFFg/L0.15 5/18/23SM21-23 6200B11,1,1-Trichloroethane ND 0.50 5/19/23 0:16 MFFg/L0.19 5/18/23SM21-23 6200B11,1,2-Trichloroethane ND 0.50 5/19/23 0:16 MFFg/L0.17 5/18/23SM21-23 6200B1Trichloroethylene ND 0.50 5/19/23 0:16 MFFg/L0.15 5/18/23SM21-23 6200B1Trichlorofluoromethane (Freon 11) ND 0.50 5/19/23 0:16 MFFg/L0.28 5/18/23SM21-23 6200B11,2,3-Trichloropropane ND 0.50 5/19/23 0:16 MFFg/L0.20 5/18/23SM21-23 6200B11,2,4-Trimethylbenzene ND 0.50 5/19/23 0:16 MFFg/L0.15 5/18/23SM21-23 6200B11,3,5-Trimethylbenzene ND 20 5/19/23 0:16 MFFg/L1.7 5/18/23SM21-23 6200B1Vinyl Acetate ND 0.50 5/19/23 0:16 MFFg/L0.24 5/18/23SM21-23 6200B1Vinyl Chloride ND 1.0 5/19/23 0:16 MFFg/L0.49 5/18/23SM21-23 6200B1m+p Xylene ND 0.50 5/19/23 0:16 MFFg/L0.24 5/18/23SM21-23 6200B1o-Xylene Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 97.8 5/19/23 0:1670-130 Toluene-d8 98.7 5/19/23 0:1670-130 4-Bromofluorobenzene 93.7 5/19/23 0:1670-130 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-03 Field Sample #: MW-3R Sample Matrix: Ground Water Sampled: 5/10/2023 14:20 [TOC_2]23E1563-03[TOC] AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Sample Flags: RL-11 Volatile Organic Compounds by GC/MS ND 200 5/18/23 6:34 EEHg/L8.0 5/15/23SM21-23 6200B4Acetone 290 2.0 5/18/23 6:34 EEHg/L0.74 5/15/23SM21-23 6200B4Benzene ND 2.0 5/18/23 6:34 EEHg/L0.59 5/15/23SM21-23 6200B4Bromobenzene ND 2.0 5/18/23 6:34 EEHg/L1.1 5/15/23SM21-23 6200B4Bromochloromethane ND 2.0 5/18/23 6:34 EEHg/L0.63 5/15/23SM21-23 6200B4Bromodichloromethane ND 2.0 5/18/23 6:34 EEHg/L1.6 5/15/23SM21-23 6200B4Bromoform ND 8.0 5/18/23 6:34 EEHg/L5.3 5/15/23SM21-23 6200B4Bromomethane ND 20 5/18/23 6:34 EEHg/L6.7 5/15/23SM21-23 6200B42-Butanone (MEK) 1.7 2.0 5/18/23 6:34 EEHg/L0.60 5/15/23SM21-23 6200B4Jn-Butylbenzene 0.92 2.0 5/18/23 6:34 EEHg/L0.51 5/15/23SM21-23 6200B4Jsec-Butylbenzene ND 2.0 5/18/23 6:34 EEHg/L0.57 5/15/23SM21-23 6200B4tert-Butylbenzene ND 2.0 5/18/23 6:34 EEHg/L0.65 5/15/23SM21-23 6200B4Carbon Tetrachloride ND 2.0 5/18/23 6:34 EEHg/L0.48 5/15/23SM21-23 6200B4Chlorobenzene ND 200 5/18/23 6:34 EEHg/L81 5/15/23SM21-23 6200B4Ethanol ND 2.0 5/18/23 6:34 EEHg/L0.80 5/15/23SM21-23 6200B4Chlorodibromomethane ND 2.0 5/18/23 6:34 EEHg/L1.4 5/15/23SM21-23 6200B4Chloroethane ND 2.0 5/18/23 6:34 EEHg/L0.56 5/15/23SM21-23 6200B4Chloroform ND 2.4 5/18/23 6:34 EEHg/L2.0 5/15/23SM21-23 6200B4Chloromethane ND 2.0 5/18/23 6:34 EEHg/L0.62 5/15/23SM21-23 6200B42-Chlorotoluene ND 2.0 5/18/23 6:34 EEHg/L0.62 5/15/23SM21-23 6200B44-Chlorotoluene 8.5 2.0 5/18/23 6:34 EEHg/L0.64 5/15/23SM21-23 6200B41,2-Dibromoethane (EDB) ND 2.0 5/18/23 6:34 EEHg/L0.52 5/15/23SM21-23 6200B41,2-Dichlorobenzene ND 2.0 5/18/23 6:34 EEHg/L0.55 5/15/23SM21-23 6200B41,3-Dichlorobenzene ND 2.0 5/18/23 6:34 EEHg/L0.51 5/15/23SM21-23 6200B41,4-Dichlorobenzene ND 2.0 5/18/23 6:34 EEHg/L0.64 5/15/23SM21-23 6200B4Dichlorodifluoromethane (Freon 12) ND 2.0 5/18/23 6:34 EEHg/L0.55 5/15/23SM21-23 6200B41,1-Dichloroethane 45 4.0 5/18/23 6:34 EEHg/L1.2 5/15/23SM21-23 6200B41,2-Dichloroethane ND 2.0 5/18/23 6:34 EEHg/L0.56 5/15/23SM21-23 6200B41,1-Dichloroethylene ND 2.0 5/18/23 6:34 EEHg/L0.56 5/15/23SM21-23 6200B4cis-1,2-Dichloroethylene ND 2.0 5/18/23 6:34 EEHg/L0.69 5/15/23SM21-23 6200B4trans-1,2-Dichloroethylene ND 2.0 5/18/23 6:34 EEHg/L0.77 5/15/23SM21-23 6200B41,2-Dichloropropane ND 2.0 5/18/23 6:34 EEHg/L0.46 5/15/23SM21-23 6200B41,3-Dichloropropane ND 2.0 5/18/23 6:34 EEHg/L1.4 5/15/23SM21-23 6200B42,2-Dichloropropane ND 2.0 5/18/23 6:34 EEHg/L0.60 5/15/23SM21-23 6200B41,1-Dichloropropene ND 2.0 5/18/23 6:34 EEHg/L0.65 5/15/23SM21-23 6200B4cis-1,3-Dichloropropene ND 2.0 5/18/23 6:34 EEHg/L0.57 5/15/23SM21-23 6200B4trans-1,3-Dichloropropene 1.6 2.0 5/18/23 6:34 EEHg/L0.81 5/15/23SM21-23 6200B4JDiisopropyl Ether (DIPE) 23 2.0 5/18/23 6:34 EEHg/L0.88 5/15/23SM21-23 6200B4Ethylbenzene 17 20 5/18/23 6:34 EEHg/L4.8 5/15/23SM21-23 6200B4J2-Hexanone (MBK) 2.3 2.0 5/18/23 6:34 EEHg/L0.60 5/15/23SM21-23 6200B4Isopropylbenzene (Cumene) 1.5 2.0 5/18/23 6:34 EEHg/L0.51 5/15/23SM21-23 6200B4Jp-Isopropyltoluene (p-Cymene) ND 2.0 5/18/23 6:34 EEHg/L0.68 5/15/23SM21-23 6200B4Methyl tert-Butyl Ether (MTBE) ND 20 5/18/23 6:34 EEHg/L0.71 5/15/23SM21-23 6200B4Methylene Chloride 10 20 5/18/23 6:34 EEHg/L5.3 5/15/23SM21-23 6200B4J4-Methyl-2-pentanone (MIBK) 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-03 Field Sample #: MW-3R Sample Matrix: Ground Water Sampled: 5/10/2023 14:20 AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Sample Flags: RL-11 Volatile Organic Compounds by GC/MS 23 2.0 5/18/23 6:34 EEHg/L1.5 5/15/23SM21-23 6200B4Naphthalene 2.1 2.0 5/18/23 6:34 EEHg/L0.50 5/15/23SM21-23 6200B4n-Propylbenzene ND 2.0 5/18/23 6:34 EEHg/L0.60 5/15/23SM21-23 6200B4Styrene ND 2.0 5/18/23 6:34 EEHg/L0.55 5/15/23SM21-23 6200B41,1,2,2-Tetrachloroethane ND 2.0 5/18/23 6:34 EEHg/L0.67 5/15/23SM21-23 6200B4Tetrachloroethylene 49 2.0 5/18/23 6:34 EEHg/L0.89 5/15/23SM21-23 6200B4Toluene ND 4.0 5/18/23 6:34 EEHg/L1.4 5/15/23SM21-23 6200B41,2,3-Trichlorobenzene ND 2.0 5/18/23 6:34 EEHg/L1.2 5/15/23SM21-23 6200B41,2,4-Trichlorobenzene ND 2.0 5/18/23 6:34 EEHg/L0.60 5/15/23SM21-23 6200B41,1,1-Trichloroethane ND 2.0 5/18/23 6:34 EEHg/L0.76 5/15/23SM21-23 6200B41,1,2-Trichloroethane ND 2.0 5/18/23 6:34 EEHg/L0.70 5/15/23SM21-23 6200B4Trichloroethylene ND 2.0 5/18/23 6:34 EEHg/L0.62 5/15/23SM21-23 6200B4Trichlorofluoromethane (Freon 11) ND 2.0 5/18/23 6:34 EEHg/L1.1 5/15/23SM21-23 6200B41,2,3-Trichloropropane 130 2.0 5/18/23 6:34 EEHg/L0.80 5/15/23SM21-23 6200B41,2,4-Trimethylbenzene 81 2.0 5/18/23 6:34 EEHg/L0.60 5/15/23SM21-23 6200B41,3,5-Trimethylbenzene ND 80 5/18/23 6:34 EEHg/L6.7 5/15/23SM21-23 6200B4Vinyl Acetate ND 2.0 5/18/23 6:34 EEHg/L0.95 5/15/23SM21-23 6200B4Vinyl Chloride 250 4.0 5/18/23 6:34 EEHg/L2.0 5/15/23SM21-23 6200B4m+p Xylene 230 2.0 5/18/23 6:34 EEHg/L0.97 5/15/23SM21-23 6200B4o-Xylene Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 103 5/18/23 6:3470-130 Toluene-d8 99.3 5/18/23 6:3470-130 4-Bromofluorobenzene 102 5/18/23 6:3470-130 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-04 Field Sample #: MW-4R Sample Matrix: Ground Water Sampled: 5/10/2023 13:44 [TOC_2]23E1563-04[TOC] AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Sample Flags: RL-11 Volatile Organic Compounds by GC/MS 230 5000 5/16/23 5:10 MFFg/L200 5/15/23SM21-23 6200B100JAcetone 840 50 5/16/23 5:10 MFFg/L18 5/15/23SM21-23 6200B100Benzene ND 50 5/16/23 5:10 MFFg/L15 5/15/23SM21-23 6200B100Bromobenzene ND 50 5/16/23 5:10 MFFg/L28 5/15/23SM21-23 6200B100Bromochloromethane ND 50 5/16/23 5:10 MFFg/L16 5/15/23SM21-23 6200B100Bromodichloromethane ND 50 5/16/23 5:10 MFFg/L41 5/15/23SM21-23 6200B100Bromoform ND 200 5/16/23 5:10 MFFg/L130 5/15/23SM21-23 6200B100Bromomethane 290 500 5/16/23 5:10 MFFg/L170 5/15/23SM21-23 6200B100J2-Butanone (MEK) 47 50 5/16/23 5:10 MFFg/L15 5/15/23SM21-23 6200B100Jn-Butylbenzene ND 50 5/16/23 5:10 MFFg/L13 5/15/23SM21-23 6200B100sec-Butylbenzene ND 50 5/16/23 5:10 MFFg/L14 5/15/23SM21-23 6200B100tert-Butylbenzene ND 50 5/16/23 5:10 MFFg/L16 5/15/23SM21-23 6200B100Carbon Tetrachloride ND 50 5/16/23 5:10 MFFg/L12 5/15/23SM21-23 6200B100Chlorobenzene ND 5000 5/16/23 5:10 MFFg/L2000 5/15/23SM21-23 6200B100Ethanol ND 50 5/16/23 5:10 MFFg/L20 5/15/23SM21-23 6200B100Chlorodibromomethane ND 50 5/16/23 5:10 MFFg/L34 5/15/23SM21-23 6200B100Chloroethane ND 50 5/16/23 5:10 MFFg/L14 5/15/23SM21-23 6200B100Chloroform ND 60 5/16/23 5:10 MFFg/L50 5/15/23SM21-23 6200B100Chloromethane ND 50 5/16/23 5:10 MFFg/L15 5/15/23SM21-23 6200B1002-Chlorotoluene ND 50 5/16/23 5:10 MFFg/L15 5/15/23SM21-23 6200B1004-Chlorotoluene ND 50 5/16/23 5:10 MFFg/L16 5/15/23SM21-23 6200B1001,2-Dibromoethane (EDB) ND 50 5/16/23 5:10 MFFg/L13 5/15/23SM21-23 6200B1001,2-Dichlorobenzene ND 50 5/16/23 5:10 MFFg/L14 5/15/23SM21-23 6200B1001,3-Dichlorobenzene ND 50 5/16/23 5:10 MFFg/L13 5/15/23SM21-23 6200B1001,4-Dichlorobenzene ND 50 5/16/23 5:10 MFFg/L16 5/15/23SM21-23 6200B100Dichlorodifluoromethane (Freon 12) ND 50 5/16/23 5:10 MFFg/L14 5/15/23SM21-23 6200B1001,1-Dichloroethane ND 50 5/16/23 5:10 MFFg/L30 5/15/23SM21-23 6200B1001,2-Dichloroethane ND 50 5/16/23 5:10 MFFg/L14 5/15/23SM21-23 6200B1001,1-Dichloroethylene ND 50 5/16/23 5:10 MFFg/L14 5/15/23SM21-23 6200B100cis-1,2-Dichloroethylene ND 50 5/16/23 5:10 MFFg/L17 5/15/23SM21-23 6200B100trans-1,2-Dichloroethylene ND 50 5/16/23 5:10 MFFg/L19 5/15/23SM21-23 6200B1001,2-Dichloropropane ND 50 5/16/23 5:10 MFFg/L12 5/15/23SM21-23 6200B1001,3-Dichloropropane ND 50 5/16/23 5:10 MFFg/L35 5/15/23SM21-23 6200B1002,2-Dichloropropane ND 50 5/16/23 5:10 MFFg/L15 5/15/23SM21-23 6200B1001,1-Dichloropropene ND 50 5/16/23 5:10 MFFg/L16 5/15/23SM21-23 6200B100cis-1,3-Dichloropropene ND 50 5/16/23 5:10 MFFg/L14 5/15/23SM21-23 6200B100trans-1,3-Dichloropropene ND 50 5/16/23 5:10 MFFg/L20 5/15/23SM21-23 6200B100Diisopropyl Ether (DIPE) 1800 50 5/16/23 5:10 MFFg/L22 5/15/23SM21-23 6200B100Ethylbenzene ND 500 5/16/23 5:10 MFFg/L120 5/15/23SM21-23 6200B1002-Hexanone (MBK) 99 50 5/16/23 5:10 MFFg/L15 5/15/23SM21-23 6200B100Isopropylbenzene (Cumene) ND 50 5/16/23 5:10 MFFg/L13 5/15/23SM21-23 6200B100p-Isopropyltoluene (p-Cymene) ND 50 5/16/23 5:10 MFFg/L17 5/15/23SM21-23 6200B100Methyl tert-Butyl Ether (MTBE) ND 500 5/16/23 5:10 MFFg/L18 5/15/23SM21-23 6200B100Methylene Chloride ND 500 5/16/23 5:10 MFFg/L130 5/15/23SM21-23 6200B1004-Methyl-2-pentanone (MIBK) 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-04 Field Sample #: MW-4R Sample Matrix: Ground Water Sampled: 5/10/2023 13:44 AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Sample Flags: RL-11 Volatile Organic Compounds by GC/MS 430 50 5/16/23 5:10 MFFg/L38 5/15/23SM21-23 6200B100Naphthalene 230 50 5/16/23 5:10 MFFg/L12 5/15/23SM21-23 6200B100n-Propylbenzene ND 50 5/16/23 5:10 MFFg/L15 5/15/23SM21-23 6200B100Styrene ND 50 5/16/23 5:10 MFFg/L14 5/15/23SM21-23 6200B1001,1,2,2-Tetrachloroethane ND 50 5/16/23 5:10 MFFg/L17 5/15/23SM21-23 6200B100Tetrachloroethylene 9900 50 5/16/23 5:10 MFFg/L22 5/15/23SM21-23 6200B100Toluene ND 100 5/16/23 5:10 MFFg/L34 5/15/23SM21-23 6200B1001,2,3-Trichlorobenzene ND 100 5/16/23 5:10 MFFg/L30 5/15/23SM21-23 6200B1001,2,4-Trichlorobenzene ND 50 5/16/23 5:10 MFFg/L15 5/15/23SM21-23 6200B1001,1,1-Trichloroethane ND 50 5/16/23 5:10 MFFg/L19 5/15/23SM21-23 6200B1001,1,2-Trichloroethane ND 50 5/16/23 5:10 MFFg/L17 5/15/23SM21-23 6200B100Trichloroethylene ND 50 5/16/23 5:10 MFFg/L15 5/15/23SM21-23 6200B100Trichlorofluoromethane (Freon 11) ND 50 5/16/23 5:10 MFFg/L28 5/15/23SM21-23 6200B100R-051,2,3-Trichloropropane 2000 50 5/16/23 5:10 MFFg/L20 5/15/23SM21-23 6200B1001,2,4-Trimethylbenzene 620 50 5/16/23 5:10 MFFg/L15 5/15/23SM21-23 6200B1001,3,5-Trimethylbenzene ND 2000 5/16/23 5:10 MFFg/L170 5/15/23SM21-23 6200B100Vinyl Acetate ND 50 5/16/23 5:10 MFFg/L24 5/15/23SM21-23 6200B100Vinyl Chloride 7700 100 5/16/23 5:10 MFFg/L49 5/15/23SM21-23 6200B100m+p Xylene 4200 50 5/16/23 5:10 MFFg/L24 5/15/23SM21-23 6200B100o-Xylene Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 93.7 5/16/23 5:1070-130 Toluene-d8 99.3 5/16/23 5:1070-130 4-Bromofluorobenzene 95.9 5/16/23 5:1070-130 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-05 Field Sample #: MW-5 Sample Matrix: Ground Water Sampled: 5/10/2023 13:06 [TOC_2]23E1563-05[TOC] AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS 2.7 50 5/16/23 1:09 MFFg/L2.0 5/15/23SM21-23 6200B1JAcetone ND 0.50 5/16/23 1:09 MFFg/L0.18 5/15/23SM21-23 6200B1Benzene ND 0.50 5/16/23 1:09 MFFg/L0.15 5/15/23SM21-23 6200B1Bromobenzene ND 0.50 5/16/23 1:09 MFFg/L0.28 5/15/23SM21-23 6200B1Bromochloromethane ND 0.50 5/16/23 1:09 MFFg/L0.16 5/15/23SM21-23 6200B1Bromodichloromethane ND 0.50 5/16/23 1:09 MFFg/L0.41 5/15/23SM21-23 6200B1Bromoform ND 2.0 5/16/23 1:09 MFFg/L1.3 5/15/23SM21-23 6200B1Bromomethane ND 5.0 5/16/23 1:09 MFFg/L1.7 5/15/23SM21-23 6200B12-Butanone (MEK) ND 0.50 5/16/23 1:09 MFFg/L0.15 5/15/23SM21-23 6200B1n-Butylbenzene ND 0.50 5/16/23 1:09 MFFg/L0.13 5/15/23SM21-23 6200B1sec-Butylbenzene ND 0.50 5/16/23 1:09 MFFg/L0.14 5/15/23SM21-23 6200B1tert-Butylbenzene ND 0.50 5/16/23 1:09 MFFg/L0.16 5/15/23SM21-23 6200B1Carbon Tetrachloride ND 0.50 5/16/23 1:09 MFFg/L0.12 5/15/23SM21-23 6200B1Chlorobenzene ND 50 5/16/23 1:09 MFFg/L20 5/15/23SM21-23 6200B1Ethanol ND 0.50 5/16/23 1:09 MFFg/L0.20 5/15/23SM21-23 6200B1Chlorodibromomethane ND 0.50 5/16/23 1:09 MFFg/L0.34 5/15/23SM21-23 6200B1Chloroethane ND 0.50 5/16/23 1:09 MFFg/L0.14 5/15/23SM21-23 6200B1Chloroform ND 0.60 5/16/23 1:09 MFFg/L0.50 5/15/23SM21-23 6200B1Chloromethane ND 0.50 5/16/23 1:09 MFFg/L0.15 5/15/23SM21-23 6200B12-Chlorotoluene ND 0.50 5/16/23 1:09 MFFg/L0.15 5/15/23SM21-23 6200B14-Chlorotoluene ND 0.50 5/16/23 1:09 MFFg/L0.16 5/15/23SM21-23 6200B11,2-Dibromoethane (EDB) ND 0.50 5/16/23 1:09 MFFg/L0.13 5/15/23SM21-23 6200B11,2-Dichlorobenzene ND 0.50 5/16/23 1:09 MFFg/L0.14 5/15/23SM21-23 6200B11,3-Dichlorobenzene ND 0.50 5/16/23 1:09 MFFg/L0.13 5/15/23SM21-23 6200B11,4-Dichlorobenzene ND 0.50 5/16/23 1:09 MFFg/L0.16 5/15/23SM21-23 6200B1Dichlorodifluoromethane (Freon 12) ND 0.50 5/16/23 1:09 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethane ND 0.50 5/16/23 1:09 MFFg/L0.30 5/15/23SM21-23 6200B11,2-Dichloroethane ND 0.50 5/16/23 1:09 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethylene ND 0.50 5/16/23 1:09 MFFg/L0.14 5/15/23SM21-23 6200B1cis-1,2-Dichloroethylene ND 0.50 5/16/23 1:09 MFFg/L0.17 5/15/23SM21-23 6200B1trans-1,2-Dichloroethylene ND 0.50 5/16/23 1:09 MFFg/L0.19 5/15/23SM21-23 6200B11,2-Dichloropropane ND 0.50 5/16/23 1:09 MFFg/L0.12 5/15/23SM21-23 6200B11,3-Dichloropropane ND 0.50 5/16/23 1:09 MFFg/L0.35 5/15/23SM21-23 6200B12,2-Dichloropropane ND 0.50 5/16/23 1:09 MFFg/L0.15 5/15/23SM21-23 6200B11,1-Dichloropropene ND 0.50 5/16/23 1:09 MFFg/L0.16 5/15/23SM21-23 6200B1cis-1,3-Dichloropropene ND 0.50 5/16/23 1:09 MFFg/L0.14 5/15/23SM21-23 6200B1trans-1,3-Dichloropropene ND 0.50 5/16/23 1:09 MFFg/L0.20 5/15/23SM21-23 6200B1Diisopropyl Ether (DIPE) ND 0.50 5/16/23 1:09 MFFg/L0.22 5/15/23SM21-23 6200B1Ethylbenzene ND 5.0 5/16/23 1:09 MFFg/L1.2 5/15/23SM21-23 6200B12-Hexanone (MBK) ND 0.50 5/16/23 1:09 MFFg/L0.15 5/15/23SM21-23 6200B1Isopropylbenzene (Cumene) ND 0.50 5/16/23 1:09 MFFg/L0.13 5/15/23SM21-23 6200B1p-Isopropyltoluene (p-Cymene) ND 0.50 5/16/23 1:09 MFFg/L0.17 5/15/23SM21-23 6200B1Methyl tert-Butyl Ether (MTBE) ND 5.0 5/16/23 1:09 MFFg/L0.18 5/15/23SM21-23 6200B1Methylene Chloride ND 5.0 5/16/23 1:09 MFFg/L1.3 5/15/23SM21-23 6200B14-Methyl-2-pentanone (MIBK) 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-05 Field Sample #: MW-5 Sample Matrix: Ground Water Sampled: 5/10/2023 13:06 AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS ND 0.50 5/16/23 1:09 MFFg/L0.38 5/15/23SM21-23 6200B1Naphthalene ND 0.50 5/16/23 1:09 MFFg/L0.12 5/15/23SM21-23 6200B1n-Propylbenzene ND 0.50 5/16/23 1:09 MFFg/L0.15 5/15/23SM21-23 6200B1Styrene ND 0.50 5/16/23 1:09 MFFg/L0.14 5/15/23SM21-23 6200B11,1,2,2-Tetrachloroethane ND 0.50 5/16/23 1:09 MFFg/L0.17 5/15/23SM21-23 6200B1Tetrachloroethylene ND 0.50 5/16/23 1:09 MFFg/L0.22 5/15/23SM21-23 6200B1Toluene ND 1.0 5/16/23 1:09 MFFg/L0.34 5/15/23SM21-23 6200B11,2,3-Trichlorobenzene ND 1.0 5/16/23 1:09 MFFg/L0.30 5/15/23SM21-23 6200B11,2,4-Trichlorobenzene ND 0.50 5/16/23 1:09 MFFg/L0.15 5/15/23SM21-23 6200B11,1,1-Trichloroethane ND 0.50 5/16/23 1:09 MFFg/L0.19 5/15/23SM21-23 6200B11,1,2-Trichloroethane ND 0.50 5/16/23 1:09 MFFg/L0.17 5/15/23SM21-23 6200B1Trichloroethylene ND 0.50 5/16/23 1:09 MFFg/L0.15 5/15/23SM21-23 6200B1Trichlorofluoromethane (Freon 11) ND 0.50 5/16/23 1:09 MFFg/L0.28 5/15/23SM21-23 6200B1R-051,2,3-Trichloropropane ND 0.50 5/16/23 1:09 MFFg/L0.20 5/15/23SM21-23 6200B11,2,4-Trimethylbenzene ND 0.50 5/16/23 1:09 MFFg/L0.15 5/15/23SM21-23 6200B11,3,5-Trimethylbenzene ND 20 5/16/23 1:09 MFFg/L1.7 5/15/23SM21-23 6200B1Vinyl Acetate ND 0.50 5/16/23 1:09 MFFg/L0.24 5/15/23SM21-23 6200B1Vinyl Chloride ND 1.0 5/16/23 1:09 MFFg/L0.49 5/15/23SM21-23 6200B1m+p Xylene ND 0.50 5/16/23 1:09 MFFg/L0.24 5/15/23SM21-23 6200B1o-Xylene Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 97.1 5/16/23 1:0970-130 Toluene-d8 98.8 5/16/23 1:0970-130 4-Bromofluorobenzene 92.3 5/16/23 1:0970-130 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-06 Field Sample #: MW-6 Sample Matrix: Ground Water Sampled: 5/10/2023 13:19 [TOC_2]23E1563-06[TOC] AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS ND 50 5/16/23 1:36 MFFg/L2.0 5/15/23SM21-23 6200B1Acetone ND 0.50 5/16/23 1:36 MFFg/L0.18 5/15/23SM21-23 6200B1Benzene ND 0.50 5/16/23 1:36 MFFg/L0.15 5/15/23SM21-23 6200B1Bromobenzene ND 0.50 5/16/23 1:36 MFFg/L0.28 5/15/23SM21-23 6200B1Bromochloromethane ND 0.50 5/16/23 1:36 MFFg/L0.16 5/15/23SM21-23 6200B1Bromodichloromethane ND 0.50 5/16/23 1:36 MFFg/L0.41 5/15/23SM21-23 6200B1Bromoform ND 2.0 5/16/23 1:36 MFFg/L1.3 5/15/23SM21-23 6200B1Bromomethane ND 5.0 5/16/23 1:36 MFFg/L1.7 5/15/23SM21-23 6200B12-Butanone (MEK) ND 0.50 5/16/23 1:36 MFFg/L0.15 5/15/23SM21-23 6200B1n-Butylbenzene ND 0.50 5/16/23 1:36 MFFg/L0.13 5/15/23SM21-23 6200B1sec-Butylbenzene ND 0.50 5/16/23 1:36 MFFg/L0.14 5/15/23SM21-23 6200B1tert-Butylbenzene ND 0.50 5/16/23 1:36 MFFg/L0.16 5/15/23SM21-23 6200B1Carbon Tetrachloride ND 0.50 5/16/23 1:36 MFFg/L0.12 5/15/23SM21-23 6200B1Chlorobenzene ND 50 5/16/23 1:36 MFFg/L20 5/15/23SM21-23 6200B1Ethanol ND 0.50 5/16/23 1:36 MFFg/L0.20 5/15/23SM21-23 6200B1Chlorodibromomethane ND 0.50 5/16/23 1:36 MFFg/L0.34 5/15/23SM21-23 6200B1Chloroethane ND 0.50 5/16/23 1:36 MFFg/L0.14 5/15/23SM21-23 6200B1Chloroform ND 0.60 5/16/23 1:36 MFFg/L0.50 5/15/23SM21-23 6200B1Chloromethane ND 0.50 5/16/23 1:36 MFFg/L0.15 5/15/23SM21-23 6200B12-Chlorotoluene ND 0.50 5/16/23 1:36 MFFg/L0.15 5/15/23SM21-23 6200B14-Chlorotoluene ND 0.50 5/16/23 1:36 MFFg/L0.16 5/15/23SM21-23 6200B11,2-Dibromoethane (EDB) ND 0.50 5/16/23 1:36 MFFg/L0.13 5/15/23SM21-23 6200B11,2-Dichlorobenzene ND 0.50 5/16/23 1:36 MFFg/L0.14 5/15/23SM21-23 6200B11,3-Dichlorobenzene ND 0.50 5/16/23 1:36 MFFg/L0.13 5/15/23SM21-23 6200B11,4-Dichlorobenzene ND 0.50 5/16/23 1:36 MFFg/L0.16 5/15/23SM21-23 6200B1Dichlorodifluoromethane (Freon 12) ND 0.50 5/16/23 1:36 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethane ND 0.50 5/16/23 1:36 MFFg/L0.30 5/15/23SM21-23 6200B11,2-Dichloroethane ND 0.50 5/16/23 1:36 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethylene ND 0.50 5/16/23 1:36 MFFg/L0.14 5/15/23SM21-23 6200B1cis-1,2-Dichloroethylene ND 0.50 5/16/23 1:36 MFFg/L0.17 5/15/23SM21-23 6200B1trans-1,2-Dichloroethylene ND 0.50 5/16/23 1:36 MFFg/L0.19 5/15/23SM21-23 6200B11,2-Dichloropropane ND 0.50 5/16/23 1:36 MFFg/L0.12 5/15/23SM21-23 6200B11,3-Dichloropropane ND 0.50 5/16/23 1:36 MFFg/L0.35 5/15/23SM21-23 6200B12,2-Dichloropropane ND 0.50 5/16/23 1:36 MFFg/L0.15 5/15/23SM21-23 6200B11,1-Dichloropropene ND 0.50 5/16/23 1:36 MFFg/L0.16 5/15/23SM21-23 6200B1cis-1,3-Dichloropropene ND 0.50 5/16/23 1:36 MFFg/L0.14 5/15/23SM21-23 6200B1trans-1,3-Dichloropropene ND 0.50 5/16/23 1:36 MFFg/L0.20 5/15/23SM21-23 6200B1Diisopropyl Ether (DIPE) ND 0.50 5/16/23 1:36 MFFg/L0.22 5/15/23SM21-23 6200B1Ethylbenzene ND 5.0 5/16/23 1:36 MFFg/L1.2 5/15/23SM21-23 6200B12-Hexanone (MBK) ND 0.50 5/16/23 1:36 MFFg/L0.15 5/15/23SM21-23 6200B1Isopropylbenzene (Cumene) ND 0.50 5/16/23 1:36 MFFg/L0.13 5/15/23SM21-23 6200B1p-Isopropyltoluene (p-Cymene) ND 0.50 5/16/23 1:36 MFFg/L0.17 5/15/23SM21-23 6200B1Methyl tert-Butyl Ether (MTBE) ND 5.0 5/16/23 1:36 MFFg/L0.18 5/15/23SM21-23 6200B1Methylene Chloride ND 5.0 5/16/23 1:36 MFFg/L1.3 5/15/23SM21-23 6200B14-Methyl-2-pentanone (MIBK) 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-06 Field Sample #: MW-6 Sample Matrix: Ground Water Sampled: 5/10/2023 13:19 AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS ND 0.50 5/16/23 1:36 MFFg/L0.38 5/15/23SM21-23 6200B1Naphthalene ND 0.50 5/16/23 1:36 MFFg/L0.12 5/15/23SM21-23 6200B1n-Propylbenzene ND 0.50 5/16/23 1:36 MFFg/L0.15 5/15/23SM21-23 6200B1Styrene ND 0.50 5/16/23 1:36 MFFg/L0.14 5/15/23SM21-23 6200B11,1,2,2-Tetrachloroethane ND 0.50 5/16/23 1:36 MFFg/L0.17 5/15/23SM21-23 6200B1Tetrachloroethylene ND 0.50 5/16/23 1:36 MFFg/L0.22 5/15/23SM21-23 6200B1Toluene ND 1.0 5/16/23 1:36 MFFg/L0.34 5/15/23SM21-23 6200B11,2,3-Trichlorobenzene ND 1.0 5/16/23 1:36 MFFg/L0.30 5/15/23SM21-23 6200B11,2,4-Trichlorobenzene ND 0.50 5/16/23 1:36 MFFg/L0.15 5/15/23SM21-23 6200B11,1,1-Trichloroethane ND 0.50 5/16/23 1:36 MFFg/L0.19 5/15/23SM21-23 6200B11,1,2-Trichloroethane ND 0.50 5/16/23 1:36 MFFg/L0.17 5/15/23SM21-23 6200B1Trichloroethylene ND 0.50 5/16/23 1:36 MFFg/L0.15 5/15/23SM21-23 6200B1Trichlorofluoromethane (Freon 11) ND 0.50 5/16/23 1:36 MFFg/L0.28 5/15/23SM21-23 6200B1R-051,2,3-Trichloropropane ND 0.50 5/16/23 1:36 MFFg/L0.20 5/15/23SM21-23 6200B11,2,4-Trimethylbenzene ND 0.50 5/16/23 1:36 MFFg/L0.15 5/15/23SM21-23 6200B11,3,5-Trimethylbenzene ND 20 5/16/23 1:36 MFFg/L1.7 5/15/23SM21-23 6200B1Vinyl Acetate ND 0.50 5/16/23 1:36 MFFg/L0.24 5/15/23SM21-23 6200B1Vinyl Chloride ND 1.0 5/16/23 1:36 MFFg/L0.49 5/15/23SM21-23 6200B1m+p Xylene ND 0.50 5/16/23 1:36 MFFg/L0.24 5/15/23SM21-23 6200B1o-Xylene Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 99.4 5/16/23 1:3670-130 Toluene-d8 98.4 5/16/23 1:3670-130 4-Bromofluorobenzene 90.9 5/16/23 1:3670-130 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-07 Field Sample #: MW-7 Sample Matrix: Ground Water Sampled: 5/10/2023 14:04 [TOC_2]23E1563-07[TOC] AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS 2.9 50 5/16/23 2:03 MFFg/L2.0 5/15/23SM21-23 6200B1JAcetone ND 0.50 5/16/23 2:03 MFFg/L0.18 5/15/23SM21-23 6200B1Benzene ND 0.50 5/16/23 2:03 MFFg/L0.15 5/15/23SM21-23 6200B1Bromobenzene ND 0.50 5/16/23 2:03 MFFg/L0.28 5/15/23SM21-23 6200B1Bromochloromethane ND 0.50 5/16/23 2:03 MFFg/L0.16 5/15/23SM21-23 6200B1Bromodichloromethane ND 0.50 5/16/23 2:03 MFFg/L0.41 5/15/23SM21-23 6200B1Bromoform ND 2.0 5/16/23 2:03 MFFg/L1.3 5/15/23SM21-23 6200B1Bromomethane ND 5.0 5/16/23 2:03 MFFg/L1.7 5/15/23SM21-23 6200B12-Butanone (MEK) ND 0.50 5/16/23 2:03 MFFg/L0.15 5/15/23SM21-23 6200B1n-Butylbenzene ND 0.50 5/16/23 2:03 MFFg/L0.13 5/15/23SM21-23 6200B1sec-Butylbenzene ND 0.50 5/16/23 2:03 MFFg/L0.14 5/15/23SM21-23 6200B1tert-Butylbenzene ND 0.50 5/16/23 2:03 MFFg/L0.16 5/15/23SM21-23 6200B1Carbon Tetrachloride ND 0.50 5/16/23 2:03 MFFg/L0.12 5/15/23SM21-23 6200B1Chlorobenzene ND 50 5/16/23 2:03 MFFg/L20 5/15/23SM21-23 6200B1Ethanol ND 0.50 5/16/23 2:03 MFFg/L0.20 5/15/23SM21-23 6200B1Chlorodibromomethane ND 0.50 5/16/23 2:03 MFFg/L0.34 5/15/23SM21-23 6200B1Chloroethane ND 0.50 5/16/23 2:03 MFFg/L0.14 5/15/23SM21-23 6200B1Chloroform ND 0.60 5/16/23 2:03 MFFg/L0.50 5/15/23SM21-23 6200B1Chloromethane ND 0.50 5/16/23 2:03 MFFg/L0.15 5/15/23SM21-23 6200B12-Chlorotoluene ND 0.50 5/16/23 2:03 MFFg/L0.15 5/15/23SM21-23 6200B14-Chlorotoluene ND 0.50 5/16/23 2:03 MFFg/L0.16 5/15/23SM21-23 6200B11,2-Dibromoethane (EDB) ND 0.50 5/16/23 2:03 MFFg/L0.13 5/15/23SM21-23 6200B11,2-Dichlorobenzene ND 0.50 5/16/23 2:03 MFFg/L0.14 5/15/23SM21-23 6200B11,3-Dichlorobenzene ND 0.50 5/16/23 2:03 MFFg/L0.13 5/15/23SM21-23 6200B11,4-Dichlorobenzene ND 0.50 5/16/23 2:03 MFFg/L0.16 5/15/23SM21-23 6200B1Dichlorodifluoromethane (Freon 12) ND 0.50 5/16/23 2:03 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethane ND 0.50 5/16/23 2:03 MFFg/L0.30 5/15/23SM21-23 6200B11,2-Dichloroethane ND 0.50 5/16/23 2:03 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethylene ND 0.50 5/16/23 2:03 MFFg/L0.14 5/15/23SM21-23 6200B1cis-1,2-Dichloroethylene ND 0.50 5/16/23 2:03 MFFg/L0.17 5/15/23SM21-23 6200B1trans-1,2-Dichloroethylene ND 0.50 5/16/23 2:03 MFFg/L0.19 5/15/23SM21-23 6200B11,2-Dichloropropane ND 0.50 5/16/23 2:03 MFFg/L0.12 5/15/23SM21-23 6200B11,3-Dichloropropane ND 0.50 5/16/23 2:03 MFFg/L0.35 5/15/23SM21-23 6200B12,2-Dichloropropane ND 0.50 5/16/23 2:03 MFFg/L0.15 5/15/23SM21-23 6200B11,1-Dichloropropene ND 0.50 5/16/23 2:03 MFFg/L0.16 5/15/23SM21-23 6200B1cis-1,3-Dichloropropene ND 0.50 5/16/23 2:03 MFFg/L0.14 5/15/23SM21-23 6200B1trans-1,3-Dichloropropene ND 0.50 5/16/23 2:03 MFFg/L0.20 5/15/23SM21-23 6200B1Diisopropyl Ether (DIPE) ND 0.50 5/16/23 2:03 MFFg/L0.22 5/15/23SM21-23 6200B1Ethylbenzene ND 5.0 5/16/23 2:03 MFFg/L1.2 5/15/23SM21-23 6200B12-Hexanone (MBK) ND 0.50 5/16/23 2:03 MFFg/L0.15 5/15/23SM21-23 6200B1Isopropylbenzene (Cumene) ND 0.50 5/16/23 2:03 MFFg/L0.13 5/15/23SM21-23 6200B1p-Isopropyltoluene (p-Cymene) ND 0.50 5/16/23 2:03 MFFg/L0.17 5/15/23SM21-23 6200B1Methyl tert-Butyl Ether (MTBE) ND 5.0 5/16/23 2:03 MFFg/L0.18 5/15/23SM21-23 6200B1Methylene Chloride ND 5.0 5/16/23 2:03 MFFg/L1.3 5/15/23SM21-23 6200B14-Methyl-2-pentanone (MIBK) 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-07 Field Sample #: MW-7 Sample Matrix: Ground Water Sampled: 5/10/2023 14:04 AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS ND 0.50 5/16/23 2:03 MFFg/L0.38 5/15/23SM21-23 6200B1Naphthalene ND 0.50 5/16/23 2:03 MFFg/L0.12 5/15/23SM21-23 6200B1n-Propylbenzene ND 0.50 5/16/23 2:03 MFFg/L0.15 5/15/23SM21-23 6200B1Styrene ND 0.50 5/16/23 2:03 MFFg/L0.14 5/15/23SM21-23 6200B11,1,2,2-Tetrachloroethane ND 0.50 5/16/23 2:03 MFFg/L0.17 5/15/23SM21-23 6200B1Tetrachloroethylene ND 0.50 5/16/23 2:03 MFFg/L0.22 5/15/23SM21-23 6200B1Toluene ND 1.0 5/16/23 2:03 MFFg/L0.34 5/15/23SM21-23 6200B11,2,3-Trichlorobenzene ND 1.0 5/16/23 2:03 MFFg/L0.30 5/15/23SM21-23 6200B11,2,4-Trichlorobenzene ND 0.50 5/16/23 2:03 MFFg/L0.15 5/15/23SM21-23 6200B11,1,1-Trichloroethane ND 0.50 5/16/23 2:03 MFFg/L0.19 5/15/23SM21-23 6200B11,1,2-Trichloroethane ND 0.50 5/16/23 2:03 MFFg/L0.17 5/15/23SM21-23 6200B1Trichloroethylene ND 0.50 5/16/23 2:03 MFFg/L0.15 5/15/23SM21-23 6200B1Trichlorofluoromethane (Freon 11) ND 0.50 5/16/23 2:03 MFFg/L0.28 5/15/23SM21-23 6200B1R-051,2,3-Trichloropropane ND 0.50 5/16/23 2:03 MFFg/L0.20 5/15/23SM21-23 6200B11,2,4-Trimethylbenzene ND 0.50 5/16/23 2:03 MFFg/L0.15 5/15/23SM21-23 6200B11,3,5-Trimethylbenzene ND 20 5/16/23 2:03 MFFg/L1.7 5/15/23SM21-23 6200B1Vinyl Acetate ND 0.50 5/16/23 2:03 MFFg/L0.24 5/15/23SM21-23 6200B1Vinyl Chloride ND 1.0 5/16/23 2:03 MFFg/L0.49 5/15/23SM21-23 6200B1m+p Xylene ND 0.50 5/16/23 2:03 MFFg/L0.24 5/15/23SM21-23 6200B1o-Xylene Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 96.6 5/16/23 2:0370-130 Toluene-d8 97.8 5/16/23 2:0370-130 4-Bromofluorobenzene 93.3 5/16/23 2:0370-130 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-08 Field Sample #: DW-1 Sample Matrix: Ground Water Sampled: 5/10/2023 11:20 [TOC_2]23E1563-08[TOC] AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS 3.4 50 5/16/23 3:23 MFFg/L2.0 5/15/23SM21-23 6200B1JAcetone ND 0.50 5/16/23 3:23 MFFg/L0.18 5/15/23SM21-23 6200B1Benzene ND 0.50 5/16/23 3:23 MFFg/L0.15 5/15/23SM21-23 6200B1Bromobenzene ND 0.50 5/16/23 3:23 MFFg/L0.28 5/15/23SM21-23 6200B1Bromochloromethane ND 0.50 5/16/23 3:23 MFFg/L0.16 5/15/23SM21-23 6200B1Bromodichloromethane ND 0.50 5/16/23 3:23 MFFg/L0.41 5/15/23SM21-23 6200B1Bromoform ND 2.0 5/16/23 3:23 MFFg/L1.3 5/15/23SM21-23 6200B1Bromomethane ND 5.0 5/16/23 3:23 MFFg/L1.7 5/15/23SM21-23 6200B12-Butanone (MEK) ND 0.50 5/16/23 3:23 MFFg/L0.15 5/15/23SM21-23 6200B1n-Butylbenzene ND 0.50 5/16/23 3:23 MFFg/L0.13 5/15/23SM21-23 6200B1sec-Butylbenzene ND 0.50 5/16/23 3:23 MFFg/L0.14 5/15/23SM21-23 6200B1tert-Butylbenzene ND 0.50 5/16/23 3:23 MFFg/L0.16 5/15/23SM21-23 6200B1Carbon Tetrachloride ND 0.50 5/16/23 3:23 MFFg/L0.12 5/15/23SM21-23 6200B1Chlorobenzene ND 50 5/16/23 3:23 MFFg/L20 5/15/23SM21-23 6200B1Ethanol ND 0.50 5/16/23 3:23 MFFg/L0.20 5/15/23SM21-23 6200B1Chlorodibromomethane ND 0.50 5/16/23 3:23 MFFg/L0.34 5/15/23SM21-23 6200B1Chloroethane ND 0.50 5/16/23 3:23 MFFg/L0.14 5/15/23SM21-23 6200B1Chloroform ND 0.60 5/16/23 3:23 MFFg/L0.50 5/15/23SM21-23 6200B1Chloromethane ND 0.50 5/16/23 3:23 MFFg/L0.15 5/15/23SM21-23 6200B12-Chlorotoluene ND 0.50 5/16/23 3:23 MFFg/L0.15 5/15/23SM21-23 6200B14-Chlorotoluene ND 0.50 5/16/23 3:23 MFFg/L0.16 5/15/23SM21-23 6200B11,2-Dibromoethane (EDB) ND 0.50 5/16/23 3:23 MFFg/L0.13 5/15/23SM21-23 6200B11,2-Dichlorobenzene ND 0.50 5/16/23 3:23 MFFg/L0.14 5/15/23SM21-23 6200B11,3-Dichlorobenzene ND 0.50 5/16/23 3:23 MFFg/L0.13 5/15/23SM21-23 6200B11,4-Dichlorobenzene ND 0.50 5/16/23 3:23 MFFg/L0.16 5/15/23SM21-23 6200B1Dichlorodifluoromethane (Freon 12) ND 0.50 5/16/23 3:23 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethane 0.82 0.50 5/16/23 3:23 MFFg/L0.30 5/15/23SM21-23 6200B11,2-Dichloroethane ND 0.50 5/16/23 3:23 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethylene ND 0.50 5/16/23 3:23 MFFg/L0.14 5/15/23SM21-23 6200B1cis-1,2-Dichloroethylene ND 0.50 5/16/23 3:23 MFFg/L0.17 5/15/23SM21-23 6200B1trans-1,2-Dichloroethylene ND 0.50 5/16/23 3:23 MFFg/L0.19 5/15/23SM21-23 6200B11,2-Dichloropropane ND 0.50 5/16/23 3:23 MFFg/L0.12 5/15/23SM21-23 6200B11,3-Dichloropropane ND 0.50 5/16/23 3:23 MFFg/L0.35 5/15/23SM21-23 6200B12,2-Dichloropropane ND 0.50 5/16/23 3:23 MFFg/L0.15 5/15/23SM21-23 6200B11,1-Dichloropropene ND 0.50 5/16/23 3:23 MFFg/L0.16 5/15/23SM21-23 6200B1cis-1,3-Dichloropropene ND 0.50 5/16/23 3:23 MFFg/L0.14 5/15/23SM21-23 6200B1trans-1,3-Dichloropropene ND 0.50 5/16/23 3:23 MFFg/L0.20 5/15/23SM21-23 6200B1Diisopropyl Ether (DIPE) ND 0.50 5/16/23 3:23 MFFg/L0.22 5/15/23SM21-23 6200B1Ethylbenzene ND 5.0 5/16/23 3:23 MFFg/L1.2 5/15/23SM21-23 6200B12-Hexanone (MBK) ND 0.50 5/16/23 3:23 MFFg/L0.15 5/15/23SM21-23 6200B1Isopropylbenzene (Cumene) 0.34 0.50 5/16/23 3:23 MFFg/L0.13 5/15/23SM21-23 6200B1Jp-Isopropyltoluene (p-Cymene) ND 0.50 5/16/23 3:23 MFFg/L0.17 5/15/23SM21-23 6200B1Methyl tert-Butyl Ether (MTBE) ND 5.0 5/16/23 3:23 MFFg/L0.18 5/15/23SM21-23 6200B1Methylene Chloride ND 5.0 5/16/23 3:23 MFFg/L1.3 5/15/23SM21-23 6200B14-Methyl-2-pentanone (MIBK) 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-08 Field Sample #: DW-1 Sample Matrix: Ground Water Sampled: 5/10/2023 11:20 AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS ND 0.50 5/16/23 3:23 MFFg/L0.38 5/15/23SM21-23 6200B1Naphthalene ND 0.50 5/16/23 3:23 MFFg/L0.12 5/15/23SM21-23 6200B1n-Propylbenzene ND 0.50 5/16/23 3:23 MFFg/L0.15 5/15/23SM21-23 6200B1Styrene ND 0.50 5/16/23 3:23 MFFg/L0.14 5/15/23SM21-23 6200B11,1,2,2-Tetrachloroethane ND 0.50 5/16/23 3:23 MFFg/L0.17 5/15/23SM21-23 6200B1Tetrachloroethylene ND 0.50 5/16/23 3:23 MFFg/L0.22 5/15/23SM21-23 6200B1Toluene ND 1.0 5/16/23 3:23 MFFg/L0.34 5/15/23SM21-23 6200B11,2,3-Trichlorobenzene ND 1.0 5/16/23 3:23 MFFg/L0.30 5/15/23SM21-23 6200B11,2,4-Trichlorobenzene ND 0.50 5/16/23 3:23 MFFg/L0.15 5/15/23SM21-23 6200B11,1,1-Trichloroethane ND 0.50 5/16/23 3:23 MFFg/L0.19 5/15/23SM21-23 6200B11,1,2-Trichloroethane ND 0.50 5/16/23 3:23 MFFg/L0.17 5/15/23SM21-23 6200B1Trichloroethylene ND 0.50 5/16/23 3:23 MFFg/L0.15 5/15/23SM21-23 6200B1Trichlorofluoromethane (Freon 11) ND 0.50 5/16/23 3:23 MFFg/L0.28 5/15/23SM21-23 6200B1R-051,2,3-Trichloropropane ND 0.50 5/16/23 3:23 MFFg/L0.20 5/15/23SM21-23 6200B11,2,4-Trimethylbenzene ND 0.50 5/16/23 3:23 MFFg/L0.15 5/15/23SM21-23 6200B11,3,5-Trimethylbenzene ND 20 5/16/23 3:23 MFFg/L1.7 5/15/23SM21-23 6200B1Vinyl Acetate ND 0.50 5/16/23 3:23 MFFg/L0.24 5/15/23SM21-23 6200B1Vinyl Chloride ND 1.0 5/16/23 3:23 MFFg/L0.49 5/15/23SM21-23 6200B1m+p Xylene ND 0.50 5/16/23 3:23 MFFg/L0.24 5/15/23SM21-23 6200B1o-Xylene Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 98.5 5/16/23 3:2370-130 Toluene-d8 99.9 5/16/23 3:2370-130 4-Bromofluorobenzene 92.7 5/16/23 3:2370-130 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-09 Field Sample #: Eq. Rinse Sample Matrix: Ground Water Sampled: 5/10/2023 14:15 [TOC_2]23E1563-09[TOC] AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS 9.6 50 5/15/23 22:56 MFFg/L2.0 5/15/23SM21-23 6200B1JAcetone ND 0.50 5/15/23 22:56 MFFg/L0.18 5/15/23SM21-23 6200B1Benzene ND 0.50 5/15/23 22:56 MFFg/L0.15 5/15/23SM21-23 6200B1Bromobenzene ND 0.50 5/15/23 22:56 MFFg/L0.28 5/15/23SM21-23 6200B1Bromochloromethane ND 0.50 5/15/23 22:56 MFFg/L0.16 5/15/23SM21-23 6200B1Bromodichloromethane ND 0.50 5/15/23 22:56 MFFg/L0.41 5/15/23SM21-23 6200B1Bromoform ND 2.0 5/15/23 22:56 MFFg/L1.3 5/15/23SM21-23 6200B1Bromomethane ND 5.0 5/15/23 22:56 MFFg/L1.7 5/15/23SM21-23 6200B12-Butanone (MEK) ND 0.50 5/15/23 22:56 MFFg/L0.15 5/15/23SM21-23 6200B1n-Butylbenzene ND 0.50 5/15/23 22:56 MFFg/L0.13 5/15/23SM21-23 6200B1sec-Butylbenzene ND 0.50 5/15/23 22:56 MFFg/L0.14 5/15/23SM21-23 6200B1tert-Butylbenzene ND 0.50 5/15/23 22:56 MFFg/L0.16 5/15/23SM21-23 6200B1Carbon Tetrachloride ND 0.50 5/15/23 22:56 MFFg/L0.12 5/15/23SM21-23 6200B1Chlorobenzene ND 50 5/15/23 22:56 MFFg/L20 5/15/23SM21-23 6200B1Ethanol ND 0.50 5/15/23 22:56 MFFg/L0.20 5/15/23SM21-23 6200B1Chlorodibromomethane ND 0.50 5/15/23 22:56 MFFg/L0.34 5/15/23SM21-23 6200B1Chloroethane ND 0.50 5/15/23 22:56 MFFg/L0.14 5/15/23SM21-23 6200B1Chloroform ND 0.60 5/15/23 22:56 MFFg/L0.50 5/15/23SM21-23 6200B1Chloromethane ND 0.50 5/15/23 22:56 MFFg/L0.15 5/15/23SM21-23 6200B12-Chlorotoluene ND 0.50 5/15/23 22:56 MFFg/L0.15 5/15/23SM21-23 6200B14-Chlorotoluene ND 0.50 5/15/23 22:56 MFFg/L0.16 5/15/23SM21-23 6200B11,2-Dibromoethane (EDB) ND 0.50 5/15/23 22:56 MFFg/L0.13 5/15/23SM21-23 6200B11,2-Dichlorobenzene ND 0.50 5/15/23 22:56 MFFg/L0.14 5/15/23SM21-23 6200B11,3-Dichlorobenzene ND 0.50 5/15/23 22:56 MFFg/L0.13 5/15/23SM21-23 6200B11,4-Dichlorobenzene ND 0.50 5/15/23 22:56 MFFg/L0.16 5/15/23SM21-23 6200B1Dichlorodifluoromethane (Freon 12) ND 0.50 5/15/23 22:56 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethane ND 0.50 5/15/23 22:56 MFFg/L0.30 5/15/23SM21-23 6200B11,2-Dichloroethane ND 0.50 5/15/23 22:56 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethylene ND 0.50 5/15/23 22:56 MFFg/L0.14 5/15/23SM21-23 6200B1cis-1,2-Dichloroethylene ND 0.50 5/15/23 22:56 MFFg/L0.17 5/15/23SM21-23 6200B1trans-1,2-Dichloroethylene ND 0.50 5/15/23 22:56 MFFg/L0.19 5/15/23SM21-23 6200B11,2-Dichloropropane ND 0.50 5/15/23 22:56 MFFg/L0.12 5/15/23SM21-23 6200B11,3-Dichloropropane ND 0.50 5/15/23 22:56 MFFg/L0.35 5/15/23SM21-23 6200B12,2-Dichloropropane ND 0.50 5/15/23 22:56 MFFg/L0.15 5/15/23SM21-23 6200B11,1-Dichloropropene ND 0.50 5/15/23 22:56 MFFg/L0.16 5/15/23SM21-23 6200B1cis-1,3-Dichloropropene ND 0.50 5/15/23 22:56 MFFg/L0.14 5/15/23SM21-23 6200B1trans-1,3-Dichloropropene ND 0.50 5/15/23 22:56 MFFg/L0.20 5/15/23SM21-23 6200B1Diisopropyl Ether (DIPE) ND 0.50 5/15/23 22:56 MFFg/L0.22 5/15/23SM21-23 6200B1Ethylbenzene ND 5.0 5/15/23 22:56 MFFg/L1.2 5/15/23SM21-23 6200B12-Hexanone (MBK) ND 0.50 5/15/23 22:56 MFFg/L0.15 5/15/23SM21-23 6200B1Isopropylbenzene (Cumene) ND 0.50 5/15/23 22:56 MFFg/L0.13 5/15/23SM21-23 6200B1p-Isopropyltoluene (p-Cymene) ND 0.50 5/15/23 22:56 MFFg/L0.17 5/15/23SM21-23 6200B1Methyl tert-Butyl Ether (MTBE) ND 5.0 5/15/23 22:56 MFFg/L0.18 5/15/23SM21-23 6200B1Methylene Chloride ND 5.0 5/15/23 22:56 MFFg/L1.3 5/15/23SM21-23 6200B14-Methyl-2-pentanone (MIBK) 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-09 Field Sample #: Eq. Rinse Sample Matrix: Ground Water Sampled: 5/10/2023 14:15 AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS ND 0.50 5/15/23 22:56 MFFg/L0.38 5/15/23SM21-23 6200B1Naphthalene ND 0.50 5/15/23 22:56 MFFg/L0.12 5/15/23SM21-23 6200B1n-Propylbenzene ND 0.50 5/15/23 22:56 MFFg/L0.15 5/15/23SM21-23 6200B1Styrene ND 0.50 5/15/23 22:56 MFFg/L0.14 5/15/23SM21-23 6200B11,1,2,2-Tetrachloroethane ND 0.50 5/15/23 22:56 MFFg/L0.17 5/15/23SM21-23 6200B1Tetrachloroethylene ND 0.50 5/15/23 22:56 MFFg/L0.22 5/15/23SM21-23 6200B1Toluene ND 1.0 5/15/23 22:56 MFFg/L0.34 5/15/23SM21-23 6200B11,2,3-Trichlorobenzene ND 1.0 5/15/23 22:56 MFFg/L0.30 5/15/23SM21-23 6200B11,2,4-Trichlorobenzene ND 0.50 5/15/23 22:56 MFFg/L0.15 5/15/23SM21-23 6200B11,1,1-Trichloroethane ND 0.50 5/15/23 22:56 MFFg/L0.19 5/15/23SM21-23 6200B11,1,2-Trichloroethane ND 0.50 5/15/23 22:56 MFFg/L0.17 5/15/23SM21-23 6200B1Trichloroethylene ND 0.50 5/15/23 22:56 MFFg/L0.15 5/15/23SM21-23 6200B1Trichlorofluoromethane (Freon 11) ND 0.50 5/15/23 22:56 MFFg/L0.28 5/15/23SM21-23 6200B1R-051,2,3-Trichloropropane ND 0.50 5/15/23 22:56 MFFg/L0.20 5/15/23SM21-23 6200B11,2,4-Trimethylbenzene ND 0.50 5/15/23 22:56 MFFg/L0.15 5/15/23SM21-23 6200B11,3,5-Trimethylbenzene ND 20 5/15/23 22:56 MFFg/L1.7 5/15/23SM21-23 6200B1Vinyl Acetate ND 0.50 5/15/23 22:56 MFFg/L0.24 5/15/23SM21-23 6200B1Vinyl Chloride ND 1.0 5/15/23 22:56 MFFg/L0.49 5/15/23SM21-23 6200B1m+p Xylene ND 0.50 5/15/23 22:56 MFFg/L0.24 5/15/23SM21-23 6200B1o-Xylene Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 96.0 5/15/23 22:5670-130 Toluene-d8 88.8 5/15/23 22:5670-130 4-Bromofluorobenzene 91.4 5/15/23 22:5670-130 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-10 Field Sample #: Trip Blank Sample Matrix: Trip Blank Water Sampled: 5/10/2023 00:00 [TOC_2]23E1563-10[TOC] AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS 2.9 50 5/15/23 23:23 MFFg/L2.0 5/15/23SM21-23 6200B1JAcetone ND 0.50 5/15/23 23:23 MFFg/L0.18 5/15/23SM21-23 6200B1Benzene ND 0.50 5/15/23 23:23 MFFg/L0.15 5/15/23SM21-23 6200B1Bromobenzene ND 0.50 5/15/23 23:23 MFFg/L0.28 5/15/23SM21-23 6200B1Bromochloromethane ND 0.50 5/15/23 23:23 MFFg/L0.16 5/15/23SM21-23 6200B1Bromodichloromethane ND 0.50 5/15/23 23:23 MFFg/L0.41 5/15/23SM21-23 6200B1Bromoform ND 2.0 5/15/23 23:23 MFFg/L1.3 5/15/23SM21-23 6200B1Bromomethane ND 5.0 5/15/23 23:23 MFFg/L1.7 5/15/23SM21-23 6200B12-Butanone (MEK) ND 0.50 5/15/23 23:23 MFFg/L0.15 5/15/23SM21-23 6200B1n-Butylbenzene ND 0.50 5/15/23 23:23 MFFg/L0.13 5/15/23SM21-23 6200B1sec-Butylbenzene ND 0.50 5/15/23 23:23 MFFg/L0.14 5/15/23SM21-23 6200B1tert-Butylbenzene ND 0.50 5/15/23 23:23 MFFg/L0.16 5/15/23SM21-23 6200B1Carbon Tetrachloride ND 0.50 5/15/23 23:23 MFFg/L0.12 5/15/23SM21-23 6200B1Chlorobenzene ND 50 5/15/23 23:23 MFFg/L20 5/15/23SM21-23 6200B1Ethanol ND 0.50 5/15/23 23:23 MFFg/L0.20 5/15/23SM21-23 6200B1Chlorodibromomethane ND 0.50 5/15/23 23:23 MFFg/L0.34 5/15/23SM21-23 6200B1Chloroethane ND 0.50 5/15/23 23:23 MFFg/L0.14 5/15/23SM21-23 6200B1Chloroform ND 0.60 5/15/23 23:23 MFFg/L0.50 5/15/23SM21-23 6200B1Chloromethane ND 0.50 5/15/23 23:23 MFFg/L0.15 5/15/23SM21-23 6200B12-Chlorotoluene ND 0.50 5/15/23 23:23 MFFg/L0.15 5/15/23SM21-23 6200B14-Chlorotoluene ND 0.50 5/15/23 23:23 MFFg/L0.16 5/15/23SM21-23 6200B11,2-Dibromoethane (EDB) ND 0.50 5/15/23 23:23 MFFg/L0.13 5/15/23SM21-23 6200B11,2-Dichlorobenzene ND 0.50 5/15/23 23:23 MFFg/L0.14 5/15/23SM21-23 6200B11,3-Dichlorobenzene ND 0.50 5/15/23 23:23 MFFg/L0.13 5/15/23SM21-23 6200B11,4-Dichlorobenzene ND 0.50 5/15/23 23:23 MFFg/L0.16 5/15/23SM21-23 6200B1Dichlorodifluoromethane (Freon 12) ND 0.50 5/15/23 23:23 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethane ND 0.50 5/15/23 23:23 MFFg/L0.30 5/15/23SM21-23 6200B11,2-Dichloroethane ND 0.50 5/15/23 23:23 MFFg/L0.14 5/15/23SM21-23 6200B11,1-Dichloroethylene ND 0.50 5/15/23 23:23 MFFg/L0.14 5/15/23SM21-23 6200B1cis-1,2-Dichloroethylene ND 0.50 5/15/23 23:23 MFFg/L0.17 5/15/23SM21-23 6200B1trans-1,2-Dichloroethylene ND 0.50 5/15/23 23:23 MFFg/L0.19 5/15/23SM21-23 6200B11,2-Dichloropropane ND 0.50 5/15/23 23:23 MFFg/L0.12 5/15/23SM21-23 6200B11,3-Dichloropropane ND 0.50 5/15/23 23:23 MFFg/L0.35 5/15/23SM21-23 6200B12,2-Dichloropropane ND 0.50 5/15/23 23:23 MFFg/L0.15 5/15/23SM21-23 6200B11,1-Dichloropropene ND 0.50 5/15/23 23:23 MFFg/L0.16 5/15/23SM21-23 6200B1cis-1,3-Dichloropropene ND 0.50 5/15/23 23:23 MFFg/L0.14 5/15/23SM21-23 6200B1trans-1,3-Dichloropropene ND 0.50 5/15/23 23:23 MFFg/L0.20 5/15/23SM21-23 6200B1Diisopropyl Ether (DIPE) ND 0.50 5/15/23 23:23 MFFg/L0.22 5/15/23SM21-23 6200B1Ethylbenzene ND 5.0 5/15/23 23:23 MFFg/L1.2 5/15/23SM21-23 6200B12-Hexanone (MBK) ND 0.50 5/15/23 23:23 MFFg/L0.15 5/15/23SM21-23 6200B1Isopropylbenzene (Cumene) ND 0.50 5/15/23 23:23 MFFg/L0.13 5/15/23SM21-23 6200B1p-Isopropyltoluene (p-Cymene) ND 0.50 5/15/23 23:23 MFFg/L0.17 5/15/23SM21-23 6200B1Methyl tert-Butyl Ether (MTBE) ND 5.0 5/15/23 23:23 MFFg/L0.18 5/15/23SM21-23 6200B1Methylene Chloride ND 5.0 5/15/23 23:23 MFFg/L1.3 5/15/23SM21-23 6200B14-Methyl-2-pentanone (MIBK) 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Date Received: 5/11/2023 Work Order: 23E1563Sample Description:Project Location: Apex, NC Sample ID: 23E1563-10 Field Sample #: Trip Blank Sample Matrix: Trip Blank Water Sampled: 5/10/2023 00:00 AnalystAnalyzedDilutionFlag/QualRLResultsAnalyte Date/Time DL Units Date PreparedMethod Volatile Organic Compounds by GC/MS ND 0.50 5/15/23 23:23 MFFg/L0.38 5/15/23SM21-23 6200B1Naphthalene ND 0.50 5/15/23 23:23 MFFg/L0.12 5/15/23SM21-23 6200B1n-Propylbenzene ND 0.50 5/15/23 23:23 MFFg/L0.15 5/15/23SM21-23 6200B1Styrene ND 0.50 5/15/23 23:23 MFFg/L0.14 5/15/23SM21-23 6200B11,1,2,2-Tetrachloroethane ND 0.50 5/15/23 23:23 MFFg/L0.17 5/15/23SM21-23 6200B1Tetrachloroethylene ND 0.50 5/15/23 23:23 MFFg/L0.22 5/15/23SM21-23 6200B1Toluene ND 1.0 5/15/23 23:23 MFFg/L0.34 5/15/23SM21-23 6200B11,2,3-Trichlorobenzene ND 1.0 5/15/23 23:23 MFFg/L0.30 5/15/23SM21-23 6200B11,2,4-Trichlorobenzene ND 0.50 5/15/23 23:23 MFFg/L0.15 5/15/23SM21-23 6200B11,1,1-Trichloroethane ND 0.50 5/15/23 23:23 MFFg/L0.19 5/15/23SM21-23 6200B11,1,2-Trichloroethane ND 0.50 5/15/23 23:23 MFFg/L0.17 5/15/23SM21-23 6200B1Trichloroethylene ND 0.50 5/15/23 23:23 MFFg/L0.15 5/15/23SM21-23 6200B1Trichlorofluoromethane (Freon 11) ND 0.50 5/15/23 23:23 MFFg/L0.28 5/15/23SM21-23 6200B1R-051,2,3-Trichloropropane ND 0.50 5/15/23 23:23 MFFg/L0.20 5/15/23SM21-23 6200B11,2,4-Trimethylbenzene ND 0.50 5/15/23 23:23 MFFg/L0.15 5/15/23SM21-23 6200B11,3,5-Trimethylbenzene ND 20 5/15/23 23:23 MFFg/L1.7 5/15/23SM21-23 6200B1Vinyl Acetate ND 0.50 5/15/23 23:23 MFFg/L0.24 5/15/23SM21-23 6200B1Vinyl Chloride ND 1.0 5/15/23 23:23 MFFg/L0.49 5/15/23SM21-23 6200B1m+p Xylene ND 0.50 5/15/23 23:23 MFFg/L0.24 5/15/23SM21-23 6200B1o-Xylene Surrogates % Recovery Recovery Limits Flag/Qual 1,2-Dichloroethane-d4 99.7 5/15/23 23:2370-130 Toluene-d8 99.5 5/15/23 23:2370-130 4-Bromofluorobenzene 93.2 5/15/23 23:2370-130 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Sample Extraction Data Prep Method: SW-846 5030B-SM21-23 6200B Lab Number [Field ID]Batch DateInitial [mL]Final [mL] B340215 05/15/230.25 5.0023E1563-01 [MW-1] B340215 05/15/230.05 5.0023E1563-04 [MW-4R] B340215 05/15/235 5.0023E1563-05 [MW-5] B340215 05/15/235 5.0023E1563-06 [MW-6] B340215 05/15/235 5.0023E1563-07 [MW-7] B340215 05/15/235 5.0023E1563-08 [DW-1] B340215 05/15/235 5.0023E1563-09 [Eq. Rinse] B340215 05/15/235 5.0023E1563-10 [Trip Blank] Prep Method: SW-846 5030B-SM21-23 6200B Lab Number [Field ID]Batch DateInitial [mL]Final [mL] B340343 05/15/231.25 5.0023E1563-03 [MW-3R] Prep Method: SW-846 5030B-SM21-23 6200B Lab Number [Field ID]Batch DateInitial [mL]Final [mL] B340602 05/18/235 5.0023E1563-02 [MW-2] [TOC_1]Sample Preparation Information[TOC] 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL [TOC_2]Volatile Organic Compounds by GC/MS[TOC] Batch B340215 - SW-846 5030B [TOC_3]B340215[TOC] Blank (B340215-BLK1) Prepared & Analyzed: 05/15/23 Acetone g/L50ND Benzene g/L0.50ND Bromobenzene g/L0.50ND Bromochloromethane g/L0.50ND Bromodichloromethane g/L0.50ND Bromoform g/L0.50ND Bromomethane g/L2.0ND 2-Butanone (MEK)g/L5.0ND n-Butylbenzene g/L0.50ND sec-Butylbenzene g/L0.50ND tert-Butylbenzene g/L0.50ND Carbon Tetrachloride g/L0.50ND Chlorobenzene g/L0.50ND Ethanol g/L50ND Chlorodibromomethane g/L0.50ND Chloroethane g/L0.50ND Chloroform g/L0.50ND Chloromethane g/L0.60ND 2-Chlorotoluene g/L0.50ND 4-Chlorotoluene g/L0.50ND 1,2-Dibromoethane (EDB)g/L0.50ND 1,2-Dichlorobenzene g/L0.50ND 1,3-Dichlorobenzene g/L0.50ND 1,4-Dichlorobenzene g/L0.50ND Dichlorodifluoromethane (Freon 12)g/L0.50ND 1,1-Dichloroethane g/L0.50ND 1,2-Dichloroethane g/L0.50ND 1,1-Dichloroethylene g/L0.50ND cis-1,2-Dichloroethylene g/L0.50ND trans-1,2-Dichloroethylene g/L0.50ND 1,2-Dichloropropane g/L0.50ND 1,3-Dichloropropane g/L0.50ND 2,2-Dichloropropane g/L0.50ND 1,1-Dichloropropene g/L0.50ND cis-1,3-Dichloropropene g/L0.50ND trans-1,3-Dichloropropene g/L0.50ND Diisopropyl Ether (DIPE)g/L0.50ND Ethylbenzene g/L0.50ND 2-Hexanone (MBK)g/L5.0ND Isopropylbenzene (Cumene)g/L0.50ND p-Isopropyltoluene (p-Cymene)g/L0.50ND Methyl tert-Butyl Ether (MTBE)g/L0.50ND Methylene Chloride g/L5.0ND 4-Methyl-2-pentanone (MIBK)g/L5.0ND Naphthalene g/L0.50ND n-Propylbenzene g/L0.50ND Styrene g/L0.50ND 1,1,2,2-Tetrachloroethane g/L0.50ND Tetrachloroethylene g/L0.50ND Toluene g/L0.50ND 1,2,3-Trichlorobenzene g/L1.0ND 1,2,4-Trichlorobenzene g/L0.50ND [TOC_1]QC Data[TOC] 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340215 - SW-846 5030B Blank (B340215-BLK1) Prepared & Analyzed: 05/15/23 1,1,1-Trichloroethane g/L0.50ND 1,1,2-Trichloroethane g/L0.50ND Trichloroethylene g/L0.50ND Trichlorofluoromethane (Freon 11)g/L0.50ND 1,2,3-Trichloropropane g/L0.50 R-05ND 1,2,4-Trimethylbenzene g/L0.50ND 1,3,5-Trimethylbenzene g/L0.50ND Vinyl Acetate g/L20ND Vinyl Chloride g/L0.50ND m+p Xylene g/L1.0ND o-Xylene g/L0.50ND g/L 25.0 70-130Surrogate: 1,2-Dichloroethane-d4 97.524.4 g/L 25.0 70-130Surrogate: Toluene-d8 97.224.3 g/L 25.0 70-130Surrogate: 4-Bromofluorobenzene 92.023.0 LCS (B340215-BS1) Prepared & Analyzed: 05/15/23 Acetone g/L50 100 70-13093.093.0 Benzene g/L0.50 10.0 70-13011411.4 Bromobenzene g/L0.50 10.0 70-13010310.3 Bromochloromethane g/L0.50 10.0 70-13011711.7 Bromodichloromethane g/L0.50 10.0 70-13097.69.76 Bromoform g/L0.50 10.0 70-13082.38.23 Bromomethane g/L2.0 10.0 60-14013513.5 2-Butanone (MEK)g/L5.0 100 70-130104104 n-Butylbenzene g/L0.50 10.0 70-13010410.4 sec-Butylbenzene g/L0.50 10.0 70-13099.69.96 tert-Butylbenzene g/L0.50 10.0 70-13010110.1 Carbon Tetrachloride g/L0.50 10.0 70-13094.69.46 Chlorobenzene g/L0.50 10.0 70-13011011.0 Ethanol g/L50 100 70-13086.286.2 Chlorodibromomethane g/L0.50 10.0 70-13095.39.53 Chloroethane g/L0.50 10.0 60-14098.09.80 Chloroform g/L0.50 10.0 70-13010510.5 Chloromethane g/L0.60 10.0 60-14010910.9 2-Chlorotoluene g/L0.50 10.0 70-13010510.5 4-Chlorotoluene g/L0.50 10.0 70-13010410.4 1,2-Dibromoethane (EDB)g/L0.50 10.0 70-13099.29.92 1,2-Dichlorobenzene g/L0.50 10.0 70-13010610.6 1,3-Dichlorobenzene g/L0.50 10.0 70-13010910.9 1,4-Dichlorobenzene g/L0.50 10.0 70-13010610.6 Dichlorodifluoromethane (Freon 12)g/L0.50 10.0 60-14093.39.33 1,1-Dichloroethane g/L0.50 10.0 70-13010510.5 1,2-Dichloroethane g/L0.50 10.0 70-13010810.8 1,1-Dichloroethylene g/L0.50 10.0 70-13096.89.68 cis-1,2-Dichloroethylene g/L0.50 10.0 70-13010210.2 trans-1,2-Dichloroethylene g/L0.50 10.0 70-13099.89.98 1,2-Dichloropropane g/L0.50 10.0 70-13010510.5 1,3-Dichloropropane g/L0.50 10.0 70-13010310.3 2,2-Dichloropropane g/L0.50 10.0 70-13084.08.40 1,1-Dichloropropene g/L0.50 10.0 70-13010610.6 cis-1,3-Dichloropropene g/L0.50 10.0 70-13010110.1 trans-1,3-Dichloropropene g/L0.50 10.0 70-13097.79.77 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340215 - SW-846 5030B LCS (B340215-BS1) Prepared & Analyzed: 05/15/23 Diisopropyl Ether (DIPE)g/L0.50 10.0 70-13010710.7 Ethylbenzene g/L0.50 10.0 70-13010910.9 2-Hexanone (MBK)g/L5.0 100 70-13087.687.6 Isopropylbenzene (Cumene)g/L0.50 10.0 70-13010310.3 p-Isopropyltoluene (p-Cymene)g/L0.50 10.0 70-13010210.2 Methyl tert-Butyl Ether (MTBE)g/L0.50 10.0 70-13096.39.63 Methylene Chloride g/L5.0 10.0 70-13010210.2 4-Methyl-2-pentanone (MIBK)g/L5.0 100 70-13085.885.8 Naphthalene g/L0.50 10.0 70-13089.98.99 n-Propylbenzene g/L0.50 10.0 70-13010610.6 Styrene g/L0.50 10.0 70-13010710.7 1,1,2,2-Tetrachloroethane g/L0.50 10.0 70-13095.49.54 Tetrachloroethylene g/L0.50 10.0 70-13010710.7 Toluene g/L0.50 10.0 70-13010610.6 1,2,3-Trichlorobenzene g/L1.0 10.0 70-13010210.2 1,2,4-Trichlorobenzene g/L0.50 10.0 70-13010310.3 1,1,1-Trichloroethane g/L0.50 10.0 70-13099.69.96 1,1,2-Trichloroethane g/L0.50 10.0 70-13010110.1 Trichloroethylene g/L0.50 10.0 70-13010310.3 Trichlorofluoromethane (Freon 11)g/L0.50 10.0 70-13096.39.63 1,2,3-Trichloropropane g/L0.50 10.0 R-0570-13012012.0 1,2,4-Trimethylbenzene g/L0.50 10.0 70-13010410.4 1,3,5-Trimethylbenzene g/L0.50 10.0 70-13010210.2 Vinyl Acetate g/L20 100 70-13082.882.8 Vinyl Chloride g/L0.50 10.0 60-14099.29.92 m+p Xylene g/L1.0 20.0 70-13010821.7 o-Xylene g/L0.50 10.0 70-13010510.5 g/L 25.0 70-130Surrogate: 1,2-Dichloroethane-d4 95.924.0 g/L 25.0 70-130Surrogate: Toluene-d8 10025.0 g/L 25.0 70-130Surrogate: 4-Bromofluorobenzene 96.824.2 LCS Dup (B340215-BSD1) Prepared & Analyzed: 05/15/23 Acetone g/L50 100 2570-13092.1 0.87592.1 Benzene g/L0.50 10.0 2570-130115 0.43711.5 Bromobenzene g/L0.50 10.0 2570-130106 2.7810.6 Bromochloromethane g/L0.50 10.0 2570-130114 2.6911.4 Bromodichloromethane g/L0.50 10.0 2570-13085.4 13.38.54 Bromoform g/L0.50 10.0 2570-13079.5 3.467.95 Bromomethane g/L2.0 10.0 2560-140139 2.4813.9 2-Butanone (MEK)g/L5.0 100 2570-130101 3.62101 n-Butylbenzene g/L0.50 10.0 2570-130105 0.85810.5 sec-Butylbenzene g/L0.50 10.0 2570-130101 0.99910.1 tert-Butylbenzene g/L0.50 10.0 2570-13099.3 1.509.93 Carbon Tetrachloride g/L0.50 10.0 2570-13096.5 1.999.65 Chlorobenzene g/L0.50 10.0 2570-130110 0.18111.0 Ethanol g/L50 100 2570-13083.4 3.1883.4 Chlorodibromomethane g/L0.50 10.0 2570-13081.9 15.18.19 Chloroethane g/L0.50 10.0 2560-140101 2.7210.1 Chloroform g/L0.50 10.0 2570-130103 1.8210.3 Chloromethane g/L0.60 10.0 2560-140108 1.2010.8 2-Chlorotoluene g/L0.50 10.0 2570-130105 0.0010.5 4-Chlorotoluene g/L0.50 10.0 2570-130107 3.2210.7 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340215 - SW-846 5030B LCS Dup (B340215-BSD1) Prepared & Analyzed: 05/15/23 1,2-Dibromoethane (EDB)g/L0.50 10.0 2570-13091.6 7.979.16 1,2-Dichlorobenzene g/L0.50 10.0 2570-130108 1.2110.8 1,3-Dichlorobenzene g/L0.50 10.0 2570-130106 3.3610.6 1,4-Dichlorobenzene g/L0.50 10.0 2570-130102 3.1710.2 Dichlorodifluoromethane (Freon 12)g/L0.50 10.0 2560-14096.0 2.859.60 1,1-Dichloroethane g/L0.50 10.0 2570-130104 0.96110.4 1,2-Dichloroethane g/L0.50 10.0 2570-13095.5 12.19.55 1,1-Dichloroethylene g/L0.50 10.0 2570-13097.4 0.6189.74 cis-1,2-Dichloroethylene g/L0.50 10.0 2570-130102 0.49010.2 trans-1,2-Dichloroethylene g/L0.50 10.0 2570-13098.2 1.629.82 1,2-Dichloropropane g/L0.50 10.0 2570-13094.0 10.89.40 1,3-Dichloropropane g/L0.50 10.0 2570-13093.2 9.999.32 2,2-Dichloropropane g/L0.50 10.0 2570-13083.0 1.208.30 1,1-Dichloropropene g/L0.50 10.0 2570-130106 0.28210.6 cis-1,3-Dichloropropene g/L0.50 10.0 2570-13087.3 14.28.73 trans-1,3-Dichloropropene g/L0.50 10.0 2570-13084.0 15.18.40 Diisopropyl Ether (DIPE)g/L0.50 10.0 2570-130108 1.1210.8 Ethylbenzene g/L0.50 10.0 2570-130111 1.7211.1 2-Hexanone (MBK)g/L5.0 100 2570-13079.9 9.1079.9 Isopropylbenzene (Cumene)g/L0.50 10.0 2570-130106 2.5910.6 p-Isopropyltoluene (p-Cymene)g/L0.50 10.0 2570-130102 0.49110.2 Methyl tert-Butyl Ether (MTBE)g/L0.50 10.0 2570-13095.2 1.159.52 Methylene Chloride g/L5.0 10.0 2570-13099.6 1.999.96 4-Methyl-2-pentanone (MIBK)g/L5.0 100 2570-13076.6 11.376.6 Naphthalene g/L0.50 10.0 2570-13088.4 1.688.84 n-Propylbenzene g/L0.50 10.0 2570-130109 2.7010.9 Styrene g/L0.50 10.0 2570-130107 0.65510.7 1,1,2,2-Tetrachloroethane g/L0.50 10.0 2570-13095.8 0.4189.58 Tetrachloroethylene g/L0.50 10.0 2570-13096.2 10.79.62 Toluene g/L0.50 10.0 2570-13098.4 7.539.84 1,2,3-Trichlorobenzene g/L1.0 10.0 2570-130100 1.4810.0 1,2,4-Trichlorobenzene g/L0.50 10.0 2570-13099.6 3.369.96 1,1,1-Trichloroethane g/L0.50 10.0 2570-13099.8 0.2019.98 1,1,2-Trichloroethane g/L0.50 10.0 2570-13092.7 8.379.27 Trichloroethylene g/L0.50 10.0 2570-130105 1.8310.5 Trichlorofluoromethane (Freon 11)g/L0.50 10.0 2570-13098.8 2.569.88 1,2,3-Trichloropropane g/L0.50 10.0 25 R-0570-13085.8 33.1 *8.58 1,2,4-Trimethylbenzene g/L0.50 10.0 2570-130102 1.4610.2 1,3,5-Trimethylbenzene g/L0.50 10.0 2570-130106 3.9610.6 Vinyl Acetate g/L20 100 2570-13084.0 1.4984.0 Vinyl Chloride g/L0.50 10.0 2560-140100 1.2010.0 m+p Xylene g/L1.0 20.0 2570-130110 1.6022.0 o-Xylene g/L0.50 10.0 2570-130107 1.6910.7 g/L 25.0 70-130Surrogate: 1,2-Dichloroethane-d4 96.024.0 g/L 25.0 70-130Surrogate: Toluene-d8 89.722.4 g/L 25.0 70-130Surrogate: 4-Bromofluorobenzene 98.324.6 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340343 - SW-846 5030B [TOC_3]B340343[TOC] Blank (B340343-BLK1) Prepared: 05/16/23 Analyzed: 05/18/23 Acetone g/L50ND Benzene g/L0.50ND Bromobenzene g/L0.50ND Bromochloromethane g/L0.50ND Bromodichloromethane g/L0.50ND Bromoform g/L0.50ND Bromomethane g/L2.0ND 2-Butanone (MEK)g/L5.0ND n-Butylbenzene g/L0.50ND sec-Butylbenzene g/L0.50ND tert-Butylbenzene g/L0.50ND Carbon Tetrachloride g/L0.50ND Chlorobenzene g/L0.50ND Ethanol g/L50ND Chlorodibromomethane g/L0.50ND Chloroethane g/L0.50ND Chloroform g/L0.50ND Chloromethane g/L0.60ND 2-Chlorotoluene g/L0.50ND 4-Chlorotoluene g/L0.50ND 1,2-Dibromoethane (EDB)g/L0.50ND 1,2-Dichlorobenzene g/L0.50ND 1,3-Dichlorobenzene g/L0.50ND 1,4-Dichlorobenzene g/L0.50ND Dichlorodifluoromethane (Freon 12)g/L0.50ND 1,1-Dichloroethane g/L0.50ND 1,2-Dichloroethane g/L0.50ND 1,1-Dichloroethylene g/L0.50ND cis-1,2-Dichloroethylene g/L0.50ND trans-1,2-Dichloroethylene g/L0.50ND 1,2-Dichloropropane g/L0.50ND 1,3-Dichloropropane g/L0.50ND 2,2-Dichloropropane g/L0.50ND 1,1-Dichloropropene g/L0.50ND cis-1,3-Dichloropropene g/L0.50ND trans-1,3-Dichloropropene g/L0.50ND Diisopropyl Ether (DIPE)g/L0.50ND Ethylbenzene g/L0.50ND 2-Hexanone (MBK)g/L5.0ND Isopropylbenzene (Cumene)g/L0.50ND p-Isopropyltoluene (p-Cymene)g/L0.50ND Methyl tert-Butyl Ether (MTBE)g/L0.50ND Methylene Chloride g/L5.0ND 4-Methyl-2-pentanone (MIBK)g/L5.0ND Naphthalene g/L0.50ND n-Propylbenzene g/L0.50ND Styrene g/L0.50ND 1,1,2,2-Tetrachloroethane g/L0.50ND Tetrachloroethylene g/L0.50ND Toluene g/L0.50ND 1,2,3-Trichlorobenzene g/L1.0ND 1,2,4-Trichlorobenzene g/L0.50ND 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340343 - SW-846 5030B Blank (B340343-BLK1) Prepared: 05/16/23 Analyzed: 05/18/23 1,1,1-Trichloroethane g/L0.50ND 1,1,2-Trichloroethane g/L0.50ND Trichloroethylene g/L0.50ND Trichlorofluoromethane (Freon 11)g/L0.50ND 1,2,3-Trichloropropane g/L0.50ND 1,2,4-Trimethylbenzene g/L0.50ND 1,3,5-Trimethylbenzene g/L0.50ND Vinyl Acetate g/L20ND Vinyl Chloride g/L0.50ND m+p Xylene g/L1.0ND o-Xylene g/L0.50ND g/L 25.0 70-130Surrogate: 1,2-Dichloroethane-d4 10225.6 g/L 25.0 70-130Surrogate: Toluene-d8 10025.1 g/L 25.0 70-130Surrogate: 4-Bromofluorobenzene 98.324.6 LCS (B340343-BS1) Prepared: 05/16/23 Analyzed: 05/17/23 Acetone g/L50 100 70-13084.684.6 Benzene g/L0.50 10.0 70-13010610.6 Bromobenzene g/L0.50 10.0 70-13010410.4 Bromochloromethane g/L0.50 10.0 70-13010810.8 Bromodichloromethane g/L0.50 10.0 70-13099.49.94 Bromoform g/L0.50 10.0 70-13084.28.42 Bromomethane g/L2.0 10.0 60-14010510.5 2-Butanone (MEK)g/L5.0 100 70-130105105 n-Butylbenzene g/L0.50 10.0 70-13098.69.86 sec-Butylbenzene g/L0.50 10.0 70-13010110.1 tert-Butylbenzene g/L0.50 10.0 70-13010110.1 Carbon Tetrachloride g/L0.50 10.0 70-13010210.2 Chlorobenzene g/L0.50 10.0 70-13099.99.99 Ethanol g/L50 100 70-13092.092.0 Chlorodibromomethane g/L0.50 10.0 70-13097.89.78 Chloroethane g/L0.50 10.0 60-14096.59.65 Chloroform g/L0.50 10.0 70-13010810.8 Chloromethane g/L0.60 10.0 60-14011811.8 2-Chlorotoluene g/L0.50 10.0 70-13092.59.25 4-Chlorotoluene g/L0.50 10.0 70-13099.09.90 1,2-Dibromoethane (EDB)g/L0.50 10.0 70-13010510.5 1,2-Dichlorobenzene g/L0.50 10.0 70-13010210.2 1,3-Dichlorobenzene g/L0.50 10.0 70-13010410.4 1,4-Dichlorobenzene g/L0.50 10.0 70-13099.19.91 Dichlorodifluoromethane (Freon 12)g/L0.50 10.0 60-14084.78.47 1,1-Dichloroethane g/L0.50 10.0 70-13011211.2 1,2-Dichloroethane g/L0.50 10.0 70-13010210.2 1,1-Dichloroethylene g/L0.50 10.0 70-13081.88.18 cis-1,2-Dichloroethylene g/L0.50 10.0 70-13010910.9 trans-1,2-Dichloroethylene g/L0.50 10.0 70-13010810.8 1,2-Dichloropropane g/L0.50 10.0 70-13010210.2 1,3-Dichloropropane g/L0.50 10.0 70-13010610.6 2,2-Dichloropropane g/L0.50 10.0 70-13085.68.56 1,1-Dichloropropene g/L0.50 10.0 70-13010610.6 cis-1,3-Dichloropropene g/L0.50 10.0 70-13010310.3 trans-1,3-Dichloropropene g/L0.50 10.0 70-13010110.1 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340343 - SW-846 5030B LCS (B340343-BS1) Prepared: 05/16/23 Analyzed: 05/17/23 Diisopropyl Ether (DIPE)g/L0.50 10.0 70-13010310.3 Ethylbenzene g/L0.50 10.0 70-13010110.1 2-Hexanone (MBK)g/L5.0 100 70-130107107 Isopropylbenzene (Cumene)g/L0.50 10.0 70-13097.89.78 p-Isopropyltoluene (p-Cymene)g/L0.50 10.0 70-13097.89.78 Methyl tert-Butyl Ether (MTBE)g/L0.50 10.0 70-13099.49.94 Methylene Chloride g/L5.0 10.0 70-13083.68.36 4-Methyl-2-pentanone (MIBK)g/L5.0 100 70-130106106 Naphthalene g/L0.50 10.0 70-13096.89.68 n-Propylbenzene g/L0.50 10.0 70-13097.79.77 Styrene g/L0.50 10.0 70-13099.09.90 1,1,2,2-Tetrachloroethane g/L0.50 10.0 70-13099.59.95 Tetrachloroethylene g/L0.50 10.0 70-13010210.2 Toluene g/L0.50 10.0 70-13010510.5 1,2,3-Trichlorobenzene g/L1.0 10.0 70-13010410.4 1,2,4-Trichlorobenzene g/L0.50 10.0 70-13099.59.95 1,1,1-Trichloroethane g/L0.50 10.0 70-13010610.6 1,1,2-Trichloroethane g/L0.50 10.0 70-13010810.8 Trichloroethylene g/L0.50 10.0 70-13010810.8 Trichlorofluoromethane (Freon 11)g/L0.50 10.0 70-13076.37.63 1,2,3-Trichloropropane g/L0.50 10.0 70-13010710.7 1,2,4-Trimethylbenzene g/L0.50 10.0 70-13010210.2 1,3,5-Trimethylbenzene g/L0.50 10.0 70-13096.79.67 Vinyl Acetate g/L20 100 70-13098.098.0 Vinyl Chloride g/L0.50 10.0 60-14073.77.37 m+p Xylene g/L1.0 20.0 70-13099.820.0 o-Xylene g/L0.50 10.0 70-13010310.3 g/L 25.0 70-130Surrogate: 1,2-Dichloroethane-d4 10325.7 g/L 25.0 70-130Surrogate: Toluene-d8 10025.1 g/L 25.0 70-130Surrogate: 4-Bromofluorobenzene 10125.4 LCS Dup (B340343-BSD1) Prepared: 05/16/23 Analyzed: 05/17/23 Acetone g/L50 100 2570-13088.4 4.4488.4 Benzene g/L0.50 10.0 2570-130109 2.8910.9 Bromobenzene g/L0.50 10.0 2570-130106 2.3810.6 Bromochloromethane g/L0.50 10.0 2570-130112 4.0911.2 Bromodichloromethane g/L0.50 10.0 2570-130101 1.6010.1 Bromoform g/L0.50 10.0 2570-13084.3 0.1198.43 Bromomethane g/L2.0 10.0 2560-140110 5.4011.0 2-Butanone (MEK)g/L5.0 100 2570-130103 2.26103 n-Butylbenzene g/L0.50 10.0 2570-130104 5.2310.4 sec-Butylbenzene g/L0.50 10.0 2570-130107 5.2010.7 tert-Butylbenzene g/L0.50 10.0 2570-130107 5.9510.7 Carbon Tetrachloride g/L0.50 10.0 2570-130107 4.8710.7 Chlorobenzene g/L0.50 10.0 2570-130104 4.4110.4 Ethanol g/L50 100 2570-13094.3 2.4994.3 Chlorodibromomethane g/L0.50 10.0 2570-13099.4 1.629.94 Chloroethane g/L0.50 10.0 2560-14089.8 7.198.98 Chloroform g/L0.50 10.0 2570-130109 1.6610.9 Chloromethane g/L0.60 10.0 2560-14099.3 17.09.93 2-Chlorotoluene g/L0.50 10.0 2570-13095.6 3.309.56 4-Chlorotoluene g/L0.50 10.0 2570-130104 4.5410.4 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340343 - SW-846 5030B LCS Dup (B340343-BSD1) Prepared: 05/16/23 Analyzed: 05/17/23 1,2-Dibromoethane (EDB)g/L0.50 10.0 2570-130105 0.19010.5 1,2-Dichlorobenzene g/L0.50 10.0 2570-130106 4.7110.6 1,3-Dichlorobenzene g/L0.50 10.0 2570-130107 2.7510.7 1,4-Dichlorobenzene g/L0.50 10.0 2570-130102 2.8810.2 Dichlorodifluoromethane (Freon 12)g/L0.50 10.0 2560-14087.5 3.258.75 1,1-Dichloroethane g/L0.50 10.0 2570-130116 3.6811.6 1,2-Dichloroethane g/L0.50 10.0 2570-130103 0.78010.3 1,1-Dichloroethylene g/L0.50 10.0 2570-13084.8 3.608.48 cis-1,2-Dichloroethylene g/L0.50 10.0 2570-130113 3.8811.3 trans-1,2-Dichloroethylene g/L0.50 10.0 2570-130112 3.0911.2 1,2-Dichloropropane g/L0.50 10.0 2570-130108 5.2510.8 1,3-Dichloropropane g/L0.50 10.0 2570-130109 2.2310.9 2,2-Dichloropropane g/L0.50 10.0 2570-13085.1 0.5868.51 1,1-Dichloropropene g/L0.50 10.0 2570-130111 4.7011.1 cis-1,3-Dichloropropene g/L0.50 10.0 2570-130106 2.7810.6 trans-1,3-Dichloropropene g/L0.50 10.0 2570-130101 0.29610.1 Diisopropyl Ether (DIPE)g/L0.50 10.0 2570-130108 3.8910.8 Ethylbenzene g/L0.50 10.0 2570-130105 3.8910.5 2-Hexanone (MBK)g/L5.0 100 2570-130108 0.569108 Isopropylbenzene (Cumene)g/L0.50 10.0 2570-130101 3.6110.1 p-Isopropyltoluene (p-Cymene)g/L0.50 10.0 2570-130102 4.3010.2 Methyl tert-Butyl Ether (MTBE)g/L0.50 10.0 2570-13098.6 0.8089.86 Methylene Chloride g/L5.0 10.0 2570-13082.8 0.9628.28 4-Methyl-2-pentanone (MIBK)g/L5.0 100 2570-130104 1.61104 Naphthalene g/L0.50 10.0 2570-13098.7 1.949.87 n-Propylbenzene g/L0.50 10.0 2570-130103 5.3810.3 Styrene g/L0.50 10.0 2570-130101 1.6010.1 1,1,2,2-Tetrachloroethane g/L0.50 10.0 2570-13098.7 0.8079.87 Tetrachloroethylene g/L0.50 10.0 2570-130108 5.2310.8 Toluene g/L0.50 10.0 2570-130109 4.3910.9 1,2,3-Trichlorobenzene g/L1.0 10.0 2570-130108 4.1510.8 1,2,4-Trichlorobenzene g/L0.50 10.0 2570-13099.7 0.2019.97 1,1,1-Trichloroethane g/L0.50 10.0 2570-130110 3.9011.0 1,1,2-Trichloroethane g/L0.50 10.0 2570-130110 1.7411.0 Trichloroethylene g/L0.50 10.0 2570-130112 4.0911.2 Trichlorofluoromethane (Freon 11)g/L0.50 10.0 2570-13079.1 3.607.91 1,2,3-Trichloropropane g/L0.50 10.0 2570-130109 2.1310.9 1,2,4-Trimethylbenzene g/L0.50 10.0 2570-130107 4.6110.7 1,3,5-Trimethylbenzene g/L0.50 10.0 2570-130101 4.4510.1 Vinyl Acetate g/L20 100 2570-13087.3 11.587.3 Vinyl Chloride g/L0.50 10.0 2560-14081.2 9.688.12 m+p Xylene g/L1.0 20.0 2570-130104 4.0220.8 o-Xylene g/L0.50 10.0 2570-130106 3.1510.6 g/L 25.0 70-130Surrogate: 1,2-Dichloroethane-d4 10325.7 g/L 25.0 70-130Surrogate: Toluene-d8 99.224.8 g/L 25.0 70-130Surrogate: 4-Bromofluorobenzene 10125.2 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340602 - SW-846 5030B [TOC_3]B340602[TOC] Blank (B340602-BLK1) Prepared & Analyzed: 05/18/23 Acetone g/L50ND Benzene g/L0.50ND Bromobenzene g/L0.50ND Bromochloromethane g/L0.50ND Bromodichloromethane g/L0.50ND Bromoform g/L0.50ND Bromomethane g/L2.0ND 2-Butanone (MEK)g/L5.0ND n-Butylbenzene g/L0.50ND sec-Butylbenzene g/L0.50ND tert-Butylbenzene g/L0.50ND Carbon Tetrachloride g/L0.50ND Chlorobenzene g/L0.50ND Ethanol g/L50ND Chlorodibromomethane g/L0.50ND Chloroethane g/L0.50ND Chloroform g/L0.50ND Chloromethane g/L0.60ND 2-Chlorotoluene g/L0.50ND 4-Chlorotoluene g/L0.50ND 1,2-Dibromoethane (EDB)g/L0.50ND 1,2-Dichlorobenzene g/L0.50ND 1,3-Dichlorobenzene g/L0.50ND 1,4-Dichlorobenzene g/L0.50ND Dichlorodifluoromethane (Freon 12)g/L0.50ND 1,1-Dichloroethane g/L0.50ND 1,2-Dichloroethane g/L0.50ND 1,1-Dichloroethylene g/L0.50ND cis-1,2-Dichloroethylene g/L0.50ND trans-1,2-Dichloroethylene g/L0.50ND 1,2-Dichloropropane g/L0.50ND 1,3-Dichloropropane g/L0.50ND 2,2-Dichloropropane g/L0.50ND 1,1-Dichloropropene g/L0.50ND cis-1,3-Dichloropropene g/L0.50ND trans-1,3-Dichloropropene g/L0.50ND Diisopropyl Ether (DIPE)g/L0.50ND Ethylbenzene g/L0.50ND 2-Hexanone (MBK)g/L5.0ND Isopropylbenzene (Cumene)g/L0.50ND p-Isopropyltoluene (p-Cymene)g/L0.50ND Methyl tert-Butyl Ether (MTBE)g/L0.50ND Methylene Chloride g/L5.0ND 4-Methyl-2-pentanone (MIBK)g/L5.0ND Naphthalene g/L0.50ND n-Propylbenzene g/L0.50ND Styrene g/L0.50ND 1,1,2,2-Tetrachloroethane g/L0.50ND Tetrachloroethylene g/L0.50ND Toluene g/L0.50ND 1,2,3-Trichlorobenzene g/L1.0ND 1,2,4-Trichlorobenzene g/L0.50ND 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340602 - SW-846 5030B Blank (B340602-BLK1) Prepared & Analyzed: 05/18/23 1,1,1-Trichloroethane g/L0.50ND 1,1,2-Trichloroethane g/L0.50ND Trichloroethylene g/L0.50ND Trichlorofluoromethane (Freon 11)g/L0.50ND 1,2,3-Trichloropropane g/L0.50ND 1,2,4-Trimethylbenzene g/L0.50ND 1,3,5-Trimethylbenzene g/L0.50ND Vinyl Acetate g/L20ND Vinyl Chloride g/L0.50ND m+p Xylene g/L1.0ND o-Xylene g/L0.50ND g/L 25.0 70-130Surrogate: 1,2-Dichloroethane-d4 96.224.0 g/L 25.0 70-130Surrogate: Toluene-d8 99.224.8 g/L 25.0 70-130Surrogate: 4-Bromofluorobenzene 96.024.0 LCS (B340602-BS1) Prepared & Analyzed: 05/18/23 Acetone g/L50 100 70-13089.289.2 Benzene g/L0.50 10.0 70-13011211.2 Bromobenzene g/L0.50 10.0 70-13010210.2 Bromochloromethane g/L0.50 10.0 70-13011511.5 Bromodichloromethane g/L0.50 10.0 70-13099.29.92 Bromoform g/L0.50 10.0 70-13079.07.90 Bromomethane g/L2.0 10.0 60-14011911.9 2-Butanone (MEK)g/L5.0 100 70-130101101 n-Butylbenzene g/L0.50 10.0 70-13010710.7 sec-Butylbenzene g/L0.50 10.0 70-13010210.2 tert-Butylbenzene g/L0.50 10.0 70-13010110.1 Carbon Tetrachloride g/L0.50 10.0 70-13010110.1 Chlorobenzene g/L0.50 10.0 70-13010510.5 Ethanol g/L50 100 70-13072.772.7 Chlorodibromomethane g/L0.50 10.0 70-13093.79.37 Chloroethane g/L0.50 10.0 60-14093.59.35 Chloroform g/L0.50 10.0 70-13010210.2 Chloromethane g/L0.60 10.0 60-14010110.1 2-Chlorotoluene g/L0.50 10.0 70-13010210.2 4-Chlorotoluene g/L0.50 10.0 70-13010310.3 1,2-Dibromoethane (EDB)g/L0.50 10.0 70-13010110.1 1,2-Dichlorobenzene g/L0.50 10.0 70-13010410.4 1,3-Dichlorobenzene g/L0.50 10.0 70-13010210.2 1,4-Dichlorobenzene g/L0.50 10.0 70-13010010.0 Dichlorodifluoromethane (Freon 12)g/L0.50 10.0 60-14097.69.76 1,1-Dichloroethane g/L0.50 10.0 70-13010410.4 1,2-Dichloroethane g/L0.50 10.0 70-13094.79.47 1,1-Dichloroethylene g/L0.50 10.0 70-13093.99.39 cis-1,2-Dichloroethylene g/L0.50 10.0 70-13010310.3 trans-1,2-Dichloroethylene g/L0.50 10.0 70-13098.39.83 1,2-Dichloropropane g/L0.50 10.0 70-13010910.9 1,3-Dichloropropane g/L0.50 10.0 70-13010710.7 2,2-Dichloropropane g/L0.50 10.0 70-13085.68.56 1,1-Dichloropropene g/L0.50 10.0 70-13010410.4 cis-1,3-Dichloropropene g/L0.50 10.0 70-13010510.5 trans-1,3-Dichloropropene g/L0.50 10.0 70-13098.09.80 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340602 - SW-846 5030B LCS (B340602-BS1) Prepared & Analyzed: 05/18/23 Diisopropyl Ether (DIPE)g/L0.50 10.0 70-13010810.8 Ethylbenzene g/L0.50 10.0 70-13010610.6 2-Hexanone (MBK)g/L5.0 100 70-13090.890.8 Isopropylbenzene (Cumene)g/L0.50 10.0 70-13010310.3 p-Isopropyltoluene (p-Cymene)g/L0.50 10.0 70-13010410.4 Methyl tert-Butyl Ether (MTBE)g/L0.50 10.0 70-13097.69.76 Methylene Chloride g/L5.0 10.0 70-13099.09.90 4-Methyl-2-pentanone (MIBK)g/L5.0 100 70-13089.889.8 Naphthalene g/L0.50 10.0 70-13093.29.32 n-Propylbenzene g/L0.50 10.0 70-13010410.4 Styrene g/L0.50 10.0 70-13010710.7 1,1,2,2-Tetrachloroethane g/L0.50 10.0 70-13090.69.06 Tetrachloroethylene g/L0.50 10.0 70-13010010.0 Toluene g/L0.50 10.0 70-13010610.6 1,2,3-Trichlorobenzene g/L1.0 10.0 70-13010110.1 1,2,4-Trichlorobenzene g/L0.50 10.0 70-13010010.0 1,1,1-Trichloroethane g/L0.50 10.0 70-13098.89.88 1,1,2-Trichloroethane g/L0.50 10.0 70-13010410.4 Trichloroethylene g/L0.50 10.0 70-13010410.4 Trichlorofluoromethane (Freon 11)g/L0.50 10.0 70-13091.49.14 1,2,3-Trichloropropane g/L0.50 10.0 70-13012012.0 1,2,4-Trimethylbenzene g/L0.50 10.0 70-13010110.1 1,3,5-Trimethylbenzene g/L0.50 10.0 70-13010210.2 Vinyl Acetate g/L20 100 70-13079.979.9 Vinyl Chloride g/L0.50 10.0 60-14011211.2 m+p Xylene g/L1.0 20.0 70-13010420.8 o-Xylene g/L0.50 10.0 70-13010210.2 g/L 25.0 70-130Surrogate: 1,2-Dichloroethane-d4 93.923.5 g/L 25.0 70-130Surrogate: Toluene-d8 10125.3 g/L 25.0 70-130Surrogate: 4-Bromofluorobenzene 99.124.8 LCS Dup (B340602-BSD1) Prepared & Analyzed: 05/18/23 Acetone g/L50 100 2570-13091.2 2.2591.2 Benzene g/L0.50 10.0 2570-130110 2.3411.0 Bromobenzene g/L0.50 10.0 2570-130104 1.7410.4 Bromochloromethane g/L0.50 10.0 2570-130112 2.5611.2 Bromodichloromethane g/L0.50 10.0 2570-13098.4 0.8109.84 Bromoform g/L0.50 10.0 2570-13079.6 0.7577.96 Bromomethane g/L2.0 10.0 2560-140123 3.4612.3 2-Butanone (MEK)g/L5.0 100 2570-130101 0.148101 n-Butylbenzene g/L0.50 10.0 2570-130102 4.4010.2 sec-Butylbenzene g/L0.50 10.0 2570-130100 1.7810.0 tert-Butylbenzene g/L0.50 10.0 2570-13099.2 2.099.92 Carbon Tetrachloride g/L0.50 10.0 2570-13097.1 4.239.71 Chlorobenzene g/L0.50 10.0 2570-130102 2.7110.2 Ethanol g/L50 100 2570-13078.5 7.7178.5 Chlorodibromomethane g/L0.50 10.0 2570-13092.4 1.409.24 Chloroethane g/L0.50 10.0 2560-14087.8 6.298.78 Chloroform g/L0.50 10.0 2570-130102 0.58910.2 Chloromethane g/L0.60 10.0 2560-14095.9 5.189.59 2-Chlorotoluene g/L0.50 10.0 2570-130103 0.68510.3 4-Chlorotoluene g/L0.50 10.0 2570-130102 0.29310.2 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 Result Limit Reporting Units Level Spike Result Source %REC %REC Limits RPD RPD Limit Notes Analyte Volatile Organic Compounds by GC/MS - Quality Control QUALITY CONTROL Batch B340602 - SW-846 5030B LCS Dup (B340602-BSD1) Prepared & Analyzed: 05/18/23 1,2-Dibromoethane (EDB)g/L0.50 10.0 2570-130101 0.0010.1 1,2-Dichlorobenzene g/L0.50 10.0 2570-130101 2.4410.1 1,3-Dichlorobenzene g/L0.50 10.0 2570-130103 0.29310.3 1,4-Dichlorobenzene g/L0.50 10.0 2570-13097.0 3.159.70 Dichlorodifluoromethane (Freon 12)g/L0.50 10.0 2560-14087.7 10.78.77 1,1-Dichloroethane g/L0.50 10.0 2570-130102 2.7210.2 1,2-Dichloroethane g/L0.50 10.0 2570-13094.8 0.1069.48 1,1-Dichloroethylene g/L0.50 10.0 2570-13089.6 4.698.96 cis-1,2-Dichloroethylene g/L0.50 10.0 2570-13098.6 4.569.86 trans-1,2-Dichloroethylene g/L0.50 10.0 2570-13091.8 6.849.18 1,2-Dichloropropane g/L0.50 10.0 2570-130106 3.0610.6 1,3-Dichloropropane g/L0.50 10.0 2570-130102 4.2110.2 2,2-Dichloropropane g/L0.50 10.0 2570-13081.1 5.408.11 1,1-Dichloropropene g/L0.50 10.0 2570-130101 3.4110.1 cis-1,3-Dichloropropene g/L0.50 10.0 2570-130101 4.4610.1 trans-1,3-Dichloropropene g/L0.50 10.0 2570-13096.7 1.349.67 Diisopropyl Ether (DIPE)g/L0.50 10.0 2570-130104 3.5910.4 Ethylbenzene g/L0.50 10.0 2570-130104 2.0910.4 2-Hexanone (MBK)g/L5.0 100 2570-13091.7 1.0191.7 Isopropylbenzene (Cumene)g/L0.50 10.0 2570-130101 1.7710.1 p-Isopropyltoluene (p-Cymene)g/L0.50 10.0 2570-130102 2.4210.2 Methyl tert-Butyl Ether (MTBE)g/L0.50 10.0 2570-13096.3 1.349.63 Methylene Chloride g/L5.0 10.0 2570-13095.4 3.709.54 4-Methyl-2-pentanone (MIBK)g/L5.0 100 2570-13090.2 0.47890.2 Naphthalene g/L0.50 10.0 2570-13089.3 4.278.93 n-Propylbenzene g/L0.50 10.0 2570-130104 0.096310.4 Styrene g/L0.50 10.0 2570-130106 0.75010.6 1,1,2,2-Tetrachloroethane g/L0.50 10.0 2570-13091.2 0.6609.12 Tetrachloroethylene g/L0.50 10.0 2570-13099.6 0.7009.96 Toluene g/L0.50 10.0 2570-130103 2.8710.3 1,2,3-Trichlorobenzene g/L1.0 10.0 2570-13097.7 3.129.77 1,2,4-Trichlorobenzene g/L0.50 10.0 2570-130101 0.79410.1 1,1,1-Trichloroethane g/L0.50 10.0 2570-13098.8 0.009.88 1,1,2-Trichloroethane g/L0.50 10.0 2570-130102 1.3610.2 Trichloroethylene g/L0.50 10.0 2570-130102 2.3310.2 Trichlorofluoromethane (Freon 11)g/L0.50 10.0 2570-13085.8 6.328.58 1,2,3-Trichloropropane g/L0.50 10.0 2570-13093.3 24.79.33 1,2,4-Trimethylbenzene g/L0.50 10.0 2570-13097.6 3.629.76 1,3,5-Trimethylbenzene g/L0.50 10.0 2570-130100 2.1710.0 Vinyl Acetate g/L20 100 2570-13072.2 10.172.2 Vinyl Chloride g/L0.50 10.0 2560-140107 5.2010.7 m+p Xylene g/L1.0 20.0 2570-130102 2.0920.4 o-Xylene g/L0.50 10.0 2570-130101 1.1810.1 g/L 25.0 70-130Surrogate: 1,2-Dichloroethane-d4 93.623.4 g/L 25.0 70-130Surrogate: Toluene-d8 10125.2 g/L 25.0 70-130Surrogate: 4-Bromofluorobenzene 98.824.7 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 *QC result is outside of established limits. Wide recovery limits established for difficult compound. Wide RPD limits established for difficult compound. #Data exceeded client recommended or regulatory level Percent recoveries and relative percent differences (RPDs) are determined by the software using values in the calculation which have not been rounded. No results have been blank subtracted unless specified in the case narrative section. FLAG/QUALIFIER SUMMARY Detected but below the Reporting Limit (lowest calibration standard); therefore, result is an estimated concentration (CLP J-Flag). J Laboratory fortified blank duplicate RPD is outside of control limits. Reduced precision is anticipated for any reported value for this compound. R-05 Elevated reporting limit due to high concentration of target compounds.RL-11 [TOC_1]Flag/Qualifier Summary[TOC] 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 CertificationsAnalyte CERTIFICATIONS Certified Analyses included in this Report SM21-23 6200B in Water NCAcetone NCBenzene NCBromobenzene NCBromochloromethane NCBromodichloromethane NCBromoform NCBromomethane NC2-Butanone (MEK) NCn-Butylbenzene NCsec-Butylbenzene NCtert-Butylbenzene NCCarbon Tetrachloride NCChlorobenzene NCEthanol NCChlorodibromomethane NCChloroethane NCChloroform NCChloromethane NC2-Chlorotoluene NC4-Chlorotoluene NC1,2-Dibromoethane (EDB) NC1,2-Dichlorobenzene NC1,3-Dichlorobenzene NC1,4-Dichlorobenzene NCDichlorodifluoromethane (Freon 12) NC1,1-Dichloroethane NC1,2-Dichloroethane NC1,1-Dichloroethylene NCcis-1,2-Dichloroethylene NCtrans-1,2-Dichloroethylene NC1,2-Dichloropropane NC1,3-Dichloropropane NC2,2-Dichloropropane NC1,1-Dichloropropene NCcis-1,3-Dichloropropene NCtrans-1,3-Dichloropropene NCDiisopropyl Ether (DIPE) NCEthylbenzene NC2-Hexanone (MBK) NCIsopropylbenzene (Cumene) NCp-Isopropyltoluene (p-Cymene) NCMethyl tert-Butyl Ether (MTBE) NCMethylene Chloride NC4-Methyl-2-pentanone (MIBK) NCNaphthalene NCn-Propylbenzene NCStyrene [TOC_1]Certifications[TOC] 39 Spruce Street * East Longmeadow, MA 01028 * FAX 413/525-6405 * TEL. 413/525-2332 CertificationsAnalyte CERTIFICATIONS Certified Analyses included in this Report SM21-23 6200B in Water NC1,1,2,2-Tetrachloroethane NCTetrachloroethylene NCToluene NC1,2,3-Trichlorobenzene NC1,2,4-Trichlorobenzene NC1,1,1-Trichloroethane NC1,1,2-Trichloroethane NCTrichloroethylene NCTrichlorofluoromethane (Freon 11) NC1,2,3-Trichloropropane NC1,2,4-Trimethylbenzene NC1,3,5-Trimethylbenzene NCVinyl Acetate NCVinyl Chloride NCm+p Xylene NCo-Xylene The CON-TEST Environmental Laboratory operates under the following certifications and accreditations: Code Description Number Expires 652North Carolina Div. of Water QualityNC 12/31/2023