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1119_DukeAsheville_GWMR_Sept2022_FID1767696_20230113
(� DUKE ENERGY January 13, 2023 North Carolina Department of Environmental Quality Division of Waste Management Solid Waste Section 2090 U.S. Highway 70 Swannanoa, NC 28778 Attn: Ms. Sarah Moutos (submitted electronically) Re: Semiannual Water Quality Monitoring Report — September 2022 CCR Landfill Permit No. 1119-INDUS-2020 Asheville Steam Electric Plant Buncombe County, North Carolina Dear Ms. Moutos: 526 South Church St. Charlotte, NC 28202 Mailing Address P.O. Box 1006 Mail Code EC 13K. Charlotte, NC 28201-1006 Duke Energy is providing the results of the September 2022 semiannual water quality monitoring for the Duke Energy Progress Asheville CCR Landfill (1119-INDUS), located in Arden, Buncombe County, North Carolina. Sampling was conducted on September 26, 2022, in accordance with the approved Water Quality Monitoring Plan (WQMP). The September 2022 monitoring event included samples from nine groundwater monitoring wells, two surface water locations, and one sample of composite leachate. Three surface water locations and one seep location are designated in the WQMP, however surface water sample LF-SW-1 and seep sample DP-4 were not sampled during the September 2022 sampling event because of dry conditions. The groundwater analytical results are compared to the groundwater standards found in Title 15A NCAC 02L .0202 (02L Standards). The surface water and seep analytical results are compared to the surface water standards found in Title 15A NCAC 02B .0211 (02B Standard) for Class C waters. Leachate analytical results are not compared to groundwater or surface water quality standards. Duke Energy personnel sample designated locations for groundwater, surface water, and leachate at the Asheville CCR Landfill semiannually during March and September. The next water quality monitoring event for the CCR Landfill is planned for March 2023 with a report of monitoring results to follow. If you have any questions or concerns with this submittal, please do not hesitate to contact me at Ashley. Healv(o)duke-energv.com or (717) 982-0986. Respectfully submitted, j4VAi Ashley Healy, P.G. Environmental Services Attachments: Semiannual Water Quality Monitoring Report — September 2022 Sampling Event; SynTerra, January 2023 www.duke-energy.com Page 1 of 2 cc (via e-mail): Claire Osborn, NCDEQ Elizabeth Werner, NCDEQ Sherri Stanley, NCDEQ Ed Mussler, NCDEQ Joe Wilson, Duke Energy John Toepfer, Duke Energy Connor Zahora, Duke Energy Nathan Grant, Duke Energy Teresa Williams, Duke Energy Tyler Hardin, Duke Energy Kelly Ferri, SynTerra Craig Eady, SynTerra www.duke-energy.com Page 2 of 2 DENR USE ONLY ❑Paper Report [-]Electronic Data - Email CD (data loaded: Yes / No) Doc/Event #: NC DENR I I Environmental Monitoring Division of Waste Management - Solid Waste Reporting Form Notice: This form and any information attached to it are "Public Records" as defined in NC General Statute 132-1. As such, these documents are available for inspection and examination by any person upon request (NC General Statute 132-6). Instructions: • Prepare one form for each individually monitored unit. • Please type or print legibly. • Attach a notification table with values that attain or exceed NC 2L groundwater standards or NC 2B surface water standards. The notification must include a preliminary analysis of the cause and significance of each value. (e.g. naturally occurring, off -site source, pre-existing condition, etc.). • Attach a notification table of any groundwater or surface water values that equal or exceed the reporting limits. • Attach a notification table of any methane gas values that attain or exceed explosive gas levels. This includes any structures on or nearby the facility (NCAC 13B .1629 (4)(a)(i). • Send the original signed and sealed form, any tables, and Electronic Data Deliverable to: Compliance Unit, NCDENR-DWM, Solid Waste Section, 1646 Mail Service Center, Raleigh, NC 27699-1646. Solid Waste Monitoring Data Submittal Information Name of entity submitting data (laboratory, consultant, facility owner): SynTerra Corporation (Consultant) Contact for questions about data formatting. Include data preparer's name, telephone number and E-mail address: Name: Kelly Ferri Phone: (864) 421-9999 E-mail: kferri(cDsvnterracorp.com NC Landfill Rule: Actual sampling dates (e.g., Facility name: Facility Address: Facility Permit# (.0500 or.1600) October 20-24, 2006) Duke Energy Progress 46 Duke Energy Lane 11119-INDUS-2020 1.0500 Se tember 26, 2022 Asheville Steam Electric Plant Arden, NC 28704 CCR Landfill Environmental Status: (Check all that apply) ❑ Initial/Background Monitoring ❑X Detection Monitoring ❑ Assessment Monitoring ❑ Corrective Action of data submitted: (Check all that apply) Groundwater monitoring data from monitoring wells ❑ Groundwater monitoring data from private water supply wells ❑ Leachate monitoring data Surface water monitoring data ❑ Methane gas monitoring data Corrective action data (specify) Other(specify) Notification attached? No. No groundwater or surface water standards were exceeded. X Yes, a notification of values exceeding a groundwater or surface water standard is attached. It includes a list of groundwater and surface water monitoring points, dates, analytical values, NC 2L groundwater standard, NC 2B surface water standard or NC Solid Waste GWPS and preliminary analysis of the cause and significance of any concentration. ❑ Yes, a notification of values exceeding an explosive methane gas limit is attached. It includes the methane monitoring points, dates, sample values and explosive methane gas limits. Certification To the best of my knowledge, the information reported and statements made on this data submittal and attachments are true and correct. Furthermore, I have attached complete notification of any sampling values meeting or exceeding groundwater standards or explosive gas levels, and a preliminary analysis of the cause and significance of concentrations exceeding groundwater standards. I am aware that there are significant penalties for making any false statement, representation, or certification including the possibility of a fine and imprisonment. Craig D. Eady Project Manager Facility Representative Name (Print) Title 1 /11 /2023 Signature 6. Date 148 River Street, Suite 220, Greenville, SC 29601 Facility Representative Address C-1478 / North Carolina Geological Corporation Number C-387 (864)421-9999 (Area Code) Telephone Number Affix NC Licensed/ Professional Geologist Seal `h CAROf r \ +•• S •tj I' + SEAL i�i ' •;COI, pCa��;+' �i�: NC PE Firm License Number (if applicable effective May 1, 2009) Revised 6/2009 REPORT VERIFICATION PROJECT: SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT ASHEVILLE STEAM ELECTRIC PLANT CCR LANDFILL PERMIT NO. 1119-INDUS-2020 TITLE: SEPTEMEBR 2022 SAMPLING EVENT This document has been reviewed for accuracy and quality commensurate with the intended application. Prepared by: F Date Approved by: `� Date Project Manager: Craig Eady, G 1/11/2023 1/11/2023 Licensed Geologist Seal: 4L�t1tiCArR{ff{! :7 SEAL g • q �fO u�p�� SynTerra 148 River Street, Suite 220 Greenville, SC 29601 North Carolina Geological Corporation Number C-387 17 Terra Science &Engineering Consultants synsynterracorp.com SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT CCR LANDFILL PERMIT NO. 1119-INDUS-2020) ASHEVILLE STEAM ELECTRIC PLANT 46 DUKE ENERGY LANE ARDEN, NORTH CAROLINA 28704 JANUARY 12, 2023 PREPARED FOR DUKE ENERGY.: PROGRESS DUKE ENERGY PROGRESS, LLC t Crai ady, NC L.G. # 99 Ryan Badum enior Peer Revi4er Project Scientist Kelly Ferri Project Manager Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina TABLE OF CONTENTS SECTION PAGE 1.0 INTRODUCTION AND BACKGROUND..........................................................................1-1 1.1 Site and Landfill Information......................................................................................1-1 1.2 Hydrogeologic Setting................................................................................................1-1 1.3 Landfill Semiannual Monitoring Program...................................................................1-2 2.0 METHODS.................................................................................................................. 2-1 2.1 Sampling and Analysis Methods.................................................................................2-1 2.2 Regulatory Criteria.....................................................................................................2-1 2.3 Statement of Work.....................................................................................................2-1 3.0 RESULTS.....................................................................................................................3-1 3.1 Site Groundwater Flow...............................................................................................3-1 3.2 Historical Range Data.................................................................................................3-1 3.3 Analytical Results.......................................................................................................3-2 3.4 Quality Assurance/Quality Control.............................................................................3-2 4.0 REFERENCES...............................................................................................................4-1 LIST OF FIGURES Figure 1 Site Location Map Figure 2 Sample Locations Figure 3A Groundwater Level Map — Surficial and Transition Flow Zones Figure 3B Groundwater Level Map — Bedrock Flow Zone LIST OF TABLES Table 1 Well Construction Summary Table 2 Groundwater, Surface Water, and Leachate Monitoring Parameters Table 3 Field Data Parameters Table 4 Groundwater Seepage Velocities Table 5 Groundwater Field Results and Analytical Detections Table 6 Field and Analytical Results that Equal or Exceed Groundwater Quality Standards Table 7 Surface Water Field Results and Analytical Detections Table 8 Leachate Field Results and Analytical Detections LIST OF APPENDICES Appendix A Field Sampling Forms Appendix B Laboratory Report and Chain -of -Custody Forms January 2023 Page i Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina LIST OF ACRONYMS 02L Title 15A, NCAC 02L .0202(g) Groundwater Quality Standards 02B Title 15A, NCAC 02B .0200 Surface Water and Wetland standards Asheville Plant Asheville Steam Electric Plant CAMA Coal Ash Management Act CCR coal combustion residuals Duke Energy Duke Energy Progress, LLC DWM Division of Waste Management EDD electronic data deliverable Landfill Asheville CCR Landfill MSE mechanically stabilized earth NCAC North Carolina Administrative Code NCDEQ North Carolina Department of Environmental Quality Site Asheville Steam Electric Plant SWLF Solid Waste Landfill SWS Solid Waste Section TDS total dissolved solids USEPA U.S. Environmental Protection Agency WQMP Water Quality Monitoring Plan January 2023 Page H Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina f��>• I ►19.1611111I4111 9 IQ ► I_10 1113Uffel KC11:191110 L7 This semiannual report pertains to the Duke Energy Progress, LLC (Duke Energy) Asheville Steam Electric Plant (Asheville Plant, Site) Coal Combustion Residual (CCR) Landfill (Landfill; Permit No. 1119-INDUS-2020) and documents the results of the September 2022 groundwater, surface water, seep, and leachate monitoring event. Monitoring results show that groundwater constituents greater than comparison criteria are attributable to natural variation and not the CCR Landfill, except sulfate concentrations in one monitoring well (LMW-3B). Additional monitoring and data are needed to determine the cause and significance of the sulfate concentration greater than historical background concentrations. 1.1 Site and Landfill Information Duke Energy owns and operates the Asheville Steam Electric Plant, located on approximately 786 acres, addressed at 46 Duke Energy Lane in Arden, Buncombe County, North Carolina. (Figure 1). The Asheville Plant began operations in 1964 with construction of two coal-fired power - generating units to generate electricity. Throughout the period of coal-fired generation, CCR was managed and stored on -Site in the 1964 and 1982 Ash Basins. The Asheville Plant ceased burning coal in January 2020, and the coal-fired units were replaced with a natural gas combined cycle station for electricity generation; thus, the facility no longer generates CCR. Excavation of the 1982 Ash Basin was completed in September 2016, and excavation of the 1964 Ash Basin was completed in June 2022. Development and construction activities for the on -Site double lined CCR Landfill began in February 2020 and were completed in March 2021. The CCR Landfill was constructed in an area previously developed as a laydown yard, located north of and adjacent to the 1964 Ash Basin (Figure 1). The CCR Landfill was constructed to support the last phase of ash excavation from the 1964 Ash Basin. The Landfill received a Permit Approval to Operate from the North Carolina Department of Environmental Quality (NCDEQ) on April 1, 2021, and initial placement of CCR material in the Landfill occurred on the same day. The Landfill Operations Plan (Geosyntec, 2021) and Landfill Permit outline a variety of landfill -approved wastes; however, the primary waste disposed of in the Landfill is CCR (fly ash and bottom ash). Landfill closure was initiated in September 2022. Closure is expected to be complete in early 2023. 1.2 Hydrogeologic Setting The Asheville Plant is located within the Blue Ridge physiographic province, where soil overlying the bedrock has formed from the in -place weathering of bedrock. Groundwater at the Site typically occurs in three interconnected flow zones. The shallowest groundwater flow zone — the surficial flow zone — occurs in the residual soil and/or the upper section of saprolite. Beneath the surficial flow zone, the transition zone flow zone occurs in the lower portions of the saprolite and partially weathered bedrock and is the most permeable part of the Site January 2023 Page 1-1 Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina hydrogeologic system. Bedrock underlies the transition zone and comprises the least permeable flow zone of the Site's hydrogeologic system, where groundwater flow occurs predominantly along fractures, joints, and faults. Groundwater is usually encountered in the surficial flow zone; however, as the hydrogeologic units above the bedrock thin to the west and northwest, groundwater is encountered only within the lower hydrogeologic unit(s). Groundwater flow direction at the Landfill is generally to the west toward an unnamed stream, and to the northwest toward a wetland area and several unnamed streams, which converge into Powell Creek. The wetland area and streams act as groundwater discharge zones downgradient of the Landfill. Those surface waters are classified as Class C under Title 15A of the North Carolina Administrative Code (NCAC), Subchapter 02B, Surface Water and Standards (02B standards). Flow from those surface water features eventually reaches the French Broad River, located to the west. 1.3 Landfill Semiannual Monitoring Program The Water Quality Monitoring Plan (WQMP), Revision 2 (Geosyntec, 2019) for the CCR Landfill was submitted to NCDEQ on October 31, 2019, and approved on February 7, 2020. The Landfill semiannual monitoring program, described in detail in the WQMP, consists of 9 groundwater, 3 surface water, 1 seep, and 1 leachate monitoring locations summarized in the following table. The monitoring locations are shown on Figure 2. A summary of monitoring well construction information is presented in Table 1 and analytical parameters for the Landfill semiannual groundwater monitoring program is summarized in Table 2. January 2023 Page 1-2 Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina MONITORING WELLS MEDIA COMMENTS OR SAMPLE LOCATIONS Background CB-9, CB-9SL, CB-9BR Groundwater LMW-1S, LMW-1B See Table 1 Well Construction Summary for monitoring well LMW-2T, LMW-2B, construction information. Downgradient Groundwater LWM-313, LMW-4B Three surface water monitoring locations in two streams located west and north-northwest, adjacent, and LF-SW-1, LF-SW-2, LF-SW-3 downgradient of the Landfill (sampled if flow is present during semiannual monitoring). Surface Water Drainpipe for groundwater seepage from the northwest portion of the DP-4 Landfill's mechanically stabilized earth (MSE) berm (sampled if flow is present during semiannual monitoring). Leachate sample, representing leachate from the entire Landfill, was Leachate LCS-1 collected from an in -line sampling point along the forcemain conveying leachate from the Landfill to the Leachate Storage Tank. Notes: 1. The WQMP identifies the surface water samples as SW-1, SW-2, and SW-3. Identification was revised to differentiate between other Site monitoring program surface water locations. 2. The WQMP identifies the leachate collection sample as L-1. Identification was revised in the field during sample collection. 3. Two additional groundwater monitoring wells (LMW-1T and LMW-2S) were included as proposed monitoring wells in the WQMP but were not installed. Monitoring well LMW-1T was proposed to be screened in the transition zone; however, no transition zone was observed during drilling. Monitoring well LMW-2S was not installed because the surficial aquifer was not present at the proposed location. January 2023 Page 1-3 Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina 2.0 METHODS 2.1 Sampling and Analysis Methods Groundwater, surface water, seep, and leachate sampling was conducted by Duke Energy personnel (Duke Energy North Carolina Field Certification #5193) on September 26, 2022, in accordance with the North Carolina Solid Waste Management Guidelines. Copies of the field sampling forms are included in Appendix A. Duke Energy Analytical Laboratory (North Carolina Laboratory Certification #248) and Pace Analytical Laboratory (North Carolina Laboratory Certification #40) analyzed the reported parameters and constituents. The laboratory report and chain -of -custody forms are included in Appendix B. The samples were analyzed for the list of parameters and constituents outlined in the WQMP and guidance from the NCDEQ Division of Waste Management (DWM), Solid Waste Section (SWS). The monitoring parameters, along with the U.S. Environmental Protection Agency (USEPA) Solid Waste (SW)-846 analytical methods, Title 15A, NCAC, Subchapter 02L .0202(g), Groundwater Quality Standards (02L standards), and 15A NCAC 02B .0200 Surface Water and Wetland standards (0213 standards) for Class C waters are present in Table 2. 2.2 Regulatory Criteria Evaluation of the semiannual monitoring analytical results are compared to the following regulatory criteria: Groundwater • 02L standards Surface Water/Seep • 02B standards 2.3 Statement of Work The following tasks were completed for semiannual water quality monitoring: • Groundwater, surface water, and leachate were collected on September 26, 2022. (Duke personnel completed this task.) • Compared groundwater analytical results to 02L standards and historical concentration ranges. • Compared surface water analytical results to 02B standards and historical concentration ranges. • Developed generalized groundwater contour maps using groundwater elevation data collected during the September 2022 groundwater monitoring event. • Calculated groundwater flow velocities based on groundwater elevations at wells perpendicular to groundwater flow. January 2023 Page 2-1 Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina • Converted the laboratory provided electronic data deliverable (EDD) to the format requirements of the NCDEQ DWM EDD template and submitted copies of the EDDs to the NCDEQ DWM with this report. • Prepared and submitted this Semiannual Water Quality Monitoring Report. January 2023 Page 2-2 Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina 3.1 Site Groundwater Flow Groundwater flow in the aquifer beneath the Landfill footprint flows generally to the west toward an unnamed stream, and to the northwest toward a wetland area and several unnamed streams, which converge into Powell Creek. Generalized groundwater elevation contours and groundwater flow direction arrows in the vicinity of the CCR Landfill are shown on Figure 3A for the surficial and transition flow zones, and Figure 313 for the bedrock flow zone. These contours were developed by calculating groundwater elevations in each monitoring well using the depth -to -water -level measurements taken during the September 2022 monitoring event. In addition, water -level measurements from nearby groundwater monitoring wells included in other Site groundwater monitoring programs were used. Depth -to -water measurements and calculated groundwater elevations are presented in Table 3. Calculated groundwater flow velocities are presented in Table 4. Calculated groundwater elevations based on depth -to -water measurements gauged during the September 2022 monitoring event indicate groundwater at the Landfill generally flows to the west and northwest, consistent with historical Site observations. 3.2 Historical Range Data Newly Installed Landfill Groundwater Monitoring Wells The WQMP included collecting four groundwater samples from each new Landfill monitoring well prior to the Landfill becoming operational (baseline samples). The four baseline monitoring events occurred between September 2020 and January 2021, with samples collected from each well approximately once every 30 days. The baseline monitoring included measuring groundwater field parameters, gauging depth -to -water in the wells, and analysis of the collected groundwater samples for the list of parameters and constituents outlined in the WQMP (same parameter list sampled and analyzed for in the Landfill semiannual monitoring program). The results of the four baseline sampling events were submitted in the Groundwater Monitoring Report Baseline Sampling Events #1 Through #4 — CCR Landfill (Baseline Report) (SynTerra, 2021). For each newly installed monitoring well, historical ranges of constituent concentrations were calculated using the analytical results from the four baseline monitoring events. Existing Wells Incorporated into the Landfill Monitoring Program Monitoring wells CB-9, CP-9SL, and CP-9BR existed at the Site prior to Landfill development but are incorporated into the Landfill monitoring program. Those three wells were not sampled during baseline sampling events for the newly installed wells. Rather, data from these wells, collected as part of other regulatory sampling programs well in advance of Landfill operations, were used to satisfy the initial baseline sampling requirements. Historical concentration ranges January 2023 Page 3-1 Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina for existing wells were established using all available data collected prior to initiation of Landfill operations (November 2012 to January 2021). 3.3 Analytical Results A summary of the groundwater, surface water, and leachate field data is presented in Table 3. The analytical results and reference comparisons discussed below are summarized in Tables 5 through 8. Sample locations are depicted on Figure 2. Groundwater Results Field and analytical results for the collected downgradient and background groundwater samples are presented in Table 5. Groundwater analytical results are compared with 02L standards. Constituent concentrations equal to or greater than their 02L standard are noted in Table 5 in bold font. The laboratory analytical reports are included as Appendix B. A summary of the downgradient groundwater field and analytical results that are equal to or greater than applicable comparison criteria are presented in Table 6. The groundwater concentrations in Table 6, which are identified as being equal to or greater than the 02L standard, are attributable to natural variation, except for sulfate in LMW-313. The sulfate concentration in LMW-313 is only slightly greater than the 02L standard and greater than historical background concentrations for the first time; therefore, a cause and significance cannot be determined at this time. Surface Water Field and analytical results for surface water samples are presented in Table 7. The sample locations are shown on Figure 2. Analytical results for surface water and seep samples, as available, are compared with applicable 02B Class C surface water standards. Surface water sample LF-SW-1 and seep location DP-4 were not sampled during the September 2022 sampling event because of dry conditions. No surface water samples collected during the September 2022 sampling event were greater than or equal to applicable 02B Class C surface water standards. Leachate A leachate sample (LCS-1) was collected from the leachate collection discharge pipe on the west side of the Landfill. Analytical results are presented in Table 8. Leachate analytical results are not compared to groundwater (02L standards) or surface water (0213 standards) quality standards and are provided for informational purposes only. 3.4 Quality Assurance/Quality Control Field -performed quality assurance and quality control (QA/QC) consisted of the collection and analysis of two field blanks (one on each day of sampling) to evaluate if possible impacts were imparted to the samples by the sample container, preservative, or other exogenous sources. A field duplicate sample was also collected to estimate sampling and laboratory precision. Iron January 2023 Page 3-2 Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina was detected in the field blank at a concentration greater than the method detection limit. However, all data were validated and deemed usable. Select samples were diluted, as is normal laboratory practice, to bring samples within the calibrated range of the analysis. Specifics regarding the samples that were diluted, including the dilution amount, are reported in the lab report. Additional QA/QC data, laboratory analyses, and chain -of -custody forms are included in Appendix B. January 2023 Page 3-3 Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina Geosyntec. (2019). Water Quality Monitoring Plan Revision Z Asheville Steam Electric Plant CCR Landfill, October 2019. Geosyntec. (2021). Operations Plan, Asheville Steam Electric Plant, CCR Landfill (1119-INDUS) Rev. Z February 19, 2021. SynTerra. (2021). Groundwater Monitoring Report Baseline Sampling Events #1 Through #4 — CCR Landfill, Asheville Steam Electric Plant. April 2021. January 2023 Page 4-1 Project: 00.0069.34.07.02 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina FIGURES L7 synTerra Science & Engineering Consultants 1964 ASH BASIN WA BOUNDARY . r � 0 ♦ r- .'/0 I - RETIRED ASHEVILLE I I STEAM ELECTRIC ♦ r ; I ` • 1982 ASH BASIN - - - WASTE BOUNDARY ,r ♦ ''; l i • ` - - ' DUKE ENERGY PROGRESS PROPERTY BOUNDARY �> ASHEVILLE COMBINED CYCLE STATION NOTES: 1. ALL BOUNDARIES ARE APPROXIMATE. 2. PROPERTY BOUNDARY PROVIDED BY DUKE ENERGY PROGRESS. 3. USGS TOPOGRAPHIC MAP OBTAINED FROM ESRI ONLINE, LAST UPDATED AUGUST 2021. DUKE ENERGY It BUNCOMBE COUNTY � PROGRESS r ASHEVILLEA FIGURE 1 SITE LOCATION MAP SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT ASHEVILLE STEAM ELECTRIC PLANT IRLOTTE ARDEN, NORTH CAROLINA DRAWN BY: B. MCGANN DATE: 12/08/2021 GRAPHIC SCALE REVISED BY KING DATE: 12/21/2022 CHECKED BY: R. BADUM DATE: 12/21/2022 APPROVED BY: K. FERRI DATE: 12/21/2022 PROJECT MANAGER_ K. FERRI 1,000 0 1,000 2000, )IN FEET) LEGEND SURFACE WATER SAMPLE LOCATION �® _- - -- LEACHATE SAMPLE LOCATION f.. DRAINPIPE SEEP SAMPLE LOCATION 000, � DOWNGRADIENT MONITORING WELL BACKGROUND MONITORING WELL LEACHATE FORCEMAIN L `� LANDFILL LIMIT OF WASTE LMW-2T \� ��` \\\� LANDFILL REVIEW BOUNDARY - / -- LANDFILL COMPLIANCE BOUNDARY )► STREAM (TWT) WETLANDS (TWT) NOTES: 1. LF-SW-1, LF-SW-2, AND LF-SW-3 SAMPLE IDS HAVE BEEN REVISED FROM THE WQMP IN ORDER TO DIFFERENTIATE BETWEEN OTHER SITE MONITORING PROGRAM SURFACE WATER SAMPLES WITH THE SAME SAMPLE IDS AS PRESENTED IN THE WQMP. LEACHATE SAMPLE _CS-1 IS IDENTIFIEDAS L-1 IN THE WQMP. 2. WQMP - WATER QUALITY MONITORING PLAN t 0000 ` 3. ALL SAMPLE LOCATIONS ARE APPROXIMATE. 4. THE DEPICTED STREAMS AND WETLANDS DATA WERE APPROVED BY THE US ARMY CORPS OF ENGINEERS (USACE) ON MAY 19, 2016 - JURISDICTIONAL DETERMINATION DP-4 SAW 2014-00189. TAYLOR WISEMAN AND TAYLOR (TWT) PERFORMED THE SURVEY OF LMW-1 B, THE FEATURES. 5. ALL BOU NDARI ES ARE APPROXI MATE. LMW-1 S I 6. PROPERTY BOUNDARY PROVIDED BY DUKE ENERGY PROGRESS. / LMW-4B _ - I 7. LANDFILLAERIAL SURVEY AND TOPOGRAPHY COLLECTED ON NOVEMBER 30, 2021 BY WASTE MANAGEMENT. ADDITIONAL AERIAL IMAGERY OBTAINED FROM GOOGLE EARTH ON APRIL 27, 2022. IMAGE DATED APRIL 2022. LANDFILL LIMIT 8. DRAWING HAS BEEN SET WITH A PROJECTION OF NORTH CAROLINASTATE PLANE OF WASTE COORDINATE SYSTEM RIPS 3200 (NAD83) 1. 0 LEACHATE FORCEMAIN CB-9SL CB-9� 31 f — '� �: v MW-13D 1000, �. DUKE }d-r ENERGY \ PROGRESS synTerra LANDFILL REVIEW BOUNDARY (APPROXIMATELY 80' FROM ' =s LIMIT OF WASTE) /4 r LANDFILL COMPLIANCE BOUNDARY (APPROXIMATELY 160' FROM LIMIT OF WASTE) , ..vim- GRAPHIC SCALE 75 0 75 150 FIGURE 2 SAMPLE LOCATIONS (IN FEET) CCR LANDFILL DRAWN BY e MCGANN DATE iz/os/zozi SEMIANNUAL WATER QUALITY MONITORING REPORT REUSED BY T KING DATE 01/11/2023 SEPTEMBER 2022 SAMPLING EVENT AH PROVED R eADUM DATE 01/11/2023 ASHEVILLE STEAM ELECTRIC PLANT APPROVED BY K. FERRI DATE_01/11/2023 PROJECTMANAGER:K-FERRI ARDEN, NORTH CAROLINA www.synterracorp.com I 1) 1-� i��o_- / ti MW 13D" 2123.85 z17 loep I o LANDFILL LIMI OF WASTE I �o LANDFILL REVIEW BOUNDAF (APPROXIMATELY 80' FROM LIMIT OF WASTE) C6 ' 2144.948 c 3-9SL / 44.82 LANDFILL COMPLIANCE BOUNDARY (APPROXIMATEL' 160' FROM LIMIT OF WASTE) 2170 - -' LEGEND SURFACE WATER SAMPLE LOCATION LEACHATE SAMPLE LOCATION O DRAINPIPE SEEP SAMPLE LOCATION BACKGROUND MONITORING WELL DOWNGRADIENT MONITORING WELL GROUNDWATER FLOW DIRECTION -- INFERRED WATER ELEVATION CONTOUR (20' INTERVAL) LANDFILL LIMIT OF WASTE LANDFILL REVIEW BOUNDARY -- LANDFILL COMPLIANCE BOUNDARY ►— STREAM (TWT) WETLANDS (TWT) TOPOGRAPHIC CONTOUR (10' INTERVAL) NOTES: 1. THE WQMP IDENTIFIES THE SURFACE WATER SAMPLES AS SW-1, SW-2, AND SW-3. .'.C; IDENTIFIFICATION WAS REVISED TO DIFFERENTIATE BETWEEN OTHER SITE MONITORING PROGRAM SURFACE WATER LOCATIONS. THE WQMP IDENTIFIES THE LEACHATE COLLECTION SAMPLE AS L-1. IDENTIFICATION WAS REVISED IN THE FIELD DURING SAMPLE .,k COLLECTION. 2. * - MONITORING WELL PART OF ANOTHER REGULATORY SAMPLE PROGRAM AND USED FOR GROUNDWATER ELEVATION DATA ONLY. 3. W.E. - WATER ELEVATION (APPROXIMATE). 4. WQMP - WATER QUALITY MONITORING PLAN 5. ALL SAMPLE LOCATIONS ARE APPROXIMATE. �f} 6. THE DEPICTED STREAMS AND WETLANDS DATA WERE APPROVED BY THE US ARMY CORPS OF ENGINEERS (USAGE) ON MAY 19, 2016 - JURISDICTIONAL DETERMINATION SAW 2014-00189. TAYLOR WISEMAN AND TAYLOR (TWT) PERFORMED THE SURVEY OF THE FEATURES. 7. ALL BOUNDARIES ARE APPROXIMATE. 8. PROPERTY BOUNDARY PROVIDED BY DUKE ENERGY PROGRESS. <9. LANDFILLAERIAL SURVEYAND TOPOGRAPHY COLLECTED ON NOVEMBER 30, 2021 BY WASTE MANAGEMENT. ADDITIONAL AERIAL IMAGERY OBTAINED FROM GOOGLE EARTH ON APRIL 27, 2022. IMAGE DATED APRIL 2022. 10. DRAWING HAS BEEN SET WITH A PROJECTION OF NORTH CAROLINA STATE PLANE - _ COORDINATE SYSTEM RIPS 3200 (NAD83). 11. GROUNDWATER ELEVATIONS BASED ON WATER LEVELS COLLECTED SEPTEMBER 26, 2022. DUKE 75 GRAPHIC SCALE FIGURE 3A 0 75 150 ENERGY (IN FEET) GROUNDWATER LEVEL MAP PROGRESS SURFICIAL AND TRANSITION FLOW ZONES DRAWN BY. B. MCGANN DATE-12/08/2021 SEMIANNUAL WATER QUALITY MONITORING REPORT REVISED BY T KING DATE_ 12/21/2022 VIP CHECKED BY R. BADUM DATE: 12/21/2022 SEPTEMBER 2022 SAMPLING EVENT APPROVED BY. K. FERRI DATE_ 12/21/2022 PROJECT MANAGER: K-FERRI ASHEVILLE STEAM ELECTRIC PLANT synTerra www.synterracorp.com ARDEN, NORTH CAROLINA �- �� ' I I LMW-2B � 2056.39 1 OADi 2. 2�y0 // I/ LMW-4B I/ II 2079.87 O LEAC MW 13BR* •T ef 5maigmt ` 2124.02 z17 2160 2120 CB-8BR* ,.; 2092.05 II I I r LEGEND SURFACE WATER SAMPLE LOCATION \A LEACHATE SAMPLE LOCATION _MW-1B ` / �I 0 DRAINPIPE SEEP SAMPLE LOCATION BACKGROUND MONITORING WELL DOWNGRADIENT MONITORING WELL LANDFILL LIMIT GROUNDWATER FLOW DIRECTION OF WASTE INFERRED WATER ELEVATION CONTOUR (20' INTERVAL) I LANDFILL LIMIT OF WASTE I LANDFILL REVIEW BOUNDARY '� -- LANDFILL COMPLIANCE BOUNDARY C +( STREAM (TWT) WETLANDS (TWT) LANDFILL REVIEW BOUNDARY TOPOGRAPHIC CONTOUR (10' INTERVAL) ` (APPROXIMATELY 80' FROM LIMIT OF WASTE) NOTES: 1. THE WQMP IDENTIFIES THE SURFACE WATER SAMPLES AS SW-1, SW-2, AND SW-3. IDENTIFIFICATION WAS REVISED TO DIFFERENTIATE BETWEEN OTHER SITE MONITORING I - PROGRAM SURFACE WATER LOCATIONS. THE WQMP IDENTIFIES THE LEACHATE COLLECTION SAMPLE AS L-1. IDENTIFICATION WAS REVISED IN THE FIELD DURING SAMPLE COLLECTION. \ CB-9BR' 2. * - MONITORING WELL PART OF ANOTHER REGULATORY SAMPLE PROGRAM AND USED ... 2129.56 FOR GROUNDWATER ELEVATION DATA ONLY. 3. W.E. - WATER ELEVATION (APPROXIMATE). 2 80 4. WQMP -WATER QUALITY MONITORING PLAN f 5. ALL SAMPLE LOCATIONS ARE APPROXIMATE. z1s0 /- _ Irk 6. THE DEPICTED STREAMS AND WETLANDS DATA WERE APPROVED BY THE US ARMY CORPS OF ENGINEERS (USACE) ON MAY 19, 2016 - JURISDICTIONAL DETERMINATION SAW 2014-00189. TAYLOR WISEMAN AND TAYLOR (TWT) PERFORMED THE SURVEY OF THE LANDFILL COMPLIANCE FEATURES. 7. ALL BOUNDARIES ARE APPROXIMATE. BOUNDARY (APPROXIMATELY ' \" <160' FROM LIMIT OF WASTE) 8 PROPERTY BOUNDARY PROVIDED BY DUKE ENERGY PROGRESS. - / 9 LANDFILL AERIAL SURVEY AND TOPOGRAPHY COLLECTED ON NOVEMBER 30 2021 BY w, WASTE MANAGEMENT. ADDITIONAL AERIAL IMAGERY OBTAINED FROM GOOGLE EARTH ON APRIL 27, 2022. IMAGE DATED APRIL 2022. - - 10. DRAWING HAS BEEN SET WITH A PROJECTION OF NORTH CAROLINA STATE PLANE - - COORDINATE SYSTEM RIPS 3200 (NAD83). "T 11. GROUNDWATER ELEVATIONS BASED ON WATER LEVELS COLLECTED SEPTEMBER 26, 2022. DUKE GRAPHIC SCALE FIGURE 3B 75 0 75 150 ENERGY (IN FEET) GROUNDWATER LEVEL MAP PROGRESS BEDROCK FLOW ZONE DRAWN Br. B. MCGANN DATE 12/08/2021 SEMIANNUAL WATER QUALITY MONITORING REPORT REVISED BY T KING DATE_ 01/09/2023 VIP CHECKED BY R. BADUM DATE: 01/09/2023 SEPTEMBER 2022 SAMPLING EVENT APPROVED BY. K. FERRI DATE_ 01/09/2023 PROJECT MANAGER: K-FERRI ASHEVILLE STEAM ELECTRIC PLANT synTerra www.synterracorp.com ARDEN, NORTH CAROLINA Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina TABLES L7 synTerra Science & Engineering Consultants TABLE 1 WELL CONSTRUCTION SUMMARY SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT ASHEVILLE STEAM ELECTRIC PLANT DUKE ENERGY PROGRESS, LLC, ARDEN, NC Well ID Date Installed Flow Zone Material Diameter (Inches) Latitude (degrees) Longitude (degrees) Well Depth (Ft, BTOC) Screened Interval (Ft, BGS) Measuring Point TOC (Ft, NAVD 88) Ground Surface (Ft, NAVD 88) Groundwater Elevation (Ft NAVD 88) Depth to Water (Ft BTOC) CB-9* 10/8/2012 Surficial PVC 2 35.4720450 -82.5467520 65.60 52-62 2182.08 2178.86 2144.48 37.60 CB-9BR* 4/21/2015 Bedrock PVC 2 35.4720311 -82.5467707 97.85 83-93 2181.11 2178.15 2129.56 51.55 CB-9SL* 4/21/2015 Saprolite PVC 2 35.4720577 -82.5467646 78.10 69-74 2181.42 2178.17 2144.82 36.60 LMW-1B* 9/11/2020 Bedrock PVC 2 35.4732130 -82.5469693 103.20 91-101 2169.67 2169.53 2146.64 23.03 LMW-1ST 8/31/2020 Surficial PVC 2 35.4731733 -82.5469538 66.60 55-65 2169.73 2169.58 2143.50 26.23 LMW-2B 9/11/2020 Bedrock PVC 2 35.4740577 -82.5491559 110.30 100.5-110.5 2121.16 2120.84 2056.39 64.77 LMW-2T 9/11/2020 Transition PVC 2 35.4741121 -82.5491312 87.00 76-86 2123.11 2123.20 2058.31 64.80 LMW-3B 9/11/2020 Bedrock PVC 2 35.4734715 -82.5496049 45.30 33-43 2102.89 2102.80 2069.26 33.63 LMW-4B 9/11/2020 Bedrock PVC 2 35.4729336 -82.5506071 49.25 39-49 2102.67 2102.57 2079.87 22.80 Notes: * - Indicates background groundwater monitoring well. Groundwater elevations are based on data collected during the September 2022 sampling event. BGS - below ground surface BTOC - below top of casing CCR - coal combustion residual Ft - feet NAD 83 - Horizontal coordinates based on the North American Datum of 1983. NAVD 88 - Vertical elevations in feet based on North American Vertical Datum of 1988 NM - not measured PVC - polyvinylchloride TOC - top of casing Prepared by: RSB Checked by: KCO Page 1 of 1 TABLE 2 GROUNDWATER, SURFACE WATER, AND LEACHATE MONITORING PARAMETERS SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT ASHEVILLE STEAM ELECTRIC PLANT DUKE ENERGY PROGRESS, LLC, ARDEN, NC Field Parameters Analytical Methods Units 15A NCAC 1 02L Standard 15A NCAC 02B 2 (Class C) pH Multi -Parameter Water Quality Meter S.U. 6.5 - 8.5 6.0 - 9.0 Temperature Multi -Parameter Water Quality Meter degrees Celsius NE :529 Specific Conductance Multi -Parameter Water Quality Meter µmhos/cm NE NE Dissolved Oxygen Multi -Parameter Water Quality Meter mg/L NE >_4 Oxidation Reduction Potential Multi -Parameter Water Quality Meter millivolts NE NE Turbidity Turbidimeter NTU NE :550 Water Level Water Level Meter ft NE NE Laboratory Parameters Analytical Methods Units 15A NCAC t 02L Standard 15A NCAC 02B 2 (Class C) Antimony EPA 200.8/EPA 6020B µg/L 1 NE Arsenic EPA 200.8/EPA 6020E µg/L 10 NE Barium EPA 200.7/EPA 6010D µg/L 700 NE Beryllium EPA 200.7/EPA 6010D µg/L 4 NE Boron EPA 200.7/EPA 6010D µg/L 700 7300* Cadmium EPA 200.8/EPA 6020E µg/L 2 NE Chloride EPA 300.0/EPA 9056A mg/L 250 230 Chromium EPA 200.8/EPA 6020E µg/L 10 NE Cobalt EPA 200.8/EPA 6020B µg/L 1 NE Copper EPA 200.7/EPA 6010D µg/L 1,000 NE Fluoride EPA 300.0/EPA 9056A mg/L 2 1.8 Iron EPA 200.7/EPA 6010D µg/L 300 NE Lead EPA 200.8/EPA 6020B µg/L 15 NE Manganese EPA 200.7/EPA 6010D µg/L 50 NE Mercury EPA 7470A µg/L 1 0.012 Nickel EPA 200.7/EPA 6010D µg/L 100 NE Nitrate EPA 300.0/EPA 9056A mg-N/L 10 NE Selenium EPA 200.8/EPA 6020E µg/L 20 NE Silver EPA 200.8/EPA 6020B µg/L 20 NE Sulfate EPA 300.0/EPA 9056A mg/L 250 NE Thallium EPA 200.8/EPA 6020B µg/L 2 NE Total Dissolved Solids SM 2540C mg/L 500 NE Vanadium EPA 200.8/EPA 6020B µg/L 7 NE Zinc EPA 200.7/EPA 6010D µg/L 1,000 NE Prepared by: KHF Checked by: TCP Notes: 1- 15A NCAC 02L Standards for groundwater - North Carolina groundwater quality standards (effective April 1, 2022). z - 15A NCAC 02B Standards for Class C surface waters - North Carolina surface water and wetland standards (effective September 1, 2022). In -stream target value established per the language in 15A NCAC 02B .0202 and .0208. µg/L - micrograms per liter µmhos/cm - micromhos per centimeter EPA - US Environmental Protection Agency ft- feet mg/L- milligrams per liter my - millivolts NE - not established NTU - nephelometric turbidity units S.U. - standard units Page 1 of 1 TABLE 3 Id � � _�l_\l_1:T_1►�iL�hJ:�� SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT ASHEVILLE STEAM ELECTRIC PLANT DUKE ENERGY PROGRESS, LLC, ARDEN, NC Sample ID Sample Date Appearance Odor Purge Method Average Pump Rate (mL/min) Temp (Deg C) Specific Conductance (µmhos/cm) pH (S.U.) ORP (mV) Dissolved Oxygen (mg/L) Turbidity (NTU) Groundwater Elevation (Ft NAVD 88) Depth to Water (Ft BTOC) Groundwater Parameters C13-9 9/26/2022 Clear None Low Flow 180 19 29 4.9 348 2.45 4.3 2144.48 37.60 C13-913R 9/26/2022 Clear None Low Flow 300 18 84 5.9 289 0.29 7.3 2129.56 51.55 CB-9SL 9/26/2022 Clear None Low Flow 110 19 46 5.5 339 3.64 6.5 2144.82 36.60 LMW-113 9/26/2022 Clear None Low Flow 250 19 104 6.2 277 0.27 6.1 2146.64 23.03 LMW-1S 9/26/2022 Clear None Low Flow 300 18 62 5.9 413 2.14 4.3 2143.50 26.23 LMW-213 9/26/2022 Clear None Low Flow 300 19 69 6.5 269 1.92 4.0 2056.39 64.77 LMW-2T 9/26/2022 Clear None Low Flow 180 19 61 7.0 396 4.08 4.7 2058.31 64.80 LMW-313 9/26/2022 Clear None Low Flow 180 16 476 6.9 334 1.29 3.4 2069.26 33.63 LMW-413 9/26/2022 Clear None Low Flow 350 15 396 6.2 204 0.24 7.7 2079.87 22.80 Surface Water Parameters LF-SW-1* Dry, not sampled. LF-SW-2* 9/26/2022 Clear None NA NA 17 98 8.1 445 8.49 6.5 NA NA LF-SW-3* 9/26/2022 Clear None NA NA 19 59 7.7 374 8.13 7.1 NA NA DP-4 Dry, not sampled. Leachate Collection Parameters LCS-1** 1 9/26/2022 Clear None NA NA 21 1509 6.7 401 7.12 19.0 NA NA Notes: The WQMP identifies the surface water samples as SW-1, SW-2, and SW-3. Identification was revised to differentiate between other Site monitoring program surface water locations. ** - The WQMP identifies the leachate collection sample as L-1. Identification was revised in the field during sampling collection. µmhos/cm - micromhos per centimeter BTOC - below top of casing Deg C - degrees Celsius ft - feet mg/L - milligrams per liter mL/min - milliliters per minute mV - millivolts NA - not applicable NAVD88 - North American Vertical Datum of 1988 NTU - Nephelometric turbidity units ORP - oxidation reduction potential S.U. - standard units Prepared by: RSB Checked by: KCO WQMP - Water Quality Monitoring Plan Page 1 of 1 TABLE 4 GROUNDWATER SEEPAGE VELOCITIES SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT ASHEVILLE STEAM ELECTRIC PLANT DUKE ENERGY PROGRESS, LLC, ARDEN, NC Surficial and Transition Flow Zone Upgradient Downgradient Seepage Groundwater Groundwater K Ah Distance Well ID Effective Porosity Velocity Elevation Elevation 1 (ft/day) (ft) (ft) (ft/day) (Ft NAVD 88) (Ft NAVD 88) LMW-1S to LMW-2T 2143.50 2058.31 0.33 85.20 733 0.2 0.192 Bedrock Flow Zone Upgradient Downgradient Seepage Well ID Groundwater Groundwater K Oh Distance Effective Porosity Velocity Elevation Elevation 1 (ft/day) (ft) (ft) (ft/day)Z (Ft NAVD 88) (Ft NAVD 88) LMW-113 to LMW-26 2146.64 2056.39 1.96 90.24 720 0.001 245.7 C13-96R to LMW-36 2129.56 2069.26 1.96 60.30 993 0.001 119.0 Notes: 1- Hydraulic conductivity values taken from slug test performed on monitoring wells with in each flow zone. Z - Value represents an estimate of the velocity of groundwater through bedrock fractures. Groundwater elevations are based on water level data collected on September 26, 2022. Monitoring wells are not listed where groundwater contour information is unavailable to calculate velocity. Hydraulic gradients and groundwater velocities are approximate. Effective porosity taken from the Updated Groundwater Flow and Transport Modeling Report for Asheville Steam Electric Plant, Arden, NC - September 2022. ft - feet ft/day - feet per day NAVD 88 - North American Vertical Datum 1988 Prepared By: RSB Checked By: KHF Page 1 of 1 TABLE 5 GROUNDWATER FIELD RESULTS AND ANALYTICAL DETECTIONS SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT ASHEVILLE STEAM ELECTRIC PLANT DUKE ENERGY PROGRESS, LLC, ARDEN, NC Parameter SWS ID Units Monitoring Wells MDL SW GWPS 15A NCAC 02L Standard CB-9 CB-9BR CB-9SL LMW-1B LMW-1S LMW-2B LMW-2T LMW-3B LMW-4B pH 320 S.U. 4.9 5.9 5.5 6.2 5.9 6.5 7.0 6.9 6.2 NE 6.5-8.5 Temperature 325 Deg C 19 18 19 19 18 19 19 16 15 NE NE Specific Conductance 323 µmhos/cm 29 84 46 104 62 69 61 476 396 NE NE Dissolved Oxygen - mg/L 2.45 0.29 3.64 0.27 2.14 1.92 4.08 1.29 0.24 NE NE Oxidation Reduction Potential 336 mV 348 289 339 277 413 269 396 334 204 NE NE Eh - mV 553 494 544 482 618 474 601 539 409 NE NE Turbidity 330 NTU 4.3 7.3 6.5 6.1 4.3 4.0 4.7 3.4 7.7 - NE NE Antimony 13 µg/L <1 <1 0.135 JB <1 <1 <1 <1 <1 0.133 JB 0.104 NE 1 Arsenic 14 µg/L 0.15 J <1 <1 0.117 J 0.122 J <1 <1 0.341 J 0.375 J 0.111 NE 10 Barium 15 µg/L 27 25 44 27 41 46 31 77 28 2 NE 700 Beryllium 23 µg/L <5 <S <5 <S <5 <S <5 <S <5 2 NE 4 Boron 428 µg/L 6J <50 <50 <50 <50 12J 26J 12J 44J 5 NE 700 Cadmium 34 µg/L <1 0.048 J <1 <1 <1 <1 0.043 J <1 <1 0.032 NE 2 Chloride 301 mg/L 6.5 7.7 7.8 8.1 6.2 7.9 9.9 3.2 7.6 0.0154 NE 250 Chromium 51 µg/L 0.275 J <1 0.49 J 0.238 J 0.769 J 0.364 J <1 0.269 J <1 0.185 NE 10 Cobalt 53 µg/L 0.9 J 0.084 J <1 <1 0.674 J 0.286 J 0.404 J 0.384 J 25.8 0.077 NE 1 Copper 54 µg/L <5 <5 <5 <5 <5 <5 <5 <5 <5 1 NE 1,000 Fluoride 312 mg/L <0.1 0.05 J <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 0.45 J 0.0479 NE 2 Iron 340 µg/L 381 50J 131 39J 236 44J 95J 181 11100 4 NE 300 Lead 131 µg/L <1 0.055 J 0.045 J <1 0.06 J 0.093 J 0.06 J 0.069 J <1 0.037 NE 15 Manganese 342 µg/L 31 51 2J 31 71 12 22 300 6140 1 NE 50 Mercury 132 µg/L 0.02 JB 0.01 JB 0.01 JB 0.05 BJ 0.01 JB 0.01 JB 0.01 JB 0.02 JB 0.01 JB 0.01 NE 1 Nickel 152 µg/L <5 <5 <5 <5 2 J <5 <5 <5 8 1 NE 100 Nitrate (as N) 303 mg-N/L 0.22 0.02 0.21 0.05 0.62 0.31 3.5 0.4 0.47 J 0.002 NE 10 Selenium 183 µg/L <1 <1 <1 <1 <1 <1 <1 0.2161 <1 0.193 NE 20 Silver 184 µg/L 0.385 J 0.048 J 0.246 J <1 <1 0.036 J <1 0.466 J <1 0.035 NE 20 Sulfate 315 mg/L 0.12 1.7 0.26 0.33 0.27 2.9 4.6 260 120 0.0428 NE 250 Thallium 194 µg/L 0.08 J <0.2 <0.2 0.05 J <0.2 <0.2 <0.2 <0.2 <0.2 0.041 NE 2 Total Dissolved Solids 311 mg/L 26 84 47 85 51 65 51 473 315 25 NE 500 Vanadium 209 µg/L 0.261 JB 0.277 JB 0.318 BJ 0.627 BJ 0.524 BJ 0.743 BJ 0.435 BJ 0.332 BJ 0.142 JB 0.114 NE 7 Zinc 213 µg/L 9 <5 8 <5 6 <5 <5 <5 <5 4 NE 1,000 Notes: Analytical data presented in this table reflect the Duke Energy Biological Analytical Data Storage System as of 11/18/2022. Bold concentrations are equal to or greater than the 15A NCAC 02L Standard (for pH bold indicates a measurement less than or greater than the indicated range). ' - 15A NCAC 02L Standards for groundwater- North Carolina groundwater quality standards (effective April 1, 2022). CB-9/BR/SL and LMW-1B/S are background groundwater monitoring wells. Samples collected by Duke personnel on September 26, 2022. B - Target analyte detected in method blank at or above the reporting limit. Target analyte concentration in sample is less than 10X the concentration in the method blank. Analyte concentration in sample could be due to blank contamination. "C - degrees Celsius 1 - Estimated concentrations equal to or greater than the MDL but less than the laboratory's method reporting limit (MRL). my - millivolts MDL - Laboratory Method Detection Limit; MDL values presented are for samples not diluted by the laboratory during analysis. mg/L- milligrams per liter mg-N/L- milligrams nitrogen per liter NCAC- North Carolina Administrative Code NE - not established NTU - nephelometric turbidity units S.U. - standard units SW GWPS - Solid Waste Groundwater Protection Standard SWS ID -Solid Waste Section Identification Number µmhos/cm - micromhos per centimeter µg/L - micrograms per liter <- Concentration not detected at or above the adjusted reporting limit. Prepared by RSB Checked by: KCO Page 1 of 1 TABLE 6 FIELD AND ANALYTICAL RESULTS THAT EQUAL OR EXCEED GROUNDWATER QUALITY STANDARDS SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT ASHEVILLE STEAM ELECTRIC PLANT DUKE ENERGY PROGRESS, LLC, ARDEN, NC September 15A NCAC Historical Parameter Sample ID 2022 Units 02L Concentration Cause and Significance Concentration Standard' Range pH LMW-413 6.2 S.U. 6.5 - 8.5 6.4 - 6.6 Natural variation, within background concentration range (5.7 - 6.4).3 Cobalt LMW-413 25.8 µg/L 1 56.7 - 75.6 Natural variation, less than historical concentration range. Iron LMW-413 11,100 µg/L 300 20,800 - 27,400 Natural variation, less than historical concentration range. LMW-313 300 299 - 774 Natural variation, within historical concentration range. Manganese µg/L 50 LMW-413 6,140 10,000 - 13,800 Natural variation, less than historical concentration range. First occurrence greater than historical concentration range; therefore, cause and Sulfate LMW-313 260 mg/L 250 75 - 230 significance cannot be determined at this time. Continue monitoring. Prepared by: RSB Checked by: KCO Notes: 1 - 15A NCAC 02L Standards for groundwater - North Carolina groundwater quality standards (effective April 1, 2022). z - Historical concentration ranges are based on data from the four baseline monitoring events that occurred between September 2020 and January 2021, prior to waste placement in the CCR Landfill. 3 - The background concentration range is based on data collected from updgradient bedrock monitoring wells during Landfill compliance sampling events (September 2020 through September 2022). µg/L - micrograms per liter mg/L - milligrams per liter S.U. -standard units Page 1 of 1 TABLE 7 SURFACE WATER FIELD RESULTS AND ANALYTICAL DETECTIONS SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT ASHEVILLE STEAM ELECTRIC PLANT DUKE ENERGY PROGRESS, LLC, ARDEN, NC Parameter SWS ID Units Surface Water Sample ID MDL 15A NCAC 02B (Class C)Z LF-SW-2' LF-SW-3' pH 320 S.U. 8.1 7.7 6.0 - 9.0 Temperature 325 Deg C 17 19 <_29 Specific Conductance 323 µmhos/cm 98 59 NE Dissolved Oxygen - mg/L 8.49 8.13 >_4 Oxidation Reduction Potential 336 mV 445 374 NE Eh - mV 650 579 NE Turbidity 330 NTUs 6.5 7.1 - <_50 Antimony 13 µg/L <1 0.145 JB 0.104 NE Arsenic 14 µg/L 0.119 J 0.157 J 0.111 NE Barium 15 µg/L 15 16 2 NE Beryllium 23 µg/L <5 <5 2 NE Boron 428 µg/L 24 J 251 5 7300* Cadmium 34 µg/L 0.103 J <1 0.032 NE Chloride 301 mg/L 9 9.8 0.0154 230 Chromium 51 µg/L 0.317 J <1 0.185 NE Cobalt 53 µg/L 0.295 J 0.1361 0.077 NE Copper 54 µg/L <5 <5 1 NE Fluoride 312 mg/L 0.06J <0.5 0.0479 1.8 Iron 340 µg/L 205 153 4 NE Lead 131 µg/L <1 0.082 J 0.037 NE Manganese 342 µg/L 198 17 1 NE Mercury 132 µg/L 0.011E 0.01JB 0.01 0.012 Nickel 152 µg/L <5 <5 1 NE Nitrate (as Nitrogen) 303 mg-N/L 0.08 0.07 0.002 NE Selenium 183 µg/L <1 <1 0.193 NE Silver 184 µg/L <1 <1 0.035 NE Sulfate 315 mg/L 9.5 4.4 0.0428 NE Thallium 194 µg/L 0.07 J <0.2 0.041 NE Total Dissolved Solids 311 mg/L 50 42 25 NE Vanadium 209 µg/L 0.3 BJ 0.351 BJ 0.114 NE Zinc 213 µg/L <5 <5 4 NE Prepared by: RSB Checked by: KCO Notes: Analytical data presented in this table reflect the Duke Energy Biological Analytical Data Storage System as of 11/18/2022. Bold concentrations are equal to or greater than the 15A NCAC 02B Standards for Class C surface waters (for pH, bold indicates a measurement less than or greater than the indicated range). ' The WQMP identifies the surface water samples as SW-1, SW-2, and SW-3. Identification was revised in order to differentiate between other Site monitoring program surface water locations. 15A NCAC 02B Standards for Class C surface waters. North Carolina surface water and wetland standards (effective September 1, 2022) Samples collected by Duke Energy personnel on September 26, 2022. Surface water sample location LF-SW-1' was not sampled due to dry conditions. - In -stream target value established per the language in 15A NCAC 026 .0202 and .0208. -- no relevant information. <- Concentration not detected at or greater than the adjusted reporting limit. B -Target analyte detected in method blank at or above the reporting limit. Target analyte concentration in sample is less than 10X the concentration in the method blank. Analyte concentration in sample could be due to blank contamination. "C - degrees Celsius µg/L- micrograms per liter µmhos/cm - micromhos per centimeter 1- estimated concentrations equal to or greater than the MDL but less than the laboratory's method reporting limit (MRL) MDL - laboratory method detection limit; MDL values presented are for samples not diluted by the laboratory during analysis. mg/L - milligrams per liter mg-N/L - milligrams nitrogen per liter my - millivolts NE - Not established per 15A NCAC 02B. NTU - nephelometric turbidity units S.U. - standard units SWS ID - Solid Waste Section Identification Number Page 1 of 1 TABLE 8 LEACHATE FIELD RESULTS AND ANALYTICAL DETECTIONS SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2022 SAMPLING EVENT ASHEVILLE STEAM ELECTRIC PLANT DUKE ENERGY PROGRESS, LLC, ARDEN, NC Parameter SWS ID Units Leachate Collection Sample MDL LCS-11, 2 pH 320 S.U. 6.7 Specific Conductance 323 µmhos/cm 1,509 Temperature 325 Deg C 21 Dissolved Oxygen - mg/L 7.12 Oxidation Reduction Potential 336 mV 401 Eh - mV 606 Turbidity 330 NTUs 19.0 - Antimony 13 µg/L 1.67 0.104 Arsenic 14 µg/L 6.06 0.111 Barium 15 µg/L 61 2 Beryllium 23 µg/L <5 2 Boron 428 µg/L 8,880 5 Cadmium 34 µg/L 0.126 J 0.032 Chloride 301 mg/L 39 0.0154 Chromium 51 µg/L 1.42 0.185 Cobalt 53 µg/L 1.42 0.077 Copper 54 µg/L 3J 1 Fluoride 312 mg/L 1.1 J 0.0479 Iron 340 µg/L 1050 4 Lead 131 µg/L 1.04 0.037 Manganese 342 µg/L 2,880 1 Mercury 132 µg/L 0.02 JB 0.01 Nickel 152 µg/L 5 1 Nitrate (as N) 303 mg-N/L 0.26 0.002 Selenium 183 µg/L 46 0.193 Silver 184 µg/L <1 0.035 Sulfate 315 mg/L 700 0.0428 Thallium 194 µg/L 0.223 0.041 Total Dissolved Solids 311 mg/L 1,470 25 Vanadium 209 µg/L 5.32 0.114 Zinc 213 µg/L 1 11 4 Prepared by: RSB Checked by: KCO Notes: Analytical data presented in this table reflect the Duke Energy Biological Analytical Data Storage System as of 11/18/2022. Sample collected by SynTerra and Duke personnel on September 26, 2022. 1- Comparative criteria are not applied to leachate collection samples. 2 - The WQMP identifies the leachate collection sample as L-1. Identification was revised in the field during sampling collection. < - Concentration not detected at or greater than the adjusted reporting limit. B - Target analyte detected in method blank at or above the reporting limit. Target analyte concentration in sample is less than 10X the concentration in the method blank. Analyte concentration in sample could be due to blank contamination. °C - degrees Celsius µg/L - micrograms per liter µmhos/cm - micromhos per centimeter 1 - Estimated concentrations equal to or greater than the MDL but less than the laboratory's method reporting limit (MRL). MDL - Laboratory Method Detection Limit; MDL values presented are for samples not diluted by the laboratory during analysis. mg N/L- milligrams nitrogen per liter mg/L - milligrams per liter my - millivolts NTU - Nephelometric turbidity unit S.U. - standard units SWS ID - Solid Waste Section Identification Number WQMP - Water Quality Monitoring Plan Page 1 of 1 Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant— CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina APPENDIX A FIELD SAMPLING FORMS L7 synTerra Science & Engineering Consultants CAMA 4_CCR `Landfill �NPDES F—j DGW❑ASW ❑LRB SPECIAL STUDY FIELD SAMPLING LOG % DUKE le ENERGI Site: Well/SW ID• — Date:�- GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: WEATHER: I )SUNNY ❑ PARTLY CLOUDY ❑ OVERCAST ❑ RAI SNO AIR TEMP:a �°F COMPANY: DUKE ENERGY T FIELD METER TYPE/ SERIAL M Liq ❑ OTHER: TURBIDIMETER TYPE/ SERIAL #: START PURGE TIME: S SAMPLE COLLECTION TIME: '. ( PUMPITUBING INTAKE D%TH: 00 DEPTH TO WATER: . (tt) MULT FACTOR *: 0.163 [*(radius/12)2*3.14*7.48] WELL DIAMETq `V (in) HEIGHT OF WC: (ft) WELL VOLUME: (gap WELL DEPTH: (ft) TOTAL VOLUME PURGED: (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: P R ° (Psi) I (sec) I (sec) Low Flow Sampling Stabilization Criteria pH t 0.1 standard unit Specific Conductance t 5% In pS/cm DO f 0.2 mgiL Turbidity less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE PH ORP TURBIDITY (FT) (x.xx) U (mmin) W (gallons OR mL) (x.xx) VC) W (mg/L) (x.xx) (PS/CM) W (su) (x.xx) (mv) (x) (NTU) (x.x) (syO t b 0-0 K b 0- a -� 2� -a a i a. S a PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES �NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? KIYES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? K]YES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 — (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR on 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH one Minor Strong ADDITIONAL NOTES: APPEARANCE lea, Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOQ BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP CAMA CCR ! Landfill NPDES �' DGWI ASW LRB ll SPECIAL STUDY, ;ita• Well/SW ID: /,,, DUKE C ' ENERG' Date: WATER FLOW VOLUME TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY TIME LEVEL RATE REMOVED VC) (mg/L) (PS/cm) (Su) (mv) (NTU) (FT) (x_xx1 (mUmin) (x) (gallons OR ML) (x.xx) (x) (x.xx) (x) (x.xx) (x) (x.x) Version 1.0 Revised 12/17/2018 RDP CAMA CCR! �Landfill NPDES DGW❑ASW ELRB SPECIAL STUDY. FIELD SAMPLING LOG % DUKE Ir ENERGY Site:Well/SW ID: C g - I got. Date: GROUNDWATER SAMPLE "SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO [:]WELL DEVELOPMENT FIELD STAFF: WEATHER: SUNNY ❑ PARTLY CLOUDY ❑ OVERCAST ❑ SN RAIN OW AIR TEMP:��°F COMPANY: DU ENERGY FIELD METER TYPE/ SERIAL #: ❑ OTHER: TURBIDIMETER TYPE/ SERIAL #: 3 START PURGE TIME: 41,6 SAMPLE COLLECTION TIME: ! PUMP/TUBING INTAKE DEPTH: (ft) DEPTH TO WATER: MULT FACTOR *: 0.163 [*(radius/12)2.3.14`7.48] WELL DIAMETER: U (in) HEIGHT OF WC:� (ft) WELL VOLUME: I) WELL DEPTH: (ft) TOTAL VOLUME PURGED. h TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: (Psi) I (se°: I (Sec) I Low Flow Sampling Stabilization Criteria • pH t 0.1 standard unit • Specific Conductance t 5% in pS/cm DO t 0.2 mg/L • Turbidity less than 1n NTI Is ®® ., •- ®(ww (x.xx) 0,01 49 mom OF M, rL-r-marmarr-rt i u I Mr mAL n up- I Ml5 JMtt I It I Mt GMAK I ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? YES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES N NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE ES NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUP ICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: —•• DETECTED ODOR one 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH NUA Minor Strong ADDITIONAL NOTES: APPEARANCE le Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP CAMA J CCR Landfill NPDES 7 DGW� ! ASW LRB SPECIAL STUDY. "itp. Well/SW ID: Date: (�. DUKE " ENERG' WATER FLOW VOLUME TEMPERATURE DO SPECIFIC PH ORP TURBIDITY LEVEL RATE REMOVED CONDUCTANCE TIME (FT) (mUmin) (gallons OR mL) (°C) (mglL) (PS/cm) (su) (mv) (NTU) (x.xx) (x) (x.xx) (x) (x.xx) (x) (x.xx) W (x.x) Version 1.0 Revised 12/17/2018 RDP ❑CAMA NCCRLjAl Landfill ❑NPDES ❑ DGW❑ASW ❑LRB ❑SPECIAL STUDY FIELD SAMPLING LOG 4 1 , DUKE �C'' ENERGY Site: Aaa�'k`� Well/SW ID: C gzl,-0j Si_ Date: I' Qqf - I z GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: COMPANY: DU ENERGY ❑ OTHER: WEATHER: SUNNY ❑ PARTLY CLOUDY ❑ OVERCAST []RAIN ❑SNOW AIR TEMP-]_S-_-F FIELD METER TYPE/ SERIAL M M6 f1 7_ U TURBIDIMETER TYPE/ SERIAL M START PURGE TIME: S SAMPLE COLLECTION TIME: t Yll, PUMP/TUBING INTAKE DEPTH: 0(ft) DEPTH TO WATER: - G (ft) MULT FACTOR ": 0.163 ["(radius/12)2'3.14'7.48[ WELL DIAMETER: Q .(3 (in) HEIGHT OF WC: a `-A)a (ft) WELL VOLUME: y"C2 a (gal) WELL DEPTH: (ft) TOTAL VOLUME PURGED: 0 (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: \ SAMPLING METHOD: PUMP SETTING: R R D (psi) (sec) (sec) Low Flow Sampling Stabilization Criteria pH f 0.1 standard unit Specific Conductance f 5% in pS/cm DO f 0.2 mg/L Turbidity less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (mL/min) (x) (gallons OR mL) (x.xx) (IC) (x) (mg/L) (x.xx) (PS/CM) (x) (su) (x.xx) (mv) (x) (NTU) (x.x) 15 l( 0�o:?- 0 5. ► y (.0.01 ti q- 10 0 I�., i .(A . s Gro, 1,Jk-- PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? []YES NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES?NYES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? ES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? YES ❑ NO DUPLICATE 1 _— (NTU) DUPLIC4IE - (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR on 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH o Minor Strong ADDITIONAL NOTES: APPEARANCE le Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP ECAMA FjCCRFjLandfiill F�NPDES❑DGW❑ASW 7LRBF-] SPECIAL STUDY Site: Well/SW ID: Date: ,tom DUKE �' ENERGY WATER FLOW VOLUME TEMPERATURE DO SPECIFIC pH ORP TURBIDITY LEVEL RATE REMOVED CONDUCTANCE TIME (FT) (mL/min) I (gallons OR mL) VC) (mg/L) I (PS/cm) (su) (mv) (NTU) (x.xx) W (x.xx) (x) (x.xx) (x) (x.xx) W Version 1.0 Revised 12/17/2018 RDP ECAMA F-]CCR�iLandfill [—]NPDES [—]DGWF—]ASW F—]LRB[—] SPECIAL STUDY Site: AcJvml�- FIELD SAMPLING LOG Well/SW ID: bP-q Date: 9 Z6-ZZ DUKE ENERGY GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE[:] LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: Ci!2- COMPANY: ❑/ DUKE ENERGY ❑ OTHER: WEATHER: []SUNNY ❑ PARTLY CLOUDY []OVERCAST []RAIN []SNOW AIR TEMP: *F FIELD METER TYPE/ SERIAL M 763511f TURBIDIMETER TYPE/ SERIAL M 3 51M START PURGE TIME: 1215 SAMPLE COLLECTION TIME: PUMPITUBING INTAKE DEPTH: (ft) DEPTH TO WATER: (ft) MULT FACTOR *: 0.163 [*(radius/12)2*3.14*7.481 WELL DIAMETER: (in) HEIGHT OF WC: — (ft) WELL VOLUME: (gal) WELL DEPTH: (ft) TOTAL VOLUME PURGED: (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other( J.RA ) PURGE METHOD: SAMPLING METHOD: i PUMP SETTING: P R D (psi) (sec) (sec) 4? MY , no woLtv flow Low Flow Sampling Stabilization Criteria pH t 0.1 standard unit Specific Conductance t 5% In pS/cm DO t 0.2 mg/L Turbidity less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (mL/min) W (gallons OR mL) (x.xx) (IC) W (mg/L) (x.xx) (PS/CM) W (su) (x.xx) (mv) W (NTU) (x.x) PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES ❑ NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? []YES []NO IS A TURBIDITY METER DUPLICATE REQUIRED? [—]YES[ I NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? ❑i YES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR None 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH None Minor Strong ADDITIONAL NOTES: APPEARANCE Clear Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP E]CAMA [—]CCRF]Landfill F]NPDES U DGWF]ASW 7]LRB ❑ SPECIAL STUDY, Site: Well/SW ID: Date: �•� DUKE ' ENERGY WATER FLOW VOLUME TEMPERATURE DO SPECIFIC pH ORP TURBIDITY TIME LEVEL RATE REMOVED CONDUCTANCE (FT) (mL/min) (gallons OR mL) (°C) (mg/L) (PS/cm) (su) (mv) (NTU) (x.xx) (x) (x.xx) (x) (x.xx) (x) (x.xx) (x) (x.x) Version 1.0 Revised 12/17/2018 RDP 7CAMA 7CCR 7Landfiill ❑NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY, FIELD SAMPLING LOG RM Site: A"ot&- Well/SW ID: LGS-( Date: 916-U- GROUNDWATER SAMPLE [:]SURFACE WATER SAMPLE ❑LEACHATE SAMPLE D WLO ❑ WELL DEVELOPMENT FIELD STAFF: 67L COMPANY Q DUKE ENERGY ❑ OTHER: WEATHER: •QSUNNY ❑ PARTLY CLOUDY ❑ OVERCAST ❑ RAIN []SNOW AIR TEMP:ZZ 'F FIELD METER TYPE/ SERIAL #: 70$"71C TURBIDIMETER TYPE/ SERIAL M 3379' START PURGE TIME: 12t)5 SAMPLE COLLECTION TIME: IZ t O PUMPITUBING INTAKE DEPTH: — (ft) DEPTH TO WATER: (ft) MULT FACTOR*: 0.163 [*(radius/12)2.3.14*7.48] WELL DIAMETER: (in) HEIGHT OF WC: (ft) WELL VOLUME: (gal) WELL DEPTH: (ft) TOTAL VOLUME PURGED: r (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: F R ° (Pso I (see) I (sec) Low How Sampling Stabilization Criteria • PH f 0.1 standard unit • Specific Conductance t 5% in NS/cm • DO f 0.2 mg/1 Twhirlihr ices fl- An urTrr., TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE PH ORP TURBIDITY (FT) (x.xx) (mUmin) (x) (gallons OR nnL) (x.xx) VC) W (mg/L) (x.xx) (PS/CM) (x) (su) (x.xx) (mv) (x) (NTU) (x.x ) l ?,ifs - 500 -t N 0.50 21 7 ► 2 1509 •65 Kul N. a ri-mmoc rccrr=r% i v i mr 6At m Vt' I Nis snit I It- I tit CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES ❑ NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? AYES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES ❑ NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? ❑AYES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR t2p, 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH &—e Minor Strong ADDITIONAL NOTES: APPEARANCE tv12 Cloudy Turbid Red/Iron Film on Surface Sheen FrnA Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP [—]CAMA [—]CCR❑Landfill F—]NPDES ❑ DGWF]ASW FLRB ❑ SPECIAL STUDY Site: Well/SW ID: Date: e TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (mL/min) (x) (gallons OR mL) (x.xx) VC) (x) (mg/L) (x.xx) (PS/cm) (x) (su) (x.xx) (mv) W (NTU) (x.x) Version 1.0 Revised 12/17/2018 RDP ❑CAMA ❑CCR Landfill ❑NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY Site: As6v-k FIELD SAMPLING LOG Well/SW ID: LF-5W- PDUKE ENERGY Date: 4-a-2z GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO WELL DEVELOPMENT FIELD STAFF: C!'� WEATHER: ❑SUNNY ❑ PARTLY CLOUDY ❑ OVERCAST [—]RAIN ❑SNOW AIR TEMP: °F COMPANY: ❑ DUKE ENERGY FIELD METER TYPE/ SERIAL #: 705V ❑ OTHER: TURBI DIMETER TYPE/ SERIAL M 331,ci START PURGE TIME: 1100 SAMPLE COLLECTION TIME: •— PUMP/TUBING INTAKE DEPTH: (ft) DEPTH TO WATER: (ft) MULT FACTOR *: 0.163 [`(radius/12)2*3.14*7.48] WELL DIAMETER: (in) HEIGHT OF WC: (ft) WELL VOLUME: (gal) WELL DEPTH: (ft) TOTAL VOLUME PURGED: (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( &IZ46 ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: P R o (Peo (sec) (sec) Low Flow Sampling Stabilization Criteria • pH t 0.1 standard unit TRY , no Sqmf(c t "44 Specific Conductance t 5% In NS/cm • DO t 0.2 mg/t • Turbidltv less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (mL/min) W (gallons OR mL) (x.xx) CC) W (mg/L) (x.xx) (PS/CM) W (Sul (x.xx) (mv) W (NTU) (x.x) I'LEASt Ktt-tK I U I HE 13AUK OF THI5 5HEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? [:]YES[:] NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? ❑YES [:]NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑ YES ❑ NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? ❑YES F,� NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR None 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH None Minor Strong ADDITIONAL NOTES: APPEARANCE Clear Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP DCAMA F—]CCR ❑Landfill F—]NPDES DGW[—] ASWFILRB ❑ SPECIAL STUDY Site: Well/SW ID: Date: ,.I � DUKE �'' ENERGY WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY TIME (FT) (x.xx) (mUmin) (x) (gallons OR mL) (x.xx) VC) W (mg/L) (x.xx) (PS/cm) W (su) (x.xx) (mv) (x) (NTU) (x.x) Version 1.0 Revised 12/17/2018 RDP ❑CAMA ❑CCR gLandfill ❑NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY FIELD SAMPLING LOG Site: /lstuvt& Well/SW ID: L.F-Sw-Z Date: 9-74-z,L ❑i GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: 0 7- WEATHER: ❑SUNNY ❑ PARTLY CLOUDY ❑ OVERCAST ❑ RAIN [:jSNOW AIR TEMP: °F COMPANY: ❑ DUKE ENERGY FIELD METER TYPE/ SERIAL #: 7I SS %f ❑ OTHER: TURBIDIMETER TYPE/ SERIAL#: 33211 START PURGE TIME: Yl /� SAMPLE COLLECTION TIME: It is PUMP/TUBING INTAKE DEPTH: (ft)' DEPTH TO WATER: (h) MULT FACTOR *: 0.163 [`(radius/12)2*3.14'7.48j WELL DIAMETER: (in) HEIGHT OF WC: _ (h) WELL VOLUME: (gal) WELL DEPTH: (ft) TOTAL VOLUME PURGED: (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( 6,R40 ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: P R D (Psi) I (Sec) I (Sec) I LOW rlow Sampling Stabilization Criteria pH t 0.1 standard unit • Specific Conductance t 5% in pS/cm • DO t 0.2 mg/1 • Turbidity less than in MT1 Ic TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (nnUmin) (x) (gallons OR nnL) (x.xx) VC) W (mg/L) (x.xx) (PS/CM) (x) (Su) (x.xx) (mV) W (NTU) (x.x) Itt3 -- 5*6 nn fkIA1— $,`lq g$ 9.01 YKS 6•5 rLtHat Ktrt=K I U I Ht bAL;K Ut I HIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES ❑ NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? ❑YES [:]NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? ❑YES ® NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 _ (NTU) DUPLICATE 2 (NTU' FINAL SAMPLE OBSERVATIONS: DETECTED ODOR a 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH 12rMinor Strong ADDITIONAL NOTES: APPEARANCE &ar Cloudy Turbid Red/Iron Film on Surface Sheen 9' 00 WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE P/ GOOD BAD NONE GOOD BAD NONE GOODI BAD NONE GOOD BAD NONE GOOD BAD i Version 1.0 Revised 1>1 1) .:zt t1F nCAMA nCCRnLandfill nNPDES [-] DGW❑ASW F-]LRB ❑SPECIAL STUDY. Site: V ot DU KE ENERGY Well/SW ID: Date: WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY TIME (FT) (x.xx) (mL/min) N (gallons OR mL) (x.xx) (°C) W (mg/L) (x.xx) (PS/cm) (x) (su) (x.xx) (mv) (x) (NTU) (x.x) Version 1.0 Revised 12/17/2018 RDP ❑CAMA F-]CCR Landfill ❑NPDES ❑ DGW❑ASW F-]LRB ❑ SPECIAL STUDY. FIELD SAMPLING LOG Site: A *4 Well/SW ID: s$ LF 5tv-3 Date: ❑GROUNDWATER SAMPLE [—]SURFACE WATER SAMPLE ❑LEACHATE SAMPLE ❑WLO ❑ WELL DEVELOPMENT FIELD STAFF: G77 WEATHER: ❑SUNNY El PARTLY CLOUDY ❑OVERCAST ❑RAIN ❑SNOW AIR TEMP: °F COMPANY: ❑i DUKE ENERGY FIELD METER TYPE/ SERIAL #: ?6NA, ❑ OTHER: TURBIDIMETER TYPE/ SERIAL #: 13A START PURGE TIME: 1325 SAMPLE COLLECTION TIME: 13,70 PUMPITUBING INTAKE DEPTH: — (tt) DEPTH TO WATER: r' (ft) MULT FACTOR *• 0.163 ['(radius/12)2'3,14'7.481 WELL DIAMETER: — (in) HEIGHT OF WC: — (n) WELL VOLUME: — (gal) WELL DEPTH: (tt) TOTAL VOLUME PURGED: (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: y SAMPLING METHOD: PUMP SETTING: P R 6948 (PSD I (sec) I (sec) I Low Flow Sampling Stabilization Criteria pH t 0.1 standard unit Specific Conductance t 5% in pS/cm • DO t 0.2 mg/€ Turbidity less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (mL/min) (x) (gallons OR mL) (x.xx) (°C) (x) (mg/L) (x.xx) (PS/cm) W (su) (x.xx) (mv) W (NTU) (x.x) t32g — gfnccm w --t 1 a 3,13 5 9 7. 6 b 3?lf 7 VLtwst KtFtK I U I HE IJAGK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? [:]YES[:] NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? A YES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES ❑ NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? DYES 2 NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR H2S Petroleum Earthy Musty Undetermined ODOR STRENGTH a Minor Strong ADDITIONAL NOTES: APPEARANCE Fe r Cloudy Turbid Red/Iron Film on Surface Sheen /r s Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP F-]CAMA 7CCR Landfill F-]NPDES 7 DGW❑ASW F�LRB ❑ SPECIAL STUDY. Site: Well/SW ID: Date: WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY TIME (FT) (x.xx) (mUmin) (x) (gallons OR mL) (x.xx) (°C) (x) (mg/L) (x.xx) (us/cm) (x) (su) (x.xx) (mv) N (NTU) (x.x) Version 1.0 Revised 12/17/2018 RDP ❑CAMA [--]CCRLandfill ❑NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY Site: 464wlll FIELD SAMPLING LOG Well/SW ID: LMW- )Q Date: 9 28-vL GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: G)2 COMPANY: M DUKE ENERGY ❑ OTHER: WEATHER: ❑SUNNY OPARTLYCLOUDY ❑OVERCAST DRAIN ❑SNOW AIRTEMP:73 °F FIELD METER TYPE/ SERIAL M 763374 TURBIDIMETER TYPE/ SERIAL #: 33" START PURGE TIME: (52.7 SAMPLE COLLECTION TIME: (50 PUMP/TUBING INTAKE DEPTH: q$ (h) DEPTH TO WATER: 2>•03 (n) MULT FACTOR *• 0.163 ["(radius/12)2'3.14"7.48] WELL DIAMETER: 2•0 (in) HEIGHT OF WC: 8&, l'i (ft) WELL VOLUME: 1..07 (gal) WELL DEPTH: (05.71 (ft) TOTAL VOLUME PURGED: a• 1V (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: (psi) I (Se.) I (S.C) I Low 1-low Sampling Stabilization Criteria pH t 0.1 standard unit • Specific Conductance f 5% In pS/cm • DO t 0.2 mg/I • Turbidity less than 9n NTlts TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (nnUmin) W (gallons OR mL) (x.xx) CC) W (mg/L) (x.xx) (PS/CM) W (su) (x.xx) (mv) W (NTU) (x.x) (550 2 .Iy 750 0.30 Z7 1, 11 6.0r. 3Y2. 22.a (533 21.16 2So v,s5 o.3K R°I &(Z 719I'•5 )S36 23.(4 G.? Z"> 2 (01 `.rK 2ty &� 1�3°i Z3�(6 2110 0,1S I.Ct 6.21 sK G•c� Z7'j �.r rLMAZ& KtttK I I tit bAGK OF I HIb SHEE T IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? []YES Q NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? ElYES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES Q NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? ©YES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR o 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH ne Minor Strong ADDITIONAL NOTES: APPEARANCE ar Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP [-]CAMA FCCR❑Landfill FNPDES ❑ DGW❑ASW FLRB ❑ SPECIAL STUDY Site: Well/SW ID: Date: b WATER FLOW VOLUME TEMPERATURE DO SPECIFIC pH ORP TURBIDITY LEVEL RATE REMOVED CONDUCTANCE TIME FT ( ) (mUmin) (gallons OR mL) C (° ) (mg/L) (PS/cm) (su) (mv) (NTU) (x.xx) (x) (x.xx) (x) (x.xx) (x) (x.xx) (x) (x.x) Version 1.0 Revised 12/17/2018 RDP ❑CAMA ❑CCR Landfill ❑NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY. Site: &gA FIELD SAMPLING LOG Well/SW ID: LM,W- I S Date: 9-7d-�2 ��•� DUKE �' ENERGY GROUNDWATER SAMPLE [—]SURFACE WATER SAMPLE ❑LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: 6%. WEATHER: []SUNNY ❑PARTLYCLOUDY ❑OVERCAST DRAIN SNOW AIRTEMP: °F COMPANY: ❑/ DUKE ENERGY FIELD METER TYPE/ SERIAL M 76 I-7y ❑ OTHER: TURBIDIMETER TYPE/ SERIAL M -n2l START PURGE TIME: SAMPLE COLLECTION TIME: IS1S PUMPITUBING INTAKE DEPTH: 615 (ft) DEPTH TO WATER: 2643 (ft) MULT FACTOR *: 0.163 C(radius/12)2.3.14.7.48I WELL DIAMETER: / Zo (in) HEIGHT OF WC: No. 37 (ft) WELL VOLUME: G •58 (gal) WELL DEPTH: t;. & (ft) TOTAL VOLUME PURGED: /• S' (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: / PUMP SETTING: P R p Ps;) 5eC SeG Low Flow Sampling Stabilization Criteria pH f 0.1 standard unit Specific Conductance f 5% in pS/cm • DO t 0.2 mg/L Turbidity less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY FT ( ) (x.xx) (mL/min) W (gallons OR mL) (x.xx) (°C) W (mg/L) (x.xx) (PS/CM) W (su) (x.xx) (mv) W (NTU) (x.x) IhoZ A..-N 300 a •2S Z► 3. q N 5'6 L • U 39 2 t 7 'L 4%5 21G1 IS 15 3uD o. SS l 5 2.71 57 9•c,'7 1 Y (Z I ISOV ?U.65 300 Olen (g p (G 6 ( 5"t$ V 16 G. 6I( 19-'K I3rN I, to 11S -zoo/ 5.14 %0Z L•o ISIh74.65 I.KS [£s 2.ty L2 S.dJy Y11 tl3 PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES [;� NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? ©YES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES F_� NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? YES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 _ (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR 13),e 112S Petroleum Earthy Musty Undetermined ODOR STRENGTH � e Minor Strong ADDITIONAL NOTES: APPEARANCE ar Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP DCAMA F-] CCR F] Landfill FNPDES ❑ DGW❑ASW F]LRB ❑ SPECIAL STUDY. Site: Well/SW ID: (•.. DUKE V " ENERGY Date: WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY TIME (FT) (x.xx) (mUmin) W (gallons OR mL) (x.xx) CC) W (mg/L) (x.xx) (PS/cm) W (su) (x.xx) (mv) W (NTU) (x.x) Version 1.0 Revised 12/17/2018 RDP ❑CAMA [--]CCR ❑Landfill ❑NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY Site: 1751UIAA FIELD SAMPLING LOG Well/SW ID: L^1-26 •t� DUKE � ENERGY Date: 1-74-ZZ GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: COMPANY: ❑ DUKE ENERGY ❑ OTHER: WEATHER: []SUNNY ❑PARTLYCLOUDY ❑OVERCAST ❑RAIN SNOW AIRTEMP: *F FIELD METER TYPE/ SERIAL #: ? TURBIDIMETER TYPE/ SERIAL #: 33?l START PURGE TIME: I T % SAMPLE COLLECTION TIME: los PUMP/TUBING INTAKE DEPTH: SUS (ft) DEPTH TO WATER: A 7? (ft) MULT FACTOR ": 0.163 [*(radius/12)2*3.14*7.48] WELL DIAMETER: ' (in) HEIGHT OF WC: Y5,53 (ft) WELL VOLUME: 7.48 (gal) WELL DEPTH: TOTAL VOLUME PURGED: 155 (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other( ) PURGE METHOD: SAMPLING METHOD: / PUMP SETTING: P R o cP�i) (sec) (Sec) Low Flow Sampling Stabilization Criteria pH t 0.1 standard unit Specific Conductance f 5% in pS/cm • DO f 0.2 mg/L Turbidity less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (mUmin) (x) (gallons OR mL) (x.xx) VC) (x) (mg/L) (x.xx) (PS/cm) (x) (su) (x.xx) (mV) (x) (NTU) (x.x) Mw 65.12 300 0.10 1,6 5•54 15 6•b6) 3sl• Y. 140 65.7,0 3w 0.63 22 3.5D 62. 6.156 300 K.0 I 'b6 f, 5.4V 300 O A 2,01 6,. $ I Z-86 5.1 ijjA 641W I 3D 1.25 11 1.6A 27 -Fs Wit 6 ,9 3,0 1.55 t-1 1.012 A°► b9,61 y.o PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE 15 FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES j NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? ❑A YES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES [ZNO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? ®YES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR o 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH Minor Strong ADDITIONAL NOTES: APPEARANCE r Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP F—]CAMA F—]CCR❑Landfill F—]NPDES ❑ DGWF—]ASW [—]LRB ❑ SPECIAL STUDY Site: Well/SW ID: Date: .(� DUKE �' ENERGY WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY TIME (FT) (x.xx) (mUmin) W (gallons OR mL) (x.xx) (°C) W (mg/L) (x.xx) (PS/cm) W (Su) (x.xx) (mv) (x) (NTU) (x.x) Version 1.0 Revised 12/17/2018 RDP ❑CAMA F-1CCR Landfill ❑NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY. Site: 4S�ttA, FIELD SAMPLING LOG Well/SW ID: GMV-2T .J� DUKE � ENERGY Date: '1- 26-7Z 10 GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO [:]WELL DEVELOPMENT FIELD STAFF: t! 71- WEATHER: [:]SUNNY❑ PARTLY CLOUDY ❑ OVERCAST ❑ RAIN SNOW AIR TEMP: °F COMPANY: © DUKE ENERGY FIELD METER TYPE/ SERIAL #: %6 A ❑ OTHER: TURBIDIMETER TYPE/ SERIAL #: 337A START PURGE TIME: 1343 SAMPLE COLLECTION TIME: PUMP/TUBING INTAKE DEPTH: 66 (ft) DEPTH TO WATER: h'r � (ft) MULT FACTOR *: 0.163 [•(radius/12)2.3.14.7.48j WELL DIAMETER: 7.0 (in) HEIGHT OF WC: ZN•Z (ft) WELL VOLUME: 3.g K (gal) WELL DEPTH: 810 (ft) TOTAL VOLUME PURGED: 0.3; (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: ' SAMPLING METHOD: PUMP SETTING: P RI 11 (psi) (sec) (sec) Low Flow Sampling Stabilization Criteria pH t 0.1 standard unit Specific Conductance t 5% in pS/cm DO f 0.2 mg/L Turbidity less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (mUmin) W (gallons OR mL) (x.xx) (IC) W (mg/L) (x.xx) (PS/cm) (x) (su) (x.xx) (mv) (x) (NTU) (x.x) 13K6 5.ti'L /so 0. w Zo 7A o 5,7 Z LIS 3t Fs.'Z 13K11 GS• o I 110 t all 5.11 ao 7 2$ 7 p 7S.S tI52 .3 k 160 0. 6D l q 4.16 61 7.0q 368 '4 K ( SS b5.3k l %D 0. lot 14,04 1 6S 7.oK 3,99 it, 1356 65-$t Ito 0.1gs 19 1 7-OZ *3qt It PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES 0 NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? DYES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES 0 NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? QYES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 _ (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR N e H2S Petroleum Earthy Musty Undetermined ODOR STRENGTH a Minor Strong ADDITIONAL NOTES: APPEARANCE ar Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP [—] CAMAF—]CCRF—]Landfill F7NPDES ❑ DGWF—]ASW [—]LRB ❑ SPECIAL STUDY. Site: Well/SW ID: Date: ��� DUKE �' ENERGI WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY TIME (FT) (x.xx) (mL/min) W (gallons OR mL) (x.xx) (°C) (x) (mg/L) (x.xx) (PS/cm) (x) (su) (x.xx) (mv) W (NTU) (x.x) Version 1.0 Revised 12/17/2018 RDP ❑LAMA �CCRFj Landfill ❑NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY, FIELD SAMPLING LOG Site: 11S�wl t Well/SW ID: tMkJ-30 MM Date: 9-9-n ❑i GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF`: 6-It COMPANY: ❑i DUKE ENERGY ❑ OTHER: WEATHER: SUNNY ❑PARTLYCLOUDY ❑OVERCAST ❑RAIN ❑SNOW AIR TEMP: ?S °F FIELD METER TYPE/ SERIAL M Mik TURBIDIMETER TYPE/ SERIAL M M-91 START PURGE TIME: iZ N2 SAMPLE COLLECTION TIME: 1100 PUMPITUBING INTAKE DEPTH: DEPTH TO WATER: *33.63 (ft) MULT FACTOR *• 0:163 [*(radius/12)2"3.14*7,48] WELL DIAMETER: ZO (in) HEIGHT OF WC: 11.67 (ft) WELL VOLUME: /•90, (gal) WELL DEPTH: K5.30 If) TOTAL VOLUME PURGED: 0-ST (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: F ft D (psi (see) (se D) Low Flow Sampling Stabilization Criteria pH t 0.1 standard unit • Specific Conductance t 5% In pS/cm • DO f 0.2 mg/1 • Turbidity less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (mL/min) W (gallons OR mL) (x.xx) VC) (x) (mg/L) (x.xx) (NS/cm) W (su) (x.xx) (mv) (x) (NTU) (x.x) 1 31.0tD lso 0-to I qu K14 .cg 21q 8.0 It" 33.011 l bo 0,15 IL 2,64 1.11t7 7.07 6.2 ttiSt 3.ct°d tfso o, lb -3� N60 1v �,o ?.v 125 33•01$ I W p, 7D 16 1.3 "71 88 331 218 t25'1 3 1� Ike 1, 7 Sb 3 PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENTNEEDED (>10 NTUS)? ❑ YES [�] NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? EYES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES [�] NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? EYES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE (NTU) FINAL SAMPLE OBSERVATIONS: ��-, DETECTED ODOR . 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH Minor Strong ADDITIONAL NOTES`: APPEARANCE I a r Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE w i Version 1,0 Revised 12/1712018 RDP [—]CAMA 7CCR7Landfill 7NPDES ❑ DGW❑ASW FLRB ❑ SPECIAL STUDY, Site: Well/SW ID: V ,ot DUKE „R. TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (mUmin) (x) (gallons OR mL) (x.xx) (°C) (x) (mg/L) (x.xx) (PS/cm) (x) (su) (x.xx) (mv) (x) (NTU) (x.x) Version 1.0 Revised 12/17/201'8 RDP ❑CAMA F,-]CCR7Landfiill [:]NPDES 7DGW7ASW ❑LRB❑ SPECIAL STUDY. FIELD SAMPLING LOG Site: AsWle Well/SW ID: LA4W`g8 Date: ? ZZ-7 Z GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: G%L WEATHER: /❑SUNNY ❑ PARTLY CLOUDY ❑ OVERCAST ❑ RAIN ❑SNOW AIR TEMP: 67 -F COMPANY: [7] DUKE ENERGY FIELD METER TYPE/ SERIAL M 7435z1 ❑ OTHER: TURBIDIMETER TYPE/ SERIAL M 73ut START PURGE TIME: (l2Z SAMPLE COLLECTION TIME: 11$3 PUMP/TUBING INTAKE DEPTH: q4 (ft) DEPTH TO WATER: Z2IS0 (ft) MULT FACTOR ": 0.163 ['(radius/12)2'3.14'7.48] WELL DIAMETER: Z.o (in) HEIGHT OF WC: Z6•N5 (ft) WELL VOLUME: y 31 (gal) WELL DEPTH: Kq.15 (ft) TOTAL VOLUME PURGED: Z. rS (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: I SAMPLING METHOD: PUMP SETTING: P R o (Ps) (Sec) (sec) Aft+ oA Low Flow Sampling Stabilization Criteria pH f 0.1 standard unit Specific Conductance f 5% in pS/cm DO t 0.2mg11 Turbidity less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (nnL/min) W (gallons OR mL) (x.xx) VC) W (mg/L) (x.xx) (PS/cm) W (su) (x.xx) (mv) (x) (NTU) (x.x) 1126 23.11 3V 0.0 $ 2.00 430 6-11H 31Z Z011. 1124 z .tZ 300 ►KW 0'61/ 16 0.65 3111 6. 38 Z140 188 (tL o ZI 6 50 1.05 15 0.38 3ti . ? 3VI tk'ls 24.v1 1150 1AS ts 0, ? `1b 4.21z Z0.1 !K.► 1(4% 24.01 3SP 1.to 1s OILS 3915 6.19 206 12.q I(S( 21wt SO 2.1 S 1 o,2N q 6<I % 2 7,7 PLEASE REFER TO THE BACK OF THIS SHEET 1F THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES Q NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? © YES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES L�NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? [`EYES ❑ NO IS THE TURBIDITY METER DUPLICATE' TAKEN, WITHIN 15%? ❑YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR T'-' H2S Petroleum Earthy Musty Undetermined ODOR STRENGTH Minor Strong ADDITIONAL NOTES: APPEARANCE Cloudy Turbid Red/Iron Film on Surface Sheen ngs Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE GOOD BAD NONE Version 1.0 Revised 12/17/2018 RDP F-]CAMA F-]CCR❑Landfill F-]NPDES ❑ DGWFJASW ❑LRB ❑ SPECIAL STUDY, Site: Well/SW ID: Date: s WATER FLOW VOLUME TEMPERATURE DO SPECIFIC pH ORP TURBIDITY LEVEL RATE REMOVED CONDUCTANCE TIME (FT) (mUmin) (gallons OR mL) VC) (mg/L) (PS/cm) (su) (mv) (NTU) (x.xx) (x) (x.xx) W (x.xx) (x) (x.xx) (x) (x:x) Version 1.0 Revised 12/17/2018 RDP ❑LAMA ❑CCR❑j Landfill ❑NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY, DAILY CALIBRATION LOG Site: ASV Date: R-Z6-�L DUKE ENER FIELD PERSONNEL: G31 WEATHER: ❑SUNNY ❑ PARTLY CLOUDY ❑ OVERCAST ❑ RAIN ❑SNOW TEMPERATURE (APPROX): INSITU SERIAL M 763574 F 21000 SERIAL #: 3311 pH Time: 1�3o Lot Number Expiration p Buffer Temperature p (°C) Chart pH (Su) Meter .Reading (su) Within ± 0.1 su? 7.00 su Zt;oZ311 oq-30-Z L Zuti 50 7.02 7,08 (n� N 10.01 su 260230 o3.31—Z3 Za.S`t (o,06 IQ/o N 4.01 su 260263 04.10-23 Zo•Iq ttco K-02 N Check of 7.00 su as Live Reading 260231I oq-3o-2Z I &/• Sb 710Z 7,0? N Post Calibration- Date: Time: i015 Within 0.2 SO 7.00 su 26623�1 pq-3o-2Z 16-o2 7.65 7.07 J N 10.01 su 11 (6•03 (0.12 10.1( ( N 4.01 su 260263 66.30-Z3 16.0& 3,q 1 14.01- N Specific Conductivitv Time: 1o35 Lot Number = Expiration Buffer Temperature (°C) Meter Reading (ps) Within ± 10%°? Standard Value: 1 to ps If -to I`07•0 N Calibration Check of 2Z'] Ps as Live Reading a 18•q 226,K (J N Post Calibration- Date: ci-27.22 Time: (a( I�t�o ps gt;KogK r<<<r23 16.22 I�tc t.6 N ORP Buffer Adjusted Meter Time: Ins Lot Number Expiration Temperature Value Reading Within ± 20%? (°C) (mV) (mV) 42a my t 3�8t�- (g.90 �(Y3 yY3, K N Post Calibration- Date: - Time: wm mV g.010 N Revised 12/18/2018 K 1--]CAMA F�CCR7Landfill nNPDES ❑ DGW❑ASW nLRB ❑ SPECIAL STUDY DUKE ENERGY, DAILY CALIBRATION LOG Site: Date: 9-24-2-1- Field Personnel: viz Barometric Meter Dissolved Oxygen Temperature Pressure Chart DO Reading % Saturation Within # 0.5? Time:. (°C) (mg/L) (%Sat) fo 35 (mmHg) (mg/L) 1&61 204• 35 6.7 8.71 100,cld C 05 N Calibration Check as Live lts.65 7a'4•3c ' •b.7 ' &'71 ivr,oz� �Y N Reading e Post Calibration - Date: �%-Z? Ib•66 7o3. li . S-C(i N Time: fy Zy Turbidity Time: fDYU Standard (NTU) Acceptance_ Range,(NTU) . Meter Reading (NTU) Within + 5%? 10.0 ± .5 +U-o (y N Post Calibration - Date: 01-27 N Time: 10,0 Daily Turbidity Meter BLANK DI Water (NTU) Less than 0.10 NTU? Date: q-26•Z2 N 0', (VtO Time: Revised 12/18/2018 KKH Semiannual Water Quality Monitoring Report — September 2022 Sampling Event Asheville Steam Electric Plant — CCR Landfill (Permit No. 1119-INDUS-2020) Arden, North Carolina r APPENDIX B LABORATORY REPORT AND CHAIN -OF -CUSTODY FORMS 1610 synTerra Science & Engineering Consultants Analytical Data Review Checklist - Aqueous Facility/Site Asheville Steam Electric Plant State INC Location/Sample IDs CB-9, CB-91311, CB-9SL, LCS-1, LF-SW-2, LF-SW-3, LMW-1B, LMW-1S, LMW-213, LMW-2T, LMW-3B, LMW-4B References: - ELN/A ❑v 1 ❑ Duke Central Lab, Pace Analytical Services Lab Report ID Sample Date Sample Receipt Date Analysis Complete Date ❑ Groundwater /22090472 9/26/2022 9/27/2022 10/12/2022 ❑ Surface Water ❑ Other National Functional Guidelines for Inorganic Superfund Methods Data Review (USEPA 2020) Guidance on Environmental Data Verification and Data Validation (USEPA 2002) Radiochemical Data Verification and Validation (MARLAP 2004) � Sample Receipt and Chain of Custody 1) Do the sample IDs and laboratory analyses recorded on the Chain of Custody match the sample IDs and analyses listed in the laboratory package? ❑� ❑ ❑ la) Do the dates and times of sampling listed on the Chain of Custody match the laboratory report? 0 ❑ ❑ ❑ ❑ ❑� 2) Is the sample temperature upon receipt at the laboratory recorded on the Chain of Custody form less than 6 degrees Celsius? If NO, then: 2a) Was the presence of wet ice noted in the cooler? OR ❑ ❑ ❑� 2b) Were the samples collected less than two hours prior to receipt at the lab? ❑� ❑ ❑ 3) Was the proper sample preservation checked and documented on the Chain of Custody or sample receipt form? ❑ ❑� ❑ 4) Are there any special notes, exceptions, and/or anomalies listed either on the Chain of Custody or sample receipt form? ❑ ❑v ❑ 15) Was the transfer of custody of the samples properly documented and traceable through signature, date, and time by all persons who relinquished and/or received custody of the samples? ❑ 7❑�❑ ❑ ❑� ®®Batch 6) Do the values for the field parameters listed on the Chain of Custody match the values entered in the lab report? eAssurance/Quality 7) Was the holding time for preparation and/or analysis met for each parameter? ❑ ❑� 7a) Total Alkalinity, Bicarbonate Alkalinity, Carbonate Alkalinity: Analyzed within 14 days of collection ❑ ❑ 7b) Bromide, Chloride, Fluoride, and Sulfate (Anions): Analyzed within 28 days of collection ❑ ❑ l] 7c) Sulfide: Analyzed within 7 days of collection 0 ❑ ❑ 7d) TOC and Nitrate -Nitrite: Analyzed within 28 days of collection ❑ ❑ l] 7e) Total Phosphorus (TP) and Dissolved TP: Analyzed within 28 days of collection ❑ ❑ (] 7f) Hexavalent Chromium: Analyzed Within 24 hours (unpreserved) / 28 days (preserved) of collection 0 ❑ ❑ 7g) Mercury and Dissolved Mercury: Analyzed within 28 days of collection (preserved) 0 ❑ ❑ 7h) Total and Dissolved Metals: Analyzed within 180 days of collection 0 ❑ 71) TSS and TDS: Analyzed within 7 days of collection ❑ ❑ 0 7J) Radionuclides: Analyzed within 180 days of collection ❑ ❑ ❑ ❑ I] 0 7k) Methane: Analyzed within 14 days (preserved) / 7 days (unpreserved) of collection 71) Oil and Grease: Analyzed within 28 days of collection ❑� ❑ ❑ 8) Are there any qualifiers assigned by the laboratory and if so, are the qualifier definitions provided? ❑� ❑ 9) Method Blank- Were any parameters detected in the method blank(s)? ❑� ❑ 9a) If YES, were any target analyses detected in the samples at concentrations less than ten times the method blank concentration? ❑ ❑ ❑� ❑ ❑ )] 10) Laboratory Control Sample - Were any parameters flagged by the lab as being outside the limits of control in the associated laboratory control sample (LCS)? 1 Do) If YES, was the parameter recovery less than 50 percent or greater than 150 percent? ❑ ❑ 2 10b) Were the some parameters detected in the samples? ❑� ❑ ❑ 11) Matrix Spike Sample - Did the laboratory provide matrix spike results (MS/MSD)? If so, then: ❑� ❑ ❑ 111a) Was the original sample spiked a project sample? If so, then: ❑ ❑� ❑ 11 b) Were any parameters flagged by the lab as being outside the limits of control in the associated matrix spike sample? Batch 70!Assurance/Quality 0 ❑ ❑ 12) Laboratory Duplicate Sample - Did the laboratory provide lab duplicate sample results? If so, then: ❑ ❑ 12a) Was the sample analyzed as a laboratory duplicate a project sample? If so, then: ❑ 0 ❑ 12b) Were any parameters flagged by the lab as being outside the limits of control in the laboratory duplicate sample? 0 ❑ ❑ 13) Field Duplicate Sample - Is the relative percent difference between the parent and field duplicate sample results greater than 35 percent? 0 ❑ ❑ 14) Field/Equipment/Trip Blanks - Were any parameters detected in the associated field, equipment, and/or trip blanks? 0 ❑ ❑ 14a) If yes, were any target analytes detected in the samples at a concentration less than ten times the Field/Equipment/T(p Blank concentration? ❑v ❑ ❑ 15) Were initial and continuing calibration blank information within acceptable criteria per the lab report? ❑ ❑� ❑ 16) Were any reporting limits for diluted, non -detect results greater than the screening criteria? ❑ ❑ 17) Radionuclides: Are quality control sample results provided? ❑ ❑� 17a) Are any results flagged or qualified? ❑ ❑ ❑° 17b) Are Uncertainty, MDC, Tracer/ and/or Carrier7 provided for each sample? The questions on this checklist refer to basic review of laboratory analytical reports for completeness and accuracy of data. Any responses requiring follow up action with the analytical lab or field personnel must be noted in the summary section at the end of this form before the data can be approved for use by technical leads. Lab Qualifiers: B (Duke) -Target analyte detected in the Method/Prep Blank at or above the reporting limit; target analyte concentration in sample is less than 10x the concentration in the Method/Prep Blank. B1(Duke) -Target analyte was detected in Method/Prep Blank at or above the reporting limit; target analyte concentration in sample is below the reporting limit or greater than lox the concentration of the target analyte detected in the Method/Prep Blank. J (Duke) -Analyte detected above the MDL, but below the RL; analyte concentration should be considered an estimate. U (Duke) -Analyte was analyzed for, but not detected above the MDL. Validation Qualifiers: R- Result is unusable. The sample result is rejected due to serious deficiencies in meeting quality control criteria; the analyte may or may not be present in the sample. J - Value is estimated. The result is below the reporting limit or potentially biased based on data validation. U-Analyte was analyzed form but not detected above the minimum detectable concentration (MDC) or method detection limit (MDL). B -Target analyte detected in the method blank an in the sample at a concentration less than 10x the blank concentration. • Mercury (0.024 ug/L) was detected in the Method Blanks; Mercury was also detected in the samples at concentrations less than 10x the blank concentrations. • Antimony (0.12 ug/L) and Vanadium (0.374 ug/L) (B, B,1) were detected in the Method Blank; Antimony and Vanadium were also detected in the samples at concentrations less than lOx the blank concentrations. • The RPD between LMW-413 and the field duplicate is greater than 35% for Nitrate (2.1/0.21 mg/L) and Nitrate as N (0.47/0.05 mg/L). • Mercury (0.01 ug/L), Iron (0.012 mg/L), and Vanadium (0.18 ug/L) were detected in the Field Blank; Mercury, Iron, and Vanadium were also detected in the samples at concentrations less than lox the blank concentrations. Review Determination: ❑ Usable 0 Usable with Required Actions ❑ Unusable Signatures: Date: Data Quality Reviewer REB 10/27/2022 Technical Lead KHF 1/11/2023 DUE Analytical Laboratory ENERGY Y 13339 Hagers Ferry Road Huntersville, NC 28078-7929 McGuire Nuclear Complex - MG03A2 Phone:980-875-5245 Fax:980-875-4349 Order Summary Report Order Number: J22090472 Project Name: ASHEVILLE - ASHEVILLE STATE LF DETECTION MONITORING Task Code: LF Customer Name(s): Ashley Healy,B Moeller, D Obrien,J Stowe,C Zahora Customer Address: Asheville Steam Station 200 CP and L Drive Arden,NC 28704 Lab Contact: Peggy Kendall Phone: 980-875-5848 Report Authorized By: A, &-. mate: 10/12/2022 (Signature) Peggy Mdall Program Comments: QC Note: Iron (0.012 mg/L) was detected in the field blank. Data Flags & Calculations: Page 1 of 53 Any analytical tests or individual analytes within a test flagged with a Qualifier indicate a deviation from the method quality system or quality control requirement. The qualifier description is found at the end of the Certificate of Analysis (sample results) under the qualifiers heading. All results are reported on a dry weight basis unless otherwise noted. Subcontracted data included on the Duke Certificate of Analysis is to be used as information only. Certified vendor results can be found in the subcontracted lab final report. Duke Energy Analytical Laboratory subcontracts analyses to other vendor laboratories that have been qualified by Duke Energy to perform these analyses except where noted. Data Package: This data package includes analytical results that are applicable only to the samples described in this narrative. An estimation of the uncertainty of measurement for the results in the report is available upon request. This report shall not be reproduced, except in full, without the written consent of the Analytical Laboratory. Please contact the Analytical laboratory with any questions. The order of individual sections within this report is as follows: Job Summary Report, Sample Identification, Technical Validation of Data Package, Analytical Laboratory Certificate of Analysis, Analytical Laboratory QC Reports, Sub -contracted Laboratory Results, Customer Specific Data Sheets, Reports & Documentation, Customer Database Entries, Test Case Narratives, Chain of Custody (COC) Certification: The Analytical Laboratory holds the following State Certifications : North Carolina (DENR) Certificate #248, South Carolina (DHEC) Laboratory ID # 99005. Contact the Analytical Laboratory for definitive information about the certification status of specific methods. Sample ID's & Descriptions: Page 2 of 53 Sample ID Plant/Station Collection Date and Time Collected By Sample Description 2022025315 ASHEVILLE 26-Sep-22 11:15 AM Connor Zahora ASV_LF-SW-2 2022025316 ASHEVILLE 26-Sep-22 11:55 AM Connor Zahora ASV_LMW-4B 2022025317 ASHEVILLE 26-Sep-22 12:10 PM Connor Zahora ASV_LCS-1 2022025318 ASHEVILLE 26-Sep-22 1:00 PM Connor Zahora ASV_LMW-3B 2022025319 ASHEVILLE 26-Sep-22 1:30 PM Connor Zahora ASV_LF-SW-3 2022025320 ASHEVILLE 26-Sep-22 2:00 PM Connor Zahora ASV_LMW-2T 2022025321 ASHEVILLE 26-Sep-22 2:35 PM Connor Zahora ASV_LMW-2B 2022025322 ASHEVILLE 26-Sep-22 3:15 PM Connor Zahora ASV_LMW-1S 2022025323 ASHEVILLE 26-Sep-22 3:40PM Connor Zahora ASV_LMW-1B 2022025324 ASHEVILLE 26-Sep-22 2:49 PM Haley Seaton ASV_CB-9BR 2022025325 ASHEVILLE 26-Sep-22 3:22 PM Haley Seaton ASV_CB-9SL 2022025326 ASHEVILLE 26-Sep-22 3:49 PM Haley Seaton ASV—CB-9 2022025327 ASHEVILLE 26-Sep-22 Connor Zahora ASV_FD -20220926-1 2022025328 ASHEVILLE 26-Sep-22 2:00 PM Connor Zahora ASV_FB-20220926-1400 14 Total Samples Page 3 of 53 Technical Validation Review Checklist: COC and .pdf report are in agreement with sample totals❑ Yes ❑ No and analyses (compliance programs and procedures). All Results are less than the laboratory reporting limits. ❑ Yes❑ No All laboratory QA/QC requirements are acceptable. 0 Yes ❑ No Report Sections Included: d❑ Job Summary Report ❑ Sample Identification ❑ Technical Validation of Data Package d❑ Analytical Laboratory Certificate of Analysis ❑ Analytical Laboratory QC Report ❑ Sub -contracted Laboratory Results ❑ Customer Specific Data Sheets, Reports, & Documentation ❑ Customer Database Entries ❑ Chain of Custody ❑ Electronic Data Deliverable (EDD) Sent Separately Reviewed By: Peggy Kendall Date: 10/12/2022 Certificate of Laboratory Analysis Page 4 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV LF-SW-2 Sample #: 2022025315 Collection Date: 09/26/2022 11:15 AM Loc code: ASV LF-SW-2 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 9.0 mg/L 0.1 0.0154 1 EPA 9056A 09/27/2022 13:13 GHUTCHI Fluoride 0.06 J mg/L 0.1 0.0479 1 EPA 9056A 09/27/2022 13:13 GHUTCHI Nitrate 0.35 mg/L 0.1 0.0209 1 EPA 9056A 09/27/2022 13:13 GHUTCHI Nitrate as N 0.08 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 13:13 GHUTCHI Sulfate 9.5 mg/L 0.1 0.0428 1 EPA 9056A 09/27/2022 13:13 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.01 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 12:50 JAA5429 Barium (Ba) 0.015 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.024 J mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 0.205 mg/L 0.01 0.004 Manganese (Mn) 0.198 mg/L 0.005 0.001 Nickel (Ni) 0.001 U mg/L 0.005 0.001 Zinc (Zn) 0.004 U mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.104 U ug/L 1 Arsenic (As) 0.119 J ug/L 1 Cadmium (Cd) 0.103 J ug/L 1 Chromium (Cr) 0.317 J ug/L 1 Cobalt (Co) 0.295 J ug/L 1 Lead (Pb) 0.037 U ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.035 U ug/L 1 Thallium (TI) Low Level 0.07 J ug/L 0.2 Vanadium (V) Low Level 0.3 J ug/L B, 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 12:44 CELL106 1 SW 6010D 09/28/2022 12:44 CELL106 1 SW 6010D 09/28/2022 12:44 CELL106 1 SW 6010D 09/28/2022 12:44 CELL106 1 SW 6010D 09/28/2022 12:44 CELL106 1 SW 6010D 09/28/2022 12:44 CELL106 1 SW 6010D 09/28/2022 12:44 CELL106 1 SW 601OD 09/28/2022 12:44 CELL106 0.104 1 SW 6020B 10/04/2022 17:09 MHALL3 0.111 1 SW 6020B 10/04/2022 17:09 MHALL3 0.032 1 SW 6020B 10/04/2022 17:09 MHALL3 0.185 1 SW 6020B 10/04/2022 17:09 MHALL3 0.077 1 SW 6020B 10/04/2022 17:09 MHALL3 0.037 1 SW 6020B 10/04/2022 17:09 MHALL3 0.193 1 SW 6020B 10/04/2022 17:09 MHALL3 0.035 1 SW 6020B 10/04/2022 17:09 MHALL3 0.041 1 SW 6020B 10/04/2022 17:09 MHALL3 0.114 1 SW 6020B 10/04/2022 17:09 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 5 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV LMW-4B Sample #: 2022025316 Collection Date: 09/26/2022 11:55 AM Loc code: ASV LMW-4B Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 7.6 mg/L 0.5 0.0154 5 EPA 9056A 09/27/2022 13:28 GHUTCHI Fluoride 0.45 J mg/L 0.5 0.0479 5 EPA 9056A 09/27/2022 13:28 GHUTCHI Nitrate 2.1 mg/L 0.5 0.0209 5 EPA 9056A 09/27/2022 13:28 GHUTCHI Nitrate as N 0.47 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 13:28 GHUTCHI Sulfate 120 mg/L 5 0.0428 50 EPA 9056A 09/27/2022 13:28 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.01 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:02 JAA5429 Barium (Ba) 0.028 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.044 J mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 11.1 mg/L 0.01 0.004 Manganese (Mn) 6.14 mg/L 0.005 0.001 Nickel (Ni) 0.008 mg/L 0.005 0.001 Zinc (Zn) 0.004 U mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.133 J ug/L 1 Arsenic (As) 0.375 J ug/L 1 Cadmium (Cd) 0.032 U ug/L 1 Chromium (Cr) 0.185 U ug/L 1 Cobalt (Co) 25.8 ug/L 1 Lead (Pb) 0.037 U ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.035 U ug/L 1 Thallium (TI) Low Level 0.041 U ug/L 0.2 Vanadium (V) Low Level 0.142 J ug/L B, 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 12:57 CELL106 1 SW 6010D 09/28/2022 12:57 CELL106 1 SW 6010D 09/28/2022 12:57 CELL106 1 SW 6010D 09/28/2022 12:57 CELL106 1 SW 6010D 09/28/2022 12:57 CELL106 1 SW 6010D 09/28/2022 12:57 CELL106 1 SW 6010D 09/28/2022 12:57 CELL106 1 SW 601OD 09/28/2022 12:57 CELL106 0.104 1 SW 6020B 10/04/2022 16:28 MHALL3 0.111 1 SW 6020B 10/04/2022 16:28 MHALL3 0.032 1 SW 6020B 10/04/2022 16:28 MHALL3 0.185 1 SW 6020B 10/04/2022 16:28 MHALL3 0.077 1 SW 6020B 10/04/2022 16:28 MHALL3 0.037 1 SW 6020B 10/04/2022 16:28 MHALL3 0.193 1 SW 6020B 10/04/2022 16:28 MHALL3 0.035 1 SW 6020B 10/04/2022 16:28 MHALL3 0.041 1 SW 6020B 10/04/2022 16:28 MHALL3 0.114 1 SW 6020B 10/04/2022 16:28 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 6 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV LCS-1 Sample #: 2022025317 Collection Date: 09/26/2022 12:10 PM Loc code: ASV LCS-1 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 39 mg/L 2 0.0154 20 EPA 9056A 09/27/2022 13:43 GHUTCHI Fluoride 1.1 J mg/L 2 0.0479 20 EPA 9056A 09/27/2022 13:43 GHUTCHI Nitrate 1.2 J mg/L 2 0.0209 20 EPA 9056A 09/27/2022 13:43 GHUTCHI Nitrate as N 0.26 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 13:43 GHUTCHI Sulfate 700 mg/L 20 0.0428 200 EPA 9056A 09/27/2022 13:43 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.02 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:09 JAA5429 Barium (Ba) 0.061 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 8.88 mg/L 0.05 0.005 Copper (Cu) 0.003 J mg/L 0.005 0.001 Iron (Fe) 1.05 mg/L 0.01 0.004 Manganese (Mn) 2.88 mg/L 0.005 0.001 Nickel (Ni) 0.005 mg/L 0.005 0.001 Zinc (Zn) 0.011 mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 1.67 ug/L 1 Arsenic (As) 6.06 ug/L 1 Cadmium (Cd) 0.126 J ug/L 1 Chromium (Cr) 1.42 ug/L 1 Cobalt (Co) 1.42 ug/L 1 Lead (Pb) 1.04 ug/L 1 Selenium (Se) 46.0 ug/L 1 Silver (Ag) 0.035 U ug/L 1 Thallium (TI) Low Level 0.223 ug/L 0.2 Vanadium (V) Low Level 5.32 ug/L B1, 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:02 CELL106 1 SW 6010D 09/28/2022 13:02 CELL106 1 SW 6010D 09/28/2022 13:02 CELL106 1 SW 6010D 09/28/2022 13:02 CELL106 1 SW 6010D 09/28/2022 13:02 CELL106 1 SW 6010D 09/28/2022 13:02 CELL106 1 SW 6010D 09/28/2022 13:02 CELL106 1 SW 601OD 09/28/2022 13:02 CELL106 0.104 1 SW 6020B 10/04/2022 17:18 MHALL3 0.111 1 SW 6020B 10/04/2022 17:18 MHALL3 0.032 1 SW 6020B 10/04/2022 17:18 MHALL3 0.185 1 SW 6020B 10/04/2022 17:18 MHALL3 0.077 1 SW 6020B 10/04/2022 17:18 MHALL3 0.037 1 SW 6020B 10/04/2022 17:18 MHALL3 0.193 1 SW 6020B 10/04/2022 17:18 MHALL3 0.035 1 SW 6020B 10/04/2022 17:18 MHALL3 0.041 1 SW 6020B 10/04/2022 17:18 MHALL3 0.114 1 SW 6020B 10/04/2022 17:18 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 7 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV LMW-3B Sample #: 2022025318 Collection Date: 09/26/2022 01:00 PM Loc code: ASV LMW-3B Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 3.2 mg/L 0.2 0.0154 2 EPA 9056A 09/27/2022 13:58 GHUTCHI Fluoride 0.0479 U mg/L 0.2 0.0479 2 EPA 9056A 09/27/2022 13:58 GHUTCHI Nitrate 1.8 mg/L 0.2 0.0209 2 EPA 9056A 09/27/2022 13:58 GHUTCHI Nitrate as N 0.40 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 13:58 GHUTCHI Sulfate 260 mg/L 5 0.0428 50 EPA 9056A 09/27/2022 13:58 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.02 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:11 JAA5429 Barium (Ba) 0.077 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.012 J mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 0.181 mg/L 0.01 0.004 Manganese (Mn) 0.300 mg/L 0.005 0.001 Nickel (Ni) 0.001 U mg/L 0.005 0.001 Zinc (Zn) 0.004 U mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.104 U ug/L 1 Arsenic (As) 0.341 J ug/L 1 Cadmium (Cd) 0.032 U ug/L 1 Chromium (Cr) 0.269 J ug/L 1 Cobalt (Co) 0.384 J ug/L 1 Lead (Pb) 0.069 J ug/L 1 Selenium (Se) 0.216 J ug/L 1 Silver (Ag) 0.466 J ug/L 1 Thallium (TI) Low Level 0.041 U ug/L 0.2 Vanadium (V) Low Level 0.332 ug/L B, 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:06 CELL106 1 SW 6010D 09/28/2022 13:06 CELL106 1 SW 6010D 09/28/2022 13:06 CELL106 1 SW 6010D 09/28/2022 13:06 CELL106 1 SW 6010D 09/28/2022 13:06 CELL106 1 SW 6010D 09/28/2022 13:06 CELL106 1 SW 6010D 09/28/2022 13:06 CELL106 1 SW 601OD 09/28/2022 13:06 CELL106 0.104 1 SW 6020B 10/04/2022 17:26 MHALL3 0.111 1 SW 6020B 10/04/2022 17:26 MHALL3 0.032 1 SW 6020B 10/04/2022 17:26 MHALL3 0.185 1 SW 6020B 10/04/2022 17:26 MHALL3 0.077 1 SW 6020B 10/04/2022 17:26 MHALL3 0.037 1 SW 6020B 10/04/2022 17:26 MHALL3 0.193 1 SW 6020B 10/04/2022 17:26 MHALL3 0.035 1 SW 6020B 10/04/2022 17:26 MHALL3 0.041 1 SW 6020B 10/04/2022 17:26 MHALL3 0.114 1 SW 6020B 10/04/2022 17:26 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 8 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV LF-SW-3 Sample #: 2022025319 Collection Date: 09/26/2022 01:30 PM Loc code: ASV LF-SW-3 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 9.8 mg/L 0.5 0.0154 5 EPA 9056A 09/27/2022 14:13 GHUTCHI Fluoride 0.0479 U mg/L 0.5 0.0479 5 EPA 9056A 09/27/2022 14:13 GHUTCHI Nitrate 0.29 J mg/L 0.5 0.0209 5 EPA 9056A 09/27/2022 14:13 GHUTCHI Nitrate as N 0.07 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 14:13 GHUTCHI Sulfate 4.4 mg/L 0.5 0.0428 5 EPA 9056A 09/27/2022 14:13 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.01 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:14 JAA5429 Barium (Ba) 0.016 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.025 J mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 0.153 mg/L 0.01 0.004 Manganese (Mn) 0.017 mg/L 0.005 0.001 Nickel (Ni) 0.001 U mg/L 0.005 0.001 Zinc (Zn) 0.004 U mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.145 J ug/L 1 Arsenic (As) 0.157 J ug/L 1 Cadmium (Cd) 0.032 U ug/L 1 Chromium (Cr) 0.185 U ug/L 1 Cobalt (Co) 0.136 J ug/L 1 Lead (Pb) 0.082 J ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.035 U ug/L 1 Thallium (TI) Low Level 0.041 U ug/L 0.2 Vanadium (V) Low Level 0.351 ug/L B, 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:11 CELL106 1 SW 6010D 09/28/2022 13:11 CELL106 1 SW 6010D 09/28/2022 13:11 CELL106 1 SW 6010D 09/28/2022 13:11 CELL106 1 SW 6010D 09/28/2022 13:11 CELL106 1 SW 6010D 09/28/2022 13:11 CELL106 1 SW 6010D 09/28/2022 13:11 CELL106 1 SW 601OD 09/28/2022 13:11 CELL106 0.104 1 SW 6020B 10/04/2022 17:34 MHALL3 0.111 1 SW 6020B 10/04/2022 17:34 MHALL3 0.032 1 SW 6020B 10/04/2022 17:34 MHALL3 0.185 1 SW 6020B 10/04/2022 17:34 MHALL3 0.077 1 SW 6020B 10/04/2022 17:34 MHALL3 0.037 1 SW 6020B 10/04/2022 17:34 MHALL3 0.193 1 SW 6020B 10/04/2022 17:34 MHALL3 0.035 1 SW 6020B 10/04/2022 17:34 MHALL3 0.041 1 SW 6020B 10/04/2022 17:34 MHALL3 0.114 1 SW 6020B 10/04/2022 17:34 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 9 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV LMW-2T Sample #: 2022025320 Collection Date: 09/26/2022 02:00 PM Loc code: ASV LMW-2T Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 9.9 mg/L 0.1 0.0154 1 EPA 9056A 09/28/2022 09:07 GHUTCHI Fluoride 0.0479 U mg/L 0.1 0.0479 1 EPA 9056A 09/28/2022 09:07 GHUTCHI Nitrate 16 mg/L 0.5 0.0209 5 EPA 9056A 09/28/2022 09:07 GHUTCHI Nitrate as N 3.5 mg-N/L 0.023 0.002 1 EPA 9056A 09/28/2022 09:07 GHUTCHI Sulfate 4.6 mg/L 0.1 0.0428 1 EPA 9056A 09/28/2022 09:07 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.01 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:16 JAA5429 Barium (Ba) 0.031 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.026 J mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 0.095 mg/L 0.01 0.004 Manganese (Mn) 0.022 mg/L 0.005 0.001 Nickel (Ni) 0.001 U mg/L 0.005 0.001 Zinc (Zn) 0.004 U mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.104 U ug/L 1 Arsenic (As) 0.111 U ug/L 1 Cadmium (Cd) 0.043 J ug/L 1 Chromium (Cr) 0.185 U ug/L 1 Cobalt (Co) 0.404 J ug/L 1 Lead (Pb) 0.06 J ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.035 U ug/L 1 Thallium (TI) Low Level 0.041 U ug/L 0.2 Vanadium (V) Low Level 0.435 ug/L B, 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:15 CELL106 1 SW 6010D 09/28/2022 13:15 CELL106 1 SW 6010D 09/28/2022 13:15 CELL106 1 SW 6010D 09/28/2022 13:15 CELL106 1 SW 6010D 09/28/2022 13:15 CELL106 1 SW 6010D 09/28/2022 13:15 CELL106 1 SW 6010D 09/28/2022 13:15 CELL106 1 SW 601OD 09/28/2022 13:15 CELL106 0.104 1 SW 6020B 10/04/2022 17:43 MHALL3 0.111 1 SW 6020B 10/04/2022 17:43 MHALL3 0.032 1 SW 6020B 10/04/2022 17:43 MHALL3 0.185 1 SW 6020B 10/04/2022 17:43 MHALL3 0.077 1 SW 6020B 10/04/2022 17:43 MHALL3 0.037 1 SW 6020B 10/04/2022 17:43 MHALL3 0.193 1 SW 6020B 10/04/2022 17:43 MHALL3 0.035 1 SW 6020B 10/04/2022 17:43 MHALL3 0.041 1 SW 6020B 10/04/2022 17:43 MHALL3 0.114 1 SW 6020B 10/04/2022 17:43 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 10 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV LMW-2B Sample #: 2022025321 Collection Date: 09/26/2022 02:35 PM Loc code: ASV LMW-2B Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 7.9 mg/L 0.1 0.0154 1 EPA 9056A 09/27/2022 14:43 GHUTCHI Fluoride 0.0479 U mg/L 0.1 0.0479 1 EPA 9056A 09/27/2022 14:43 GHUTCHI Nitrate 1.4 mg/L 0.1 0.0209 1 EPA 9056A 09/27/2022 14:43 GHUTCHI Nitrate as N 0.31 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 14:43 GHUTCHI Sulfate 2.9 mg/L 0.1 0.0428 1 EPA 9056A 09/27/2022 14:43 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.01 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:19 JAA5429 Barium (Ba) 0.046 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.012 J mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 0.044 mg/L 0.01 0.004 Manganese (Mn) 0.012 mg/L 0.005 0.001 Nickel (Ni) 0.001 U mg/L 0.005 0.001 Zinc (Zn) 0.004 U mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.104 U ug/L 1 Arsenic (As) 0.111 U ug/L 1 Cadmium (Cd) 0.032 U ug/L 1 Chromium (Cr) 0.364 J ug/L 1 Cobalt (Co) 0.286 J ug/L 1 Lead (Pb) 0.093 J ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.036 J ug/L 1 Thallium (TI) Low Level 0.041 U ug/L 0.2 Vanadium (V) Low Level 0.743 ug/L B, 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:20 CELL106 1 SW 6010D 09/28/2022 13:20 CELL106 1 SW 6010D 09/28/2022 13:20 CELL106 1 SW 6010D 09/28/2022 13:20 CELL106 1 SW 6010D 09/28/2022 13:20 CELL106 1 SW 6010D 09/28/2022 13:20 CELL106 1 SW 6010D 09/28/2022 13:20 CELL106 1 SW 601OD 09/28/2022 13:20 CELL106 0.104 1 SW 6020B 10/04/2022 17:51 MHALL3 0.111 1 SW 6020B 10/04/2022 17:51 MHALL3 0.032 1 SW 6020B 10/04/2022 17:51 MHALL3 0.185 1 SW 6020B 10/04/2022 17:51 MHALL3 0.077 1 SW 6020B 10/04/2022 17:51 MHALL3 0.037 1 SW 6020B 10/04/2022 17:51 MHALL3 0.193 1 SW 6020B 10/04/2022 17:51 MHALL3 0.035 1 SW 6020B 10/04/2022 17:51 MHALL3 0.041 1 SW 6020B 10/04/2022 17:51 MHALL3 0.114 1 SW 6020B 10/04/2022 17:51 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 11 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV LMW-lS Sample #: 2022025322 Collection Date: 09/26/2022 03:15 PM Loc code: ASV LMW-lS Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 6.2 mg/L 0.1 0.0154 1 EPA 9056A 09/27/2022 12:27 GHUTCHI Fluoride 0.0479 U mg/L 0.1 0.0479 1 EPA 9056A 09/27/2022 12:27 GHUTCHI Nitrate 2.7 mg/L 0.1 0.0209 1 EPA 9056A 09/27/2022 12:27 GHUTCHI Nitrate as N 0.62 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 12:27 GHUTCHI Sulfate 0.27 mg/L 0.1 0.0428 1 EPA 9056A 09/27/2022 12:27 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.01 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:21 JAA5429 Barium (Ba) 0.041 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.005 U mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 0.236 mg/L 0.01 0.004 Manganese (Mn) 0.071 mg/L 0.005 0.001 Nickel (Ni) 0.002 J mg/L 0.005 0.001 Zinc (Zn) 0.006 mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.104 U ug/L 1 Arsenic (As) 0.122 J ug/L 1 Cadmium (Cd) 0.032 U ug/L 1 Chromium (Cr) 0.769 J ug/L 1 Cobalt (Co) 0.674 J ug/L 1 Lead (Pb) 0.06 J ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.035 U ug/L 1 Thallium (TI) Low Level 0.041 U ug/L 0.2 Vanadium (V) Low Level 0.524 ug/L B, 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:24 CELL106 1 SW 6010D 09/28/2022 13:24 CELL106 1 SW 6010D 09/28/2022 13:24 CELL106 1 SW 6010D 09/28/2022 13:24 CELL106 1 SW 6010D 09/28/2022 13:24 CELL106 1 SW 6010D 09/28/2022 13:24 CELL106 1 SW 6010D 09/28/2022 13:24 CELL106 1 SW 601OD 09/28/2022 13:24 CELL106 0.104 1 SW 6020B 10/04/2022 18:00 MHALL3 0.111 1 SW 6020B 10/04/2022 18:00 MHALL3 0.032 1 SW 6020B 10/04/2022 18:00 MHALL3 0.185 1 SW 6020B 10/04/2022 18:00 MHALL3 0.077 1 SW 6020B 10/04/2022 18:00 MHALL3 0.037 1 SW 6020B 10/04/2022 18:00 MHALL3 0.193 1 SW 6020B 10/04/2022 18:00 MHALL3 0.035 1 SW 6020B 10/04/2022 18:00 MHALL3 0.041 1 SW 6020B 10/04/2022 18:00 MHALL3 0.114 1 SW 6020B 10/04/2022 18:00 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 12 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV LMW-1 B Sample #: 2022025323 Collection Date: 09/26/2022 03:40 PM Loc code: ASV LMW-1 B Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 8.1 mg/L 0.1 0.0154 1 EPA 9056A 09/27/2022 15:14 GHUTCHI Fluoride 0.0479 U mg/L 0.1 0.0479 1 EPA 9056A 09/27/2022 15:14 GHUTCHI Nitrate 0.21 mg/L 0.1 0.0209 1 EPA 9056A 09/27/2022 15:14 GHUTCHI Nitrate as N 0.05 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 15:14 GHUTCHI Sulfate 0.33 mg/L 0.1 0.0428 1 EPA 9056A 09/27/2022 15:14 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.05 ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:24 JAA5429 Barium (Ba) 0.027 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.005 U mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 0.039 mg/L 0.01 0.004 Manganese (Mn) 0.003 J mg/L 0.005 0.001 Nickel (Ni) 0.001 U mg/L 0.005 0.001 Zinc (Zn) 0.004 U mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.104 U ug/L 1 Arsenic (As) 0.117 J ug/L 1 Cadmium (Cd) 0.032 U ug/L 1 Chromium (Cr) 0.238 J ug/L 1 Cobalt (Co) 0.077 U ug/L 1 Lead (Pb) 0.037 U ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.035 U ug/L 1 Thallium (TI) Low Level 0.05 J ug/L 0.2 Vanadium (V) Low Level 0.627 ug/L B 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:29 CELL106 1 SW 6010D 09/28/2022 13:29 CELL106 1 SW 6010D 09/28/2022 13:29 CELL106 1 SW 6010D 09/28/2022 13:29 CELL106 1 SW 6010D 09/28/2022 13:29 CELL106 1 SW 6010D 09/28/2022 13:29 CELL106 1 SW 6010D 09/28/2022 13:29 CELL106 1 SW 601OD 09/28/2022 13:29 CELL106 0.104 1 SW 6020B 10/04/2022 18:33 MHALL3 0.111 1 SW 6020B 10/04/2022 18:33 MHALL3 0.032 1 SW 6020B 10/04/2022 18:33 MHALL3 0.185 1 SW 6020B 10/04/2022 18:33 MHALL3 0.077 1 SW 6020B 10/04/2022 18:33 MHALL3 0.037 1 SW 6020B 10/04/2022 18:33 MHALL3 0.193 1 SW 6020B 10/04/2022 18:33 MHALL3 0.035 1 SW 6020B 10/04/2022 18:33 MHALL3 0.041 1 SW 6020B 10/04/2022 18:33 MHALL3 0.114 1 SW 6020B 10/04/2022 18:33 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 13 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV CB-9BR Sample #: 2022025324 Collection Date: 09/26/2022 02:49 PM Loc code: ASV CB-9BR Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 7.7 mg/L 0.1 0.0154 1 EPA 9056A 09/27/2022 15:29 GHUTCHI Fluoride 0.05 J mg/L 0.1 0.0479 1 EPA 9056A 09/27/2022 15:29 GHUTCHI Nitrate 0.11 mg/L 0.1 0.0209 1 EPA 9056A 09/27/2022 15:29 GHUTCHI Nitrate as N 0.02 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 15:29 GHUTCHI Sulfate 1.7 mg/L 0.1 0.0428 1 EPA 9056A 09/27/2022 15:29 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.01 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:26 JAA5429 Barium (Ba) 0.025 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.005 U mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 0.050 mg/L 0.01 0.004 Manganese (Mn) 0.051 mg/L 0.005 0.001 Nickel (Ni) 0.001 U mg/L 0.005 0.001 Zinc (Zn) 0.004 U mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.104 U ug/L 1 Arsenic (As) 0.111 U ug/L 1 Cadmium (Cd) 0.048 J ug/L 1 Chromium (Cr) 0.185 U ug/L 1 Cobalt (Co) 0.084 J ug/L 1 Lead (Pb) 0.055 J ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.048 J ug/L 1 Thallium (TI) Low Level 0.041 U ug/L 0.2 Vanadium (V) Low Level 0.277 J ug/L B 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:33 CELL106 1 SW 6010D 09/28/2022 13:33 CELL106 1 SW 6010D 09/28/2022 13:33 CELL106 1 SW 6010D 09/28/2022 13:33 CELL106 1 SW 6010D 09/28/2022 13:33 CELL106 1 SW 6010D 09/28/2022 13:33 CELL106 1 SW 6010D 09/28/2022 13:33 CELL106 1 SW 601OD 09/28/2022 13:33 CELL106 0.104 1 SW 6020B 10/04/2022 18:41 MHALL3 0.111 1 SW 6020B 10/04/2022 18:41 MHALL3 0.032 1 SW 6020B 10/04/2022 18:41 MHALL3 0.185 1 SW 6020B 10/04/2022 18:41 MHALL3 0.077 1 SW 6020B 10/04/2022 18:41 MHALL3 0.037 1 SW 6020B 10/04/2022 18:41 MHALL3 0.193 1 SW 6020B 10/04/2022 18:41 MHALL3 0.035 1 SW 6020B 10/04/2022 18:41 MHALL3 0.041 1 SW 6020B 10/04/2022 18:41 MHALL3 0.114 1 SW 6020B 10/04/2022 18:41 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 14 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV CB-9SL Sample #: 2022025325 Collection Date: 09/26/2022 03:22 PM Loc code: ASV CB-9SL Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 7.8 mg/L 0.1 0.0154 1 EPA 9056A 09/27/2022 16:29 GHUTCHI Fluoride 0.0479 U mg/L 0.1 0.0479 1 EPA 9056A 09/27/2022 16:29 GHUTCHI Nitrate 0.94 mg/L 0.1 0.0209 1 EPA 9056A 09/27/2022 16:29 GHUTCHI Nitrate as N 0.21 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 16:29 GHUTCHI Sulfate 0.26 mg/L 0.1 0.0428 1 EPA 9056A 09/27/2022 16:29 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.01 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:29 JAA5429 Barium (Ba) 0.044 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.005 U mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 0.013 mg/L 0.01 0.004 Manganese (Mn) 0.002 J mg/L 0.005 0.001 Nickel (Ni) 0.001 U mg/L 0.005 0.001 Zinc (Zn) 0.008 mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.135 J ug/L 1 Arsenic (As) 0.111 U ug/L 1 Cadmium (Cd) 0.032 U ug/L 1 Chromium (Cr) 0.49 J ug/L 1 Cobalt (Co) 0.077 U ug/L 1 Lead (Pb) 0.045 J ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.246 J ug/L 1 Thallium (TI) Low Level 0.041 U ug/L 0.2 Vanadium (V) Low Level 0.318 ug/L B 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:46 CELL106 1 SW 6010D 09/28/2022 13:46 CELL106 1 SW 6010D 09/28/2022 13:46 CELL106 1 SW 6010D 09/28/2022 13:46 CELL106 1 SW 6010D 09/28/2022 13:46 CELL106 1 SW 6010D 09/28/2022 13:46 CELL106 1 SW 6010D 09/28/2022 13:46 CELL106 1 SW 601OD 09/28/2022 13:46 CELL106 0.104 1 SW 6020B 10/04/2022 18:50 MHALL3 0.111 1 SW 6020B 10/04/2022 18:50 MHALL3 0.032 1 SW 6020B 10/04/2022 18:50 MHALL3 0.185 1 SW 6020B 10/04/2022 18:50 MHALL3 0.077 1 SW 6020B 10/04/2022 18:50 MHALL3 0.037 1 SW 6020B 10/04/2022 18:50 MHALL3 0.193 1 SW 6020B 10/04/2022 18:50 MHALL3 0.035 1 SW 6020B 10/04/2022 18:50 MHALL3 0.041 1 SW 6020B 10/04/2022 18:50 MHALL3 0.114 1 SW 6020B 10/04/2022 18:50 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 15 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV CB-9 Sample #: 2022025326 Collection Date: 09/26/2022 03:49 PM Loc code: ASV-CB-9 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 6.5 mg/L 0.1 0.0154 1 EPA 9056A 09/27/2022 16:44 GHUTCHI Fluoride 0.0479 U mg/L 0.1 0.0479 1 EPA 9056A 09/27/2022 16:44 GHUTCHI Nitrate 0.98 mg/L 0.1 0.0209 1 EPA 9056A 09/27/2022 16:44 GHUTCHI Nitrate as N 0.22 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 16:44 GHUTCHI Sulfate 0.12 mg/L 0.1 0.0428 1 EPA 9056A 09/27/2022 16:44 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.02 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:36 JAA5429 Barium (Ba) 0.027 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.006 J mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 0.038 mg/L 0.01 0.004 Manganese (Mn) 0.031 mg/L 0.005 0.001 Nickel (Ni) 0.001 U mg/L 0.005 0.001 Zinc (Zn) 0.009 mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.104 U ug/L 1 Arsenic (As) 0.15 J ug/L 1 Cadmium (Cd) 0.032 U ug/L 1 Chromium (Cr) 0.275 J ug/L 1 Cobalt (Co) 0.9 J ug/L 1 Lead (Pb) 0.037 U ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.385 J ug/L 1 Thallium (TI) Low Level 0.08 J ug/L 0.2 Vanadium (V) Low Level 0.261 J ug/L B 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:51 CELL106 1 SW 6010D 09/28/2022 13:51 CELL106 1 SW 6010D 09/28/2022 13:51 CELL106 1 SW 6010D 09/28/2022 13:51 CELL106 1 SW 6010D 09/28/2022 13:51 CELL106 1 SW 6010D 09/28/2022 13:51 CELL106 1 SW 6010D 09/28/2022 13:51 CELL106 1 SW 601OD 09/28/2022 13:51 CELL106 0.104 1 SW 6020B 10/04/2022 18:58 MHALL3 0.111 1 SW 6020B 10/04/2022 18:58 MHALL3 0.032 1 SW 6020B 10/04/2022 18:58 MHALL3 0.185 1 SW 6020B 10/04/2022 18:58 MHALL3 0.077 1 SW 6020B 10/04/2022 18:58 MHALL3 0.037 1 SW 6020B 10/04/2022 18:58 MHALL3 0.193 1 SW 6020B 10/04/2022 18:58 MHALL3 0.035 1 SW 6020B 10/04/2022 18:58 MHALL3 0.041 1 SW 6020B 10/04/2022 18:58 MHALL3 0.114 1 SW 6020B 10/04/2022 18:58 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 16 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV_FD-20220926-1 Duplicate Sample #: 2022025327 Collection Date: 09/26/2022 Loc code: ASV FD Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 7.7 mg/L 0.5 0.0154 5 EPA 9056A 09/27/2022 17:14 GHUTCHI Fluoride 0.46 J mg/L 0.5 0.0479 5 EPA 9056A 09/27/2022 17:14 GHUTCHI Nitrate 0.21 J mg/L 0.5 0.0209 5 EPA 9056A 09/27/2022 17:14 GHUTCHI Nitrate as N 0.05 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 17:14 GHUTCHI Sulfate 120 mg/L 5 0.0428 50 EPA 9056A 09/27/2022 17:14 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.01 J ug/L 0.05 TOTAL RECOVERABLE METALS BY ICP - Q22090328 0.01 1 EPA 7470A 10/04/2022 13:43 JAA5429 Barium (Ba) 0.027 mg/L 0.005 0.002 Beryllium (Be) 0.002 U mg/L 0.005 0.002 Boron (B) 0.038 J mg/L 0.05 0.005 Copper (Cu) 0.001 U mg/L 0.005 0.001 Iron (Fe) 10.6 mg/L 0.01 0.004 Manganese (Mn) 5.89 mg/L 0.005 0.001 Nickel (Ni) 0.007 mg/L 0.005 0.001 Zinc (Zn) 0.004 U mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.104 U ug/L 1 Arsenic (As) 0.326 J ug/L 1 Cadmium (Cd) 0.032 U ug/L 1 Chromium (Cr) 0.185 U ug/L 1 Cobalt (Co) 26.2 ug/L 1 Lead (Pb) 0.037 U ug/L 1 Selenium (Se) 0.193 U ug/L 1 Silver (Ag) 0.097 J ug/L 1 Thallium (TI) Low Level 0.041 U ug/L 0.2 Vanadium (V) Low Level 0.114 U ug/L B 0.3 TOTAL DISSOLVED SOLIDS - (Analvsis Performed by Pace Laboratories) 1 SW 6010D 09/28/2022 13:55 CELL106 1 SW 6010D 09/28/2022 13:55 CELL106 1 SW 6010D 09/28/2022 13:55 CELL106 1 SW 6010D 09/28/2022 13:55 CELL106 1 SW 6010D 09/28/2022 13:55 CELL106 1 SW 6010D 09/28/2022 13:55 CELL106 1 SW 6010D 09/28/2022 13:55 CELL106 1 SW 601OD 09/28/2022 13:55 CELL106 0.104 1 SW 6020B 10/04/2022 19:07 MHALL3 0.111 1 SW 6020B 10/04/2022 19:07 MHALL3 0.032 1 SW 6020B 10/04/2022 19:07 MHALL3 0.185 1 SW 6020B 10/04/2022 19:07 MHALL3 0.077 1 SW 6020B 10/04/2022 19:07 MHALL3 0.037 1 SW 6020B 10/04/2022 19:07 MHALL3 0.193 1 SW 6020B 10/04/2022 19:07 MHALL3 0.035 1 SW 6020B 10/04/2022 19:07 MHALL3 0.041 1 SW 6020B 10/04/2022 19:07 MHALL3 0.114 1 SW 6020B 10/04/2022 19:07 MHALL3 Vendor Parameter Complete Vendor Method V_PACE Certificate of Laboratory Analysis Page 17 of 53 This report shall not be reproduced, except in full. Order # J22090472 Site: ASV FB-20220926-1400 Field Blank Sample #: 2022025328 Collection Date: 09/26/2022 02:00 PM Loc code: ASV QA Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q22090338 Chloride 0.0154 U mg/L 0.1 0.0154 1 EPA 9056A 09/27/2022 17:29 GHUTCHI Fluoride 0.0479 U mg/L 0.1 0.0479 1 EPA 9056A 09/27/2022 17:29 GHUTCHI Nitrate 0.0209 U mg/L 0.1 0.0209 1 EPA 9056A 09/27/2022 17:29 GHUTCHI Nitrate as N 0.002 U mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2022 17:29 GHUTCHI Sulfate 0.0428 U mg/L 0.1 0.0428 1 EPA 9056A 09/27/2022 17:29 GHUTCHI MERCURY (COLD VAPOR) IN WATER - Q22100044 Mercury (Hg) 0.01 J ug/L 0.05 0.01 1 EPA 7470A 10/04/2022 13:45 JAA5429 TOTAL RECOVERABLE METALS BY ICP - Q22090328 Barium (Ba) 0.002 U mg/L 0.005 0.002 1 SW 6010D 09/28/2022 14:00 CELL106 Beryllium (Be) 0.002 U mg/L 0.005 0.002 1 SW 6010D 09/28/2022 14:00 CELL106 Boron (B) 0.005 U mg/L 0.05 0.005 1 SW 6010D 09/28/2022 14:00 CELL106 Copper (Cu) 0.001 U mg/L 0.005 0.001 1 SW 6010D 09/28/2022 14:00 CELL106 Iron (Fe) 0.012 mg/L 0.01 0.004 1 SW 6010D 09/28/2022 14:00 CELL106 Manganese (Mn) 0.001 U mg/L 0.005 0.001 1 SW 6010D 09/28/2022 14:00 CELL106 Nickel (Ni) 0.001 U mg/L 0.005 0.001 1 SW 6010D 09/28/2022 14:00 CELL106 Zinc (Zn) 0.004 U mg/L 0.005 0.004 1 SW 601 OD 09/28/2022 14:00 CELL106 TOTAL RECOVERABLE METALS BY ICP-MS - Q22090330 Antimony (Sb) 0.104 U ug/L 1 0.104 1 SW 6020B 10/04/2022 19:15 MHALL3 Arsenic (As) 0.111 U ug/L 1 0.111 1 SW 6020B 10/04/2022 19:15 MHALL3 Cadmium (Cd) 0.032 U ug/L 1 0.032 1 SW 6020B 10/04/2022 19:15 MHALL3 Chromium (Cr) 0.185 U ug/L 1 0.185 1 SW 6020B 10/04/2022 19:15 MHALL3 Cobalt (Co) 0.077 U ug/L 1 0.077 1 SW 6020B 10/04/2022 19:15 MHALL3 Lead (Pb) 0.037 U ug/L 1 0.037 1 SW 6020B 10/04/2022 19:15 MHALL3 Selenium (Se) 0.193 U ug/L 1 0.193 1 SW 6020B 10/04/2022 19:15 MHALL3 Silver (Ag) 0.035 U ug/L 1 0.035 1 SW 6020B 10/04/2022 19:15 MHALL3 Thallium (TI) Low Level 0.041 U ug/L 0.2 0.041 1 SW 6020B 10/04/2022 19:15 MHALL3 Vanadium (V) Low Level 0.18 J ug/L B 0.3 0.114 1 SW 6020B 10/04/2022 19:15 MHALL3 Qualifiers: B Target analyte detected in Method/Prep Blank at or above the reporting limit. Target analyte concentration in sample is less than 10X the concentration in the Method/Prep Blank. Analyte concentration in sample could be due to contamination. B1 Target analyte was detected in Method/Prep Blank at or above the reporting limit. Target analyte concentration in sample is below the reporting limit or greater than 10X the concentration of the target analyte detected in the Method/Prep Blank. Analyte concentration in sample is not affected by contamination. J Analyte detected above the MDL, but below the RL. Analyte concentration should be considered an estimate. Certificate of Laboratory Analysis Page 18 of 53 This report shall not be reproduced, except in full. Order # J22090472 Level II QC Summary Q22090338 Dionex INORGANIC IONS BY IC Blank # 1 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Chloride 0 0 mg/L 1 0.0154 0.1 < MDL Fluoride 0 0 mg/L 1 0.0479 0.1 < MDL Nitrate 0 0 mg/L 1 0.0209 0.1 < MDL Sulfate 0 0 mg/L 1 0.0428 0.1 < MDL LCS # 1 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Chloride 1.96 1.96 mg/L 1 0.0154 5 98 80 120 Fluoride 2 2 mg/L 1 0.0479 5 100 80 120 Nitrate 1.98 1.98 mg/L 1 0.0209 5 98.8 80 120 Sulfate 2.03 2.03 mg/L 1 0.0428 5 101 80 120 MS # 1 Parent Sample: J22090472 -- 2022025322 Parameter Measured Final Units Dil MDL alAke % Recovery LCL UCL Qualifier Chloride 8.15 8.15 mg/L 1 0.0154 2 96.7 80 120 Fluoride 2.04 2.04 mg/L 1 0.0479 2 100 80 120 Nitrate 4.77 4.77 mg/L 1 0.0209 2 102 80 120 Sulfate 2.29 2.29 mg/L 1 0.0428 2 101 80 120 MSD # 1 Parent Sample: J22090472 -- 2022025322 Parameter Measured Final Units Dil MDL S ike % Recovery LCL UCL RPD Qualifier Chloride 8.2 8.2 mg/L 1 0.0154 2 99.5 80 120 2.91 Fluoride 2.1 2.1 mg/L 1 0.0479 2 103 80 120 2.65 Nitrate 4.82 4.82 mg/L 1 0.0209 2 105 80 120 2.62 Sulfate 2.37 2.37 mg/L 1 0.0428 2 105 80 120 3.54 Certificate of Laboratory Analysis Page 19 of 53 This report shall not be reproduced, except in full. Order # J22090472 Level II QC Summary Q22100044 HG 7470 MERCURY (COLD VAPOR) IN WATER Blank # 1 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.009 0.009 ug/L 1 0.01 0.05 < MDL Blank # 2 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.01 0.01 ug/L 1 0.01 0.05 = MDL Blank # 3 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.011 0.011 ug/L 1 0.01 0.05 > MDL Blank # 4 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.012 0.012 ug/L 1 0.01 0.05 > MDL Blank # 5 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.012 0.012 ug/L 1 0.01 0.05 > MDL Blank # 6 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.023 0.023 ug/L 1 0.01 0.05 > MDL Blank # 7 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.024 0.024 ug/L 1 0.01 0.05 > MDL Blank # 8 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.022 0.022 ug/L 1 0.01 0.05 > MDL LCS # 1 Parameter Measured Final Units Dil MDL alAke % Recovery LCL UCL Qualifier Mercury (Hg) 2.02 2.02 ug/L 1 0.01 2 101 85 115 LCS # 2 Parameter Measured Final Units Dil MDL S ike % Recovery LCL UCL Qualifier Mercury (Hg) 2.01 2.01 ug/L 1 0.01 2 101 85 115 LCS # 3 Parameter Measured Final Units Dil MDL S ike % Recovery LCL UCL Qualifier Mercury (Hg) 2.01 2.01 ug/L 1 0.01 2 100 85 115 Certificate of Laboratory Analysis Page 20 of 53 This report shall not be reproduced, except in full. Order # J22090472 Level II QC Summary 022100044 HG 7470 MERCURY (COLD VAPOR) IN WATER LCS # 4 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 2.02 2.02 ug/L 1 0.01 2 101 85 115 MS # 1 Parent Sample: J22080352 -- 2022021555 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 0.997 0.997 ug/L 1 0.01 1 98.5 75 125 MSD # 1 Parent Sample: J22080352 -- 2022021555 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 1 1 ug/L 1 0.01 1 99.3 75 125 0.809 MS # 2 Parent Sample: J22080352 -- 2022021566 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 1.02 1.02 ug/L 1 0.01 1 101 75 125 MSD # 2 Parent Sample: J22080352 -- 2022021566 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 1.02 1.02 ug/L 1 0.01 1 101 75 125 0.495 MS # 3 Parent Sample: J22090389 -- 2022024811 Parameter Measured Final Units Di MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 1.06 1.06 ug/L 1 0.01 1 105 75 125 MSD # 3 Parent Sample: J22090389 -- 2022024811 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 1.02 1.02 ug/L 1 0.01 1 100 75 125 4.2 MS # 4 Parent Sample: J22090389 -- 2022024821 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 1.01 1.01 ug/L 1 0.01 1 99.9 75 125 MSD # 4 Parent Sample: J22090389 -- 2022024821 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 0.996 0.996 ug/L 1 0.01 1 98.2 75 125 1.72 MS # 5 Parent Sample: J22090472 -- 2022025316 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 0.969 0.969 ug/L 1 0.01 1 95.8 75 125 MSD # 5 Parent Sample: J22090472 -- 2022025316 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 0.966 0.966 ug/L 1 0.01 1 95.5 75 125 0.314 Certificate of Laboratory Analysis Page 21 of 53 This report shall not be reproduced, except in full. Order # J22090472 Level II QC Summary Q22100044 HG 7470 MERCURY (COLD VAPOR) IN WATER MS # 6 Parent Sample: J22090472 -- 2022025326 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 1.02 1.02 ug/L 1 0.01 1 101 75 125 MSD # 6 Parent Sample: J22090472 -- 2022025326 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 1.03 1.03 ug/L 1 0.01 1 101 75 125 0.892 MS # 7 Parent Sample: J22090473 -- 2022025336 Parameter Measured Final Units Dil MDL 52ike % Recovery LCL UCL Qualifier Mercury (Hg) 1 1 ug/L 1 0.01 1 99.4 75 125 MSD # 7 Parent Sample: J22090473 -- 2022025336 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 1.01 1.01 ug/L 1 0.01 1 99.6 75 125 0.201 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J22090472 Level II QC Summary Q22090328 ICP_TRM TOTAL RECOVERABLE METALS BY ICP Blank # 1 Parameter Measured Final Units Dil MDL RDL Relative Concentration Barium (Ba) -0.000257 -0.000257 mg/L 1 0.002 0.005 < MDL Beryllium (Be) 0 mg/L 1 0.002 0.005 < MDL Boron (B) 0.00165 0.00165 mg/L 1 0.005 0.05 < MDL Copper (Cu) 0.000046 0.000046 mg/L 1 0.001 0.005 < MDL Iron (Fe) 0.00266 0.00266 mg/L 1 0.004 0.01 < MDL Manganese (Mn) 0.000053 0.000053 mg/L 1 0.001 0.005 < MDL Nickel (Ni) -0.000388 -0.000388 mg/L 1 0.001 0.005 < MDL Zinc (Zn) 0.000255 0.000255 mg/L 1 0.004 0.005 < MDL LCS # 1 Page 22 of 53 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Barium (Ba) 5.15 5.15 mg/L 1 0.002 5 103 80 120 Beryllium (Be) 4.87 mg/L 1 0.002 5 97.3 80 120 Boron (B) 4.76 4.76 mg/L 1 0.005 5 95.2 80 120 Copper (Cu) 4.81 4.81 mg/L 1 0.001 5 96.1 80 120 Iron (Fe) 4.69 4.69 mg/L 1 0.004 5 93.9 80 120 Manganese (Mn) 4.83 4.83 mg/L 1 0.001 5 96.5 80 120 Nickel (Ni) 4.63 4.63 mg/L 1 0.001 5 92.6 80 120 Zinc (Zn) 4.85 4.85 mg/L 1 0.004 5 97 80 120 MS # 1 Parent Sample: J22090472 -- 2022025315 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Barium (Ba) 5.27 5.27 mg/L 1 0.002 5 105 75 125 Beryllium (Be) 5.05 mg/L 1 0.002 5 101 75 125 Boron (B) 5.01 5.01 mg/L 1 0.005 5 99.8 75 125 Copper (Cu) 5 5 mg/L 1 0.001 5 99.9 75 125 Iron (Fe) 5.17 5.17 mg/L 1 0.004 5 99.2 75 125 Manganese (Mn) 5.21 5.21 mg/L 1 0.001 5 100 75 125 Nickel (Ni) 4.95 4.95 mg/L 1 0.001 5 98.9 75 125 Zinc (Zn) 5.04 5.04 mg/L 1 0.004 5 101 75 125 MSD # 1 Parent Sample: J22090472 -- 2022025315 Parameter Measured Final Units Dil MDL S ike % Recovery LCL UCL RPD Barium (Ba) 5.25 5.25 mg/L 1 0.002 5 105 75 125 0.38 Beryllium (Be) 4.93 mg/L 1 0.002 5 98.6 75 125 2.39 Boron (B) 4.88 4.88 mg/L 1 0.005 5 97 75 125 2.77 Copper (Cu) 4.9 4.9 mg/L 1 0.001 5 98 75 125 2 Iron (Fe) 4.99 4.99 mg/L 1 0.004 5 95.7 75 125 3.43 Manganese (Mn) 5.11 5.11 mg/L 1 0.001 5 98.2 75 125 2.03 Nickel (Ni) 4.73 4.73 mg/L 1 0.001 5 94.6 75 125 4.42 Qualifier Qualifier Qualifier Qualifier Certificate of Laboratory Analysis Page 23 of 53 This report shall not be reproduced, except in full. Order # J22090472 Level II QC Summary Q22090328 ICP_TRM TOTAL RECOVERABLE METALS BY ICP MSD # 1 Parent Sample: J22090472 -- 2022025315 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Zinc (Zn) 4.92 4.92 mg/L 1 0.004 5 98.3 75 125 2.43 Certificate of Laboratory Analysis Page 24 of 53 This report shall not be reproduced, except in full. Order # J22090472 Level II QC Summary Q22090330 IMS_TRM TOTAL RECOVERABLE METALS BY ICP-MS Blank # 1 Parameter Measured Final Units Dil MDL RDL Relative Concentration Antimony (Sb) 0.12 0.12 ug/L 1 0.104 1 > MDL Arsenic (As) 0.099 0.099 ug/L 1 0.111 1 < MDL Cadmium (Cd) 0.027 0.027 ug/L 1 0.032 1 < MDL Chromium (Cr) 0.034 0.034 ug/L 1 0.185 1 < MDL Cobalt (Co) 0.041 0.041 ug/L 1 0.077 1 < MDL Lead (Pb) 0.036 0.036 ug/L 1 0.037 1 < MDL Selenium (Se) 0.04 0.04 ug/L 1 0.193 1 < MDL Silver (Ag) 0.019 0.019 ug/L 1 0.035 1 < MDL Thallium (TI) Low Level 0.022 0.022 ug/L 1 0.041 0.2 < MDL Vanadium (V) Low Level 0.374 0.374 ug/L 1 0.114 0.3 > MDL LCS # 1 Parameter Measured Final Units Dil MDL S ike % Recovery LCL UCL Antimony (Sb) 51.8 51.8 ug/L 1 0.104 50 104 80 120 Arsenic (As) 52.2 52.2 ug/L 1 0.111 50 104 80 120 Cadmium (Cd) 50.8 50.8 ug/L 1 0.032 50 102 80 120 Chromium (Cr) 50.6 50.6 ug/L 1 0.185 50 101 80 120 Cobalt (Co) 52.1 52.1 ug/L 1 0.077 50 104 80 120 Lead (Pb) 51.3 51.3 ug/L 1 0.037 50 103 80 120 Selenium (Se) 48.7 48.7 ug/L 1 0.193 50 97.5 80 120 Silver (Ag) 51.6 51.6 ug/L 1 0.035 50 103 80 120 Thallium (TI) Low Level 48.7 48.7 ug/L 1 0.041 50 97.3 80 120 Vanadium (V) Low Level 50.7 50.7 ug/L 1 0.114 50 101 80 120 MS # 1 Parent Sample: J22090472 -- 2022025316 Parameter Measured Final Units Dil MDL S ike % Recovery LCL UCL Antimony (Sb) 51.9 51.9 ug/L 1 0.104 50 104 75 125 Arsenic (As) 52 52 ug/L 1 0.111 50 103 75 125 Cadmium (Cd) 50.4 50.4 ug/L 1 0.032 50 101 75 125 Chromium (Cr) 51.3 51.3 ug/L 1 0.185 50 103 75 125 Cobalt (Co) 76.6 76.6 ug/L 1 0.077 50 102 75 125 Lead (Pb) 51.2 51.2 ug/L 1 0.037 50 102 75 125 Selenium (Se) 48.9 48.9 ug/L 1 0.193 50 97.8 75 125 Silver (Ag) 51.5 51.5 ug/L 1 0.035 50 103 75 125 Thallium (TI) Low Level 47.2 47.2 ug/L 1 0.041 50 94.4 75 125 Vanadium (V) Low Level 52.1 52.1 ug/L 1 0.114 50 104 75 125 MSD # 1 Parent Sample: J22090472 -- 2022025316 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Antimony (Sb) 53.2 53.2 ug/L 1 0.104 50 106 75 125 2.54 Qualifier B,B1 Qualifier Qualifier Qualifier Certificate of Laboratory Analysis Page 25 of 53 This report shall not be reproduced, except in full. Order # J22090472 Level II QC Summary Q22090330 IMS_TRM TOTAL RECOVERABLE METALS BY ICP-MS MSD # 1 Parent Sample: J22090472 -- 2022025316 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Arsenic (As) 51.4 51.4 ug/L 1 0.111 50 102 75 125 1.23 Cadmium (Cd) 50.8 50.8 ug/L 1 0.032 50 102 75 125 0.915 Chromium (Cr) 51.8 51.8 ug/L 1 0.185 50 104 75 125 0.98 Cobalt (Co) 76.8 76.8 ug/L 1 0.077 50 102 75 125 0.289 Lead (Pb) 51.4 51.4 ug/L 1 0.037 50 103 75 125 0.39 Selenium (Se) 49.1 49.1 ug/L 1 0.193 50 98.2 75 125 0.465 Silver (Ag) 50.9 50.9 ug/L 1 0.035 50 102 75 125 1.25 Thallium (TI) Low Level 48.2 48.2 ug/L 1 0.041 50 96.4 75 125 2.06 Vanadium (V) Low Level 53 53 ug/L 1 0.114 50 106 75 125 1.64 Qualifiers: B Target analyte detected in Method/Prep Blank at or above the reporting limit. Target analyte concentration in sample is less than 10X the concentration in the Method/Prep Blank. Analyte concentration in sample could be due to contamination. B1 Target analyte was detected in Method/Prep Blank at or above the reporting limit. Target analyte concentration in sample is below the reporting limit or greater than 10X the concentration of the target analyte detected in the Method/Prep Blank. Analyte concentration in sample is not affected by contamination. Qualifier leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8� ��-6 f&Ie. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 October 04, 2022 Program Manager Duke Energy 13339 Hagers Ferry Road Bldg.7405 MG30A2 Huntersville, NC 28078 RE: Project: J22090472 ASV LF Pace Project No.: 92627920 Dear Program Manager: Enclosed are the analytical results for sample(s) received by the laboratory on September 27, 2022. The results relate only to the samples included in this report. Results reported herein conform to the applicable TNI/NELAC Standards and the laboratory's Quality Manual, where applicable, unless otherwise noted in the body of the report. The test results provided in this final report were generated by each of the following laboratories within the Pace Network: • Pace Analytical Services - Asheville If you have any questions concerning this report, please feel free to contact me. Sincerely, %D'a6- Nicole D'Oleo nicole.d'oleo@pacelabs.com (704)875-9092 Project Manager Enclosures REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 1 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8� ' le. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 CERTIFICATIONS Project: J22090472 ASV LF Pace Project No.: 92627920 Pace Analytical Services Asheville 2225 Riverside Drive, Asheville, NC 28804 South Carolina Laboratory ID: 99030 Florida/NELAP Certification #: E87648 South Carolina Certification #: 99030001 North Carolina Drinking Water Certification #: 37712 Virginia/VELAP Certification #: 460222 North Carolina Wastewater Certification #: 40 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 2 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8� �gc� le. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 SAMPLE SUMMARY Project: J22090472 ASV LF Pace Project No.: 92627920 Lab ID Sample ID Matrix Date Collected Date Received 92627920001 LF-SW-2 Water 09/26/2211:15 09/27/22 14:20 92627920002 LMW-4B Water 09/26/2211:55 09/27/22 14:20 92627920003 LCS-1 Water 09/26/2212:10 09/27/22 14:20 92627920004 LMW-3B Water 09/26/2213:00 09/27/22 14:20 92627920005 LF-SW-3 Water 09/26/22 13:30 09/27/22 14:20 92627920006 LMW-2T Water 09/26/2214:00 09/27/22 14:20 92627920007 LMW-213 Water 09/26/2214:35 09/27/22 14:20 92627920008 LMW-1S Water 09/26/2215:15 09/27/22 14:20 92627920009 LMW-1B Water 09/26/2215:40 09/27/22 14:20 92627920010 C13-913R Water 09/26/2214:49 09/27/22 14:20 92627920011 C13-9SL Water 09/26/2215:22 09/27/22 14:20 92627920012 C13-9 Water 09/26/2215:49 09/27/22 14:20 92627920013 ASV FD-20220926-1 Water 09/26/22 00:00 09/27/22 14:20 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 3 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8� ' le. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 SAMPLE ANALYTE COUNT Project: Pace Project No.: J22090472 ASV LF 92627920 Analytes Lab ID Sample ID Method Analysts Reported Laboratory 92627920001 LF-SW-2 SM 2540C-2015 CS1 1 PASI-A 92627920002 LMW-413 SM 2540C-2015 CS1 1 PASI-A 92627920003 LCS-1 SM 2540C-2015 CS1 1 PASI-A 92627920004 LMW-313 SM 2540C-2015 CS1 1 PASI-A 92627920005 LF-SW-3 SM 2540C-2015 CS1 1 PASI-A 92627920006 LMW-2T SM 2540C-2015 CS1 1 PASI-A 92627920007 LMW-213 SM 2540C-2015 CS1 1 PASI-A 92627920008 LMW-1S SM 2540C-2015 CS1 1 PASI-A 92627920009 LMW-1B SM 2540C-2015 CS1 1 PASI-A 92627920010 C13-913R SM 2540C-2015 CS1 1 PASI-A 92627920011 C13-9SL SM 2540C-2015 CS1 1 PASI-A 92627920012 C13-9 SM 2540C-2015 CS1 1 PASI-A 92627920013 ASV FD-20220926-1 SM 2540C-2015 CS1 1 PASI-A PASI-A = Pace Analytical Services - Asheville REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 4 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8� 6f&Ie. Suite 100 �J Huntersville, NC 28078 (704)875-9092 SUMMARY OF DETECTION Project: Pace Project No.: J22090472 ASV LF 92627920 Lab Sample ID Client Sample ID Method Parameters Result Units Report Limit Analyzed Qualifiers 92627920001 LF-SW-2 SM 2540C-2015 Total Dissolved Solids 50.0 mg/L 25.0 09/29/22 09:21 92627920002 LMW-46 SM 2540C-2015 Total Dissolved Solids 315 mg/L 25.0 09/29/22 09:21 92627920003 LCS-1 SM 2540C-2015 Total Dissolved Solids 1470 mg/L 50.0 09/29/22 09:21 92627920004 LMW-36 SM 2540C-2015 Total Dissolved Solids 473 mg/L 25.0 09/29/22 09:21 92627920005 LF-SW-3 SM 2540C-2015 Total Dissolved Solids 42.0 mg/L 25.0 09/29/22 09:22 92627920006 LMW-2T SM 2540C-2015 Total Dissolved Solids 51.0 mg/L 25.0 09/29/22 09:22 92627920007 LMW-26 SM 2540C-2015 Total Dissolved Solids 65.0 mg/L 25.0 09/29/22 09:22 92627920008 LMWA S SM 2540C-2015 Total Dissolved Solids 51.0 mg/L 25.0 09/29/22 09:22 92627920009 LMW-1B SM 2540C-2015 Total Dissolved Solids 85.0 mg/L 25.0 09/29/22 09:22 92627920010 C13-96R SM 2540C-2015 Total Dissolved Solids 84.0 mg/L 25.0 09/29/22 09:22 92627920011 CB-9SL SM 2540C-2015 Total Dissolved Solids 47.0 mg/L 25.0 09/30/22 09:50 92627920012 C13-9 SM 2540C-2015 Total Dissolved Solids 26.0 mg/L 25.0 09/30/22 09:50 92627920013 ASV FD-20220926-1 SM 2540C-2015 Total Dissolved Solids 305 mg/L 25.0 09/30/22 09:50 REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 5 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8ninic� �ie. Suite 100 �J Huntersville, NC 28078 (704)875-9092 PROJECT NARRATIVE Project: J22090472 ASV LF Pace Project No.: 92627920 Method: SM 2540C-2015 Description: 2540C Total Dissolved Solids Client: Duke Energy Date: October 04, 2022 General Information: 13 samples were analyzed for SM 254OC-2015 by Pace Analytical Services Asheville. All samples were received in acceptable condition with any exceptions noted below or on the chain -of custody and/or the sample condition upon receipt form (SCUR) attached at the end of this report. Hold Time: The samples were analyzed within the method required hold times with any exceptions noted below. Method Blank: All analytes were below the report limit in the method blank, where applicable, with any exceptions noted below. Laboratory Control Spike: All laboratory control spike compounds were within QC limits with any exceptions noted below. Matrix Spikes: All percent recoveries and relative percent differences (RPDs) were within acceptance criteria with any exceptions noted below. Duplicate Sample: All duplicate sample results were within method acceptance criteria with any exceptions noted below. Additional Comments: This data package has been reviewed for quality and completeness and is approved for release. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 6 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC 0g8onfele. Suite 100 �J Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: LF-SW-2 Lab ID: 92627920001 Collected: 09/26/22 11:15 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 254OC-2015 Pace Analytical Services -Asheville Total Dissolved Solids 50.0 mg/L 25.0 25.0 1 09/29/22 09:21 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 7 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8�lsiscSr&e. Suite 100 �J Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: LMW-413 Lab ID: 92627920002 Collected: 09/26/22 11:55 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 254OC-2015 Pace Analytical Services -Asheville Total Dissolved Solids 315 mg/L 25.0 25.0 1 09/29/22 09:21 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 8 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8�lsi4c6r&e. Suite 100 �J Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: LCS-1 Lab ID: 92627920003 Collected: 09/26/22 12:10 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 1470 mg/L 50.0 50.0 1 09/29/22 09:21 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 9 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC 0g8oinfelie. Suite 100 �J Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: LMW-313 Lab ID: 92627920004 Collected: 09/26/22 13:00 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 473 mg/L 25.0 25.0 1 09/29/22 09:21 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 10 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC 0g8onfele. Suite 100 �J Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: LF-SW-3 Lab ID: 92627920005 Collected: 09/26/22 13:30 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 42.0 mg/L 25.0 25.0 1 09/29/22 09:22 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 11 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8� &e. Suite 100 �J Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: LMW-2T Lab ID: 92627920006 Collected: 09/26/22 14:00 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 51.0 mg/L 25.0 25.0 1 09/29/22 09:22 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 12 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC 0g8onfele. Suite 100 �J Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: LMW-213 Lab ID: 92627920007 Collected: 09/26/22 14:35 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 65.0 mg/L 25.0 25.0 1 09/29/22 09:22 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 13 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC 0g8onfele. Suite 100 �J Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: LMW-1S Lab ID: 92627920008 Collected: 09/26/22 15:15 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 51.0 mg/L 25.0 25.0 1 09/29/22 09:22 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 14 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8� '-6f&Iie. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: LMW-113 Lab ID: 92627920009 Collected: 09/26/22 15:40 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 85.0 mg/L 25.0 25.0 1 09/29/22 09:22 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 15 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8� inlcsr&Ie. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: C13-913R Lab ID: 92627920010 Collected: 09/26/22 14:49 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 84.0 mg/L 25.0 25.0 1 09/29/22 09:22 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 16 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8�wnf&Iie. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: C13-9SL Lab ID: 92627920011 Collected: 09/26/22 15:22 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 47.0 mg/L 25.0 25.0 1 09/30/22 09:50 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 17 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8� 'Sf&Iie. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: C13-9 Lab ID: 92627920012 Collected: 09/26/22 15:49 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 26.0 mg/L 25.0 25.0 1 09/30/22 09:50 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 18 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8�wi�csr&ie. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 ANALYTICAL RESULTS Project: J22090472 ASV LF Pace Project No.: 92627920 Sample: ASV_FD-20220926-1 Lab ID: 92627920013 Collected: 09/26/22 00:00 Received: 09/27/22 14:20 Matrix: Water Report Parameters Results Units Limit MDL DF Prepared Analyzed CAS No. Qual 2540C Total Dissolved Solids Analytical Method: SM 2540C-2015 Pace Analytical Services -Asheville Total Dissolved Solids 305 mg/L 25.0 25.0 1 09/30/22 09:50 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Page 19 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8�wnf&Iie. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 QUALITY CONTROL DATA Project: J22090472 ASV LF Pace Project No.: 92627920 QC Batch: 726459 Analysis Method: SM 2540C-2015 QC Batch Method: SM 2540C-2015 Analysis Description: 2540C Total Dissolved Solids Laboratory: Pace Analytical Services -Asheville Associated Lab Samples: 92627920001, 92627920002, 92627920003, 92627920004, 92627920005, 92627920006, 92627920007, 92627920008,92627920009,92627920010 METHOD BLANK: 3783682 Matrix: Water Associated Lab Samples: 92627920001, 92627920002, 92627920003, 92627920004, 92627920005, 92627920006, 92627920007, 92627920008,92627920009,92627920010 Blank Reporting Parameter Units Result Limit MDL Analyzed Qualifiers Total Dissolved Solids mg/L ND 25.0 25.0 09/29/22 09:19 LABORATORY CONTROL SAMPLE: 3783683 Spike LCS LCS % Rec Parameter Units Conc. Result % Rec Limits Qualifiers Total Dissolved Solids mg/L 250 250 100 90-110 SAMPLE DUPLICATE: 3783684 92627917001 Dup Max Parameter Units Result Result RPD RPD Qualifiers Total Dissolved Solids mg/L 312 310 1 25 SAMPLE DUPLICATE: 3783685 92627920001 Dup Max Parameter Units Result Result RPD RPD Qualifiers Total Dissolved Solids mg/L 50.0 52.0 4 25 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 10/04/2022 12:01 PM without the written consent of Pace Analytical Services, LLC. Page 20 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8�wnf&Iie. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 QUALITY CONTROL DATA Project: J22090472 ASV LF Pace Project No.: 92627920 QC Batch: 726983 Analysis Method: SM 2540C-2015 QC Batch Method: SM 2540C-2015 Analysis Description: 2540C Total Dissolved Solids Laboratory: Pace Analytical Services -Asheville Associated Lab Samples: 92627920011, 92627920012, 92627920013 METHOD BLANK: 3785993 Matrix: Water Associated Lab Samples: 92627920011, 92627920012, 92627920013 Blank Reporting Parameter Units Result Limit Total Dissolved Solids mg/L ND 25.0 LABORATORY CONTROL SAMPLE: 3785994 Spike LCS Parameter Units Conc. Result Total Dissolved Solids mg/L 250 258 SAMPLE DUPLICATE: 3785995 92627920011 Dup Parameter Units Result Result Total Dissolved Solids mg/L 47.0 44.0 MDL Analyzed Qualifiers 25.0 09/30/22 09:50 LCS % Rec % Rec Limits Qualifiers 103 90-110 Max RPD RPD Qualifiers 7 25 SAMPLE DUPLICATE: 3785996 92628383003 Dup Max Parameter Units Result Result RPD RPD Qualifiers Total Dissolved Solids mg/L ND ND 25 Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 10/04/2022 12:01 PM without the written consent of Pace Analytical Services, LLC. Page 21 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8�wi�csr&ie. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 QUALIFIERS Project: J22090472 ASV LF Pace Project No.: 92627920 DEFINITIONS DF - Dilution Factor, if reported, represents the factor applied to the reported data due to dilution of the sample aliquot. ND - Not Detected at or above adjusted reporting limit. TNTC - Too Numerous To Count J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit. MDL -Adjusted Method Detection Limit. PQL - Practical Quantitation Limit. RL - Reporting Limit - The lowest concentration value that meets project requirements for quantitative data with known precision and bias for a specific analyte in a specific matrix. S - Surrogate 1,2-Diphenylhydrazine decomposes to and cannot be separated from Azobenzene using Method 8270. The result for each analyte is a combined concentration. Consistent with EPA guidelines, unrounded data are displayed and have been used to calculate % recovery and RPD values. LCS(D) - Laboratory Control Sample (Duplicate) MS(D) - Matrix Spike (Duplicate) DUP - Sample Duplicate RPD - Relative Percent Difference NC - Not Calculable. SG - Silica Gel - Clean -Up U - Indicates the compound was analyzed for, but not detected. Acid preservation may not be appropriate for 2 Chloroethylvinyl ether. A separate vial preserved to a pH of 4-5 is recommended in SW846 Chapter 4 for the analysis of Acrolein and Acrylonitrile by EPA Method 8260. N-Nitrosodiphenylamine decomposes and cannot be separated from Diphenylamine using Method 8270. The result reported for each analyte is a combined concentration. Reported results are not rounded until the final step prior to reporting. Therefore, calculated parameters that are typically reported as "Total" may vary slightly from the sum of the reported component parameters. Pace Analytical is TNI accredited. Contact your Pace PM for the current list of accredited analytes. TN -The NELAC Institute. REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, Date: 10/04/2022 12:01 PM without the written consent of Pace Analytical Services, LLC. Page 22 of 27 leAnalyiical www.pacelabs.com Pace Analytical Services, LLC og8�wnf&Iie. Suite 100 ��JJ Huntersville, NC 28078 (704)875-9092 QUALITY CONTROL DATA CROSS REFERENCE TABLE Project: J22090472 ASV LF Pace Project No.: 92627920 Lab ID Sample ID QC Batch Method QC Batch 92627920001 LF-SW-2 SM 2540C-2015 726459 92627920002 LMW-4B SM 2540C-2015 726459 92627920003 LCS-1 SM 2540C-2015 726459 92627920004 LMW-3B SM 2540C-2015 726459 92627920005 LF-SW-3 SM 2540C-2015 726459 92627920006 LMW-2T SM 2540C-2015 726459 92627920007 LMW-2B SM 2540C-2015 726459 92627920008 LMW-1S SM 2540C-2015 726459 92627920009 LMW-1 B SM 2540C-2015 726459 92627920010 CB-9BR SM 2540C-2015 726459 92627920011 CB-9SL SM 254OC-2015 726983 92627920012 CB-9 SM 254OC-2015 726983 92627920013 ASV FD-20220926-1 SM 254OC-2015 726983 Date: 10/04/2022 12:01 PM REPORT OF LABORATORY ANALYSIS This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC. Analytical Method Analytical Batch Page 23 of 27 DG# Title: ENV-FRM-HUN�1-0083 v0'1_Sle Condition Upon Receipt f ar e arnpPage 49 of 53 Effective Date: 05/121202205/12/2022 Laboratory receiving samples: Asheville ❑ Eden❑ Greenwood [] Huntersvilleo//Raleigh❑ Mechanicsville❑ Atlantan KernersvilleF-1 Sample Condition Client Name: Upon Receipt Project WO# : 92627920 I] IlJ 1 Courier: VeE ❑UPS 5 5 ❑Client❑ Commercial / ❑Ot er: 111 ! 1 III / 92627920 Custody Seal Present? ❑Yes ❑No Seals Intact? []Yes No Date/initials Person Examining Contents: X/� Packing Material: ❑Bubble Wrap ❑Bubble Bags ne ❑ Other Biological Tissue Froze Thermometer: Gun ID: qZ Type of Ice: Z ; 1 Correction Factor: Cooler Temp: V Add/Subtract (°C) Cooler Temp Corrected ('C): `. USDA Regulated Sail (water sample) Did samples originate in a quarantine zone within the United States: i (check maps)? MYes MNo Chain of Custody Present? Samples Arrived within Hold Time? Short Hold Time Analysis (c72 hr.)? Rush Turn Around Time Requested? Sufficient Volume? Correct Containers Used? -Pace Containers Used? Containers Intact? Dissolved analysis: Samples Field Filtered? Sample Labels Match COC? -Includes is Matrix: L/" Headspace in VOA Vials (>5-6mm)? Trip Blank Present? Trip Blank Custody Seals Present? COMMENTS/SAMPLE DISCREPANCY CLIENT NOTIFICATION/RESOLUTION Person contacted: Project Manager SCURF Review: Prpjr ct hlartager SRE Review: - []Yes ❑No �Olue None NY, or SC No Yes No J ❑N/A 6. ❑Yes ❑N/A❑N/A s [--]No ❑N/A 7. ❑Yes Na A S. s [IN. ❑N/A 9. ❑Na /A 10. []Yes []Yes ❑No koXfA 11. Temp should be above freezing to 6'C ❑Samples out of temp criteria. Samples on ice, cooling process has begun Did samples originate from a foreign source (internationally, including Hawaii and Puerto Rico)? ❑Yes []No Comments/Discrenancv: Field Data Required? ❑Yes ❑No Lot ID of split containers: Date/Time: Date: Date: - Page 24 of 27 Qualtrax ID: 69614 Page 1 of 2 aee u(X—Title: ENV-FRM-HUN1-0083 v0l -Sample Condition Upon Receipt Page 50 of 53 Effective Date: 05/121202205/12/2022 *Check mark top half of box if pH and/or dechlorination is verified and prof WO# : 92627920 within the acceptance range for preservation samples. PM: HMG Exceptions: VOA, Coliform, TOC, oil and Grease, DRO/8015 (waterl DOC, ttfig Du! Date: : le/fa4/22 *"Bottom half of box is to list number of bottles CLIENT: 92—Duke Ener ***Check all unpreserved Nitrates for chlorine V z CU 0 U u a V z Z z Z = U 0 .J y = 2 t\ v a Z N N M c z N *v V d 2 ro M rim 2 �o v N v y Q 0. ? Z N x Cci Q ro 0 ¢i CL a c v O p ¢ m a a p a m a z = ? N v v Q z 0 Lo a c O +� O N S N '3 ` u V IV � u N 2 N ' N S C. 2 N 4 0 a N O C M M ; . u c n. a lv v m'^ A a D w = Z 2 = Y W y U m m 7 a a a m ° Q m ro o E E E E a Q ¢ a Q = = = a a CL C FL Ja E E E d E ¢ ¢ 0 o 0 D p a a' a E u E E E E u E E E E v W v E ¢ E E 1 Ln ¢ N o - LM uQi N 3 = o °' o o E E E E m E E E E E E # ~ N tp .-i rl r-4 r-i ry .-4 M N �0 O 0 L 0 0 O O G E R M r ✓1 � N m LL N fv`I N Q N N V rtl C V Ur M rl M N M 01 Gl O~i T P1 C� Y m m m m aan m m m E7 t, 0 l9 [7 l7 Q l7 t7 0 M v FM 0 On CR m Q ? o a a a a a o o a 0 7 1 i as r 8 9 + 1 10 i 11 l 12 PH Adjustment Log for Preserved Samples Sample to Type of Preservative pH upon receipt Rate preservation adjusted Time preservation Amount of Preservative tat p adJusted added Note:'Wheriever there is a discrepancy affecting North Carolina compliance samples, a COPY of this form will be sent to the North Carolina DENR Certification Office (i.e. Out of hold, incorrect preservative, out Of temp, incorrect containers. Qualtrax ID: 69614 Page 2 of 2 Page 25 of 27 Pace -vuuU V J i vaa IIVIU l4Vt lilt t l till UPUIt MUCBIP1 ". Page 51 of 53 Effective Date: 05112/202205/12/2022 — *Check mark top half of box if pH and/or dechlorination is verified and Project it within the acceptance range for preservation samples, Exceptions: VOA, Coliform, TOC, Oil and Grease, DRO/8015 (water) !]OC, Wig "Bottom half of box is to list number of bottles ***Check all unpreserved Nitrates for chlorine ^ 2 v �- E z 3 � c iN E E {{!lN77 a o z N c• A n. E vie N�7 M m z d moo. ru a E 0 Vl a. m Q z v G �o a p = rF H m U v M w yyO�� rl =� r^ ° E `n ,r..�� M o V 2 V '^ Q E 0 N m m T M m u N V .N 10 E '^ H m V N '' 2 CL ro Z V .y rn E `^ N ca 7 m w M C� U L o v p , 3 m 2 v a v = N a N U iv A a L = .i a �, c � N n E E u0 M ¢ N v z 7 = m a .�' r-I rl a v g nil = .a E a E o N M a lJ ¢ y u = z 4 E a E o N per+ a a 2 U x Q o E O1 _ m O N, a O J E 0 Doi Q z a Ai C a Q O J E q O1 a l7 M 2 o J pE y m n ? Q s Q 0 E y Ulf a 2 , Z } Y x a 1 m Y > 2 — 3 — — 4 5 — - 6 7 8 — 4 — 10 11 — 12 U a � z ro m m m ? ro I I a z u d z u Q ry z `r ! m v ro n d 1 Z G M C O r C m a uy ro J E 00 N •J E to a J E 0 E < E o Q C v5 E Ory 4 E Q N H N in M ca 0 Q 7 C1 O PH Adjustment Log for Preserved Samples Sample lD Type of Preservative pH upon receipt Date preservation adjusted::Trime:preservallon Amount of Preservative Lot# justed added Note:-WhtrTrev6rttm?,M; a tllscrepancy aT ec mg ort Nina conrplsance samples, a copy of this form will he seat to the NortirCarolina l)Et�R Certification Office (i.e. Out of hold, incorrect preservative, out of temp, incorrect containers. Qualtrax ID: 69614 Page 2of2 Page 26 of 27 CHAIN OF CI ISTnnV lZr-i- 1Rn Anln ANAL vcie oC'rii it=e-rcnDae 02 Zt DUKE DukoEnegyAnalylicaiLatloratory .i._------------------------------- .--------- I.. —Anal .....a..... .....`:_._._._.__._._._._._._._._._._._.�...._._._._._._._._._._._._._._ i rclyt: oc UI O0 .4!LnMaII COG MaO]yt 18u Wi,0Mrl 'Order fl N ENERGY ,,.,:, sarN. Rtl i � Malrlx WATER e.mr —OyWmq r.a NC Page_7_of _7 �_ ! DISTRIBUTION 0 HOMuavlllr, N.C. irWl C-7 Fagrrra24s i ilap& d BY Date Tlma i ORIGINAL N P.+: Lseraafs.gose ! ! SAMPLE PROGRAM to LAB, COPY 10 CLIENT __ _ _ Project Nam* ASHEVILLE STATE LF DETECTION PM1OO. Nao ive ar MONITORING i Client ASHLEY HEALY , BRYAN MOELLER, 13EE ip0 O'BRIEN, JOSH STOWE, CONNOR ZAHORA Pace - i Cb61erT P�CL _ -...._.._.._.._.._. _.._. Filtration (OAS um) Ground 0dnkin ._.._........_.._......_........ Lt Water _X_ Water RCRA Waste_ _.......................................... lJntlltered NPDES UST_ _ i - - - 21271207,2 `----' II Flterod M d Operating UnN: AE00 P{ ----:NGRDWTR Account: _— ( Projecu AAE000315 Activity 10: Facility ID:ASV PO ` P # 9172711 Preservative ICE ICE Container Volume ImL] son 300 500 Pmgnm 1 EOuiS Task Code:ASV LF Sub-Progm;P ask Cade: Container Type vEr PET NDPE — } � ANIONS by Malale prep-6010b TRM: Ba, Be, a, Cu, c m Customer to complete aft appmprlafe non shaded areas. w Sample Description Or ID '^ d Cl.F, 9086A: TDB 03-N(46-Hr N Fe, Mn, Ni, Zn 6020B IMS: Sb, As, SAMPLEcollection Infarma0on i u n1,, Hold Tlme), 504 Cd, Cr, Cc, Pb, Se, _ 1d ER i Date Time Printed Name Signature U u Ag, VILL). VILL), and Ho 747OA 12 _ 4MW-49 1155 x I ; AS . Ws- 1 1210 sr r 1 3 w- L-mw-s6 1300 ! I kj 1.1 1e + z A5V- LMW At,T IH4o r + sz( Asv, t^w-1- S lwss C/ ,r t I I ; az A5v_ unw-i s lS15 x , r w4 - 1 15Ko 4 145v- C-9- q Be- +I4 HAWSE x , AL 3 A5v- G8-q S L I SIM i A43V_ i ?. )I j ASV. FO- 2pno em- r -U-12 C4*00e 7AHQa4 x e Z A Sv- F6 -Zez2 equ-< <lep 9 26- l Koo CvA wveZ T�11� i amramef to SI n ato etaw -�- Relinquished By DatefTims / i63D Accept Z 6 DeI rrij�e ZZ �U m Requested Turnaround Total ❑p Relinquished By Datemme Accapl a 1 DamfTima _ a, Q 21 Days Rati ulshed BY OalwTime A— tctl y: aw.m.. { '-!� • • c 14 Days Seal/Lacks y Datarrime Saalnd Lock Opened ElatetTime '7 Days E 'm -- ei �a Comments STATE EDD REQUIRED ! EQUIS REQUIRED o 'Odter g ' Add. Cost Will App}y U CHAIN OF CUSTODY RECORD AND ANALYSIS REQUEST FORM ,Zp2 21 --------------------------------------------------------------------------------------------------------------------------------------------------------------------------------- Duke Energy Analytical Laboratory i Analytical LaboratoryUse Onlyi Page 53 of 53 A DUKE MintCw MG03A2(Building7106) '•Order# � Matrix WATER NC_X_ Page _1 of 1_ ENERGY. 13339 Hager6 Fw yRd Mn p1i O1p1nitln°"O° SC— DISTRIBUTION Hunler°vltle, N.C. 20070 ;Log ed By Dates Tlme SAMPLE PROGRAM ORIGINAL to LAB, COPY to CLIENT (7") 07iZ C F.. L741 �6ae�e ._______.__! ! Ground Water X_ NPDES -.----- ------------.. - F.. Name ASHEVILLE STATE LF DETECTION Ph. -No: c Drinking Water_ UST MONITORING .._.. _.._.. .._.._. Cer T�fn.P1!±1.._.._ ._.._.._.._.._.._.._.._.._.._. RCRA Waste -.............................. Client ASHLEY HEALY , BRYAN MOELLER, DEE i PO a O'BRIEN, JOSH STOWE, CONNOR ZAHORA Pace Filtration (0.45 um) d Unfiltered b Filtered Operating Unit: AE00 Process:NGRDWTR Account: Preservative ICE ICE !._.._.. PO # 9171711 .._.._.._.. ! �) ._... Project: AAE000315 Activity ID: Facility ID:ASV Container Volume mL 500 300 600 TEST R�811 Program i EQuiS Task COde:ASV LF Sub-Program/Task Code: Container Type PET PET HDPE Metals Prep-6010D ANIONS by 5 TRM: Be' Be, B, Cu, - 9056A: Cl, F, Fe, Mn, Ni, Zn y Customer to complete all appropriate non -shaded areas. in . o TDS NO3-N 48-Hr U _ Sample Description or ID 6020B IMS: Sb, As, SAMPLE ID Collection Information Hold Time), Ctl, Cr, Co, Pb, L), SO4 pg, TILL), VILL), e NUMBER Data Time Printed Name Signature and Hg 7470A Too Z - _ELF SW-2 26-Z2 1115 X t ► ' 3 ASV- 1Mw-46 115S h t ; l 7 5. LC -1 t210 Y 6 f 3 Mv- LA%)-36 Isoo x t 3 5\/ - a- � tS o Y t I A5v- LMvi 7 (400 )r 3Z / A5V . UAW -Z 9 11135 v )r I I II 1 1 3 2Z is ASv. LMtt/-1 S IS Is x t 3-2 k161! L^ - t g rsr4o Aw. og- 9 Be- 11I Iiltl.�f sLR?ory r6 , L4 IA15v- Gg-q S L ISIT tc 3 Aw. ca -9 t 5'! k t t i ' ASV. FC-20=00126- I -Z4-22 C14woe 7414 " 3Zg ASV-F8-2e22aq�.14� 4 Z6- t�too CavWrrl TAPW44 c a t Relinquished By Date/Time Accept D�telTigle ;; Requested Turnaround Tc -.�/nn E Relinquished By Date/Time Accept B : DatelTime ° Tt 21 Days `y: A' � d 2 a 14 Days /i Reli wished By DatelTime Acce to at, C .,L � E -'. Y y 5. ! Seal/Locke y DatelTime Sealed o[k Opened By DatelTime : E '- - m `m 7 Days Comments E 'Other STATE EDD REQUIRED I EQUIS REQUIRED •Add. Cost Will Apply 0 0 tal❑ 2