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HomeMy WebLinkAbout1809_DukeMarshall FGD LF GWMR_Q3_2023_FID_20240107DUKE �, ENERGY- January 7, 2024 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 2023 Flue Gas Desulfurization Landfill Permit No.: 1809-INDUS-2006 Marshall Steam Station Terrell, North Carolina 28682 Dear Ms. Moutos: 525 N. Tryon St. Charlotte NC, 28202 Duke Energy is providing the result of the semiannual water quality monitoring for the Duke Energy Carolinas, Marshall Steam Station, Flue Gas Desulfurization (FGD) Landfill, located near Terrell, North Carolina. On September 11, 2023, leachate and groundwater samples were collected in accordance with the facility's Water Quality Monitoring Plan (WQMP) approved July 24, 2019, and the updated parameter and constituent list, approved March 20, 2023. Field sampling forms, chain of custody (COC) forms, and laboratory reports are included in Appendix A and B. The leachate sampling field and analytical results are presented in Table 5. Leachate analytical results are not compared to groundwater or surface water quality standards and are provided for informational purposes only. A summary of the groundwater sampling field and analytical results are presented in Table 6. The analytical results for the constituents are compared to the groundwater standards found in Title 15A NCAC 02L .0202 (21- Standards). Results with values that are equal to or greater than the 2L Standards are indicated on Table 6 by bold font. A summary of the analytical results that are equal to or greater than the 2L Standards and a preliminary analysis of the cause and significance of such occurrences are presented in Table 7. Leachate, groundwater, and surface water locations at the Marshall FGD Landfill are sampled semiannually during March and September. The next water quality monitoring event is planned for March 2024 with a report of monitoring results to follow. If you need additional information regarding this submittal do not hesitate to email or call me at Ashley. Healy(a)duke-energy.com or (717) 982-0986. www.duke-energy.com Page 1 of 2 Respectfully, Ashley Healy, P.G. Environmental Services Attachments: INDUS-1809 Marshall FGD LF GW Monitoring Report September 2023_01-07-2024 w cvr Itr cc (via e-mail): Claire Osborn, NCDEQ Elizabeth Werner, NCDEQ Sherri Stanley, NCDEQ Ed Mussler, NCDEQ Dan Zakary, Duke Energy Scott La Sala, Duke Energy Tyler Hardin, Duke Energy Thomas Colton, 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): Duke Energy Carolinas, LLC Contact for questions about data formatting. Include data preparer's name, telephone number and E-mail address: Name: Thomas Colton E-mail: tcolton@synterracorp.com Phone: 864.421.9999 NC Landfill Rule: Actual sampling dates (e.g., Facility name: Facility Address: Facility Permit# (.0500 or.1600) October 20-24, 2006) Duke Energy Carolinas, LLC 8320 East NC-150 Marshall Steam Station Terrell, North Carolina 28682 �1809 .0500 September 11. 2023 Flue Gas Desulfurization Residue Landfill Environmental Status: (Check all that apply) ❑ Initial/Background Monitoring ❑X Detection Monitoring ❑ 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 ❑ Assessment Monitoring Methane gas monitoring data Corrective action data (specify) Other(specify) ❑ Corrective Action Notification attached? ❑ )( No. No groundwater or surface water standards were exceeded. 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. Kathy Webb Program Manager (864) 421-9999 Facility Representative Name (Print) Title (Area Code) Telephone Number KIA, 1/5/2024 Signature Date 148 River Street, Suite 220, Greenville, SC 29601 Facility Representative Address C-1478 / North Carolina Corporation Number C-387 NC PE Firm License Number (if applicable effective May 1, 2009) Affix NC Licensed/ Professional Geologist Seal Revised 6/2009 REPORT VERIFICATION PROJECT: SEMIANNUAL WATER QUALITY MONITORING REPORT MARSHALL STEAM STATION FLUE GAS DESULFURIZATION RESIDUE LANDFILL PERMIT NO. 1809-INDUS TITLE: SEMIANNUAL WATER QUALITY MONITORING REPORT This document has been reviewed for accuracy and quality commensurate with the intended application. Prepared by: �, Date 1/5/2024 � I Approved by: C� Date: 1/5/2024 Project Manager: G. Thomas Colton, PE Licensed Geologist Seal: SynTerra 148 River Street, Suite 220 Greenville, SC 29601 North Carolina Geological Corporation Number C-387 Terra Science &Engineering Consultants synsynterracorp.com SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2023 SAMPLING EVENT FLUE GAS DESULFURIZATION RESIDUE LANDFILL PERMIT NO. 1809-INDUS) CATAWBA COUNTY MARSHALL STEAM STATION 8320 NC HIGHWAY 150E TERRELL, NORTH CAROLINA JANUARY 2024 PREPARED FOR r� DUKE ENERGY,: CAROLINAS DUKE ENERGY CAROLINAS, LLC Kathy Webb, L.G. #1328 Kevin ei ly Senior Peer Reviewer Projec Scien st Thomas Colton, P.E.#056667 Project Manager Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, 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 Analytical Results.......................................................................................................3-1 3.3 Quality Assurance/Quality Control.............................................................................3-2 4.0 REFERENCES...............................................................................................................4-1 LIST OF FIGURES Figure 1 Site Location Map Figure 2 Sample Location Map Figure 3 Water -level Map — Surficial Flow Zone — September 2023 LIST OF TABLES Table 1 Well Construction Summary Table 2 Monitoring Parameters Table 3 Monitoring Location Summary Table 4 Groundwater Seepage Velocities Table 5 Leachate Results and Analytical Detections Table 6 Groundwater Field Results and Analytical Detections Table 7 Field and Analytical Results that Greater Than or Equal to Groundwater Quality Standards LIST OF APPENDICES Appendix A Field Sampling Forms Appendix B Laboratory Report and Chain -of -Custody Forms Appendix C Time Versus Constituent Concentrations Plots January 2024 Page i Project: 00.0083.61 Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina LIST OF ACRONYMS 02B Title 15A NCAC, Subchapter 02B .0200, Surface Water and Wetland Standards 02L Title 15A NCAC, Subchapter 02L .0202(g), Groundwater Quality Standards Duke Energy Duke Energy Carolinas, LLC DWM Division of Waste Management EDD electronic data deliverable FGD Flue Gas Desulfurization Landfill Dry Ash Landfill Marshall Marshall Steam Station NCAC North Carolina Administrative Code NCDEQ North Carolina Department of Environmental Quality Piedmont Piedmont physiographic province PTO permit to operate Site Marshall Steam Station SWS Solid Waste Section USEPA U.S. Environmental Protection Agency WQMP Water Quality Monitoring Plan January 2024 Page H Project: 00.0083.61 Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina This semiannual report pertains to the Duke Energy Carolinas, LLC (Duke Energy) Marshall Steam Station (Marshall or Site) Flue Gas Desulfurization (FGD) Residue Landfill (Landfill) and documents the results of the September 2023 FGD Landfill groundwater, surface water, and leachate monitoring event. 1.1 Site and Landfill Information Duke Energy owns and operates Marshall Steam Station, located at 8320 NC Highway 150E in Terrell, Catawba County, North Carolina (Figure 1). The North Carolina Department of Environmental Quality (NCDEQ) Division of Waste Management (DWM) issued a permit to operate (PTO) the FGD Residue Landfill (Landfill; No. 1809 - INDUS) on November 21, 2006. Closure activities began in July 2018 and were completed in March 2019; the Closure Permit was issued on June 30, 2020. The Landfill encompasses an 18-acre landfill footprint. The FGD Residue Landfill is constructed with a leachate collection and removal system and an engineered liner system to prevent effects on groundwater. 1.2 Hydrogeologic Setting The Landfill site is located within the Piedmont physiographic province (Piedmont). Piedmont bedrock primarily consists of igneous and metamorphic bedrock. The fractured bedrock is overlain by a mantle of unconsolidated material known as regolith. The regolith includes, where present, the soil zone, a zone of weathered, decomposed bedrock known as saprolite, and alluvium. Saprolite, the product of chemical and mechanical weathering of the underlying bedrock, is typically composed of clay and coarser granular material up to boulder size and may reflect the texture of the rock from which it was formed. The weathering product of granitic rocks may be quartz -rich and sandy -textured, whereas rocks poor in quartz and rich in feldspar and other soluble minerals form a more clayey saprolite. 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 hydrogeologic system. Bedrock underlies the transition zone and comprises the least permeable flow zone of the Site hydrogeologic system, where groundwater flow occurs predominantly along fractures, joints, and faults. Groundwater is usually first encountered in the surficial flow zone. Groundwater flows to the south and emerges in a discharge zone. The water flows from the discharge zone to an unnamed tributary that ultimately flows to Lake Norman. The surface water classification of Lake Norman is WS-IV. January 2024 Page 1-1 Project: 00.0083.61 Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina 1.3 Landfill Semiannual Monitoring Program The initial Water Quality Monitoring Plan (WQMP) (Altamont, 2006) has been revised over time to incorporate changes. The March 2023 sampling event and this Semiannual Water Quality Monitoring Report comply with WQMP, Revision 2 (Wood, 2019) submitted to the DWM on July 24, 2019. The Landfill semiannual monitoring program, described in detail in the WQMP, consists of nine groundwater monitoring locations, one surface water monitoring location, and one leachate monitoring location (Table 3 and Figure 2). A summary of monitoring well construction information is presented in Table 1, and analytical parameter coverage for the Landfill semiannual water quality monitoring program is summarized in Table 2. January 2024 Page 1-2 Project: 00.0083.61 Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina 2.0 METHODS 2.1 Sampling and Analysis Methods Duke Energy Groundwater Science Group personnel (Duke Energy North Carolina Field Certification #5193) performed groundwater sampling on September 11, 2023, 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) analyzed the samples for reported parameters and constituents. The laboratory report and chain -of -custody forms are included in Appendix B. Duke Energy developed a list of parameters and constituents using guidance from the NCDEQ DWM, Solid Waste Section (SWS). The samples were analyzed using the updated parameter and constituent list, approved by NCDEQ on March 20, 2023. The monitoring parameters, along with the U.S. Environmental Protection Agency (USEPA) Solid Waste (SW)-846 analytical methods, Title 15A, North Carolina Administrative Code (NCAC), Subchapter 02L .0202(g) Groundwater Quality Standards (02L), and Title 1SA, NCAC, Subchapter 02B .0200, Surface Water and Wetland Standards (0213) are presented in Table 2. 2.2 Regulatory Criteria Semiannual monitoring analytical results were compared to the following regulatory criteria: Grnundwater • 02L standard Surface water • 02B standard 2.3 Statement of Work The following tasks were completed for semiannual water quality monitoring: • Collected groundwater, surface water, and leachate samples on September 11, 2023. • Reviewed the laboratory analytical results pertaining to the parameters listed in Table 2. • Compared groundwater analytical results to the 02L standard and historical concentration ranges. • Developed generalized groundwater surface contour maps using groundwater elevation data. Calculated groundwater flow velocities based on groundwater elevations at wells perpendicular to groundwater flow. • 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 2024 Page 2-1 Project: 00.0083.61 Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina 3.1 Site Groundwater Flow Groundwater flow in the aquifer beneath the Landfill footprint generally flows to the east and southeast beneath the landfill, toward the Ash Basin and Lake Norman. Generalized groundwater elevation contours and groundwater flow direction arrows in the vicinity of the Landfill are shown on Figure 3 for the shallow flow zone. Those contours were developed by calculating groundwater elevations in each monitoring well using the depth -to - water measurements taken during the September 2023 monitoring event. Depth -to -water measurements and calculated groundwater elevations are presented in Table 1. Calculated groundwater flow velocities are presented in Table 4. Calculated groundwater elevations based on depth -to -water measurements gauged during the September 2023 water -level sweep indicate groundwater at the Landfill generally flows to the east-southeast, consistent with historical Site observations. 3.2 Analytical Results Analytical results and reference comparisons discussed below are summarized in Table 5 through Table 8. Sample locations are depicted on Figure 2. Leachate A leachate sample was collected from C-1 on the east side of the Landfill. Analytical results are presented in Table S. Leachate analytical results are not compared to groundwater (02L) or surface water (02B) quality standards and are provided for informational purposes only. Groundwater Results Field and analytical results for the collected downgradient and background groundwater samples are presented in Table 6. Groundwater analytical results are compared with 02L standards. Constituent concentrations equal to or greater than 02L standards are noted in Table 6 in bold font. The laboratory analytical reports are included in Appendix B. A summary of the downgradient groundwater field and analytical results that are equal to or greater than applicable comparison criteria is presented in Table 7. Constituent concentrations greater than their applicable comparative criteria are within the historical range. The concentrations and historical range are demonstrated in Appendix C. Surface Water The sample location, SW-1, is shown on Figure 2. Surface water was not sampled during the reporting period because SW-1 was dry. Analytical results for the surface water sample, when available, are compared with applicable 02B Class C and WS-IV surface water standards. January 2024 Page 3-1 Project: 00.0083.61 Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina 3.3 Quality Assurance/Quality Control Field -performed quality assurance and quality control (QA/QC) consisted of the collection and analysis of a field blank to evaluate if contamination was 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. 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 in the lab report in Appendix B. Additional QA/QC data, laboratory analyses, and chain -of -custody forms are included in Appendix B. January 2024 Page 3-2 Project: 00.0083.61 Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina LIKIM."".4401"I Altamont. (Rev 0, 2006). Water Quality Monitoring Plan, Marshall Flue Gas Desulfurization Residue Landfill, November 2006. Wood. (Rev 2, 2019). Water Quality Monitoring Plan, Marshall Flue Gas Desulfurization Residue Landfill, July 2019. January 2024 Page 4-1 Project: 00.0083.61 Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina FIGURES L7 synTerra Science & Engineering Consultants .T ley-, V 1. DUKE ENERGY CAROLINAS PROPERTY LINE',,,# r % ek k .- 4 V Al FGD RESIDUE LANDFILL !T PERMIT #1809-INDUS 1 ,. fA r-.♦ `A 101 BASIN TE BOUN y � • L i o � MA RSHALL ♦\? fSTEAM STATION I " ' LL 'i NOTES: 1. FGD - FLUE GAS DESULFURIZATION 2. ALL BOUNDARIES ARE APPROXIMATE. 3. AERIAL IMAGERY IN THE AREA OF INTEREST IS A COMBINATION OF DUKE ENERGY PROPELLER PHOTOGRAPHY COLLECTED ON MARCH 31, 2023 AND SEPTEMBER 11, 2023. BACKGROUND AERIAL IMAGERY PROVIDED BY ESRI, COLLECTED ON MARCH 20, 2022. FIGURE 1 DUKE ENERGY® CATAWBA COUNTY WINSTON-SAIEM SITE LOCATION MAP SEPTEMBER 2023 SAMPLING EVENT FGD RESIDUE LANDFILL CAROLINAS SEMIANNUAL WATER QUALITY MONITORING REPORT ASHEVILLE CHARLOTTE MARSHALL STEAM STATION TERRELL, NORTH CAROLINA DRAWN BV_ T KING DATE 05/15/2019 REVISED 8Y L FORE O'RMAN DATE12/26/2023 CRECEDBYK LDATE: 12/26/2023 1,000 0 1,002,000 synTerra DATE: 12/26/2023 PROJECT MANAGER: T. COLTON GRAPHIC SCALE (IN FEET) WWW.S nterracor .com q ft .4 .I n ' L . LEGEND GROUNDWATER MONITORING WELL ■ SURFACE WATER SAMPLE LOCATION A LEACHATE SAMPLE LOCATION — - — LANDFILL REVIEW BOUNDARY LANDFILL LIMIT OF WASTE LANDFILL COMPLIANCE BOUNDARY ASH BASIN WASTE BOUNDARY — - DUKE ENERGY CAROLINAS PROPERTY LINE )o STREAM (MCKIM & CREED 2016) f WETLAND (MCKIM & CREED 2016) MS-14 '•3. ^I. .'1 NOTES: ` 1. FGD - FLUE GAS DESULFURIZATION. A 2. THE STREAMS AND WETLANDS JURISDICTIONAL DETERMINATION WAS APPROVED BY THE US ARMY CORPS OF ENGINEERS ON OCTOBER 25, 2017 (SAW-2015-01412). WETLANDS AND STREAMS BOUNDARIES WERE OBTAINED FROM AMEC FOSTER WHEELER ENVIRONMENTALAND INFRASTRUCTURE, INC. NATURAL RESOURCES TECHNICAL REPORT (NRTR) DATED JUNE 2015. 3. SAMPLE LOCATIONS WERE DERIVED FROM VARIOUS SOURCES AND ARE A MIX OF SURVEYED AND APPROXIMATE LOCATIONS. THFRFFORF SAMPI F I OCATIONS ARF TO RF 4DUKE ENERGY® CAROLINAS DEEMED APPROXIMATE. 4. ALL BOUNDARIES ARE APPROXIMATE 5. AERIAL IMAGERY ISACOMBINATION OF DUKE ENERGY PROPELLER PHOTOGRAPHY COLLECTED ON MARCH 31, 2023 AND AERIAL IMAGERY PROVIDED BY ESRI, COLLECTED ON �:- MARCH 20, 2022. 6. DRAWING HAS BEEN SET WITH A PROJECTION OF NORTH CAROLINA STATE PLANE ,.�'•,-^ �.-S COORDINATE SYSTEM RIPS 3200 (NAD83). GRAPHIC SCALE FIGURE 2 160 0 160 320 SAMPLE LOCATION MAP (IN FELT) SEPTEMBER 2023 SAMPLING EVENT DRAWN BY: T. KING DATE: 02/03/2021 FGD RESIDUE LANDFILL REVISED FOREMAN DATE 12/26/2023 SEMIANNUAL WATER QUALITY MONITORING REPORT CHECKED BY: K. O'REILLY DATE: 12/26/2023 CHECKED BY. APPROVED BYTCOLTON DATE12/2612023 MARSHALL STEAM STATION PROJECT MANAGER ICOLTON TERRELL, NORTH CAROLINA www.s nterracor .com P:\DARCGIS PROPROJECTS\DUKE ENERGY\MARSHALL\2023\SEMIANNUAL WATEROUALITYM ONITORI N GREPORT\SEMAN NUAL WATEROUALITYMON ITOR I HG REPORT APRX I"- N 8i0 840 gap S20 n MS-8 � 826.03 Ir t , ro r 824.79 MS-16 810 18 AT aop by a 832.09 4mm% .17 LEGEND GROUNDWATER MONITORING WELL GROUNDWATER FLOW DIRECTION INFERRED GROUNDWATER CONTOUR (NAVD88) R S ` _ A LEACHATE SAMPLE LOCATION LANDFILL LIMIT OF WASTE ■ }, y I ' MS-15 I811.22 — - — LANDFILL REVIEW BOUNDARY LANDFILL COMPLIANCE BOUNDARY o � MS-11 �'► z' 1 824.32 ASH BASIN WASTE BOUNDARY .•,�- . . — - DUKE ENERGY CAROLINAS PROPERTY LINE STREAM (MCKIM & CREED 2016) WETLAND (MCKIM & CREED 2016) TOPOGRAPHIC CONTOUR (10' INTERVAL) 07 63 NOTES: .1. WATER LEVELS GAUGED SEPTEMBER 11, 2023. �. `T.: ' 2. FGD - FLUE GAS DESULFURIZATION. 0 «. 3. THE STREAMS AND WETLANDS JURISDICTIONAL DETERMINATION WAS APPROVED '"` • BY THE US ARMY CORPS OF ENGINEERS ON OCTOBER 25, 2017 (SAW-2015-01412). MS-13 WETLANDS AND STREAMS BOUNDARIES WERE OBTAINED FROM AMEC FOSTER HOLDING 810.69 WHEELER ENVIRONMENTALAND INFRASTRUCTURE, INC. NATURAL RESOURCES BASIN TECHNICAL REPORT (NRTR) DATED JUNE 2015. w - _ n '' 4. SAMPLE LOCATIONS WERE DERIVED FROM VARIOUS SOURCES ANDAREAMIX OF SURVEYED AND APPROXIMATE LOCATIONS. THEREFORE, SAMPLE LOCATIONS ARE TO BE DEEMED APPROXIMATE. ♦ L 812.10 5. ALL BOUNDARIES ARE APPROXIMATE. A T •+Y 1 6. AERIAL IMAGERY IS ACOMBINATION OF DUKE ENERGY PROPELLER PHOTOGRAPHY COLLECTED ON MARCH 31, 2023 AND AERIAL IMAGERY PROVIDED BY ESRI, COLLECTED ON MARCH 20, 2022. • 7. DRAWING HAS BEEN SET WITH A PROJECTION OF NORTH CAROLINA STATE PLANE - _ - COORDINATE SYSTEM RIPS 3200 (NAD83). ' GRAPHIC SCALE FIGURE 3 >so o is0 320 h° ENERGY WATER LEVEL MAP - SURFICIAL FLOW ZONE CAROLINAS (IN FEET) SEPTEMBER 2023 SAMPLING EVENT DRAWN BYTKING DATE02/03/2021 FGD RESIDUE LANDFILL FIEVI5EDBY L FOREMAN DATE 12/26/2023 SEMIANNUAL WATER QUALITY MONITORING REPORT �' - Q i • - - �� CHECKED BY: K. O'REILLY DATE_ 12/26/2023 860 APPROVED BY T COLTON DATE 12/26/2023 MARSHALL STEAM STATION ! \ A - ! synTeY� PROTECT synte N TERRELL, NORTH CAROLINA ''7' ' www.s nterracor corn P:\DARCGIS PRO PROJECTS\DUKE ENERGY\MARSHALL\2023\SEMIANNUAL WATEROUALITYM ONITORI N GREPORT\SEMAN NUAL WATEROUALITYMON ITOR I HG REPORT APRX Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina TABLES L7 synTerra Science & Engineering Consultants TABLE 1 WELL CONSTRUCTION SUMMARY FGD RESIDUE LANDFILL (No. 1809-INDUS) SEMIANNUAL WATER QUALITY MONITORING REPORT MARSHALL STEAM STATION DUKE ENERGY CAROLINAS, LLC, TERRELL, NC Well ID Date Installed Flow Zone Material Diameter (Inches) Latitude (degrees) Longitude (degrees) Well Depth (Ft, BTOQ 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) MS-8* 9/12/2006 Shallow PVC 2 35.6064200 -80.9782600 48.0 38 - 48 872.34 869.35 826.03 46.31 MS-9 1/16/2003 Shallow PVC 2 35.6061300 -80.9776900 50.0 40 - 50 868.04 865.36 824.79 43.25 MS-10 7/8/2003 Shallow PVC 2 35.6051100 -80.9795500 20.0 44 - 54 851.29 848.29 832.09 19.20 MS-11 7/9/2003 Shallow PVC 2 35.6031100 -80.9797000 39.0 29 - 39 859.78 856.87 824.32 35.46 MS-12 2/11/2003 Shallow PVC 2 35.6010500 -80.9778900 27.0 17 - 27 835.66 832.70 812.1 23.56 MS-13 12/17/2002 Shallow PVC 2 35.6016100 -80.9765100 38.0 28 - 38 841.90 839.19 810.69 31.21 MS-14 1/7/2003 Shallow PVC 2 35.6022900 -80.9744300 41.0 31- 41 844.07 841.27 807.63 36.44 MS-15 12/3/2002 Shallow PVC 2 35.6035300 -80.9749200 53.6 43.6 - 53.6 854.28 851.86 811.22 43.06 MS-16 9/11/2006 Shallow PVC 2 35.6054800 -80.9766600 34.0 24 - 34 836.98 834.25 810.18 26.80 Notes: * - Indicates background groundwater monitoring well. Groundwater elevations are based on data collected in September 11, 2023. BGS - Below ground surface BTOC - Below top of casing Ft - Feet NAVD 88 - Vertical elevations in feet based on North American Vertical Datum of 1988 PVC - Polyvinylchloride TOC - Top of casing Revised by: TAW Checked by: CSM Page 1 of 1 TABLE 2 GROUNDWATER, SURFACE WATER, AND LEACHATE MONITORING PARAMETERS SEMIANNUAL WATER QUALITY MONITORING REPORT SEPTEMBER 2023 SAMPLING EVENT MARSHALL STEAM STATION DUKE ENERGY CAROLINAS, LLC, TERRELL, NC Constituent Units Analytical Methods 15A NCAC 02L Standards for Groundwater 15A NCAC 02B Standards, ISTV, and USEPA Criteria for Surface Water In Situ Parameters Field pH S.U. Multi -Parameter Water Quality Meter 6.5-8.5 6.0-9.0 Field Specific Conductance [10/cm Multi -Parameter Water Quality Meter NE NE Field Temperature degrees Celsius Multi -Parameter Water Quality Meter NE <_ 32 Field Dissolved Oxygen mg/L Multi -Parameter Water Quality Meter NE >_ 4 Field Oxidation Reduction Potential mV Multi -Parameter Water Quality Meter NE NE Field Turbidity NTU Turbidimeter NE Streams <_ 50 Water Level feet Water Level Meter NE NE Laboratory Analyses Antimony µg/L EPA 200.8 / SW 6020E 1 5,300# Arsenic µg/L EPA 200.8 / SW 6020B 10 10 Barium µg/L EPA 200.7 / SW 6010D 700 1,000 Beryllium µg/L EPA 200.8 / SW 6020B 4 NE Beryllium (dissolved) µg/L EPA 200.8 / SW 6020E NE 65^ Boron µg/L EPA 200.7 / SW 6010D 700 34,000# Cadmium µg/L EPA 200.8 / SW 6020E 2 NE Cadmium (dissolved) µg/L EPA 200.8 / SW 6020B NE 0.75^'t Calcium mg/L EPA 200.7 / SW 6010D NE NE Chloride mg/L EPA 300.0 / EPA 9056A 250 230 Chromium µg/L EPA 200.8 / SW 6020E 10 NE Chromium (dissolved) µg/L EPA 200.8 / SW 6020B NE NE Cobalt µg/L EPA 200.8 / SW 6020E 1 3 Copper µg/L EPA 200.8 / SW 6020B 1,000 1,300* Copper (dissolved) µg/L EPA 200.8 / SW 6020E NE 3.6"'t Fluoride mg/L EPA 300.0 / EPA 9056A 2 1.8 Iron µg/L EPA 200.7 / SW 6010D 300 1,000* Lead µg/L EPA 200.8 / SW 6020B 15 NE Lead (dissolved) µg/L EPA 200.8 / SW 6020E NE 14A't Lithium µg/L EPA 200.7 / SW 6010D NE NE Magnesium mg/L EPA 200.7 / SW 6010D NE NE Manganese µg/L EPA 200.7 / SW 6010D 50 50* Mercury µg/L EPA 245.1 / SW 7470A 1 0.012 Molybdenum µg/L EPA 200.8 / SW 6020B NE 160# Nickel µg/L EPA 200.8 / SW 6020E 100 25 Nickel (dissolved) µg/L EPA 200.8 / SW 6020B NE 145^'t Nitrate mg/L EPA 300.0 / EPA 9056A 10 10 Selenium µg/L EPA 200.8 / SW 6020B 20 170* Selenium (dissolved) µg/L EPA 200.8 / SW 6020E NE 3.1& Silver µg/L EPA 200.8 or SW 6020A 20 NE Silver (dissolved) µg/L EPA 200.8 or SW 6020A NE 0.30A't Sulfate mg/L EPA 300.0 / EPA 9056A 250 250 Thallium µg/L EPA 200.8 / SW 6020E 2 2$ Total Dissolved Solids mg/L SM 2540C / EPA 160.1 / ASTM D5907 500 NE Total Hardness mg/L Calculation (2.497 (calcium) + 4.118 (magnesium)) NE 100 Vanadium µg/L EPA 200.8 / SW 6020B 7 NE Zinc µg/L EPA 200.7 / SW 6010D 1,000 7,400* Zinc (dissolved) µg/L EPA 200.7 / SW 6010D NE 36.2" Prepared by: GTC Checked by: DAA TWL Notes: Constituents analyzed in the WQMP were approved by NCDEQ on March 20, 2023. 15A NCAC 02L Standards for Groundwater - North Carolina Class GA Standards found in 15A NCAC 02L .0202 Groundwater Quality Standards (effective April 1, 2022). 15A NCAC 02B Standards for Surface Water - 15A NCAC 02B Standards for Class WS-IV surface waters. North Carolina surface water and wetland standards (effective September 1, 2022). ISTV for Surface Water - In -stream target values established per 15A NCAC 02B .0202 and .0208. USEPA Criteria for Surface Water - U.S. Environmental Protection Agency National Recommended Water Quality Criteria For 15A NCAC 02B Standards and ISTVs with acute and chronic criteria, the acute criteria are considered more applicable to grab sampling; therefore, those values are presented. Dissolved constituents are applicable to surface water analytical parameters only. $ - An exceedance of a published ISTV is not automatically a violation of the water quality standard for toxicity. Comparison value presented is the lesser of the Aquatic Life & Secondary Recreation or Fish Consumption value. "- ISTV is based on acute sampling method described in 15A NCAC 02B (11)(e). Compliance with acute instream standard is not applicable to sampling method. An exceedance of a published ISTV is not automatically a violation of the water quality standard for toxicity. USEPA National Recommended Water Quality Criteria are not a regulation, nor do they impose a legally -binding requirement. Therefore, comparisons with these criteria are for situational context. Comparison criteria based on acute sampling method described in 15A NCAC 02B (11)(e). Compliance with acute instream standard is not applicable to sampling method and provided for screening purposes only. t - Hardness -dependent standard calculated using 25 mg/L hardness and not actual in -stream hardness value. Provided for screening purposes only. `- Hardness -dependent standard for chromium III calculated using 25 mg/L hardness and not actual in -stream hardness value. Provided for screening purposes only. &- Selenium standard for lotic water based on a 30-day average. Not applicable to the sampling method and provided for screening purposes only. EPA - Environmental Protection Agency µg/L - micrograms per liter µfa/cm - micro -ohms per centimeter mg/L - milligrams per liter mV - millivolts NCDEQ- North Carolina Department of Environmental Quality NE - not established NTU - nephelometric turbidity units S.U. - standard units SW - Solid Waste Page 1 of 1 TABLE 3 MONITORING LOCATION SUMMARY FGD RESIDUE LANDFILL (No. 1809-INDUS) SEMIANNUAL WATER QUALITY MONITORING REPORT MARSHALL STEAM STATION DUKE ENERGY CAROLINAS, LLC, TERRELL, NC Media Monitoring Location ID Comments MS-8 is located upgradient of the landfill and serves as a background MS-8 water quality monitoring well. See Table 1 Well Construction Summary for background monitoring well construction information. Groundwater MS-9 MS-10 MS-11 See Table 1 Well Construction Summary for monitoring well MS-12 MS-13 construction information. MS-14 MS-15 MS-16 Surface water monitoring locations in Surface Water SW-1 tributary south of the landfill (sampled if flow is present during semi-annual monitoring). Leachate sample, representing Leachate C-1 Leachate leachate from the entire landfill, collected from sampling point in collection system east of the landfill. Prepared by: GTC Checked by: DAA Page 1 of 1 TABLE 4 GROUNDWATER SEEPAGE VELOCITIES FGD RESIDUE LANDFILL (No. 1809-INDUS) SEMIANNUAL WATER QUALITY MONITORING REPORT MARSHALL STEAM STATION DUKE ENERGY CAROLINAS, LLC, TERRELL, NC Shallow and Transition Flow Zone Upgradient Downgradient Seepage Groundwater Groundwater K Ah Distance Effective Velocity Well ID Elevation Elevation (ft/day)1 (ft) (ft) PorosityZ 2 (ft/day) (ft, NAVD 88) (ft, NAVD 88) MS-10 to MS-14 832.09 807.63 0.71 24.46 559 0.2765 0.111 MS-11 to MS-13 824.32 810.69 0.71 13.63 333 0.2765 0.104 Prepared by: TAW Checked by: CSM Notes: - Values used are a calculated mean of hydraulic conductivities in MS-8, MS-9, MS-10, MS-11, MS-12 (OW-3), and MS-13(MS-6). Z - Values used are a calculated mean of effective porosities in MS-8, MS-9, MS-10, MS-11, MS-12 (OW-3), and MS-13(MS-6) taken from the Hydrogeologic Study for the Proposed FGD Scrubber Landfill, August 2003. Groundwater elevations are based on water level data collected on September 11, 2023. Hydraulic gradients and groundwater velocities are approximate. ft - feet ft/day - feet per day NAVD 88 - North American Vertical Datum 1988 Page 1 of 1 TABLE 5 LEACHATE RESULTS AND ANALYTICAL DETECTIONS FGD RESIDUE LANDFILL (No. 1809-INDUS) SEMIANNUAL WATER QUALITY MONITORING REPORT MARSHALL STEAM STATION DUKE ENERGY CAROLINAS, LLC, TERRELL, NC Parameter SWS ID Units Leachate Sample ID MDL C-1 Leachate pH 320 S.U. 4.7 Temperature 325 Deg C 18 Specific Conductance 323 µmhos/cm 4015 Dissolved Oxygen - mg/L 7.64 Oxidation Reduction Potential 336 mV 386 Eh - mV 591.0 Turbidity 330 NTUs 15.4 - Antimony 13 µg/L < 1 0.104 Arsenic 14 µg/L 1.94 0.111 Barium 15 µg/L 22 2 Beryllium 23 µg/L 3.63 2 Boron 428 µg/L 57600 5 Cadmium 34 µg/L 0.246 J 0.032 Calcium 375 mg/L 547 0.012 Chloride 301 mg/L 370 0.0154 Chromium 51 µg/L < 1 0.185 Cobalt 53 µg/L 42.7 0.077 Copper 54 µg/L 2.50 1 Fluoride 312 mg/L 1.2 J 0.0479 Iron 340 µg/L 164000 4 Lead 131 µg/L 0.126J 0.037 Lithium - µg/L 2010 2 Magnesium 376 mg/L 227 0.008 Manganese 342 µg/L 5650 1 Mercury 132 µg/L < 0.05 0.01 Molybdenum 397 µg/L 634 1 Nickel 152 µg/L 108 1 Nitrate (as N) 303 mg-N/L 2.0 0.002 Selenium 183 µg/L 46.1 0.193 Silver 184 µg/L < 1 0.035 Sulfate 315 mg/L 2800 0.0428 Thallium 194 µg/L 0.098 J 0.041 Total Dissolved Solids 311 mg/L 4900 25 Vanadium 209 µg/L < 1 0.114 Zinc 213 µg/L 264 4 Notes: A blank cell means there is no relevant information. Analytical data presented in this table reflect the Duke Energy Biological Analytical Data Storage System (BASS) as of 11/15/2023. Samples collected by Duke personnel on September 11, 2023. <- Concentration not detected at or above the adjusted reporting limit. µg/L - micrograms per liter µmhos/cm - micromhos per centimeter Deg C - degrees Celsius 1 - Value is estimated. The result is below the reporting limit or potentially biased based on data validation. MDL - Laboratory Method Detection Limit; MDL values presented are for samples not diluted by the laboratory during analysis. mg/L - miligrams per liter mg-N/L - milligrams nitrogen per liter mV - Millivolts NTUs - nephelometric turbidity units S.U. - Standard Units SWS ID - Solid Waste Section Identification Number U - Analyte was analyzed for, but not detected above the minimum detectable concentration (MDC) or method detection limit (MDL). Prepared by: CSM Checked by: TAW Page 1 of 1 TABLE 6 GROUNDWATER FIELD RESULTS AND ANALYTICAL DETECTIONS FGD RESIDUE LANDFILL (No. 1809-INDUS) SEMIANNUAL WATER QUALITY MONITORING REPORT MARSHALL STEAM STATION DUKE ENERGY CAROLINAS, LLC, TERRELL, NC Parameter SWS ID Units Monitoring Wells 15A NCAC 02L Standard MS-08 MS-09 MS-10 MS-11 MS-12 MS-13 MS-14 MS-15 MS-16 pH 320 S.U. 5.6 6.5 5.1 5.3 4.9 5.0 5.9 6.1 6.0 6.5-8.5 Temperature 325 Deg C 19 19 17 18 15 17 16 19 18 NE Specific Conductance 323 µmhos/cm 41 98 31 51 22 59 65 324 75 NE Dissolved Oxygen - mg/L 7.10 8.71 6.85 6.09 7.23 4.83 7.00 9.30 7.42 NE Oxidation Reduction Potential 336 mV 393 316 402 358 490 460 416 362 381 NE Eh - mV 598.0 521.0 607.0 563.0 695.0 665.0 621.0 567.0 586.0 NE Turbidity 330 NTUs 1.9 1.2 3.60 2.20 9.10 3.6 3.2 5.9 4.0 NE Antimony 13 µg/L < 1 0.265 J < 1 < 1 < 1 < 1 < 1 0.153 J < 1 1 Arsenic 14 µg/L <1 <1 0.151J <1 <1 <1 0.184J 0.115J 0.208J 10 Barium 15 µg/L 39 51 103 79 77 118 55 361 96 700 Beryllium 23 µg/L <1 <1 <1 <1 <1 0.43J <1 <1 <1 4 Boron 428 µg/L < 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50 700 Cadmium 34 µg/L <1 <1 <1 <1 <1 <1 <1 0.049J <1 2 Calcium 375 mg/L 4.08 16.2 0.210 2.36 0.178 6.38 5.49 32.8 8.29 NE Chloride 301 mg/L 1.2 1.5 1.10 3.90 2.70 3.3 0.96 81 1.7 250 Chromium 51 µg/L 3.84 1.60 1.30 2.59 0.518 J < 1 0.213 J 19.5 4.22 10 Cobalt 53 µg/L < 1 < 1 0.804 J 0.138 J 1.12 < 1 < 1 0.106 J 0.394 J 1 Copper 54 µg/L < 1 < 1 < 1 < 1 < 1 < 1 < 1 < 1 1.94 1,000 Fluoride 312 mg/L 0.12 < 0.1 < 0.1 < 0.1 < 0.1 < 0.1 0.08 J < 0.2 0.21 2 Iron 340 µg/L 72 23 J 1110 193 J 197 20 J 14 J 547 1530 300 Lead 131 µg/L < 1 < 1 0.611 J 0.07 J 0.261 J 0.059 J < 1 0.235 J 0.584 J 15 Lithium - µg/L < 5 <5 <5 <5 <5 <5 <5 2 J <5 NE Magnesium 376 mg/L 1.80 1.39 0.505 1.260 0.539 1.47 1.16 15.7 3.90 NE Manganese 342 µg/L 11 3 J 36 13 18 15 < 5 6 27 50 Mercury 132 µg/L < 0.05 < 0.05 < 0.05 < 0.05 0.01 J 0.02 J < 0.05 0.01 J < 0.05 1 Molybdenum 397 µg/L < 1 0.181 J 0.336 J < 1 < 1 < 1 < 1 < 1 0.306 J NE Nickel 152 µg/L 0.555 J < 1 1.2 1.2 0.298 J 0.268 J < 1 24.7 2.01 100 Nitrate (as N) 303 mg-N/L 0.16 0.11 0.22 0.02 J 0.04 J 0.85 0.01 J 2.1 0.61 10 Selenium 183 µg/L <1 <1 <1 <1 <1 <1 <1 <1 <1 20 Silver 184 µg/L <1 <1 <1 <1 <1 <1 <1 <1 <1 20 Sulfate 315 mg/L 0.18 0.65 0.09 J 0.25 0.14 0.12 0.09 J 0.67 0.39 250 Thallium 194 µg/L <1 <1 <1 <1 0.042J <1 <1 <1 <1 2 Total Dissolved Solids 311 mg/L 54.0 86.0 < 25 35.00 < 25 45.0 67.0 299 82.0 500 Vanadium 209 µg/L 4.00 2.47 2.62 0.294 J 0.433 J 0.421 J 2.27 2.89 6.31 7 Zinc 213 µg/L 1 <5 1 <5 7 4 J 4 J <5 <5 4.1 6 1,000 Notes: 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). Analytical data presented in this table reflect the Duke Energy Biological Analytical Data Storage System (BASS) as of 11/15/2023. Samples collected by Duke personnel on September 11, 2023. 15A NCAC 02L Standard refers to Class GA Standards as found in 15A NCAC 02L. 0202 Groundwater Quality Standards (last amended on April 1, 2022) A blank cell means there is no relevant information. <- Concentration not detected at or above the adjusted reporting limit. µg/L - micrograms per liter µmhos/cm - micromhos per centimeter Deg C - degrees Celsius J - Value is estimated. The result is below the reporting limit or potentially biased based on data validation. MDL - Laboratory Method Detection Limit; MDL values presented are for samples not diluted by the laboratory during analysis. mg/L - miligrams per liter mg-N/L - milligrams Nitrogen per liter mV - Millivolts NCAC - North Carolina Administrative Code NE - Not Established NTU - nephelometric turbidity units S.U. - Standard Units SWS ID - Solid Waste Section Identification Number U - Analyte was analyzed for, but not detected above the minimum detectable concentration (MDC) or method detection limit (MDL). Prepared by: TAW Checked by: CSM Page 1 of 1 TABLE 7 FIELD AND ANALYTICAL RESULTS THAT EQUAL OR EXCEED GROUNDWATER QUALITY STANDARDS FGD RESIDUE LANDFILL (No. 1809-INDUS) SEMIANNUAL WATER QUALITY MONITORING REPORT MARSHALL STEAM STATION DUKE ENERGY CAROLINAS, LLC, TERRELL, NC Parameter Sample ID September 2023 Concentration Units 15A NCAC 02L Standard Historical Concentration Range Significance pH MS-8 5.6 S.U. 6.5 - 8.5 4.9 - 6.92 pH is consistent with the range of historical readings at MS-8 MS-10 5.1 3.6 - 5.89 pH is consistent with the range of historical readings at MS-10 MS-11 5.3 4.3 - 5.8 pH is consistent with the range of historical readings at MS-11 MS-12 4.9 4.4 - 5.34 pH is consistent with the range of historical readings at MS-12 MS-13 5.0 4.2 - 5.5 pH is consistent with the range of historical readings at MS-13 MS-14 5.9 5.49 - 6.2 pH is consistent with the range of historical readings at MS-14 MS-15 6.1 5.66 - 9.8 pH is consistent with the range of historical readings at MS-15 MS-16 6 5.2 - 6.43 pH is consistent with the range of historical readings at MS-16 Chromium MS-15 19.5 µg/L 10 11.5 - 29.7 Chromium is consistent with the range of historical concentrations at MS-15 Cobalt MS-12 1.12 µg/L 1 0.752 J - 1.6 J Cobalt is consistent with the range of historical concentrations at MS-12 Iron MS-10 1110 ug/L 300 28 - 2353 Iron is consistent with the range of historical concentrations at MS-10 MS-15 547 11.5 - 1894 Iron is consistent with the range of historical concentrations at MS-15 MS-16 1530 29.5 - 57572 Iron is consistent with the range of historical concentrations at MS-16 Notes: Analytical data presented in this table reflect the Duke Energy Biological Analytical Data Storage System (BASS) as of 11/15/2023. 15A NCAC 02L Standard refers to Class GA Standards as found in 15A NCAC 02L .0202 Groundwater Quality Standards, last amended on April 1, 2022. Historical ranges are based on data from the monitoring events that occurred between September 2006 and September 2022. µg/L - micrograms per liter S.U. -Standard Units Prepared by: TAW Checked by: CSM Page 1 of 1 Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina APPENDIX A FIELD SAMPLING FORMS L7 synTerra Science & Engineering Consultants ❑CAMA ❑CCR ❑Landfill ❑NPDES ❑ DGW❑ASW ❑LRB SPECIAL STUDYto KE FIELD SAMPLING LOG ENE Site: MSS Well/SW ID: G1 _ Lec-c6a-E'- Date: 9-27-z3 El GROUNDWATER SAMPLE [:]SURFACE WATER SAMPLE ❑LEACHATE SAMPLE ❑WLO ❑ WELL DEVELOPMENT FIELD STAFF: C157- COMPANY: DUKE ENERGY ❑ OTHER: WEATHER: ❑SUNNY ❑ PARTLY CLOUDY ❑ OVERCAST ❑ RAIN ❑SNOW AIR TEMP: 'F FIELD METER TYPE/ SERIAL #: 15'tq lG TURBIDI METER TYPE/ SERIAL #:_ 337M START PURGE TIME: Ot q Z SAMPLE COLLECTION TIME: 0950 PUMP/TUBING INTAKE DEPTH: _ (ft) DEPTH TO WATER: "' N• S (ft) MOLT FACTOR *: 0.163 ['(radiusll2)2 3:14'7.48J WELL DIAMETER: (in) HEIGHT OF WC: (ft) WELL VOLUME: (gal) WELL DEPTH: (ft) TOTAL VOLUME PURGED: A SU (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: a a ° 1� QCrP ❑ Tubin /Pump Inspected I 00 I (see) I (Sec) I Low Flow Sampling Stabilization Criteria ❑Good (Tubing Bad ❑Pump Bad ❑Changed/Cleaned ❑Correct Next Event • PH f 0.1 standard unit • Speck Conductance t 5% in NS/cm Additional Notes: • DO f 0.2 mg/L or 10% saturation • 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) CC) W (mg/L) (x.xx) (PS/cm) W (su) (x.xx) (mV) W (NTU) (x.x) O$t{N Z50 01LS 1`6 7.75 qe) et K6 2 372 (I.L 0646 2S0 0.50 I 7.61-/ Not 5 °!-61 3s t5:Y 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? AYES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES ❑ NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE?Q YES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR J�' e 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH lne Minor Strong ADDITIONAL NOTES: APPEARANCE F�ar Cloudy Turbid Red/Iron Film on Surface Sheen 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 1.2 Revised 09/29/2022 HPB F-]CAMA F-]CCRF-]Landfill [:]NPDES ❑ DGW❑ASW F-]LRB ❑ SPECIAL STUDY, Site: Well/SW ID: tDUKE E1 ERGG Date: WATER FLOW VOLUME TEMPERATURE DO SPECIFIC pH ORP TURBIDITY LEVEL RATE REMOVED CONDUCTANCE TIME (FT) (mUmin) (gallons OR mL) VC) (mg/L) I (PS/cm) (su) (mv) (NTU) (x.xx) W (x.xx) (x) (x.xx) (x) (x.xx) (x) (x.x) Version 1.2 Revised 09/29/2022 HPB [:]CAMA [—]CCR❑Landfill F]NPDES ❑ DGWFIASW [—]LRB ❑ SPECIAL STUDY. FIELD SAMPLING LOG Site: M5 Well/SW ID: M S-12� P DUKE ENERGY Date: 7- 2 7- Z 3 GROUNDWATER SAMPLESURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: (7 Z— COMPANY: a DUKE ENERGY ❑ OTHER: WEATHER: ❑SUNNY ❑ PARTLY CLOUDY ❑ OVERCAST ❑ RAIN []SNOW AIR TEMP: `F FIELD METER TYPE/ SERIAL #: gS[48L TURBIDIMETER TYPE/ SERIAL #: 331'q START PURGE TIME: Of? KU SAMPLE COLLECTION TIME: 0450 PUMP/TUBING INTAKE DEPTH: yn (ft) DEPTH TO WATER: K(s•NS (ft) MULT FACTOR *: 0.163 ['(radius/12)2'3.147.48] WELL DIAMETER: 7.0 (in) HEIGHT OF WC: 5.13 (ft) WELL VOLUME: 0, Se( (gal) WELL DEPTH: 51. 5 8 (ft) TOTAL VOLUME PURGED: 6.13 Z (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: P R ❑ Tubin /Pump Inspected I (ase) I (sec) (sec) I Low Flow Sampling Stabilization Criteria OGood Tubing Bad ❑Pump Bad ❑Changed/Cleaned ❑Correct Next Event PH t 0.1 standard unit Additional Notes: Specific Conductance t 5% in VS/cm PdDOe Turbidity less than 10 NTUs saturation 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) W (mg/L) (x.xx) (PS/CM) W (su) (x.xx) (mv) (x) (NTU) (x.x) oggt,l d7.2S Itio 0.50 la g_Z5 Ct 3 S.6 2- 397 2- 3 Ok47 `17.15 lZC 132 to `f t 5159 3113 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?YES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR & e 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH 6-ne Minor Strong ADDITIONAL NOTES: APPEARANCE ee> 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 6,,I,c 1 (4&441 Version 1.2 Revised 09/29/2022 HPB F-]CAMA F-]CCRF-]Landfiill F-]NPDES ❑ DGW[—]ASW 7LRB SPECIAL STUDY Site: Well/SW ID: Date: .&, DUKE '*' ENERGI WATER FLOW VOLUME TEMPERATURE DO SPECIFIC pH ORP TURBIDITY LEVEL RATE REMOVED CONDUCTANCE TIME (FT) (mL/min) (gallons OR mL) VC) (mg/L) (PS/cm) (su) (mv) (NTU) (x.xx) (x) (x.xx) (x) (x.xx) (x) (x.xx) (x) (x.x) Version 1.2 Revised 09/29/2022 HPB OCAMA F—]CCR❑Landfill [:]NPDES DGW[—] ASWF—]LRB ❑ SPECIAL STUDY. Site: NtS5 FIELD SAMPLING LOG Well/SW ID: /14S-9 •t, DUKE ENERGY Date: q-Z-?-Z 3 GROUNDWATER SAMPLE SURFACE WATER SAMPLE 1:1LEACHATE SAMPLE ❑ WLO [:]WELL DEVELOPMENT FIELD STAFF: C WEATHER: []SUNNY ❑PARTLYCLOUDY ❑OVERCAST ❑RAINSNOW AIRTEMP: "F COMPANY: 0 DUKE ENERGY FIELD METER TYPE/ SERIAL #: °!� ❑ OTHER: TURBIDIMETER TYPE/ SERIAL #: 37Z"C START PURGE TIME: (UU't- SAMPLE COLLECTION TIME: fol± 1020 SO.Sv (ft) K3.117 (ft) MULT FACTOR" 0.163 ['(radius/12)2 3.14'7.48] PUMP/TUBING INTAKE DEPTH: DEPTH TO WATER: WELL DIAMETER: ?.v (in) HEIGHT OF WC: (ft) WELL VOLUME: 1. s6 (gal) WELL DEPTH: 53 •J (ft) TOTAL VOLUME PURGED: 0, SO (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: ' a o ❑ Tubin m /Pup Inspected I (") I (Sec) I (sec) ❑Good [Tubing Bad ❑Pump Bad ❑Changed/Cleaned [—]Correct Next Event Additional Notes: Low Flow Sampling Stabilization Gnteria • pH • Specmc Conductance • DO • Turbidity t 0.1 standard unit f 5% in pS/cm t 0.2 mg1L or 10% saturation less than 10 NTUs 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) (IC) W (mg/L) (x.xx) (PS/cm) W (su) (x.xx) (mv) W (NTU) (x.x) 1004 fl(3.71 (00 to o &SS /v( 4./ 3Ti ('25 ruu� y,cv /uo ZU 11 8•51 qT 3 M z o IOro gq.oq too 61,30 ( q 8-66 17 b•'(8 37- 10(3 '( .04 luu o.'{6 ( I r*7v `J 6•Sl 370 r-v 101(e 4q,01 IUU s.Sv 11 S.71 $ 6•57- 16 I.2 PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE 15 FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES D NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? YES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES PNO 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 Oe 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH to a Minor Strong ADDITIONAL NOTES: APPEARANCE bar 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.z Revised oslzalzulz Arts DCAMA F�CCR❑Landfill F—]NPDES ❑ DGW❑ASW F—]LRB ❑ SPECIAL STUDY Site: Well/SW ID: DUKE ENERGY Date: 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) W (mg/L) (x.xx) (PS/cm) (x) (su) (x.xx) (mv) W (NTU) (x.x) Version 1.2 Revised 09/29/2022 HPB ❑CAMA❑CCR❑Landfill ❑NPDES❑DGW❑ASW❑LRB�SPECIAL STUDY FG/� FIELD SAMPLING LOG � DUKE ENERGY Site: MSS Well/SW ID: MS -co Date: y-Z?-L3 ❑GROUNDWATER SAMPLE [:]SURFACE WATER SAMPLE ❑LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: r, -22— COMPANY: Q DUKE ENERGY ❑ OTHER: WEATHER: []SUNNY ❑ PARTLY CLOUDY ❑ OVERCAST ❑RAIN ❑SNOW AIR TEMP: "F FIELD METER TYPE/ SERIAL #: 951r166 TURBIDIMETER TYPE/ SERIAL #: 33-41 START PURGE TIME: 0111 SAMPLE COLLECTION TIME: Og3S PUMP/TUBING INTAKE DEPTH: Z0. SK (ft) DEPTH TO WATER: 7-0-&0 Ift) MULT FACTOR ": 0.163 ['(radius/12)2 3.14'7.48] WELL DIAMETER: ZO (in) HEIGHT OF WC: 3, 3K (ft) WELL VOLUME: 0_SK (gal) WELL DEPTH: Z3. 34 (ft) TOTAL VOLUME PURGED: a6U (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: P R D Tubing/Pump Inspected cPsi) (sec) (sec) OGood LTubing Bad ❑Pump Bad ❑Changed/Cleaned ❑Correct Next Event Additional Notes: Low Flow Sampling Stabilization Criteria • pH • Specific Conductance • DO • Turbidity t 0.1 standard unit t 5% in NS/cm f 0.2 mgrL or 10% saturation 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) W (mg/L) (x.xx) (PS/cm) W (Sul (x.xx) (mv) W (NTU) (x.x) On Z0.36 ("ID 0.15 1R•77 3'1 y-15 `13 Ifs C"M Zo•5v 0.36 17 6-411 30 5.oz, 100 S.( 01116 70•S0 p.NS 17 6.g2 Zq 5,041 3-1'y 3.Z Uh31 ZV40 1 110 0.60 17 -g 31 505 yvt 3.6 PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES Q NO WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? QYES ❑ 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 V;e 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 1.2 Revised 09/29/2022 HPB [:]CAMA [—ICCR Landfill FNPDES ❑ DGW❑ASW 1-7LRB SPECIAL STUDY Site: Well/SW ID: Date: •%� DUKE `r ENERGY TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY (FT) (x.xx) (mUmin) W (gallons OR mL) (x.xx) VC) (x) (mg/L) (x.xx) (PS/cm) W (su) (x.xx) (mv) W (NTU) (x.x) Version 1.2 Revised 09/29/2022 HPB ❑CAMA ❑CCRdandfill ❑NPDES ❑ DGW❑ASW nLRB ❑ SPECIAL STUDY, DUKE ENERGY Site:Nw,44a Well/SW ID: 1VI5 -1( Date: q 07 Z3 ROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT FIELD STAFF: U COMPANY: gDUKE ENERGY ❑ OTHER: WEATHER: ❑SUNNY ❑ PARTLY CLOUDY I `� OVERCAST []RAIN FISNOW AIR TEMP: (D 3 °F FIELD METER TYPE/ SERIAL#: % 93 TURBIDIMETER TYPE/ SERIAL #: 33aa- START PURGE TIME: 3 2SAMPLE COLLECTION TIME: O PUMPITUBING INTAKE DEPTH: 3�f•50 (ft) DEPTH TO WATER: .3 5 79 (ft) MULT FACTOR': 0.163 [*(radius/12)2*3.14*7.48] WELL DIAMETER: 2.oO (in) HEIGHT OF WC: 5.Ry (ft) WELL VOLUME: a G 7 (gal) WELL DEPTH: q(. 7.2- (ft) TOTAL VOLUME PURGED: 0.76 (9a1) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: e /0 F 5 ° �ubin /Pump Inspected I (Ps) I o-C) I (sec) I Low Flow Sampling Stabilization Criteria Good [Tubing Bad ❑Pump Bad ❑Changed/Cleaned ❑Correct Next Event - PH t 0.1 standard unit Additional Notes: ��L, • Speck Conductance t 5% in pS/cm Y F V _ Z(�ZJ�-I Z7—� d7tF�(� • DO t 0.2 mg/L or 10% saturation • Turbidity less than 10 NTUs TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE PH ORP TURBIDITY (FT) (x.xx) (mUnnin) (x) (gallons OR mL) (x.xx) CC) (x) (mg/L) (x.xx) (PS/CM) (x) (su) (x.xx) (mv) (x) (NTU) (x.x) Nd 5.15 120 0.Y . 3 S5 5,3X 3VI 70 01 •15 / a 0. 0 l &4 S, (p yf _f OS 5 /Zo 0/ S , / �{ 50 9 9 3515 120 + 6.09 . A IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES O 0 IS A TURBIDITY METER DUPLICATE REQUIRED? []YES v NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ N FINAL SAMPLE OBSERVATIONS: DETECTED ODOR o H2S ODOR STRENGTH ems/ - Minor ADDITIONAL NOTES: APPEARANCE I f cloudy O 'E WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? S ❑ NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE?❑ YES 210 DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) Petroleum Earthy Musty Undetermined Strong Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRYE PAD GOOD 'AAD NONE GOOD ,BAD NONE GOOD B D NONE GOOD BAD NONE GOOD /BAD NONE VA 7 Version 1.2 Revised 09/29/2022 HPB F-]CAMA F—]CCRF-]LandfiII F—]NPDES ❑ DGWFIASW F—]LRB ❑ SPECIAL STUDY Site: Well/SW ID: Date: i WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY TIME (FT) (x.xx) (mL/min) (x) (gallons OR mL) (x.xx) (°C) (x) (mg/L) (x.xx) (PS/cm) (x) (su) (x.xx) (mv) (x) (NTU) (x.x) Version 1.2 Revised 09/29/2022 HPB F]CAMA F-]CCR gLandfill F-]NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY. fin FIELD SAMPLING LOG DUKE ENERG' Site: Well/SW ID: S — Z Date: q 3 ROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑LEACHATE SAMPLE [:]WLO DWELL DEVELOPMENT FIELD STAFF: 7 K COMPANY: DUKE ENERGY ❑ OTHER: WEATHER: ❑SUNNY ❑PARTLY CLOUDY E� OVERCAST ❑RAIN nSNOW AIRTEMP:10-5 'F FIELD METER TYPE/ SERIAL #: R771n 3 TURBIDIMETER TYPE/ SERIAL #: 39 22, START PURGE TIME: l0 2 ( SAMPLE COLLECTION TIME: 60 2 U PUMP/TUBING INTAKE DEPTH: 4+ So (ft) DEPTH TO WATER: 3 �I S (ft) MULT FACTOR *• 0.163 [•(radius/12)2'3.14'7.48] WELL DIAMETER: 7 ::)&2 (in) HEIGHT OF WC: 7 (ft) WELL VOLUME: / / (a (gal) WELL DEPTH: 3% © % (ft) TOTAL VOLUME PURGED: ,?• 7Zi (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: f SAMPLING METHOD: P MP SETTING: R ubin /Pump Inspected (psi) (sec) (se-) Low Flow Sampling Stabilization Criteria Iv, — u I uu"19 Eau Urump baa Ucnanged/Gleaned UCorrect Next Event Additional Notes: pH Specific Conductance DO Turbidity t 0.1 standard unit f 5% In pS/cm t 0.2 mg/L or 10% saturation less than 1 n NTIIc TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY /a S. �Sd � 6 (FT) (x.xx) a Z �Z Y-62 Y-6Z (mL/min) W .900 o mod 0 06 (gallons OR mL) (x.xx) 0.70 >0 d . c>2, SO a CC) W 5 I's —.7,23 /S (mg/L) (x.xx 7 2 y 7. - , 3 (pS/cm ) (x) I �. 1=2119- ao2 (su) (x.xx) yd 9s 7t��/ 8 �f (mv) (x) F7 _34 9 90 (NTU) (x.x) z 3 2./ .Xy �0� 5 0 r PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES Y PO IS A TURBIDITY METER DUPLICATE REQUIRED? MYESYNO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES N FINAL SAMPLE OBSERVATIONS: DETECTED ODOR None H2S ODOR STRENGTH None Minor ADDITIONAL NOTES: APPEARANCE Clear Cloudy WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? E'']YYES [I NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE?�(ES NO O DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) Petroleum Earthy Musty Undetermined Strong Turbid Red/Iron Film nn Sivraca Shaun ra.,.,.. WELL TAG PROTECTIVE CASING LOCK DUST CAP CONCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD -BD NONE GOOD BAD NONE GOOD BAD NONE Floc Version 1.2 Revised 09/29/2022 HPB [-]CAMA F-]CCR❑Landfill F-]NPDES ❑ DGW❑ASW ❑LRB ❑ SPECIAL STUDY, Site: Well/SW ID: Date: TIME WATER LEVEL (FT) (x.xx) FLOW RATE (mL/min) W VOLUME REMOVED (gallons OR mL) (x.xx) TEMPERATURE VC) (x) DO (mg/L) (x.xx) SPECIFIC CONDUCTANCE (NS/cm) (x) p H (su) (x.xx) ORP (mv) (x) TURBIDITY (NTU) (x.x) Version 1.2 Revised 09/29/2022 HPB FICAMA RCCR Landfill ONPDES ❑ DGWRASW ❑LRB a SPECIAL STUDY. FIELD SAMPLING LOG [DUKE ENERG Site: Ma4d Well/SW ID: MS-(3 Date: I/Z71Z3 -11— GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE WLO WELL DEVELOPMENT FIELD STAFF: S WEATHER: QSUNNY El PARTLY CLOUDY [OVERCAST n RAIN SNOW AIR TEMP: (12 'F COMPANY: 7DUKE ENERGY FIELD METER TYPE/ SERIAL #: z ❑ OTHER: TURBIDIMETER TYPE/ SERIAL #: 3 a% START PURGE TIME: 0 FSo SAMPLE COLLECTION TIME: PUMPITUBING INTAKE DEPTH: 39 00(ft) DEPTH TO WATER: _ 3(.55 (ft) MULT FACTOR *• 0.163 [*(radius/12)2*3.14'9.48j WELL DIAMETER: 2. 06 (in) HEIGHT OF WC: 9 7 (ft) WELL VOLUME: I. l# Z (gal) WELL DEPTH: y 52- (ft) TOTAL VOLUME PURGED: 0,5D (gal) TYPE OF PUMP: PURGE METHOD: SAMPLING METHOD: PUMP SETTING: J ubin /Pump Inspected L Good [Tubing Bad Pump Bad Additional Notes: Bladder ) Peristaltic I 12 Volt Grundfos Other ( ) 2o`�os° (psi) tse°t o. Low Flow Sampling Stabilization Criteria Changed/Cleaned nCorrect Next Event pH t 0.1 standard unit • Specific Conductance t 5% In pS/cm DO t 0.2 mg1L or 10% saturation • Turbidity less than in KIT] Ic TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC CONDUCTANCE pH ORP TURBIDITY SS 48`S l BRCS (FT) x (x.xx) �'0 31- 3r. Jv C. �0 (mL/min) (x) ZL 2 IZO (gallons OR nnL) (x.xx) p 6 0,56 G. G• (°C) (x) / I (mg/L) (x.xx) f z y 3 (NS/cm ) (x) q 5a (su) (x.xx) (mv) W (NTU) (x.x) 5 8 5.63 � S, oZ Gr0 3, U PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? IS A TURBIDITY METER DUPLICATE REQUIRED? ❑ YES -]YES WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? 15%? Q YES NO DUPLICATE 1 CE" ES ❑ NO FINAL SAMPLE OBSERVATIONS: (NTU) DUPLICATE 2 (NTU) DETECTED ODOR Non 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH Minor Strong ADDITIONAL NOTES: APPEARANCE Cie Cloudy Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG GOOD BAD NONE LOCK I DUST CAP CONCRETE PAD GOOD BAD I NONE GOOD BAD NONE I GOOD I BAD NONE Version 1.2 Revised 09/29/2022 HPB [-]CAMA [-]CCR❑Landfill [-�NPDES a DGW❑ASW [:]LRB[—] SPECIAL STUDY_ cite• Well/SW ID: Date: �0 FLOW RATE (mUmin) (x) VOLUME REMOVED (gallons OR ML) (x.xx) TEMPERATURE VC) (x) DO (mg/L) (x.xx) SPECIFIC CONDUCTANCE (Ns/cm) (x) P H (su) (x.xx) ORP (mv) (x) TURBIDITY (NTU) (x.x) TIME WATER LEVEL (FT) (x.xx) Version 1.2 Revised 09/29/2022 HPB ❑CAMA ❑CCR41Landfill ❑NPDES ❑ DGW❑ASW F—]LRB ❑SPECIAL STUDY FIELD SAMPLING LOG 1P DUKE ENERG) Site: MoW Well/SW ID:s ' Date: Z7 L3 F12GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑LEACHATE SAMPLE ❑ WLO [:]WELL DEVELOPMENT FIELD STAFF: X WEATHER: [-]SUNNY PARTLY CLOUDY ❑ OVERCAST ❑RAIN IS OW AIR TEMP: -F COMPANY: DUKE ENERGY FIELD METER TYPE/ SERIAL #: F/<:i ❑ OTHER: TURBIDIMETER TYPE/ SERIAL #: 332.2 START PURGE TIME: 11 SAMPLE COLLECTION TIME: MS PUMPITUBING INTAKE DEPTH: I-S % (ft) DEPTH TO WATER: G-VP (ft) MULT FACTOR': 0.163 [•(radius/12)2*3.14.7.48] WELL DIAMETER: 2 ' O (in) HEIGHT OF WC: %- So2 (ft) WELL VOLUME: WELL DEPTH: LI ff• 3 $ (ft) TOTAL VOLUME PURGED: O' XS (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: PUMP SETTING: P /0 R D (ubin /Pump Inspected (psi)(see) *-) Good [Tubing Bad ❑Pump Bad ❑Changed/Cleaned ❑Correct Next Event Additional Notes: Low Flow Sampling Stabilization Criteria • pH • Specific Conductance • DO • Turbidity f 0.1standard unit t 5% in NSlcm t 0.2 mg/L or 10% saturation 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) CC) W (mg/L) (x.xx) (PS/CM) (x) (su) (x.xx) (mv) (x) (NTU) (x.x) 1 37t.2 (e6 d- 0 7/1 5.8-1 VW, 7 a l ff 3 7 0 37l2 37--u- 7 (l Q (� 106 d. SS , 7 7.r x o 3 CAS &S S'g- 5 Fs W6 W7 _3 -9. k IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES f O IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES ENO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ N FINAL SAMPLE OBSERVATIONS: DETECTED ODOR H2S ODOR STRENGTH Minor ADDITIONAL NOTES: APPEARANCE ear Cloudy WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? � ES [I NO � ❑ IS THE LOCATION FIELD VEHICLE ACCESSIBLE? YES NO O DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) Petroleum Earthy Musty Undetermined Strong Turbid Red/Iron Film on Surface Sheen Fines Floc WELL TAG PROTECTIVE CASING LOCK DUST CAP 50 NCRETE PAD GOOD BAD NONE GOOD BAD NONE GOOD AD NONE GOOD BAD NONE G D I BAD NONE Version 1.2 Revised 09/29/2022 HPB F-�CAMA F-]CCR[-]Landfill F-]NPDES ❑ DGW❑ASW FILRB ❑ SPECIAL STUDY, Site: Well/SW ID: Date: • WATER FLOW VOLUME TEMPERATURE DO SPECIFIC pH ORP TURBIDITY LEVEL RATE REMOVED CONDUCTANCE TIME (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 1.2 Revised 09/29/2022 HPB ❑CAMA ❑CCR❑Landfill ❑NPDES ❑ DGW❑ASW ❑LRB 0 SPECIAL STUDY F6-6 FIELD SAMPLING LOG ot DUKE ENE ) Site: M55 Well/SW ID: MS-/5 Date: ❑GROUNDWATER SAMPLE❑SURFACE WATER SAMPLE ❑LEACHATE SAMPLE ❑WLO ❑ WELL DEVELOPMENT FIELD STAFF: (')'L COMPANY: Q DUKE ENERGY ❑ OTHER: WEATHER: ❑SUNNY ❑PARTLY CLOUDY ❑OVERCAST ❑RAINSNOW AIR TEMP: "F FIELD METER TYPE/ SERIAL #: R 158t, TURBIDIMETER TYPE/ SERIAL M 3321 START PURGE TIME: 1100 SAMPLE COLLECTION TIME: 117,0 PUMP/TUBING INTAKE DEPTH: 60.58 (ft) DEPTH TO WATER: K3.31-- (ft) MULT FACTOR *• 0.163 [*(radius/12)2*3.14`7;48] WELL DIAMETER: 7.(2 (in) HEIGHT OF WC: I`1.74 (ft) WELL VOLUME: 3. 2 Z (gal) WELL DEPTH: 6 3.O S (ft) TOTAL VOLUME PURGED: I Lt) (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other ( ) PURGE METHOD: SAMPLING METHOD: i PUMP SETTING: P R ° Tubing/Pump /Pump Inspected (psi) (see) (see) QGood [Tubing Bad [:]]Pump Bad ❑Changed/Cleaned ❑Correct Next Event Additional Notes: Low Flow Sampling Stabilization Criteria • pH • Specific Conductance • DO • Turbidity t 0.1 standard unit ± 5% In NS/cm t 0.2 mg/L or 10% saturation 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) CC) (x) (mg/L) (x.xx) (PS/cm) (x) (su) (x.xx) (mv) (x) (NTU) (x.x ) Ito4 (i3.so 7C7 010 21 9,60 33-7 6.&T 3SS ZZ.'7 ltcn d4.D6 Tw 0.Ko 7.45 g.s$ 1 3zt( 6.12 360 tr.S I'w KN,I0 Zua 0.60 l q q•2g 3L6 6_v9 2 12.2 it(3 4L1.10 arn, 0A0 l 9.3u 320 6.06 3 Sq ff•G 11(6 HN•lU ZOO 1(w 19 9.3( 3Z3 b•US 4-2 11(� WN tv I-'W Iq v 6.06 3G2 S.Ct 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? E]YES El IS A TURBIDITY METER DUPLICATE REQUIRED? DYES R NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE? Fj YES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) FINAL SAMPLE OBSERVATIONS: DETECTED ODOR pe 1-12S Petroleum Earthy Musty Undetermined ODOR STRENGTH 1 one Minor Strong ADDITIONAL NOTES: APPEARANCE Car 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 f Version 1.2 Revised 09/29/2022 HPB F—]CAMA F—]CCR❑Landfill F—]NPDES ❑ DGW❑ASW [—]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) (mL/min) (x) (gallons OR mL) (x.xx) VC) (x) (mg/L) (x.xx) (uS/Cm) (x) (su) (x.xx) (mv) (x) (NTU) (x.x) Version 1.2 Revised 09/29/2022 HPB [:]CAMA [--]CCR ❑Landfill ONPDES DGW[:]ASW [--]LRB 0 SPECIAL STUDY FGD FIELD SAMPLING LOG ENERGY Site: 11455 Well/SW ID: M s -1! Date: 7-2-?'Z3 El GROUNDWATER SAMPLE ❑SURFACE WATER SAMPLE ❑ LEACHATE SAMPLE WLO WELL DEVELOPMENT FIELD STAFF: C)" WEATHER: ❑SUNNY ❑PARTLY CLOUDY ❑OVERCAST ❑RAIN SNOW AIRTEMP: °F COMPANY: F/ DUKE ENERGY FIELD METER TYPE/ SERIAL #: `�StQijC ❑ OTHER: TURBIDIMETER TYPE//SERIAL #: 33 of START PURGE TIME: IOZB SAMPLE COLLECTION TIME: /UKS PUMPITUBING INTAKE DEPTH: 3q.11 (ft) DEPTH TO WATER: 2'7�3 (ft) MULT FACTOR *• 0.163 [*(radius/12)2*3.14.7.48] WELL DIAMETER: 2 (in) HEIGHT OF WC: _ 16. Z WELL DEPTH: 17.Ki 1 (ft) WELL VOLUME: 1,67 (gal) (ft) TOTAL VOLUME PURGED: 0. (fS (gal) TYPE OF PUMP: Bladder Peristaltic 12 Volt Grundfos Other PURGE METHOD: SAMPLING METHOD: i PUMP SETTING: R ° 0 Tubin /Pump Inspected 1.(PSI) (sec) (see) Low Flow Sampling Stabilization Criteria ©Good []Tubing Bad Pump Bad Changed/Cleaned Correct Next Event pH f 0.1'standard unit Additional Notes: Speck Conductance t 5% In pS/cm • DO :k 0.2 mg/L or 10% saturation • Turbidity ram..., 6— , TIME I43t WATER LEVEL (FT) (x.xx) Z�SI FLOW RATE (mL/min) (x) $O VOLUME REMOVED (gallons OR mL) (x.xx) b.tv TEMPERATURE (°C) W DO (mg/L) (x.xx) SPECIFIC CONDUCTANCE (x) 7°I 77 -76 77 75 BACK OF THIS SHEET pH ORP TURBIDITY (x.xx) (x) (NTU) (x.x) 6.3Z 353 tq t�K 27.8u fst7 0.20 S-AR 01 C' 36� is-v Iv;� 27:q; Bo iso 7.5b i,.at 37 L b 2 foHO Z7.gS 6.35 l$ 7 Sl 5:917 377 N.2, (°`13 27.65 So 7.K S.aS 3fit lio PLEASE REFER TO THE IF THE CHART ABOVE IS Fill I IJ KtutvtLUPMENT NEEDED (>10 NTUS)? U YES 0 NO. IS A TURBIDITY METER DUPLICATE REQUIRED? YES 0 NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES NC FINAL SAMPLE OBSERVATIONS: DETECTED ODOR lJ" 1-12S ODOR STRENGTH Minor ADDITIONAL NOTES: APPEARANCE ZZ Cloudy WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? AYES ❑ NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE?.E] YES Q NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) Petroleum Strong Turbid Earthy Red/Iron Musty Undetermined Film on Surface Sheen Fine Floc UST CAP CONCRETE PAD BAD NONE GOOD BAD NONE version 1.2 Kevised 09/29/2022 HPB OCAMA F�CCR❑Landfill 0NPDES ❑ DGW❑ASW DLRB ❑ SPECIAL STUDY j.� DUKE ENERGY Site: Well/SW ID: Date: FLOW VOLUME SPECIFIC H ORP TURBIDITY TEMPERATURE DO CONDUCTANCE P RATE REMOVED mL/min) VC) (mglL) (NS/cm) (su) (mv) (NTU) ( (gallons OR mL) (x) (x.xx) (x) (x.xx) (x) (x.xx) (x) (x.x) TIME WATER LEVEL (FT) (x.xx) Version 1.2 Revised 09/29/2022 HPB ❑CAMA ❑CCRjLandfill ❑NPDES ❑ DGW ASW LRB SPECIAL STUDY Site: &5 —0 ❑GROUNDWATER SAMPLE FIELD STAFF: IK5 COMPANY: DUKE ENERGY ❑ OTHER: Well/SW ID: , 5 ) I WEATHER: DUKE � ENERGY Date: Z Z3 WATER SAMPLE ❑ LEACHATE SAMPLE ❑ WLO ❑ WELL DEVELOPMENT ❑SUNNY ❑PARTLY CLOUDY ❑i OVERCAST ❑RAIN ❑SNOW AIR TEMP: 67 3 *F FIELD METER TYPE/ SERIAL M 771913 TURBIDIMETER TYPE/ SERIAL #: 332 1 START PURGE TIME: 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: PURGE METHOD: SAMPLING METHOD: PUMP SETTING: ❑ Tubin /Pump Inspected (P52 ❑Good [Tubing Bad ❑Pump Bad ❑ Additional Notes: Bladder I Peristaltic 12 Volt (sec) I (sec) hanged/Cleaned ❑Correct Next Event Grundfos I Other( ) Low Flow Sampling Stabilization Criteria pH * 0.1 standard unit Specific Conductance t 5% in yS/cm DO t 0.2 mg/L or 10% saturation Turbidlty lwcs than 1n nlTI lc TIME WATER LEVEL FLOW RATE VOLUME REMOVED TEMPERATURE DO SPECIFIC pH ORP TURBIDITY CONDUCTANCE (FT) x (x.xx) (mLlmin) (x) (gallons OR mL) (x.xx) (C) (x) (mg/L) (x.xx) (PS/cm) (x) (su) (x.xx) (mv) (x) (NTU) (x.x) a� PLEASE REFER TO THE BACK OF THIS SHEET IF THE CHART ABOVE IS FULL IS REDEVELOPMENT NEEDED (>10 NTUS)? ❑ YES ❑ NO IS A TURBIDITY METER DUPLICATE REQUIRED? ❑YES ❑ NO IS THE TURBIDITY METER DUPLICATE TAKEN, WITHIN 15%? ❑ YES ❑ N FINAL SAMPLE OBSERVATIONS: DETECTED ODOR None 1-12S ODOR STRENGTH None Minor ADDITIONAL NOTES: APPEARANCE Clear Cloudv O WERE ALL SAMPLES ON ICE WITHIN 15 MINUTES? [:]YES ❑ NO IS THE LOCATION FIELD VEHICLE ACCESSIBLE?❑ YES Q"NO DUPLICATE 1 (NTU) DUPLICATE 2 (NTU) Petroleum Earthy Musty Undetermined Strong Turbid G PROT7BADNONE LOCK DUST CAP TGOODBAD NONE GOOD GOOD BAD NONE GOOD BAD NONE Karl/iron Gil..,.,., o.o.,..,. FLOC Sheen Fines CONCRETE PAD GOOD BAD NONE Version 1.2 Revised 09/29/2022 HPB [:]CAMA F�CCR❑Landfill ONPDES ❑ DGW❑ASW ❑LRB 0 SPECIAL STUDY Site: Well/SW ID: Date: FLOW RATE (mUmin) (x) VOLUME REMOVED (gallons OR mL) (x.xx) TEMPERATURE (°C) (x) DO (mg/L) (x.xx) SPECIFIC CONDUCTANCE (uS/cm) (x) p H (su) (x.xx) ORP (mv) (x) TURBIDITY (NTU) (x.x) TIME WATER LEVEL (FT) (x.xx) Version 1.2 Revised 09/29/2022 HPB [:JCAMA F-]CCR Landfill [—]NPDES ❑ DGW[--]ASW ❑LRB ❑ SPECIAL STUDY DAILY CALIBRATION LOCH Site: 'MGrrS�u�i� Date: om WEATHER: ❑SUNNY ❑PARTLY CLOUDY E4VERCAST FIELD PERSONNEL: SS ❑ RAIN ❑SNOW TEMPERATURE (APPROX): INSITU SERIAL #: Y7793 °F 2100Q SERIAL #: 3i2_ Revised 12/18/2018 KKH CAMA CCR E/ Landfill ONPDES ❑ DGW❑ ASW ❑ LRB ❑ SPECIAL STUDY DU VE ENERGY-. DAILY CALIBRATION LOG Site: Date: q/Z7/1 Field Personnel: �5ffS Barometric pressure (mmHg) Chart DO (mg/L) Meter Reading (mg/L) %Saturation (%Sat). Within ± 0.5? Dissolved Oxygen Time: -7,' `3 Temperature oC ( ) 7q&,0 �q�r .y7 q'RO $.q0 g.q2- / 00 33 Y N a N j -,y Calibration Check as Live Iq.72- Reading Post Calibration-Zt� Date: q 7 Z3 r�d •S(a -71t4-5 l 7,20 /J0,KS ay N Time: TurbiditV Time: Post Calibration - Date: yZ3 Time: Acceptance Meter Reading Within ± Standard (NTU) Range (NTU) (NTU) 5%? 160 16-/" F-7 / '7 -7 Y N D IN Daily Turbidity Meter BLANK DI Water (NTU) Less than 0.10 NTU? Date: Q Z7 2 3 N Time: 7- 33 Revised 12/18/2018 KKH F_]CAMA F_]CCRF,�LandfiII NPDES ❑ DGWF_]ASW ❑LRB a SPECIAL STUDY F > DAILY CALIBRATION LOG Site: MSS Date: q-"Z7-23 c�DUKE ENERGY FIELD PERSONNEL:_(�SZ WEATHER: ❑SUNNY ❑PARTLY CLOUDY ❑ OVERCAST ❑ RAIN []SNOW TEMPERATURE (APPROX): - INSITU SERIAL#: 951R$b F 2100Q SERIAL #: 331,9 H Buffer Chart Meter Time:y *6 ou Lot Number Expiration Temperature pH Reading Within # (°C) (Su) (su) 0.1 su? 7.00 su 7 v 156 06-30-24 I& 6 1 7.007- 70-2- CY N 10.01 su 223616 1b -30 -Z7 1S.70 10106 lo. OS N 4.01 su 2.1KZZO 06-3o-211 ig.56 Kw yvv N Check of 7.00 su as Live Reading 21$156 06-30-14 i 8. 6' I w 2 -d i N Post Calibration- Date: q-Z7-23 Time: 13U0 Within ± 0.2 su? 7.00 su 223156 DG-3o-2`{ I I. _)v 7• v2 7-o Z FYI N 10.01 su ?,236$ w-30-27 IR,71 cp.c16 ca,vS V N 4.01 su Z1KZ-W e6.30-7A 19•bS K.w idol (V N Specific Conductivity Buffer Meter Within # Time: ogo Lot Number Expiration . Temperature (°C) Reading (Ns) 100/6? ` Standard Value: 72o [is G1Z22.16 D7-oi-Z4 (6,q0 7t£5 3 (3) N Calibration Check of Z_.27 ps as Live Reading LU$22(r I1-O$-2`i tt`Ct. 22�. 6 C� N Post Calibration -Date: g1-27 Time: t3uS 7? Ns G(Z22g 7- I-23 i 1 N ORP Buffer Adjusted Meter Time: 0 81 v Lot Number Expiration Temperature Value Reading Within ± 20%? (°C) (mV) (mV) y2q n'VI 3oio mov L1K3 N Post Calibration- Date: Time: uZy mV 3uiu 0 q-12-2'� ��fic qq 1. 3 4U N ICl, qi LtL(i. Revised 12/18/2018 KKH F]CAMA F-]CCRgLandfill F-�NPDES DGW❑ASW ❑LRB SPECIAL STUDY FG'b r DUKE ENERGY. Site: - /11S5 Date: 9-2-2-Z3 Field Personnel: Cs-L Dissolved Oxygen Temperature Barometric Pressure Chart DO Meter_ Reading % Saturation Within t 0.5? Time: ('C) (mmHg) (mg/L) (m9/L) °Sat ) (1° 0615 Its.7 7q(--3a Calibration Check as Live I g.� 7N6.`34 � ' .9� l q..�a (vu.2�£ � N Reading Post Calibration - Date: °I 2?-2 �, v t 74 L: v Z N Time: 13i5 Acceptance Meter Reading Within ± Turbidity Standard (NTU) Range (NTU) , (NTU) 5%? Time, 64 (s 10.0 0.5 to.() Cy% N Post Calibration - Date: 9-2-7 -Z3 ID-0 -� 0. S s �—� G� N Time: 13 S Daily Turbidity Meter BLANK DI Water (NTU) Less than 0.10 NTU? Date: 'l -7-i-z3 N Time: °st S Revised 12/18/2018 KKH Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina APPENDIX B LABORATORY REPORT AND CHAIN -OF -CUSTODY FORMS L7 synTerra Science & Engineering Consultants Analytical Data Review Checklist - Aqueous Facility/Site "aram Station State NC Location/Sample IDs Cl-LEACHATE, MS-8, MS-9, MS-10, MS-11, MS-12, MS-13, MS-14, MS 15, MS-16 Duke Central Lab Lab Report ID Sample Date Sample Receipt Date Analysis Complete Date ❑ Groundwater J23090511 9/27/2023 9/27/2023 10/13/2023 ❑ Surface Water ❑v Other References: 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 ®® ❑v ❑ I� 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? ❑v [Il ❑ 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 ❑ ❑ 0 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? O ❑ ❑ 5) 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? ❑ ❑ ❑� ®®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 ❑ ❑ (] 7c) Sulfide: Analyzed within 7 days of collection 0 ❑ ❑ 7d) TOC and/or Nitrate -Nitrite: Analyzed within 28 days of collection ❑ ❑ (] 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? ❑ ❑ 0 ❑ 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)? 10a) If YES, was the parameter recovery less than 50 percent or greater than 150 percent? ❑ ❑ ❑v 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: ❑� ❑ ❑ 11 a) 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 7❑e!Assurance/Quality ❑v ❑ ❑ 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? ❑e ❑ ❑ 13) Field Duplicate Sample - Is the relative percent difference between the parent and field duplicate sample results greater than 35 percent? ❑v ❑ ❑ 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/Mia Blank concentration? ❑v ❑ ❑ 15) Were initial and continuing calibration blank information within acceptable criteria per the lab report? ❑ ❑v ❑ 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 Carrier/ 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: J-Analyte detected above the MDL, but below the RL; analyte concentration should be considered an estimate. 7 U-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 lox the blank concentration. • The RPD between MS-11 and the field duplicate is greater than 35%for Iron (0.193/0.314 mg/L). • Chloride (0.03 mg/L), Nitrate (0.05 mg/L), Nitrate as N (0.01 mg-N/L), Boron (0.018 mg/L), and Iron (0.005 mg/L) were detected in the Equipment Blank; Nitrate, Nitrate as N, Boron, and Iron were also detected in the samples at concentrations less than lox the blank concentrations. • Nitrate (0.04 mg/L), Nitrate as N (0.01 mg-N/L), and Boron (0.012 mg/L) were detected in the Field Blank; Nitrate, Nitrate as N, and Boron 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 10/17/2023 Technical Lead GTC 1/2/2024 DUKE Analytical Laboratory ENERGY 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: J23090511 Project Name: MARSHALL - GW FGD LANDFILL Task Code: LF Customer Name(s): Ashley Healy, Bryan Moeller, Josh Stowe,Dee Obrien Customer Address: Marshall Steam Station 8320 NC Hwy 150 East Mail Code: Marshall Steam Station Terrell, NC 28682 Lab Contact: Peggy Kendall Phone: 980-875-5848 Report Authorized By: Date: (Signature) eg Kendall Program Comments: Please contact the Program Manager (Peggy Kendall) with any questions regarding this report. Data Flags & Calculations: 10/13/2023 Page 1 of 28 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: Collection Sample ID Plant/Station Date and Time Collected By Page 2 of 28 Sample Description 2023024019 MARSHALL 27-Sep-23 9:50 AM Connor Zahora MSS—MS-8 2023024020 MARSHALL 27-Sep-23 10:20 AM Connor Zahora MSS—MS-9 2023024021 MARSHALL 27-Sep-23 9:35 AM Connor Zahora MSS_MS-10 2023024022 MARSHALL 27-Sep-23 9:50 AM Ethan Smith MSS_MS-11 2023024023 MARSHALL 27-Sep-23 11:00 AM Ethan Smith MSS_MS-12 2023024024 MARSHALL 27-Sep-23 9:05 AM Ethan Smith MSS_MS-13 2023024025 MARSHALL 27-Sep-23 11:45 AM Ethan Smith MSS_MS-14 2023024026 MARSHALL 27-Sep-23 11:20 AM Connor Zahora MSS_MS-15 2023024027 MARSHALL 27-Sep-23 10:45 AM Connor Zahora MSS_MS-16 2023024029 MARSHALL 27-Sep-23 8:50 AM Connor Zahora MSS_Cl-LEACHATE 2023024030 MARSHALL 27-Sep-23 Ethan Smith MSS_FD-20230927-1 2023024031 MARSHALL 27-Sep-23 8:15 AM Connor Zahora MSS_EB-20230927-0815 2023024032 MARSHALL 27-Sep-23 8:30 AM Connor Zahora MSS_FB-20230927-0830 13 Total Samples Page 3 of 28 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 0 No All laboratory QA/QC requirements are acceptable.❑ Yes ❑ No Report Sections Included: W Job Summary Report 0 Sample Identification ❑� Technical Validation of Data Package ❑� Analytical Laboratory Certificate of Analysis ❑� Analytical Laboratory QC Report ❑ Sub -contracted Laboratory Results ❑ Customer Specific Data Sheets, Reports, & Documentation ❑ Customer Database Entries ❑d Chain of Custody ❑ Electronic Data Deliverable (EDD) Sent Separately Reviewed By: Peggy Kendall Date: 10/13/2023 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J23090511 Site: MSS MS-8 Collection Date: 09/27/2023 09:50 AM Loc code: MSS-MS-8 Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 1.2 mg/L Fluoride 0.12 mg/L Nitrate 0.72 mg/L Nitrate as N 0.16 mg-N/L Sulfate 0.18 mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 U ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.039 mg/L Boron (B) 0.005 U mg/L Calcium (Ca) 4.08 mg/L Iron (Fe) 0.072 mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 1.80 mg/L Manganese (Mn) 0.001 J mg/L Zinc (Zn) 0.004 U mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L Arsenic (As) 0.111 U ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 3.84 ug/L Cobalt (Co) 0.077 U ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.037 U ug/L Molybdenum (Mo) 0.18 U ug/L Nickel (Ni) 0.555 J ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 4.00 ug/L TOTAL DISSOLVED SOLIDS - 023090428 TDS 54.0 mg/L Sample #: 2023024019 Matrix: GW RCRA Page 4 of 28 Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/27/2023 16:16 EBATIAN 0.1 0.0479 1 EPA 9056A 09/27/2023 16:16 EBATIAN 0.1 0.0209 1 EPA 9056A 09/27/2023 16:16 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 16:16 EBATIAN 0.1 0.0428 1 EPA 9056A 09/27/2023 16:16 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 11:33 SNEGLIA 0.005 0.002 1 SW 601OD 09/29/2023 19:10 CELL106 0.05 0.005 1 SW 601OD 09/29/2023 19:10 CELL106 0.05 0.012 1 SW 601OD 09/29/2023 19:10 CELL106 0.01 0.004 1 SW 601OD 09/29/2023 19:10 CELL106 0.005 0.002 1 SW 601OD 09/29/2023 19:10 CELL106 0.02 0.008 1 SW 601OD 09/29/2023 19:10 CELL106 0.005 0.001 1 SW 601OD 09/29/2023 19:10 CELL106 0.005 0.004 1 SW 601OD 09/29/2023 19:10 CELL106 1 0.104 1 SW 6020B 09/29/2023 19:44 MHALL3 1 0.111 1 SW 6020B 09/29/2023 19:44 MHALL3 1 0.249 1 SW 6020E 09/29/2023 19:44 MHALL3 1 0.032 1 SW 6020E 09/29/2023 19:44 MHALL3 1 0.185 1 SW 6020B 09/29/2023 19:44 MHALL3 1 0.077 1 SW 6020E 09/29/2023 19:44 MHALL3 1 0.787 1 SW 6020B 09/29/2023 19:44 MHALL3 1 0.037 1 SW 6020E 09/29/2023 19:44 MHALL3 1 0.18 1 SW 6020E 09/29/2023 19:44 MHALL3 1 0.256 1 SW 6020B 09/29/2023 19:44 MHALL3 1 0.193 1 SW 6020B 09/29/2023 19:44 MHALL3 1 0.035 1 SW 6020E 09/29/2023 19:44 MHALL3 1 0.041 1 SW 6020B 09/29/2023 19:44 MHALL3 1 0.114 1 SW 6020E 09/29/2023 19:44 MHALL3 25 25 1 SM2540C 09/29/2023 09:00 HHOOGKA Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J23090511 Site: MSS MS-9 Collection Date: 09/27/2023 10:20 AM Loc code: MSS-MS-9 Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 1.5 mg/L Fluoride 0.0479 U mg/L Nitrate 0.50 mg/L Nitrate as N 0.11 mg-N/L Sulfate 0.65 mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 U ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.051 mg/L Boron (B) 0.005 U mg/L Calcium (Ca) 16.2 mg/L Iron (Fe) 0.023 mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 1.39 mg/L Manganese (Mn) 0.003 J mg/L Zinc (Zn) 0.004 U mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.265 J ug/L Arsenic (As) 0.111 U ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 1.60 ug/L Cobalt (Co) 0.077 U ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.037 U ug/L Molybdenum (Mo) 0.181 J ug/L Nickel (Ni) 0.256 U ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 2.47 ug/L TOTAL DISSOLVED SOLIDS - 023090428 TDS 86.0 mg/L Sample #: 2023024020 Matrix: GW RCRA Page 5 of 28 Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/27/2023 17:16 EBATIAN 0.1 0.0479 1 EPA 9056A 09/27/2023 17:16 EBATIAN 0.1 0.0209 1 EPA 9056A 09/27/2023 17:16 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 17:16 EBATIAN 0.1 0.0428 1 EPA 9056A 09/27/2023 17:16 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 11:36 SNEGLIA 0.005 0.002 1 SW 601OD 09/29/2023 19:15 CELL106 0.05 0.005 1 SW 601OD 09/29/2023 19:15 CELL106 0.05 0.012 1 SW 601OD 09/29/2023 19:15 CELL106 0.01 0.004 1 SW 601OD 09/29/2023 19:15 CELL106 0.005 0.002 1 SW 601OD 09/29/2023 19:15 CELL106 0.02 0.008 1 SW 601OD 09/29/2023 19:15 CELL106 0.005 0.001 1 SW 601OD 09/29/2023 19:15 CELL106 0.005 0.004 1 SW 601OD 09/29/2023 19:15 CELL106 1 0.104 1 SW 6020B 09/29/2023 19:53 MHALL3 1 0.111 1 SW 6020B 09/29/2023 19:53 MHALL3 1 0.249 1 SW 6020E 09/29/2023 19:53 MHALL3 1 0.032 1 SW 6020E 09/29/2023 19:53 MHALL3 1 0.185 1 SW 6020B 09/29/2023 19:53 MHALL3 1 0.077 1 SW 6020E 09/29/2023 19:53 MHALL3 1 0.787 1 SW 6020B 09/29/2023 19:53 MHALL3 1 0.037 1 SW 6020E 09/29/2023 19:53 MHALL3 1 0.18 1 SW 6020E 09/29/2023 19:53 MHALL3 1 0.256 1 SW 6020B 09/29/2023 19:53 MHALL3 1 0.193 1 SW 6020B 09/29/2023 19:53 MHALL3 1 0.035 1 SW 6020E 09/29/2023 19:53 MHALL3 1 0.041 1 SW 6020B 09/29/2023 19:53 MHALL3 1 0.114 1 SW 6020E 09/29/2023 19:53 MHALL3 25 25 1 SM2540C 09/29/2023 09:01 HHOOGKA Certificate of Laboratory Analysis Page 6 of 28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS MS-10 Sample #: 2023024021 Collection Date: 09/27/2023 09:35 AM Loc code: MSS MS-10 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 1.1 mg/L Fluoride 0.0479 U mg/L Nitrate 0.95 mg/L Nitrate as N 0.22 mg-N/L Sulfate 0.09 J mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 U ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.103 mg/L Boron (B) 0.005 U mg/L Calcium (Ca) 0.210 mg/L Iron (Fe) 1.11 mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 0.505 mg/L Manganese (Mn) 0.036 mg/L Zinc (Zn) 0.007 mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L Arsenic (As) 0.151 J ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 1.30 ug/L Cobalt (Co) 0.804 J ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.611 J ug/L Molybdenum (Mo) 0.336 J ug/L Nickel (Ni) 1.22 ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 2.62 ug/L TOTAL DISSOLVED SOLIDS - 023090428 TDS 25 U mg/L Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/27/2023 17:35 EBATIAN 0.1 0.0479 1 EPA 9056A 09/27/2023 17:35 EBATIAN 0.1 0.0209 1 EPA 9056A 09/27/2023 17:35 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 17:35 EBATIAN 0.1 0.0428 1 EPA 9056A 09/27/2023 17:35 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 11:39 SNEGLIA 0.005 0.002 1 SW 601OD 09/29/2023 19:19 CELL106 0.05 0.005 1 SW 601OD 09/29/2023 19:19 CELL106 0.05 0.012 1 SW 601OD 09/29/2023 19:19 CELL106 0.01 0.004 1 SW 601OD 09/29/2023 19:19 CELL106 0.005 0.002 1 SW 601OD 09/29/2023 19:19 CELL106 0.02 0.008 1 SW 601OD 09/29/2023 19:19 CELL106 0.005 0.001 1 SW 601OD 09/29/2023 19:19 CELL106 0.005 0.004 1 SW 601OD 09/29/2023 19:19 CELL106 1 0.104 1 SW 6020B 09/29/2023 20:03 MHALL3 1 0.111 1 SW 6020B 09/29/2023 20:03 MHALL3 1 0.249 1 SW 6020E 09/29/2023 20:03 MHALL3 1 0.032 1 SW 6020E 09/29/2023 20:03 MHALL3 1 0.185 1 SW 6020B 09/29/2023 20:03 MHALL3 1 0.077 1 SW 6020E 09/29/2023 20:03 MHALL3 1 0.787 1 SW 6020B 09/29/2023 20:03 MHALL3 1 0.037 1 SW 6020E 09/29/2023 20:03 MHALL3 1 0.18 1 SW 6020E 09/29/2023 20:03 MHALL3 1 0.256 1 SW 6020B 09/29/2023 20:03 MHALL3 1 0.193 1 SW 6020B 09/29/2023 20:03 MHALL3 1 0.035 1 SW 6020E 09/29/2023 20:03 MHALL3 1 0.041 1 SW 6020B 09/29/2023 20:03 MHALL3 1 0.114 1 SW 6020E 09/29/2023 20:03 MHALL3 25 25 1 SM2540C 09/29/2023 09:01 HHOOGKA Certificate of Laboratory Analysis Page 7 of 28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS MS-11 Sample #: 2023024022 Collection Date: 09/27/2023 09:50 AM Loc code: MSS-MS-1 1 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 3.9 mg/L Fluoride 0.0479 U mg/L Nitrate 0.09 J mg/L Nitrate as N 0.02 J mg-N/L Sulfate 0.25 mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 U ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.079 mg/L Boron (B) 0.005 U mg/L Calcium (Ca) 2.36 mg/L Iron (Fe) 0.193 mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 1.26 mg/L Manganese (Mn) 0.013 mg/L Zinc (Zn) 0.004 J mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L Arsenic (As) 0.111 U ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 2.59 ug/L Cobalt (Co) 0.138 J ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.07 J ug/L Molybdenum (Mo) 0.18 U ug/L Nickel (Ni) 1.16 ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 0.294 J ug/L TOTAL DISSOLVED SOLIDS - 023090428 TDS 35.0 mg/L Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/27/2023 17:55 EBATIAN 0.1 0.0479 1 EPA 9056A 09/27/2023 17:55 EBATIAN 0.1 0.0209 1 EPA 9056A 09/27/2023 17:55 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 17:55 EBATIAN 0.1 0.0428 1 EPA 9056A 09/27/2023 17:55 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 11:41 SNEGLIA 0.005 0.002 1 SW 601OD 09/29/2023 19:32 CELL106 0.05 0.005 1 SW 601OD 09/29/2023 19:32 CELL106 0.05 0.012 1 SW 601OD 09/29/2023 19:32 CELL106 0.01 0.004 1 SW 601OD 09/29/2023 19:32 CELL106 0.005 0.002 1 SW 601OD 09/29/2023 19:32 CELL106 0.02 0.008 1 SW 601OD 09/29/2023 19:32 CELL106 0.005 0.001 1 SW 601OD 09/29/2023 19:32 CELL106 0.005 0.004 1 SW 601OD 09/29/2023 19:32 CELL106 1 0.104 1 SW 6020B 09/29/2023 20:40 MHALL3 1 0.111 1 SW 6020B 09/29/2023 20:40 MHALL3 1 0.249 1 SW 6020E 09/29/2023 20:40 MHALL3 1 0.032 1 SW 6020E 09/29/2023 20:40 MHALL3 1 0.185 1 SW 6020B 09/29/2023 20:40 MHALL3 1 0.077 1 SW 6020E 09/29/2023 20:40 MHALL3 1 0.787 1 SW 6020B 09/29/2023 20:40 MHALL3 1 0.037 1 SW 6020E 09/29/2023 20:40 MHALL3 1 0.18 1 SW 6020E 09/29/2023 20:40 MHALL3 1 0.256 1 SW 6020B 09/29/2023 20:40 MHALL3 1 0.193 1 SW 6020B 09/29/2023 20:40 MHALL3 1 0.035 1 SW 6020E 09/29/2023 20:40 MHALL3 1 0.041 1 SW 6020B 09/29/2023 20:40 MHALL3 1 0.114 1 SW 6020E 09/29/2023 20:40 MHALL3 25 25 1 SM2540C 09/29/2023 09:01 HHOOGKA Certificate of Laboratory Analysis Page 8 of 28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS MS-12 Sample #: 2023024023 Collection Date: 09/27/2023 11:00 AM Loc code: MSS MS-12 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 2.7 mg/L Fluoride 0.0479 U mg/L Nitrate 0.19 mg/L Nitrate as N 0.04 mg-N/L Sulfate 0.14 mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 J ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.077 mg/L Boron (B) 0.005 U mg/L Calcium (Ca) 0.178 mg/L Iron (Fe) 0.197 mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 0.539 mg/L Manganese (Mn) 0.018 mg/L Zinc (Zn) 0.004 J mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L Arsenic (As) 0.111 U ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 0.518 J ug/L Cobalt (Co) 1.12 ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.261 J ug/L Molybdenum (Mo) 0.18 U ug/L Nickel (Ni) 0.298 J ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.042 J ug/L Vanadium (V) 0.433 J ug/L TOTAL DISSOLVED SOLIDS - 023090428 TDS 25 U mg/L Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/27/2023 18:15 EBATIAN 0.1 0.0479 1 EPA 9056A 09/27/2023 18:15 EBATIAN 0.1 0.0209 1 EPA 9056A 09/27/2023 18:15 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 18:15 EBATIAN 0.1 0.0428 1 EPA 9056A 09/27/2023 18:15 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 11:44 SNEGLIA 0.005 0.002 1 SW 601OD 09/29/2023 19:37 CELL106 0.05 0.005 1 SW 601OD 09/29/2023 19:37 CELL106 0.05 0.012 1 SW 601OD 09/29/2023 19:37 CELL106 0.01 0.004 1 SW 601OD 09/29/2023 19:37 CELL106 0.005 0.002 1 SW 601OD 09/29/2023 19:37 CELL106 0.02 0.008 1 SW 601OD 09/29/2023 19:37 CELL106 0.005 0.001 1 SW 601OD 09/29/2023 19:37 CELL106 0.005 0.004 1 SW 601OD 09/29/2023 19:37 CELL106 1 0.104 1 SW 6020B 09/29/2023 20:50 MHALL3 1 0.111 1 SW 6020B 09/29/2023 20:50 MHALL3 1 0.249 1 SW 6020E 09/29/2023 20:50 MHALL3 1 0.032 1 SW 6020E 09/29/2023 20:50 MHALL3 1 0.185 1 SW 6020B 09/29/2023 20:50 MHALL3 1 0.077 1 SW 6020E 09/29/2023 20:50 MHALL3 1 0.787 1 SW 6020B 09/29/2023 20:50 MHALL3 1 0.037 1 SW 6020E 09/29/2023 20:50 MHALL3 1 0.18 1 SW 6020E 09/29/2023 20:50 MHALL3 1 0.256 1 SW 6020B 09/29/2023 20:50 MHALL3 1 0.193 1 SW 6020B 09/29/2023 20:50 MHALL3 1 0.035 1 SW 6020E 09/29/2023 20:50 MHALL3 1 0.041 1 SW 6020B 09/29/2023 20:50 MHALL3 1 0.114 1 SW 6020E 09/29/2023 20:50 MHALL3 25 25 1 SM2540C 09/29/2023 09:01 HHOOGKA Certificate of Laboratory Analysis Page 9 of 28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS MS-13 Sample #: 2023024024 Collection Date: 09/27/2023 09:05 AM Loc code: MSS MS-13 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 3.3 mg/L Fluoride 0.0479 U mg/L Nitrate 3.8 mg/L Nitrate as N 0.85 mg-N/L Sulfate 0.12 mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.02 J ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.118 mg/L Boron (B) 0.005 U mg/L Calcium (Ca) 6.38 mg/L Iron (Fe) 0.020 mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 1.47 mg/L Manganese (Mn) 0.015 mg/L Zinc (Zn) 0.004 U mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L Arsenic (As) 0.111 U ug/L Beryllium (Be) 0.43 J ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 0.185 U ug/L Cobalt (Co) 0.077 U ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.059 J ug/L Molybdenum (Mo) 0.18 U ug/L Nickel (Ni) 0.268 J ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 0.421 J ug/L TOTAL DISSOLVED SOLIDS - 023090428 TDS 45.0 mg/L Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/27/2023 18:34 EBATIAN 0.1 0.0479 1 EPA 9056A 09/27/2023 18:34 EBATIAN 0.1 0.0209 1 EPA 9056A 09/27/2023 18:34 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 18:34 EBATIAN 0.1 0.0428 1 EPA 9056A 09/27/2023 18:34 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 11:47 SNEGLIA 0.005 0.002 1 SW 601OD 09/29/2023 19:42 CELL106 0.05 0.005 1 SW 601OD 09/29/2023 19:42 CELL106 0.05 0.012 1 SW 601OD 09/29/2023 19:42 CELL106 0.01 0.004 1 SW 601OD 09/29/2023 19:42 CELL106 0.005 0.002 1 SW 601OD 09/29/2023 19:42 CELL106 0.02 0.008 1 SW 601OD 09/29/2023 19:42 CELL106 0.005 0.001 1 SW 601OD 09/29/2023 19:42 CELL106 0.005 0.004 1 SW 601OD 09/29/2023 19:42 CELL106 1 0.104 1 SW 6020B 09/29/2023 20:59 MHALL3 1 0.111 1 SW 6020B 09/29/2023 20:59 MHALL3 1 0.249 1 SW 6020E 09/29/2023 20:59 MHALL3 1 0.032 1 SW 6020E 09/29/2023 20:59 MHALL3 1 0.185 1 SW 6020B 09/29/2023 20:59 MHALL3 1 0.077 1 SW 6020E 09/29/2023 20:59 MHALL3 1 0.787 1 SW 6020B 09/29/2023 20:59 MHALL3 1 0.037 1 SW 6020E 09/29/2023 20:59 MHALL3 1 0.18 1 SW 6020E 09/29/2023 20:59 MHALL3 1 0.256 1 SW 6020B 09/29/2023 20:59 MHALL3 1 0.193 1 SW 6020B 09/29/2023 20:59 MHALL3 1 0.035 1 SW 6020E 09/29/2023 20:59 MHALL3 1 0.041 1 SW 6020B 09/29/2023 20:59 MHALL3 1 0.114 1 SW 6020E 09/29/2023 20:59 MHALL3 25 25 1 SM2540C 09/29/2023 09:02 HHOOGKA Certificate of Laboratory Analysis Page 10 of 28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS MS-14 Sample #: 2023024025 Collection Date: 09/27/2023 11:45 AM Loc code: MSS MS-14 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 0.96 mg/L Fluoride 0.08 J mg/L Nitrate 0.04 J mg/L Nitrate as N 0.01 J mg-N/L Sulfate 0.09 J mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 U ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.055 mg/L Boron (B) 0.005 U mg/L Calcium (Ca) 5.49 mg/L Iron (Fe) 0.014 mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 1.16 mg/L Manganese (Mn) 0.001 U mg/L Zinc (Zn) 0.004 U mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L Arsenic (As) 0.184 J ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 0.213 J ug/L Cobalt (Co) 0.077 U ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.037 U ug/L Molybdenum (Mo) 0.18 U ug/L Nickel (Ni) 0.256 U ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 2.27 ug/L TOTAL DISSOLVED SOLIDS - 023090428 TDS 67.0 mg/L Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/27/2023 18:54 EBATIAN 0.1 0.0479 1 EPA 9056A 09/27/2023 18:54 EBATIAN 0.1 0.0209 1 EPA 9056A 09/27/2023 18:54 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 18:54 EBATIAN 0.1 0.0428 1 EPA 9056A 09/27/2023 18:54 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 11:56 SNEGLIA 0.005 0.002 1 SW 601OD 09/29/2023 19:47 CELL106 0.05 0.005 1 SW 601OD 09/29/2023 19:47 CELL106 0.05 0.012 1 SW 601OD 09/29/2023 19:47 CELL106 0.01 0.004 1 SW 601OD 09/29/2023 19:47 CELL106 0.005 0.002 1 SW 601OD 09/29/2023 19:47 CELL106 0.02 0.008 1 SW 601OD 09/29/2023 19:47 CELL106 0.005 0.001 1 SW 601OD 09/29/2023 19:47 CELL106 0.005 0.004 1 SW 601OD 09/29/2023 19:47 CELL106 1 0.104 1 SW 6020B 09/29/2023 21:08 MHALL3 1 0.111 1 SW 6020B 09/29/2023 21:08 MHALL3 1 0.249 1 SW 6020E 09/29/2023 21:08 MHALL3 1 0.032 1 SW 6020E 09/29/2023 21:08 MHALL3 1 0.185 1 SW 6020B 09/29/2023 21:08 MHALL3 1 0.077 1 SW 6020E 09/29/2023 21:08 MHALL3 1 0.787 1 SW 6020B 09/29/2023 21:08 MHALL3 1 0.037 1 SW 6020E 09/29/2023 21:08 MHALL3 1 0.18 1 SW 6020E 09/29/2023 21:08 MHALL3 1 0.256 1 SW 6020B 09/29/2023 21:08 MHALL3 1 0.193 1 SW 6020B 09/29/2023 21:08 MHALL3 1 0.035 1 SW 6020E 09/29/2023 21:08 MHALL3 1 0.041 1 SW 6020B 09/29/2023 21:08 MHALL3 1 0.114 1 SW 6020E 09/29/2023 21:08 MHALL3 25 25 1 SM2540C 09/29/2023 09:02 HHOOGKA Certificate of Laboratory Analysis Page 11 of28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS MS-15 Sample #: 2023024026 Collection Date: 09/27/2023 11:20 AM Loc code: MSS MS-15 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 81 mg/L Fluoride 0.0479 U mg/L Nitrate 9.4 mg/L Nitrate as N 2.1 mg-N/L Sulfate 0.67 mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 J ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.361 mg/L Boron (B) 0.005 U mg/L Calcium (Ca) 32.8 mg/L Iron (Fe) 0.547 mg/L Lithium (Li) 0.002 J mg/L Magnesium (Mg) 15.7 mg/L Manganese (Mn) 0.006 mg/L Zinc (Zn) 0.004 J mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.153 J ug/L Arsenic (As) 0.115 J ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.049 J ug/L Chromium (Cr) 19.5 ug/L Cobalt (Co) 0.106 J ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.235 J ug/L Molybdenum (Mo) 0.18 U ug/L Nickel (Ni) 24.7 ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 2.89 ug/L TOTAL DISSOLVED SOLIDS - 023090428 TDS 299 mg/L Method Analysis Date/Time Analyst 2 0.0154 20 EPA 9056A 09/27/2023 23:07 EBATIAN 0.2 0.0479 2 EPA 9056A 09/27/2023 23:07 EBATIAN 0.2 0.0209 2 EPA 9056A 09/27/2023 23:07 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 23:07 EBATIAN 0.2 0.0428 2 EPA 9056A 09/27/2023 23:07 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 12:05 SNEGLIA 0.005 0.002 1 SW 601OD 09/29/2023 19:51 CELL106 0.05 0.005 1 SW 601OD 09/29/2023 19:51 CELL106 0.05 0.012 1 SW 601OD 09/29/2023 19:51 CELL106 0.01 0.004 1 SW 601OD 09/29/2023 19:51 CELL106 0.005 0.002 1 SW 601OD 09/29/2023 19:51 CELL106 0.02 0.008 1 SW 601OD 09/29/2023 19:51 CELL106 0.005 0.001 1 SW 601OD 09/29/2023 19:51 CELL106 0.005 0.004 1 SW 601OD 09/29/2023 19:51 CELL106 1 0.104 1 SW 6020B 09/29/2023 21:18 MHALL3 1 0.111 1 SW 6020B 09/29/2023 21:18 MHALL3 1 0.249 1 SW 6020E 09/29/2023 21:18 MHALL3 1 0.032 1 SW 6020E 09/29/2023 21:18 MHALL3 1 0.185 1 SW 6020B 09/29/2023 21:18 MHALL3 1 0.077 1 SW 6020E 09/29/2023 21:18 MHALL3 1 0.787 1 SW 6020B 09/29/2023 21:18 MHALL3 1 0.037 1 SW 6020E 09/29/2023 21:18 MHALL3 1 0.18 1 SW 6020E 09/29/2023 21:18 MHALL3 1 0.256 1 SW 6020B 09/29/2023 21:18 MHALL3 1 0.193 1 SW 6020B 09/29/2023 21:18 MHALL3 1 0.035 1 SW 6020E 09/29/2023 21:18 MHALL3 1 0.041 1 SW 6020B 09/29/2023 21:18 MHALL3 1 0.114 1 SW 6020E 09/29/2023 21:18 MHALL3 25 25 1 SM2540C 09/29/2023 09:02 HHOOGKA Certificate of Laboratory Analysis Page 12 of 28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS MS-16 Sample #: 2023024027 Collection Date: 09/27/2023 10:45 AM Loc code: MSS MS-16 Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 1.7 mg/L Fluoride 0.21 mg/L Nitrate 2.7 mg/L Nitrate as N 0.61 mg-N/L Sulfate 0.39 mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 U ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.096 mg/L Boron (B) 0.005 U mg/L Calcium (Ca) 8.29 mg/L Iron (Fe) 1.53 mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 3.90 mg/L Manganese (Mn) 0.027 mg/L Zinc (Zn) 0.006 mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L Arsenic (As) 0.208 J ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 4.22 ug/L Cobalt (Co) 0.394 J ug/L Copper (Cu) 1.94 ug/L Lead (Pb) 0.584 J ug/L Molybdenum (Mo) 0.306 J ug/L Nickel (Ni) 2.01 ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 6.31 ug/L TOTAL DISSOLVED SOLIDS - 023090428 TDS 82.0 mg/L Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/27/2023 19:33 EBATIAN 0.1 0.0479 1 EPA 9056A 09/27/2023 19:33 EBATIAN 0.1 0.0209 1 EPA 9056A 09/27/2023 19:33 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 19:33 EBATIAN 0.1 0.0428 1 EPA 9056A 09/27/2023 19:33 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 12:07 SNEGLIA 0.005 0.002 1 SW 601OD 09/29/2023 19:56 CELL106 0.05 0.005 1 SW 601OD 09/29/2023 19:56 CELL106 0.05 0.012 1 SW 601OD 09/29/2023 19:56 CELL106 0.01 0.004 1 SW 601OD 09/29/2023 19:56 CELL106 0.005 0.002 1 SW 601OD 09/29/2023 19:56 CELL106 0.02 0.008 1 SW 601OD 09/29/2023 19:56 CELL106 0.005 0.001 1 SW 601OD 09/29/2023 19:56 CELL106 0.005 0.004 1 SW 601OD 09/29/2023 19:56 CELL106 1 0.104 1 SW 6020B 09/29/2023 21:27 MHALL3 1 0.111 1 SW 6020B 09/29/2023 21:27 MHALL3 1 0.249 1 SW 6020E 09/29/2023 21:27 MHALL3 1 0.032 1 SW 6020E 09/29/2023 21:27 MHALL3 1 0.185 1 SW 6020B 09/29/2023 21:27 MHALL3 1 0.077 1 SW 6020E 09/29/2023 21:27 MHALL3 1 0.787 1 SW 6020B 09/29/2023 21:27 MHALL3 1 0.037 1 SW 6020E 09/29/2023 21:27 MHALL3 1 0.18 1 SW 6020E 09/29/2023 21:27 MHALL3 1 0.256 1 SW 6020B 09/29/2023 21:27 MHALL3 1 0.193 1 SW 6020B 09/29/2023 21:27 MHALL3 1 0.035 1 SW 6020E 09/29/2023 21:27 MHALL3 1 0.041 1 SW 6020B 09/29/2023 21:27 MHALL3 1 0.114 1 SW 6020E 09/29/2023 21:27 MHALL3 25 25 1 SM2540C 09/29/2023 09:02 HHOOGKA Certificate of Laboratory Analysis Page 13 of 28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS Cl-LEACHATE Sample #: 2023024029 Collection Date: 09/27/2023 08:50 AM Loc code: MSS C1-LEACHATE Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst INORGANIC IONS BY IC - Q23090400 Chloride 370 mg/L 5 0.0154 50 EPA 9056A 09/27/2023 22:48 EBATIAN Fluoride 1.2 J mg/L 5 0.0479 50 EPA 9056A 09/27/2023 22:48 EBATIAN Nitrate 8.9 mg/L 5 0.0209 50 EPA 9056A 09/27/2023 22:48 EBATIAN Nitrate as N 2.0 mg-N/L 0.023 0.002 1 EPA 9056A 09/27/2023 22:48 EBATIAN Sulfate 2800 mg/L 50 0.0428 500 EPA 9056A 09/27/2023 22:48 EBATIAN MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 U ug/L 0.05 0.01 TOTAL RECOVERABLE METALS BY ICP (DISSOLVED) - Q23100007 Zinc (Zn) 0.263 mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.022 mg/L 0.005 0.002 Boron (B) 57.6 mg/L 0.5 0.005 Calcium (Ca) 547 mg/L 0.5 0.012 Iron (Fe) 164 mg/L 0.1 0.004 Lithium (Li) 2.01 mg/L 0.005 0.002 Magnesium (Mg) 227 mg/L 0.2 0.008 Manganese (Mn) 5.65 mg/L 0.005 0.001 Zinc (Zn) 0.264 mg/L 0.005 0.004 TOTAL RECOVERABLE METALS BY ICP-MS (DISSOLVED) - Q23100013 Beryllium (Be) 2.51 ug/L 1 0.249 Cadmium (Cd) 0.274 J ug/L 1 0.032 Chromium (Cr) 0.185 U ug/L 1 0.185 Copper (Cu) 5.57 ug/L 1 0.787 Lead (Pb) 0.131 J ug/L 1 0.037 Nickel (Ni) 112 ug/L 1 0.256 Silver (Ag) 0.035 U ug/L 1 0.035 1 EPA 7470A 09/29/2023 12:10 SNEGLIA 1 SW 601 OD 10/03/2023 18:07 CELL106 1 SW 601 OD 09/29/2023 20:01 CELL106 10 SW 601 OD 09/29/2023 20:01 CELL106 10 SW 601 OD 09/29/2023 20:01 CELL106 10 SW 601 OD 09/29/2023 20:01 CELL106 1 SW 601 OD 09/29/2023 20:01 CELL106 10 SW 601 OD 09/29/2023 20:01 CELL106 1 SW 601 OD 09/29/2023 20:01 CELL106 1 SW 601 OD 09/29/2023 20:01 CELL106 1 SW 6020B 10/03/2023 18:55 MHALL3 1 SW 6020B 10/03/2023 18:55 MHALL3 1 SW 6020E 10/03/2023 18:55 MHALL3 1 SW 6020B 10/03/2023 18:55 MHALL3 1 SW 6020E 10/03/2023 18:55 MHALL3 1 SW 6020B 10/03/2023 18:55 MHALL3 1 SW 6020B 10/03/2023 18:55 MHALL3 Certificate of Laboratory Analysis Page 14 of 28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS C1-LEACHATE Sample #: 2023024029 Collection Date: 09/27/2023 08:50 AM Loc code: MSS C1-LEACHATE Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF Method Analysis Date/Time Analyst TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L 1 0.104 1 SW 6020B 09/29/2023 21:36 MHALL3 Arsenic (As) 1.94 ug/L 1 0.111 1 SW 6020B 09/29/2023 21:36 MHALL3 Beryllium (Be) 3.63 ug/L 1 0.249 1 SW 6020E 09/29/2023 21:36 MHALL3 Cadmium (Cd) 0.246 J ug/L 1 0.032 1 SW 6020B 09/29/2023 21:36 MHALL3 Chromium (Cr) 0.185 U ug/L 1 0.185 1 SW 6020B 09/29/2023 21:36 MHALL3 Cobalt (Co) 42.7 ug/L 1 0.077 1 SW 6020E 09/29/2023 21:36 MHALL3 Copper (Cu) 2.50 ug/L 1 0.787 1 SW 6020B 09/29/2023 21:36 MHALL3 Lead (Pb) 0.126 J ug/L 1 0.037 1 SW 6020E 09/29/2023 21:36 MHALL3 Molybdenum (Mo) 634 ug/L 100 0.18 100 SW 6020B 09/29/2023 21:36 MHALL3 Nickel (Ni) 108 ug/L 1 0.256 1 SW 6020E 09/29/2023 21:36 MHALL3 Selenium (Se) 46.1 ug/L 1 0.193 1 SW 6020B 09/29/2023 21:36 MHALL3 Silver (Ag) 0.035 U ug/L 1 0.035 1 SW 6020E 09/29/2023 21:36 MHALL3 Thallium (TI) 0.098 J ug/L 1 0.041 1 SW 6020B 09/29/2023 21:36 MHALL3 Vanadium (V) 0.114 U ug/L 1 0.114 1 SW 6020E 09/29/2023 21:36 MHALL3 TOTAL DISSOLVED SOLIDS - Q23090428 TDS 4900 mg/L 100 25 1 SM2540C 09/29/2023 09:02 HHOOGKA Site: MSS FD-20230927-1 Collection Date: 09/27/2023 Certificate of Laboratory Analysis Page 15 of 28 This report shall not be reproduced, except in full. Order # J23090511 Sample #: 2023024030 Loc code: MSS FD Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 3.4 mg/L Fluoride 0.0479 U mg/L Nitrate 0.08 J mg/L Nitrate as N 0.02 J mg-N/L Sulfate 0.23 mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 U ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.079 mg/L Boron (B) 0.027 J mg/L Calcium (Ca) 2.48 mg/L Iron (Fe) 0.314 mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 1.29 mg/L Manganese (Mn) 0.016 mg/L Zinc (Zn) 0.004 J mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L Arsenic (As) 0.111 U ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 2.85 ug/L Cobalt (Co) 0.221 J ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.087 J ug/L Molybdenum (Mo) 0.371 J ug/L Nickel (Ni) 1.23 ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 0.268 J ug/L TOTAL DISSOLVED SOLIDS - 023090428 TDS 35.0 mg/L Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/28/2023 12:14 Ebatian 0.1 0.0479 1 EPA 9056A 09/28/2023 12:14 Ebatian 0.1 0.0209 1 EPA 9056A 09/28/2023 12:14 Ebatian 0.023 0.002 1 EPA 9056A 09/28/2023 12:14 Ebatian 0.1 0.0428 1 EPA 9056A 09/28/2023 12:14 Ebatian 0.05 0.01 1 EPA 7470A 09/29/2023 12:13 SNEGLIA 0.005 0.002 1 SW 601 OD 09/29/2023 20:06 CELL106 0.05 0.005 1 SW 601 OD 09/29/2023 20:06 CELL106 0.05 0.012 1 SW 601 OD 09/29/2023 20:06 CELL106 0.01 0.004 1 SW 601 OD 09/29/2023 20:06 CELL106 0.005 0.002 1 SW 601 OD 09/29/2023 20:06 CELL106 0.02 0.008 1 SW 601 OD 09/29/2023 20:06 CELL106 0.005 0.001 1 SW 601 OD 09/29/2023 20:06 CELL106 0.005 0.004 1 SW 601 OD 09/29/2023 20:06 CELL106 1 0.104 1 SW 6020B 09/29/2023 21:46 MHALL3 1 0.111 1 SW 6020B 09/29/2023 21:46 MHALL3 1 0.249 1 SW 6020E 09/29/2023 21:46 MHALL3 1 0.032 1 SW 6020E 09/29/2023 21:46 MHALL3 1 0.185 1 SW 6020B 09/29/2023 21:46 MHALL3 1 0.077 1 SW 6020E 09/29/2023 21:46 MHALL3 1 0.787 1 SW 6020B 09/29/2023 21:46 MHALL3 1 0.037 1 SW 6020E 09/29/2023 21:46 MHALL3 1 0.18 1 SW 6020E 09/29/2023 21:46 MHALL3 1 0.256 1 SW 6020B 09/29/2023 21:46 MHALL3 1 0.193 1 SW 6020B 09/29/2023 21:46 MHALL3 1 0.035 1 SW 6020E 09/29/2023 21:46 MHALL3 1 0.041 1 SW 6020B 09/29/2023 21:46 MHALL3 1 0.114 1 SW 6020E 09/29/2023 21:46 MHALL3 25 25 1 SM2540C 09/29/2023 09:03 HHOOGKA Certificate of Laboratory Analysis Page 16 of 28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS EB-20230927-0815 Sample #: 2023024031 Collection Date: 09/27/2023 08:15 AM Loc code: MSS EB Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 0.03 J mg/L Fluoride 0.0479 U mg/L Nitrate 0.05 J mg/L Nitrate as N 0.01 J mg-N/L Sulfate 0.0428 U mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 U ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.002 U mg/L Boron (B) 0.018 J mg/L Calcium (Ca) 0.012 U mg/L Iron (Fe) 0.005 J mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 0.008 U mg/L Manganese (Mn) 0.001 U mg/L Zinc (Zn) 0.004 U mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L Arsenic (As) 0.111 U ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 0.185 U ug/L Cobalt (Co) 0.077 U ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.037 U ug/L Molybdenum (Mo) 0.18 U ug/L Nickel (Ni) 0.256 U ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 0.114 U ug/L Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/27/2023 21:50 EBATIAN 0.1 0.0479 1 EPA 9056A 09/27/2023 21:50 EBATIAN 0.1 0.0209 1 EPA 9056A 09/27/2023 21:50 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 21:50 EBATIAN 0.1 0.0428 1 EPA 9056A 09/27/2023 21:50 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 12:16 SNEGLIA 0.005 0.002 1 SW 601 OD 09/29/2023 20:11 CELL106 0.05 0.005 1 SW 601 OD 09/29/2023 20:11 CELL106 0.05 0.012 1 SW 601 OD 09/29/2023 20:11 CELL106 0.01 0.004 1 SW 601 OD 09/29/2023 20:11 CELL106 0.005 0.002 1 SW 601 OD 09/29/2023 20:11 CELL106 0.02 0.008 1 SW 601 OD 09/29/2023 20:11 CELL106 0.005 0.001 1 SW 601 OD 09/29/2023 20:11 CELL106 0.005 0.004 1 SW 601 OD 09/29/2023 20:11 CELL106 1 0.104 1 SW 6020B 09/29/2023 21:55 MHALL3 1 0.111 1 SW 6020B 09/29/2023 21:55 MHALL3 1 0.249 1 SW 6020E 09/29/2023 21:55 MHALL3 1 0.032 1 SW 6020E 09/29/2023 21:55 MHALL3 1 0.185 1 SW 6020B 09/29/2023 21:55 MHALL3 1 0.077 1 SW 6020E 09/29/2023 21:55 MHALL3 1 0.787 1 SW 6020B 09/29/2023 21:55 MHALL3 1 0.037 1 SW 6020E 09/29/2023 21:55 MHALL3 1 0.18 1 SW 6020E 09/29/2023 21:55 MHALL3 1 0.256 1 SW 6020B 09/29/2023 21:55 MHALL3 1 0.193 1 SW 6020B 09/29/2023 21:55 MHALL3 1 0.035 1 SW 6020E 09/29/2023 21:55 MHALL3 1 0.041 1 SW 6020B 09/29/2023 21:55 MHALL3 1 0.114 1 SW 6020E 09/29/2023 21:55 MHALL3 Certificate of Laboratory Analysis Page 17 of 28 This report shall not be reproduced, except in full. Order # J23090511 Site: MSS FB-20230927-0830 Sample #: 2023024032 Collection Date: 09/27/2023 08:30 AM Loc code: MSS QA Matrix: GW RCRA Analyte Result Units Qualifiers RDL MDL DF INORGANIC IONS BY IC - Q23090400 Chloride 0.0154 U mg/L Fluoride 0.0479 U mg/L Nitrate 0.04 J mg/L Nitrate as N 0.01 J mg-N/L Sulfate 0.0428 U mg/L MERCURY (COLD VAPOR) IN WATER - Q23090422 Mercury (Hg) 0.01 U ug/L TOTAL RECOVERABLE METALS BY ICP - Q23090409 Barium (Ba) 0.002 U mg/L Boron (B) 0.012 J mg/L Calcium (Ca) 0.012 U mg/L Iron (Fe) 0.004 U mg/L Lithium (Li) 0.002 U mg/L Magnesium (Mg) 0.008 U mg/L Manganese (Mn) 0.001 U mg/L Zinc (Zn) 0.004 U mg/L TOTAL RECOVERABLE METALS BY ICP-MS - Q23090413 Antimony (Sb) 0.104 U ug/L Arsenic (As) 0.111 U ug/L Beryllium (Be) 0.249 U ug/L Cadmium (Cd) 0.032 U ug/L Chromium (Cr) 0.185 U ug/L Cobalt (Co) 0.077 U ug/L Copper (Cu) 0.787 U ug/L Lead (Pb) 0.037 U ug/L Molybdenum (Mo) 0.18 U ug/L Nickel (Ni) 0.256 U ug/L Selenium (Se) 0.193 U ug/L Silver (Ag) 0.035 U ug/L Thallium (TI) 0.041 U ug/L Vanadium (V) 0.114 U ug/L Method Analysis Date/Time Analyst 0.1 0.0154 1 EPA 9056A 09/27/2023 22:09 EBATIAN 0.1 0.0479 1 EPA 9056A 09/27/2023 22:09 EBATIAN 0.1 0.0209 1 EPA 9056A 09/27/2023 22:09 EBATIAN 0.023 0.002 1 EPA 9056A 09/27/2023 22:09 EBATIAN 0.1 0.0428 1 EPA 9056A 09/27/2023 22:09 EBATIAN 0.05 0.01 1 EPA 7470A 09/29/2023 12:19 SNEGLIA 0.005 0.002 1 SW 601 OD 09/29/2023 20:16 CELL106 0.05 0.005 1 SW 601 OD 09/29/2023 20:16 CELL106 0.05 0.012 1 SW 601 OD 09/29/2023 20:16 CELL106 0.01 0.004 1 SW 601 OD 09/29/2023 20:16 CELL106 0.005 0.002 1 SW 601 OD 09/29/2023 20:16 CELL106 0.02 0.008 1 SW 601 OD 09/29/2023 20:16 CELL106 0.005 0.001 1 SW 601 OD 09/29/2023 20:16 CELL106 0.005 0.004 1 SW 601 OD 09/29/2023 20:16 CELL106 1 0.104 1 SW 6020B 09/29/2023 22:05 MHALL3 1 0.111 1 SW 6020B 09/29/2023 22:05 MHALL3 1 0.249 1 SW 6020E 09/29/2023 22:05 MHALL3 1 0.032 1 SW 6020E 09/29/2023 22:05 MHALL3 1 0.185 1 SW 6020B 09/29/2023 22:05 MHALL3 1 0.077 1 SW 6020E 09/29/2023 22:05 MHALL3 1 0.787 1 SW 6020B 09/29/2023 22:05 MHALL3 1 0.037 1 SW 6020E 09/29/2023 22:05 MHALL3 1 0.18 1 SW 6020E 09/29/2023 22:05 MHALL3 1 0.256 1 SW 6020B 09/29/2023 22:05 MHALL3 1 0.193 1 SW 6020B 09/29/2023 22:05 MHALL3 1 0.035 1 SW 6020E 09/29/2023 22:05 MHALL3 1 0.041 1 SW 6020B 09/29/2023 22:05 MHALL3 1 0.114 1 SW 6020E 09/29/2023 22:05 MHALL3 Qualifiers: J Analyte detected above the MDL, but below the RL. Analyte concentration should be considered an estimate. Certificate of Laboratory Analysis Page 18 of 28 This report shall not be reproduced, except in full. Order # J23090511 Level II QC Summary Q23090400 Dionex INORGANIC IONS BY IC Blank # 1 LCS # 1 MS # 1 MSD # 1 MS # 2 MSD # 2 Parameter Measured Final Units Dil MDL RDL Relative Concentration 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 0.002 0.002 mg/L 1 0.0428 0.1 < MDL Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Chloride 4.98 4.98 mg/L 1 0.0154 5 99.6 80 120 Fluoride 5.14 5.14 mg/L 1 0.0479 5 103 80 120 Nitrate 5.01 5.01 mg/L 1 0.0209 5 100 80 120 Sulfate 5 5 mg/L 1 0.0428 5 99.9 80 120 Parent Sample: J23080627 -- 2023021556 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Chloride 1.97 19.7 mg/L 10 0.0154 5 100 80 120 Fluoride Not Tested mg/L 1 0.0479 5 80 120 Nitrate 6.84 6.84 mg/L 1 0.0209 5 102 80 120 Sulfate 5.17 51.6 mg/L 10 0.0428 5 91 80 120 Parent Sample: J23080627 -- 2023021556 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Chloride 1.95 19.5 mg/L 10 0.0154 5 96.8 80 120 3.45 Fluoride Not Tested mg/L 1 0.0479 5 80 120 Nitrate 6.72 6.72 mg/L 1 0.0209 5 100 80 120 2.37 Sulfate 5.15 51.5 mg/L 10 0.0428 5 87.4 80 120 4.04 Parent Sample: J23090511 -- 2023024019 Parameter Measured Final Units Dil MDL Spike % Recover v LCL UCL Chloride 6.32 6.32 mg/L 1 0.0154 5 101 80 120 Fluoride 5.37 5.37 mg/L 1 0.0479 5 105 80 120 Nitrate 5.81 5.81 mg/L 1 0.0209 5 102 80 120 Sulfate 5.27 5.27 mg/L 1 0.0428 5 102 80 120 Parent Sample: J23090511 -- 2023024019 Parameter Measured Final Units Dil MDL Spike % Recover v LCL UCL RPD Chloride 6.22 6.22 mg/L 1 0.0154 5 99.5 80 120 1.89 Fluoride 5.3 5.3 mg/L 1 0.0479 5 104 80 120 1.36 Nitrate 5.71 5.71 mg/L 1 0.0209 5 99.7 80 120 2.1 Sulfate 5.18 5.18 mg/L 1 0.0428 5 100 80 120 1.71 Qualifier Qualifier Qualifier Qualifier Qualifier Qualifier Certificate of Laboratory Analysis Page 19 of 28 This report shall not be reproduced, except in full. Order # J23090511 Level II QC Summary Q23090422 HG 7470 MERCURY (COLD VAPOR) IN WATER Blank # 1 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.004 0.004 ug/L 1 0.01 0.05 < MDL Blank # 2 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.003 0.003 ug/L 1 0.01 0.05 < MDL Blank # 3 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.006 0.006 ug/L 1 0.01 0.05 < MDL Blank # 4 Parameter Measured Final Units Dil MDL RDL Relative Concentration Qualifier Mercury (Hg) 0.002 0.002 ug/L 1 0.01 0.05 < MDL LCS # 1 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 1.99 1.99 ug/L 1 0.01 2 99.6 85 115 LCS # 2 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 1.98 1.98 ug/L 1 0.01 2 99 85 115 MS # 1 Parent Sample: J23090047 -- 2023021929 Parameter Measured Final Units Dil MDL Spike % Recover v LCL UCL Qualifier Mercury (Hg) 1.16 1.16 ug/L 1 0.01 1 111 75 125 MSD # 1 Parent Sample: J23090047 -- 2023021929 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 1.14 1.14 ug/L 1 0.01 1 109 75 125 1.55 MS # 2 Parent Sample: J23090473 -- 2023023821 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 0.994 0.994 ug/L 1 0.01 1 99.3 75 125 MSD # 2 Parent Sample: J23090473 -- 2023023821 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 0.98 0.98 ug/L 1 0.01 1 97.9 75 125 1.42 MS # 3 Parent Sample: J23090496 -- 2023023951 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 1.1 1.1 ug/L 1 0.01 1 109 75 125 Certificate of Laboratory Analysis Page 20 of 28 This report shall not be reproduced, except in full. Order # J23090511 Level II QC Summary Q23090422 HG 7470 MERCURY (COLD VAPOR) IN WATER MSD # 3 Parent Sample: J23090496 -- 2023023951 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 1.09 1.09 ug/L 1 0.01 1 107 75 125 1.11 MS # 4 Parent Sample: J23090511 -- 2023024025 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Qualifier Mercury (Hg) 1.04 1.04 ug/L 1 0.01 1 103 75 125 MSD # 4 Parent Sample: J23090511 -- 2023024025 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Mercury (Hg) 1.04 1.04 ug/L 1 0.01 1 103 75 125 0.0969 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J23090511 Level II QC Summary Q23100007 ICP_DIS_TRM TOTAL RECOVERABLE METALS BY ICP (DISSOLVED) Blank # 1 Page 21 of 28 Parameter Measured Final Units Dil MDL RDL Relative Concentration Zinc (Zn) -0.000345 -0.000345 mg/L 1 0.004 0.005 < MDL LCS # 1 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Zinc (Zn) 5.08 5.08 mg/L 1 0.004 5 102 80 120 MS # 1 Parent Sample: J23090047 -- 2023021948 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Zinc (Zn) 5.05 5.05 mg/L 1 0.004 5 101 70 130 MSD # 1 Parent Sample: J23090047 -- 2023021948 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Zinc (Zn) 5.04 5.04 mg/L 1 0.004 5 101 70 130 0.297 Qualifier Qualifier Qualifier Qualifier Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J23090511 Level II QC Summary Q23090409 ICP_TRM TOTAL RECOVERABLE METALS BY iCP Blank # 1 Parameter Measured Final Units Dil MDL RDL Relative Concentration Barium (Ba) -0.0012 -0.0012 mg/L 1 0.002 0.005 < MDL Boron (B) -0.000589 -0.000589 mg/L 1 0.005 0.05 < MDL Calcium (Ca) 0.00558 0.00558 mg/L 1 0.012 0.05 < MDL Iron (Fe) 0.000933 0.000933 mg/L 1 0.004 0.01 < MDL Lithium (Li) -0.00124 -0.00124 mg/L 1 0.002 0.005 < MDL Magnesium (Mg) 0.0012 0.0012 mg/L 1 0.008 0.02 < MDL Manganese (Mn) -0.000029 -0.000029 mg/L 1 0.001 0.005 < MDL Zinc (Zn) -0.000047 -0.000047 mg/L 1 0.004 0.005 < MDL LCS # 1 Page 22 of 28 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Barium (Ba) 4.99 4.99 mg/L 1 0.002 5 99.7 80 120 Boron (B) 4.86 4.86 mg/L 1 0.005 5 97.3 80 120 Calcium (Ca) 5.06 5.06 mg/L 1 0.012 5 101 80 120 Iron (Fe) 5 5 mg/L 1 0.004 5 100 80 120 Lithium (Li) 4.83 4.83 mg/L 1 0.002 5 96.6 80 120 Magnesium (Mg) 4.96 4.96 mg/L 1 0.008 5 99.1 80 120 Manganese (Mn) 5.02 5.02 mg/L 1 0.001 5 100 80 120 Zinc (Zn) 5 5 mg/L 1 0.004 5 100 80 120 MS # 1 Parent Sample: J23090047 -- 2023021929 Parameter Measured Final Units Dil MDL Spike % Recover v LCL UCL Barium (Ba) 5.19 5.19 mg/L 1 0.002 5 103 75 125 Boron (B) 5.04 5.04 mg/L 1 0.005 5 101 75 125 Calcium (Ca) 15 15 mg/L 1 0.012 5 102 75 125 Iron (Fe) 5.27 5.27 mg/L 1 0.004 5 103 75 125 Lithium (Li) 5 5 mg/L 1 0.002 5 99.8 75 125 Magnesium (Mg) 9.75 9.75 mg/L 1 0.008 5 98.4 75 125 Manganese (Mn) 5.17 5.17 mg/L 1 0.001 5 103 75 125 Zinc (Zn) 5.11 5.11 mg/L 1 0.004 5 102 75 125 MSD # 1 Parent Sample: J23090047 -- 2023021929 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Barium (Ba) 5.2 5.2 mg/L 1 0.002 5 103 75 125 0.212 Boron (B) 5.01 5.01 mg/L 1 0.005 5 100 75 125 0.597 Calcium (Ca) 15.1 15.1 mg/L 1 0.012 5 103 75 125 0.419 Iron (Fe) 5.27 5.27 mg/L 1 0.004 5 103 75 125 0.0948 Lithium (Li) 4.99 4.99 mg/L 1 0.002 5 99.6 75 125 0.18 Magnesium (Mg) 9.77 9.77 mg/L 1 0.008 5 98.9 75 125 0.225 Manganese (Mn) 5.19 5.19 mg/L 1 0.001 5 104 75 125 0.328 Qualifier Qualifier Qualifier Qualifier Certificate of Laboratory Analysis Page 23 of 28 This report shall not be reproduced, except in full. Order # J23090511 Level II QC Summary Q23090409 ICP_TRM TOTAL RECOVERABLE METALS BY ICP MSD # 1 Parent Sample: J23090047 -- 2023021929 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL RPD Qualifier Zinc (Zn) 5.12 5.12 mg/L 1 0.004 5 102 75 125 0.117 Certificate of Laboratory Analysis Page 24 of 28 This report shall not be reproduced, except in full. Order # J23090511 Level II QC Summary Q23100013 IMS_DIS_TRM TOTAL RECOVERABLE METALS BY ICP-MS (DISSOLVED) Blank # 1 LCS # 1 MS # 1 MSD # 1 Parameter Measured Final Units Dil MDL RDL Relative Concentration Beryllium (Be) 0.002 0.002 ug/L 1 0.249 1 < MDL Cadmium (Cd) 0.003 0.003 ug/L 1 0.032 1 < MDL Chromium (Cr) -0.001 -0.001 ug/L 1 0.185 1 < MDL Copper (Cu) 0.016 0.016 ug/L 1 0.787 1 < MDL Lead (Pb) 0.009 0.009 ug/L 1 0.037 1 < MDL Nickel (Ni) 0.009 0.009 ug/L 1 0.256 1 < MDL Silver (Ag) 0.003 0.003 ug/L 1 0.035 1 < MDL Parameter Measured Final Units Dil MDL S ike % Recovery LCL UCL Beryllium (Be) 50.3 50.3 ug/L 1 0.249 50 101 80 120 Cadmium (Cd) 50.2 50.2 ug/L 1 0.032 50 100 80 120 Chromium (Cr) 51.3 51.3 ug/L 1 0.185 50 103 80 120 Copper(Cu) 51.9 51.9 ug/L 1 0.787 50 104 80 120 Lead (Pb) 50.7 50.7 ug/L 1 0.037 50 101 80 120 Nickel (Ni) 50.8 50.8 ug/L 1 0.256 50 102 80 120 Silver (Ag) 50.9 50.9 ug/L 1 0.035 50 102 80 120 Parent Sample: J23090511 -- 2023024029 Parameter Measured Final Units Dil MDL Spike % Recover v LCL UCL Beryllium (Be) 47.6 47.6 ug/L 1 0.249 50 90.2 75 125 Cadmium (Cd) 48.3 48.3 ug/L 1 0.032 50 96 75 125 Chromium (Cr) 48 48 ug/L 1 0.185 50 95.8 75 125 Copper (Cu) 56.2 56.2 ug/L 1 0.787 50 101 75 125 Lead (Pb) 50.9 50.9 ug/L 1 0.037 50 101 75 125 Nickel (Ni) 165 165 ug/L 1 0.256 50 107 75 125 Silver (Ag) 48.7 48.7 ug/L 1 0.035 50 97.5 75 125 Parent Sample: J23090511 -- 2023024029 Parameter Measured Final Units Dil MDL Spike % Recover v LCL UCL RPD Beryllium (Be) 46.1 46.1 ug/L 1 0.249 50 87.2 75 125 3.44 Cadmium (Cd) 48.9 48.9 ug/L 1 0.032 50 97.2 75 125 1.2 Chromium (Cr) 48.3 48.3 ug/L 1 0.185 50 96.5 75 125 0.757 Copper (Cu) 56.5 56.5 ug/L 1 0.787 50 102 75 125 0.703 Lead (Pb) 51.4 51.4 ug/L 1 0.037 50 103 75 125 1.08 Nickel (Ni) 166 166 ug/L 1 0.256 50 108 75 125 1.35 Silver (Ag) 49.2 49.2 ug/L 1 0.035 50 98.5 75 125 1.01 Qualifier Qualifier Qualifier Qualifier Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J23090511 Level II QC Summary Q23090413 IMS_TRM TOTAL RECOVERABLE METALS BY ICP-MS Blank # 1 Parameter Measured Final Units Dil MDL RDL Relative Concentration Antimony (Sb) -0.024 -0.024 ug/L 1 0.104 1 < MDL Arsenic (As) 0.005 0.005 ug/L 1 0.111 1 < MDL Beryllium (Be) 0.015 0.015 ug/L 1 0.249 1 < MDL Cadmium (Cd) 0.006 0.006 ug/L 1 0.032 1 < MDL Chromium (Cr) -0.118 -0.118 ug/L 1 0.185 1 < MDL Cobalt (Co) -0.001 -0.001 ug/L 1 0.077 1 < MDL Copper (Cu) -0.033 -0.033 ug/L 1 0.787 1 < MDL Lead (Pb) -0.001 -0.001 ug/L 1 0.037 1 < MDL Molybdenum (Mo) 0.009 0.009 ug/L 1 0.18 1 < MDL Nickel (Ni) -0.019 -0.019 ug/L 1 0.256 1 < MDL Selenium (Se) -0.063 -0.063 ug/L 1 0.193 1 < MDL Silver (Ag) 0.009 0.009 ug/L 1 0.035 1 < MDL Thallium (TI) -0.006 -0.006 ug/L 1 0.041 1 < MDL Vanadium (V) -0.017 -0.017 ug/L 1 0.114 1 < MDL LCS # 1 Page 25 of 28 Parameter Measured Final Units Dil MDL Spike % Recover v LCL UCL Antimony (Sb) 49.5 49.5 ug/L 1 0.104 50 99.1 80 120 Arsenic (As) 49.7 49.7 ug/L 1 0.111 50 99.4 80 120 Beryllium (Be) 51.9 51.9 ug/L 1 0.249 50 104 80 120 Cadmium (Cd) 49.5 49.5 ug/L 1 0.032 50 99.1 80 120 Chromium (Cr) 48.9 48.9 ug/L 1 0.185 50 97.8 80 120 Cobalt (Co) 48.7 48.7 ug/L 1 0.077 50 97.3 80 120 Copper (Cu) 48.7 48.7 ug/L 1 0.787 50 97.4 80 120 Lead (Pb) 49.1 49.1 ug/L 1 0.037 50 98.2 80 120 Molybdenum (Mo) 49.5 49.5 ug/L 1 0.18 50 99 80 120 Nickel (Ni) 49 49 ug/L 1 0.256 50 97.9 80 120 Selenium (Se) 47.9 47.9 ug/L 1 0.193 50 95.8 80 120 Silver (Ag) 50.2 50.2 ug/L 1 0.035 50 100 80 120 Thallium (TI) 48.9 48.9 ug/L 1 0.041 50 97.8 80 120 Vanadium (V) 49.3 49.3 ug/L 1 0.114 50 98.6 80 120 MS # 1 Parent Sample: J23090047 -- 2023021934 Parameter Measured Final Units Dil MDL Spike % Recovery LCL UCL Antimony (Sb) 48.8 48.8 ug/L 1 0.104 50 97.5 75 125 Arsenic (As) 47.6 47.6 ug/L 1 0.111 50 95 75 125 Beryllium (Be) 52.1 52.1 ug/L 1 0.249 50 104 75 125 Cadmium (Cd) 49.1 49.1 ug/L 1 0.032 50 98.2 75 125 Chromium (Cr) 49.5 49.5 ug/L 1 0.185 50 97.6 75 125 Cobalt (Co) 47.7 47.7 ug/L 1 0.077 50 94.1 75 125 Qualifier Qualifier Qualifier Certificate of Laboratory Analysis Page 26 of 28 This report shall not be reproduced, except in full. Order # J23090511 Level II QC Summary Q23090413 IMS_TRM TOTAL RECOVERABLE METALS BY ICP-MS MS # 1 Parameter Measured Final Units Dil MDL Copper (Cu) 48.5 48.5 ug/L 1 0.787 Lead (Pb) 48.3 48.3 ug/L 1 0.037 Molybdenum (Mo) 49.3 49.3 ug/L 1 0.18 Nickel (Ni) 48.6 48.6 ug/L 1 0.256 Selenium (Se) 46.3 46.3 ug/L 1 0.193 Silver (Ag) 49.9 49.9 ug/L 1 0.035 Thallium (TI) 47.6 47.6 ug/L 1 0.041 Vanadium (V) 49.7 49.7 ug/L 1 0.114 MSD # 1 Parameter Measured Final Units Dil MDL Antimony (Sb) 49.2 49.2 ug/L 1 0.104 Arsenic (As) 48.1 48.1 ug/L 1 0.111 Beryllium (Be) 54.3 54.3 ug/L 1 0.249 Cadmium (Cd) 49.7 49.7 ug/L 1 0.032 Chromium (Cr) 50.6 50.6 ug/L 1 0.185 Cobalt (Co) 48.3 48.3 ug/L 1 0.077 Copper (Cu) 49.1 49.1 ug/L 1 0.787 Lead (Pb) 49 49 ug/L 1 0.037 Molybdenum (Mo) 49.9 49.9 ug/L 1 0.18 Nickel (Ni) 48.8 48.8 ug/L 1 0.256 Selenium (Se) 47.4 47.4 ug/L 1 0.193 Silver (Ag) 50.2 50.2 ug/L 1 0.035 Thallium (TI) 48.2 48.2 ug/L 1 0.041 Vanadium (V) 50.4 50.4 ug/L 1 0.114 Parent Sample: J23090047 -- 2023021934 Spike % Recovery LCL UCL 50 95.3 75 125 50 96.3 75 125 50 97.2 75 125 50 95.4 75 125 50 92.7 75 125 50 98.5 75 125 50 95.1 75 125 50 98.4 75 125 Parent Sample: J23090047 -- 2023021934 Spike % Recovery LCL UCL RPD 50 98.2 75 125 0.74 50 96 75 125 1.04 50 109 75 125 4.25 50 99.3 75 125 1.14 50 99.8 75 125 2.24 50 95.3 75 125 1.23 50 96.5 75 125 1.31 50 97.7 75 125 1.41 50 98.4 75 125 1.21 50 95.7 75 125 0.293 50 94.7 75 125 2.17 50 99.2 75 125 0.686 50 96.4 75 125 1.33 50 99.8 75 125 1.43 Qualifier Qualifier Certificate of Laboratory Analysis Page 27 of 28 This report shall not be reproduced, except in full. Order # J23090511 Level II QC Summary Q23090428 TDS TOTAL DISSOLVED SOLIDS Blank # 1 Blank # 2 Parameter Measured Final TDS 0 Parameter Measured Final TDS -0.1 Duplicate # 1 Parameter Measured Final TDS 56 Duplicate # 2 Parameter Measured Final TDS 530 LCS # 1 LCS # 2 Parameter Measured Final TDS 485 Parameter Measured Final TDS 485 Units Dil MDL RDL Relative Concentration Qualifier mg/L 1 25 25 < MDL Units Dil MDL RDL Relative Concentration Qualifier mg/L 1 25 25 < MDL Parent Sample: J23090511 -- 2023024019 Units Dil MDL RPD Qualifier mg/L 1 25 3.64 Parent Sample: J23090517 -- 2023024071 Units Dil MDL RPD Qualifier mg/L 1 25 0.377 Units Dil MDL Spike % Recovery LCL UCL Qualifier mg/L 1 25 500 97 90 110 Units Dil MDL Spike % Recovery LCL UCL Qualifier mg/L 1 25 500 97 90 110 Page 28 of 28 CHAIN OF CUSTODY RECORD AND ANALYSIS RFOtIFST FORM Duke En. ---Anel Ilaborito --•' r------------------------- ---•-•-•-•-----------•-•-•-•-•-•-•---------------- -•......................... .......................................................................... r0Y Y ry-99 An 1 Laboratory Use Only �%DUKE—IcoNmO nlulldlg746) Matrix WATER ENERGY ,asssH.a..r.rryRd ;;order#�l89a03iilj i ,.ma..oa..awren Nc_x_ sc_ Iwntenvnle, n.C. mre iLogped BY D me / pul arsefns /%�/ SAMPLE PROGRAM fA&URL?`+_e_p?e ('�/ Ground Weter X NPDES Project Name MARSHALL FGD LANDFILL P^°"`"°: iV°nd°r -S( Drinking Water_ UST_ ! i I Page _1_of1_ ORIGINALDtoS BBCOPY to CLIENT Confer em C RCRA Waste _ ■� Client ASHLEY HEALY, BRYAN MOELLER, !Po a - - - .._..- - --.._RLJ_.-- -._.._..----- - - - --._.._..--------- --- --- - - - - - - DEE O-BRIEN, JOSH STOWE,DAVID HANLEY I i Filtration (0.45 um) 8 Unfiltered b Filtered Operating Unit: MS00 Procass:NGRDWfR Account: :._.._.._.._.._.._.._.._.. Preservative ICE ICE ................................................ Project•. AMS000640 Activity ID: Facility iMMSS TEST_SWT Container Volume (mL) Soo 300 Soo 250 ..... Program I EQuiS Task Code: MSS I LF I Sub-Programrfask Code: Container Type HOPE PET PET HDPE .,usmmcr fo conrPlefc all appropnafe raon-shaded areas. m ¢ O ._. _. _. _. _. _. _. ! Sample Description or ID P P Collectbn Inlom Information SAMPLE ID i NUMBER TO. Dab Time Primed Name Si nature (Metals Prep - TRM) ICP - SW6010D: Be, B, Ca, Fe, Li, Mg, Mn, Zn (8)1 Hg EPA 7470A I INS - SW60208: Sb, As, Ba, Cd, Cy Co, Cu, Pb, Mo, Ni, Se, AgTl, V (l4)Pb, EPA 9056: Cl, F, NO3-N (48 Hr Hold Time), SO4 ) TD$ SW60101) Zn I SVM20B Be, Cd, Cr, Cu, NI, Ag C � ! MSS_MS-B �� 4-Z7-2 GASg (ONItr 2 N M X 1 1 1 3 i.i9@104ma i MSS-MS-9 C'1 t0ZO X 1 1 t 3 :.�9l�94tlhBYi MSS_MS-10 0935 X 1 1 1 3 f29l9G3a{0 a MSS_MS-11 Uq So ETIP11V SAI,Ni X 1 1 1 3 lbl99A949S MSS_MS-12 S�/ (tU0 X 1 1 1 3 T tlll"41 �e li MSS_MS-13 Oq0$ ETtIAN S,+�IM X 1 1 1 3 i �ese9aai�asr. MSS _M S-14 X 1 1 1 3 i. 3tM' MSS y V i- l 120 UVA-01Z LA HoaA X 1 1 1 3 ^W2&Q+n+,,,:,' MSS MS-16 X 1 1 1 3 IAG9_3bt�1-(TGBtF}- G72 .� _ .- — �. y -�— •4— -4- 1M30t9499 I i—i MSS_C1-LEACHATE I y q-VN,3 0SSo LOAYtOC %ANON x 1 1 1 1 4 L2QV" A11& MSS_FD - wZ,30g211 - I — CjUI{N 5A1tjL4 X MSS _EB- W7-30927- 0915 9b) 08 1 i CVV-'0Q- 7AµVIZA x 1 1 O 4 MSS_FB- 20 230927 -0830 OP 30 X 1 1 2 i t Customer to si n &date be ow Relinquished 8y Daterrime 9-? 2_21 r2To Ac d By: D telTime ! u_ Requested Turnaround Relinquished By OaterTlme Accepted By: Daterrime m v 21 Days rt c y Relinquished By Datertime Accepted By: DeterTime .. E c E C y 14 Days _X SesYLocked By Daterrlme Sealedll.-1 Opened By Detertime a '- 2 E - � 7 Days Comments Regulatory Agency: NCDENR/DWM - SW Section - NCDEQ EDD Required I Permit #18-09 EQUIS EDD REQUIRED Use indicated or comparable methods. Note: Hardness by Calculation (Ca + Mg ICP_TRM) added to SW-1 e` o V 'Other •Add. Cost Will Apply Semiannual Water Quality Monitoring Report — September 2023 Sampling Event Marshall Steam Station — FGD Residue Landfill (Permit No. 1809-INDUS) Terrell, North Carolina APPENDIX C TIME VERSUS CONSTITUENT CONCENTRATIONS PLOTS L7 synTerra Science & Engineering Consultants MS-8 MS-10 10 10 9 9 8 8 D 6 D 6 -0 c 5 -0 5 c 4 S 4 Q' 3 a 3 2 2 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N N N N N N N N N N N N N N N N N N N N N N N N N N O O V OD O O O O O co NO N N W O A O O V O O O O O O O O 0 W co O N W O_ O O A (Ji O O O O O O O O O N N N N V Do O O N W A Date Date MS-11 MS-12 10 10 9 9 8 8 D 6 6- -2 -o c 5 -0 5 c 4 4 2 Q' 3 = 3 2 2 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o O o O o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N N N N O O O O N N N N N N N N N N N N O O O O O O O O O O O Cl N N O O 71 N OO N N N N OO O O O N ON N N N N Cl ClN N ON ClO O O O OD O O N NNN N W A cy, O) V 00 (D O W O VOD OO CD O — W _ A U. 0) jNV V OD (D O WN? Date Date LEGEND Notes: S.U.— Standard units 15A NCAC 02L PH STANDARD (6.5-8.5) DUKE DRAWN BY: D. AVARD DATE: 06/06/2022 APPENDIX C � Deteat tect ENERGY REVISED BY: K. O'REILLY DATE: 12/04/2023 TIME VERSUS PH CONCENTRATIONS GAROLI�: CHECKED BY: T. COLTON DATE: 12/04/2023 FGD LANDFILL APPROVED BY: T. COLTON DATE: 12/04/2023 SEMIANNUAL WATER QUALITY 410 PROJECT MANAGER: T. COLTON MONITORING REPORT 1 MARSHALL STEAM STATION www.synterracorp.com WnTerm TERRELL, NORTH CAROLINA MS-13 MS-14 10 10 9 9 8 8 N 7 7 6 6 5 5 ca ca 4 4 2 CL 3 2 CL 3 2 2 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N N N N N N N N N fJ N N N O O N O N N O O N O N O N N N N N N N N N N N N N N N N N N OD (OO O N W A Cn O V co CD O j N W ? O OV co O O_ O O O OOD w O — N W O_ A M O V co CD O j N W A Date Date MS-15 MS-16 10 10 9 N A — 8 8 7 N 7 6 6- 5- 4 4 CL 3 CL 3 2 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 NO NO N N N N ON ON ON ON ON ON ON N O ON ON ON ON ON ON Cl OOO V OD w O O W O A Cf 0) --4 co w O O O O jN O W O ? V OD w O — N W A N D) V coOD w O j N W ? Date Date LEGEND Notes: s.U.— standard Units 15A NCAC 02L PH STANDARD (6.5-8.5) DUKE DRAWN BY: D. AVARD DATE: 06/06/2022 APPENDIX C Detedt tect ENERGY REVISED BY: K. Y DATE: 12/04/2023 TIME VERSUS PH CONCENTRATIONS CAROLIN.• COLTON CHECKED BY: T. COLTON DATE: 12/04/2023 FGD LANDFILL APPROVED BY: T. COLTON DATE: 12/04/2023 SEMIANNUAL WATER QUALITY 41P PROJECT MANAGER: T. COLTON MONITORING REPORT MARSHALL STEAM STATION www.synterracorp.com synTerra TERRELL, NORTH CAROLINA MS-1 5 35 J 28 0) =. 0 cu 21 aD U 0 U � 14 0 U 7 Q o 1 Q 1 o 1 0 1 0 1 0 0 0 1 0 0 0 1 1 1 0 0 0 1 1 1 0 0 0 1 0 1 N3 N N N IV N N N N IV N N IV IV N N N N 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 CD a CD s s 1 1 1 1 1 s N N N N IV 4 00 (D a N W -0:1 01 d) -I OO (D Q N W -1�:. Date LEGEND Notes: 15A NCAC 02L CHROMIUM STANDARD DUKE DRAWN BY: D. AVARD DATE: 06/06/2022 APPENDIX C Non -detect Detect µg/L— micrograms per liter (10 µg/L) 441) r ENERGY REVISED BY: K. O'REILLY DATE: 12/04/2023 TIME VERSUS CHROMIUM CONCENTRATIONS CHECKED BY: T. COLTON DATE: 12/04/2023 FGD LANDFILL APPROVED BY: T. COLTON DATE: 12/04/2023 SEMIANNUAL WATER QUALITY ,trip PROJECT MANAGER: T. COLTON MONITORING REPORT MARSHALL STEAM STATION www.synterracorp.com synTerm TERRELL, NORTH CAROLINA MS-1 2 10 8 J o � Cu U 0 U 4 Cu 0 V r V 0 0 0 0 0 0 0 0 N 1 N 1 N N N N N R] 0 O 0 0 C)Q C) � � Q —4 oo (o 0 1 N w 4i.. Date LEGEND Notes: 15A NCAC 02L COBALT STANDARD DUKE r� DRAWN BY: D. AVARD DATE: 06/06/2022 APPENDIX C Non -detect Detect µg/L— micrograms per liter (1 µg/L) NERVr Y ENERGY REVISED BY: K. O'REILLY DATE: 12/04/2023 TIME VERSUS COBALT CONCENTRATIONS CHECKED BY: T. COLTON DATE: 12/04/2023 FGD LANDFILL APPROVED BY: T. COLTON DATE: 12/04/2023 SEMIANNUAL WATER QUALITY ,trip PROJECT MANAGER: T. COLTON MONITORING REPORT MARSHALL STEAM STATION www.synterracorp.com synTerm TERRELL, NORTH CAROLINA MS-1 5 2000 1600 J 0 1200 Cu aD U 0 800 U 0 L H 11 V o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N N N N N N N N N N N N N N N N N N 0 a 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 � � � � � 1 1 1 1 � N N N N N 4 Od (D O N W Gil ai —1 07 (D O N W 4i.. Date LEGEND Notes: 15A NCAC 02L IRON STANDARD — micrograms liter (300 DUKE DRAWN BY: D. AVARD DATE: 06/06/2022 APPENDIX C Non -detect � Detect µg/Lper µg/L) r tENERGY REVISED BY: K. O'REILLY DATE: 12/04/2023 TIME VERSUS IRON CONCENTRATIONS NERVY CHECKED BY: T. COLTON DATE: 12/04/2023 FGD LANDFILL APPROVED BY: T. COLTON DATE: 12/04/2023 SEMIANNUAL WATER QUALITY ,trip PROJECT MANAGER: T. COLTON MONITORING REPORT MARSHALL STEAM STATION www.synterracorp.com synTerm TERRELL, NORTH CAROLINA