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HomeMy WebLinkAbout1804_DukeMarshallDryAsh_Aug2016_2ndSemiAnnual_DIN26923_20161025 Marshall Steam Station Semiannual Groundwater Monitoring Report Dry Ash Landfill, Permit No. 1804 August 2016 Sampling Event October 25, 2016 Duke Energy Carolinas, LLC | Semiannual Groundwater Monitoring Report Marshall Steam Station Dry Ash Landfill, Permit No.1804 August 2016 Sampling Event Contents ii Contents Page Report Verification ......................................................................................................................... i Contents ........................................................................................................................................ ii Section 1 - Background ................................................................................................................. 1 Section 2 - Methods ...................................................................................................................... 2 2.1 Sampling and Analysis Methods .................................................................................... 2 2.2 Statement of Work .......................................................................................................... 2 Section 3 - Results ........................................................................................................................ 4 3.1 Site Groundwater Flow ................................................................................................... 4 3.2 Analytical Results ........................................................................................................... 4 FIGURES 1. Site Location Map 2. Sample Locations 3. Generalized Groundwater Surface Contours TABLES 1. Well Construction Information 2. Groundwater Flow Velocities 3. Field Data Parameters 4. Groundwater Field and Analytical Results 5. Field and Analytical Results that Equal or Exceed NCAC 2L Groundwater Quality Standards APPENDICES A. Field Sampling Forms B. Laboratory Report and Chain-of-Custody Forms Duke Energy Carolinas, LLC | Semiannual Groundwater Monitoring Report Marshall Steam Station Dry Ash Landfill, Permit No.1804 August 2016 Sampling Event Section 1 - Background 1 Section 1 - Background The Marshall Dry Ash Landfill is located at Marshall Steam Station which is owned and operated by Duke Energy Carolinas, LLC (Duke Energy). Marshall Steam Station is a four-unit, coal-fired generating facility located on Lake Norman in Catawba County, North Carolina. The Marshall Dry Ash Landfill consists of two separate disposal areas permitted in December 1983 under North Carolina Department of Environmental Quality (NCDEQ) Solid Waste Permit No. 1804. Placement of fly-ash began in September 1984 in the area designated as Phase I. Phase I consists of approximately 14.5 acres and approximately 280,000 tons of fly-ash placed between September 1984 and March 1986. Placement of ash in this area was completed around March 1986. Placement of ash in Phase II, approximately 46 acres, began around March 1986 and was completed in 1999. The location of the landfill and nearby surrounding areas is shown on Figure 1. The landfill is located north of the power plant and south of Island Point Road. The Marshall Steam Station ash basin is located adjacent to the western boundary of the landfill. The groundwater monitoring system for the Marshall Dry Ash Landfill consists of the following: Monitoring Wells: MW-1 MW-2 MW-3 MW-4 MW-5 Observation Well: OB-1 OB-2 OB-3 The locations of the wells are shown on Figure 2. Monitoring wells MW-2, MW-3, and MW-5 are located adjacent to the 46-acre landfill. Monitoring well MW-1 and observation well OB-1 are located adjacent to the 14.5-acre landfill. Observation wells OB-1, OB-2, and OB-3 are used to measure groundwater levels only. Observation wells OB-2 and OB-3 were added to the monitoring location list in the Post-Closure Ground-Water Monitoring Program Sampling and Analysis Plan1 (SAP) upon approval from NCDEQ Division of Waste Management. These observation wells were originally named MW-6 and MW-7 and appear as such in the field sampling forms in Appendix A. Monitoring well MW-4 is located upgradient from the 46-acre landfill and is described in the SAP as representing upgradient groundwater quality. All of the groundwater monitoring wells are screened to monitor the shallow aquifer. Table 1 presents well construction information for the landfill monitoring wells. MW-2 is located 98.5 feet inside of the landfill review boundary and MW-3 is located 43.8 feet inside of the landfill review boundary. 1 Groundwater Monitoring Program – Sampling and Analysis Plan, Marshall Steam Station Dry Ash Landfill, Permit No. 1804, October 22, 2012. Approved on August 15th, 2015. Duke Energy Carolinas, LLC | Semiannual Groundwater Monitoring Report Marshall Steam Station Dry Ash Landfill, Permit No.1804 August 2016 Sampling Event Section 2 - Methods 2 Section 2 - Methods 2.1 Sampling and Analysis Methods Groundwater sampling and documentation of sampling activities were performed by Duke Energy personnel (Field Certification #5193) according to the North Carolina Solid Waste Management Guidelines. Copies of the field sampling forms are included in Appendix A. The parameters and constituents reported were selected by Duke Energy and the North Carolina Department of Environmental Quality (NCDEQ) Division of Solid Waste and were analyzed by the Duke Energy Analytical Laboratory (North Carolina Laboratory Certification #248). The groundwater samples were analyzed for the following constituents and/or parameters:  Barium, boron, calcium, chromium, copper, iron, manganese, nickel, silver, and zinc using Solid Waste (SW)-8462 Method 6010D  Arsenic, cadmium, lead, and selenium using SW-846 Method 6020B  Mercury using U.S. Environmental Protection Agency (EPA) Method 7040A  Total Dissolved Solids using Standard Method (SM) 2540C  Chloride, fluoride, nitrate as nitrogen, and sulfate using SW-846 Method 9056A 2.2 Statement of Work HDR completed the following tasks:  Received field sampling information provided by Duke Energy for monitoring wells MW-1, MW-2, MW-3, MW-4, and MW-5 and water level information for observation wells OB-1, OB-2, and OB-3. The samples were collected on August 3, 2016, and HDR received the data on August 24, 2016.  Reviewed the laboratory analytical results for samples. The Electronic Data Deliverable (EDD) provided by Duke Energy was adapted to conform to the format requirements of the NCDEQ EDD template. HDR added an italicized J data qualifier (J) to indicate a detected concentration that equals or is greater than the laboratory’s method reporting limit (MRL) but less than the Solid Waste Section Limit3 (SWSL). A copy of the original EDD is retained in HDR’s files. 2 EPA Hazardous Waste Test Methods (SW-846); available online at https://www.epa.gov/hw-sw846 (Accessed August 30, 2016) 3 The Solid Waste Section Limit (SWSL) is defined by NCDEQ as the lowest amount of analyte in a sample that can be quantitatively determined with suitable precision and accuracy. The SWSL is the concentration below which reported results must be qualified as estimated. NCDENR Division of Waste Management Memorandum dated February 23, 2007. Duke Energy Carolinas, LLC | Semiannual Groundwater Monitoring Report Marshall Steam Station Dry Ash Landfill, Permit No.1804 August 2016 Sampling Event Section 2 - Methods 3  Developed a generalized groundwater surface contour map using map data and groundwater elevation data supplied by Duke Energy. Calculated groundwater flow velocities based on groundwater surface contours.  Prepared and submitted this Semiannual Groundwater Monitoring Report to Duke Energy. Duke Energy Carolinas, LLC | Semiannual Groundwater Monitoring Report Marshall Steam Station Dry Ash Landfill, Permit No.1804 August 2016 Sampling Event Section 3 - Results 4 Section 3 - Results 3.1 Site Groundwater Flow Generalized groundwater surface contours and groundwater flow direction arrows for the site are shown on Figure 3. These contours were developed using the groundwater elevations measured in the wells on the date of sampling and using the approximate surface water elevations for the Marshall Ash Basin and the adjacent Lake Norman. Calculated groundwater flow velocities are presented in Table 2. The ground surface in the area of the larger landfill slopes from the elevation along Island Point Road (located north of MW-4), approximate elevation 880 feet to 890 feet, downward toward the Marshall Ash Basin which has a surface water elevation of approximately 790 feet. Lake Norman is located to the east of the Marshall Ash Basin. The full pond elevation of Lake Norman is 760 feet. Groundwater flow at the site is from areas of higher topography toward the ash basin and on toward Lake Norman. Monitoring well MW-4 is located north of the 46-acre landfill and is at the highest topographic elevation. Groundwater flow is generally from MW-4 toward the 46-acre landfill and to the ash basin. It is expected that flow would be from the topographically higher region north of MW-3 and MW-5 toward the 46-acre landfill, or in the case of MW-5, toward the portion of ash basin located to the east of the 46-acre landfill. Monitoring well MW-3 was installed in 1989 near the review boundary at that time and is approximately 75 feet outside of the limit of waste. Due to a property purchase in 2013, monitoring well is located approximately 44 feet inside of the landfill review boundary. The water elevation at monitoring well MW-3 is approximately the same as the pond elevation of two adjacent ponded areas. These ponded areas were part of the original ash basin and were cut off from the main body of the ash basin during construction of the 46-acre landfill. Monitoring well MW-5 is located on the east side of the 46-acre landfill adjacent to an inactive portion of the ash basin. This inactive portion of the ash basin no longer contains appreciable free water and is filled with ash that was sluiced from the ash basin. The groundwater flow in the region near the 14.5-acre landfill area appears to be from the ash basin (elevation 790 feet) toward the arm of Lake Norman (elevation 760 feet) located east of OB-1 and MW-1. 3.2 Analytical Results A summary of the field data is presented in Table 3. The field and laboratory results of groundwater sampling are summarized in Table 4. Concentrations with values that equal or are greater than the SWSLs are noted on Table 4 by gray cells. Concentrations with values that attain or exceed the Title 15A NCAC 02L .0202 (g) Standards (2L Standards) are noted on Table 4 by bold font. A summary of the field and analytical results that attain or exceed the 2L Standards and a preliminary analysis of the cause and significance of the exceedances are presented in Table 5. Duke Energy Carolinas, LLC | Semiannual Groundwater Monitoring Report Marshall Steam Station Dry Ash Landfill, Permit No.1804 August 2016 Sampling Event Section 3 - Results 5 Selected samples were diluted as is normal laboratory practice to bring samples to the calibrated range of the analysis. Specifics regarding the samples that were diluted, including the dilution amount, are reported in the EDD. The laboratory report and chain-of-custody forms can be found in Appendix B. HDR prepared and submitted an assessment to NCDEQ on historic exceedances of the 2L Standards at this landfill (Groundwater Assessment, Marshall Steam Station, Dry Ash Landfill, December 21, 2012). The report assessed 2L Standard exceedances for manganese at monitoring wells MW-3 and MW-5. The report concluded that for the period of analytical results reviewed, the manganese exceedances at monitoring wells MW-3 and MW-5 were likely the result of naturally-occurring manganese and were not caused by impacts from the landfill. FIGURES TABLES Ta b l e 1 - W e l l C o n s t r u c t i o n I n f o r m a t i o n Du k e E n e r g y C a r o l i n a s , L L C / M a r s h a l l S t e a m S t a t i o n Dr y A s h L a n d f i l l - P e r m i t N o . 1 8 0 4 La t i t u d e L o n g i t u d e MW - 1 8 / 1 5 / 1 9 8 9 3 5 . 6 1 0 3 7 9 7 - 8 0 . 9 6 0 9 1 2 9 8 2 3 . 7 0 8 2 1 . 2 0 2 . 5 0 7 7 2 . 3 9 5 1 . 3 1 7 8 . 7 5 6 8 . 7 5 6 8 . 7 5 - 7 8 . 7 5 S a p r o l i t e 2 P V C MW - 2 8 / 1 5 / 1 9 8 8 3 5 . 6 1 3 1 9 7 3 - 8 0 . 9 6 7 9 7 5 3 7 9 7 . 2 1 7 9 4 . 9 0 2 . 3 1 7 8 9 . 9 6 7 . 2 6 3 5 . 1 0 2 5 . 1 0 2 5 . 1 0 - 3 5 . 1 0 S a p r o l i t e 2 P V C MW - 3 8 / 1 5 / 1 9 8 9 3 5 . 6 1 9 1 3 5 5 - 8 0 . 9 6 7 2 3 4 1 8 1 3 . 0 7 8 1 1 . 0 0 2 . 0 7 8 0 4 . 1 7 8 . 9 0 2 8 . 1 5 1 8 . 1 5 1 8 . 1 5 - 2 8 . 1 5 S a p r o l i t e 2 P V C MW - 4 8 / 1 5 / 1 9 8 9 3 5 . 6 2 0 9 1 8 4 - 8 0 . 9 7 0 3 6 2 3 8 6 7 . 1 5 8 6 4 . 5 0 2 . 6 5 8 3 0 . 6 3 3 6 . 7 5 5 0 . 2 0 4 0 . 2 0 4 0 . 2 0 - 5 0 . 2 0 S a p r o l i t e 2 P V C MW - 5 8 / 1 0 / 2 0 0 0 3 5 . 6 1 5 8 4 5 0 - 8 0 . 9 6 5 6 9 0 1 8 2 2 . 6 9 8 2 0 . 1 9 2 . 5 0 7 9 6 . 6 0 2 6 . 0 9 3 0 . 7 1 2 0 . 7 1 2 0 . 7 1 - 3 0 . 7 1 S a p r o l i t e 2 P V C OB - 1 6 / 2 8 / 1 9 8 9 3 5 . 6 1 0 0 5 0 7 - 8 0 . 9 6 1 0 5 3 0 8 2 5 . 8 5 8 2 3 . 6 0 2 . 2 5 7 7 9 . 4 0 4 6 . 4 5 6 5 . 5 0 5 5 . 5 0 5 5 . 5 0 - 6 5 . 5 0 S a p r o l i t e 2 P V C OB - 2 1 2 / 1 7 / 2 0 1 0 3 5 . 6 1 6 8 1 6 4 - 8 0 . 9 6 9 5 6 4 0 9 1 9 . 6 5 9 1 7 . 1 8 2 . 4 7 7 9 7 . 5 1 1 2 2 . 1 4 1 2 2 . 1 4 1 0 2 . 5 0 1 0 2 . 5 0 - 1 2 2 . 1 4 S a p r o l i t e 2 P V C OB - 3 1 2 / 1 6 / 2 0 1 0 3 5 . 6 1 7 2 2 2 7 - 8 0 . 9 7 0 4 3 8 7 8 5 9 . 1 6 8 5 6 . 5 6 2 . 6 0 8 1 4 . 2 8 4 4 . 8 8 5 7 . 2 5 3 9 . 0 0 3 9 . 0 0 - 5 7 . 2 5 S a p r o l i t e 2 P V C No t e s : 1 . T O C i n d i c a t e s t o p o f c a s i n g . 2 . f t . i n d i c a t e s f e e t . 3 . i n . i n d i c a t e s i n c h e s n o m i n a l d i a m e t e r . 4 . P V C i n d i c a t e s p o l y v i n y l c h l o r i d e . 5 . P W R i n d i c a t e s p a r t i a l l y w e a t h e r e d r o c k . 6 . H o r i z o n t a l d a t u m N A D 8 3 . 7 . V e r t i c a l d a t u m i s N A V D 8 8 . 8 . D e p t h t o g r o u n d w a t e r g a u g e d o n A u g u s t 3 , 2 0 1 6 . 9 . I n f o r m a t i o n p r o v i d e d b y D u k e E n e r g y o n A u g u s t 2 4 , 2 0 1 6 . 10 . S c r e e n e d g e o l o g y p r e s e n t e d f o r O B - 1 i s f r o m M W - 1 , a s t h e g e o l o g y a t O B - 1 w a s n o t r e c o r d e d a n d M W - 1 i s t h e c l o s e s t p r o x i m i t y t o O B - 1 . Sc r e e n e d I n t e r v a l be l o w T O C (f t . ) Casing TypeWell Diameter (in.)Geology of Screened Interval We l l S t i c k - u p He i g h t A b o v e Gr o u n d S u r f a c e (f t . ) Gr o u n d w a t e r Ele v a t i o n (f t . ) De p t h t o W a t e r be l o w T O C (f t . ) To t a l W e l l De p t h b e l o w TO C (f t . ) De p t h t o T o p o f Sc r e e n f r o m T O C (f t . ) Co o r d i n a t e s We l l I D We l l In s t a l l a t i o n Da t e W e l l T O C Ele v a t i o n ( f t . ) Gr o u n d S u r f a c e El e v a t i o n (f t . ) Ta b l e 2 - G r o u n d w a t e r F l o w V e l o c i t i e s Du k e E n e r g y C a r o l i n a s , L L C / M a r s h a l l S t e a m S t a t i o n Dr y A s h L a n d f i l l - P e r m i t N o . 1 8 0 4 MW - 1 77 5 77 0 12 6 0 . 0 4 0 . 4 1 0. 2 5 9 0 . 0 6 MW - 2 79 0 78 9 . 9 6 41 0 . 0 0 1 0 . 4 1 0. 2 5 9 0 . 0 0 2 MW - 3 80 5 80 4 . 1 7 22 0 . 0 4 0 . 4 1 0. 2 5 9 0 . 0 6 MW - 4 83 0 . 6 3 82 5 18 8 0 . 0 3 0 . 4 1 0. 2 5 9 0 . 0 5 MW - 5 80 0 79 5 15 6 0 . 0 3 0 . 4 1 0. 2 5 9 0 . 0 5 OB - 1 78 0 77 5 12 1 0 . 0 4 0 . 4 1 0. 2 5 9 0 . 0 7 OB - 2 80 0 79 5 81 3 0 . 0 1 0 . 4 1 0. 2 5 9 0 . 0 1 OB - 3 81 5 81 0 26 0 0 . 0 2 0 . 4 1 0. 2 5 9 0 . 0 3 No t e s : 1 . L i n e a r d i s t a n c e m e a s u r e d t h r o u g h m o n i t o r i n g w e l l s i s a p p r o x i m a t e l y p e r p e n d i c u l a r t o g r o u n d w a t e r c o n t o u r s . 2 . A t m o n i t o r i n g w e l l l o c a t i o n s w h e r e d o w n g r a d i e n t c o n t o u r s a r e n o t p r e s e n t , t h e g r o u n d w a t e r e l e v a t i o n a t t h e m o n i t o r i n g w e l l i s u s e d a s t h e d o w n g r a d i e n t g r o u n d w a t e r e l e v a t i o n . 3 . A t m o n i t o r i n g w e l l l o c a t i o n s w h e r e u p g r a d i e n t c o n t o u r s a r e n o t p r e s e n t , t h e g r o u n d w a t e r e l e v a t i o n a t t h e m o n i t o r i n g w e l l i s u s e d a s t h e u p g r a d i e n t g r o u n d w a t e r e l e v a t i o n . 4 . M o n i t o r i n g w e l l s a r e n o t l i s t e d w h e r e i n s u f f i c i e n t g r o u n d w a t e r c o n t o u r i n f o r m a t i o n o r w e l l c o n s t r u c t i o n d a t a i s a v a i l a b l e t o c a l c u l a t e v e l o c i t y . 5 . H y d r a u l i c g r a d i e n t s a n d g r o u n d w a t e r v e l o c i t i e s a r e a p p r o x i m a t e . 6 . H y d r a u l i c c o n d u c t i v i t y p r e s e n t e d i s t h e g e o m e t r i c m e a n o f t h e c o n d u c t i v i t y d a t a f o r t h e a l l u v i u m / s o i l / s a p r o l i t e a n d P W R h y d r o s t r a t i g r a p h i c l a y e r i n t h e H D R C o n d u c t i v i t y D a t a b a s e ( u n p u b l i s h e d d a t a f r o m P i e d m o n t C a r o l i n a s i t e s w i t h f o l i a t e d / l a y e r e d b e d r o c k ) . 7 . E f f e c t i v e p o r o s i t y p r e s e n t e d i s t h e m e a n v a l u e o f t h e a l l u v i u m / s o i l / s a p r o l i t e a n d P W R h y d r o s t r a t i g r a p h i c l a y e r e s t i m a t e d f r o m s o i l t e s t i n g u s i n g F e t t e r / B e a r D i a g r a m s . Ef f e c t i v e Po r o s i t y (% / 1 0 0 ) Groundwater Velocity (ft/day) We l l I D U p g r a d i e n t Gr o u n d w a t e r Co n t o u r E l e v a t i o n (f t ) D o w n g r a d i e n t Gr o u n d w a t e r Co n t o u r E l e v a t i o n (f t ) Li n e a r Di s t a n c e Be t w e e n Co n t o u r s th r o u g h W e l l (f t ) Hy d r a u l i c Gr a d i e n t (f t / f t ) Hy d r a u l i c Co n d u c t i v i t y (f t / d a y ) Ta b l e 3 - F i e l d D a t a P a r a m e t e r s Du k e E n e r g y C a r o l i n a s , L L C / M a r s h a l l S t e a m S t a t i o n Dr y A s h L a n d f i l l - P e r m i t N o . 1 8 0 4 8/ 3 / 2 0 1 6 M W - 1 7 8 . 7 5 5 1 . 3 1 7 7 2 . 3 9 N o r m a l N o n e C P N / A 4 . 4 8 1 3 . 5 0 N O 1 5 . 9 2 3 8 0 5.6 4 . 3 3 6 6 0 . 4 5 8/ 3 / 2 0 1 6 M W - 2 3 5 . 1 0 7 . 2 6 7 8 9 . 9 6 N o r m a l N o n e C P N / A 4 . 5 4 1 4 . 2 5 N O 1 6 . 0 8 4 1 5 5.4 2 . 8 4 2 3 0 . 5 1 8/ 3 / 2 0 1 6 M W - 3 2 8 . 1 5 8 . 9 0 8 0 4 . 1 7 N o r m a l N o n e C P N / A 3 . 1 4 9 . 7 5 N O 1 5 . 6 5 8 1 4.9 2 . 2 4 5 5 2 . 4 1 8/ 3 / 2 0 1 6 M W - 4 5 0 . 2 0 3 6 . 7 5 8 3 0 . 6 3 N o r m a l N o n e C P N / A 2 . 1 9 5 . 2 5 N O 1 7 . 0 4 4 6 5.7 4 . 7 3 9 4 7 . 5 2 8/ 3 / 2 0 1 6 M W - 5 3 0 . 7 1 2 6 . 0 9 7 9 6 . 6 0 N o r m a l N o n e C P N / A 0 . 7 5 2 . 2 5 N O 1 5 . 8 2 3 6 5.3 2 . 8 4 0 1 2 . 6 4 8/ 3 / 2 0 1 6 O B - 1 6 5 . 5 0 4 6 . 4 5 7 7 9 . 4 0 N / A N / A N / A N / A N / A N / A N / A N / A N/ A N/ A N / A N / A N / A 8/ 3 / 2 0 1 6 O B - 2 1 2 2 . 1 4 1 2 2 . 1 4 7 9 7 . 5 1 N / A N / A N / A N / A N / A N / A N / A N / A N/ A N/ A N / A N / A N / A 8/ 3 / 2 0 1 6 O B - 3 5 7 . 2 5 4 4 . 8 8 8 1 4 . 2 8 N / A N / A N / A N / A N / A N / A N / A N / A N/ A N/ A N / A N / A N / A No t e s : 1 . P u r g e M e t h o d s ; L F = L o w F l o w , C P = C o n v e n t i o n a l P u r g e ( 3 - 5 w e l l v o l u m e s ) , N P = N o P u r g e ( H y d r a S l e e v e ) , E O P = E q u i p m e n t O n l y P u r g e . P u m p r a t e a p p l i c a b l e t o L F p u r g i n g o n l y . 2 . F i e l d s a m p l i n g p e r f o r m e d b y D u k e E n e r g y C a r o l i n a s , L L C p e r s o n n e l . 3 . E V A C i n d i c a t e s w h e t h e r t h e w a t e r l e v e l i n t h e w e l l w a s d r a w n d o w n t o t h e l e v e l o f t h e p u m p d u r i n g p u r g i n g . 4 . µ Լ /c m i n d i c a t e s m i c r o m h o s p e r c e n t i m e t e r . 5 . m L / m i n i n d i c a t e s m i l l i l i t e r s p e r m i n u t e . 6 . S U i n d i c a t e s S t a n d a r d U n i t s . 7 . N T U i n d i c a t e s N e p h e l o m e t r i c T u r b i d i t y U n i t s . 8 . m V - N H E i n d i c a t e s m i l l i v o l t s - N o r m a l H y d r o g e n E l e c t r o d e . 9 . m g / L i n d i c a t e s m i l l i g r a m s p e r l i t e r . 10 . N / A i n d i c a t e s n o t a p p l i c a b l e . 11 . I n f o r m a t i o n p r o v i d e d b y T i m H u n s u c k e r o f D u k e E n e r g y C a r o l i n a s o n A u g u s t 2 4 , 2 0 1 6 . DO (mg/L) OD O R PU R G E ME T H O D PU M P RA T E (m L / m i n ) WE L L VO L U M E (g a l ) EV A C VO L U M E (g a l ) EV A C (y e s / n o ) TE M P (d e g C ) SP E C I F I C CO N D U C T A N C E (µ Լ /c m ) pH (S U ) TURBIDITY (NTU)ORP (mV-NHE) AP P E A R A N C E DA T E S A M P L E I D WE L L DE P T H (f e e t ) DE P T H T O WA T E R (f e e t ) WA T E R EL E V . (f e e t ) Ta b l e 4 - G r o u n d w a t e r F i e l d a n d A n a l y t i c a l R e s u l t s Du k e E n e r g y C a r o l i n a s , L L C / M a r s h a l l S t e a m S t a t i o n Dr y A s h L a n d f i l l - P e r m i t N o . 1 8 0 4 Fie l d p H 32 0 SU 51 9 3 - N E 6 . 5 - 8 . 5 6 . 5 - 8 . 5 * Sp e c i f i c C o n d u c t a n c e 32 3 µ Լ /cm 5 1 9 3 -N E N E N E Te m p e r a t u r e 32 5 °C 51 9 3 -N E N E N E To p o f C a s i n g 32 8 fe e t - -N E N E N E De p t h t o W a t e r 31 8 fe e t - -N E N E N E Wa t e r E l e v a t i o n 4 2 7 f e e t - -N E N E N E We l l D e p t h 4 1 1 f e e t - -N E N E N E Ar s e n i c 1 4 µg/ L 24 8 0 . 0 7 8 U 0 . 0 7 8 U 0 . 0 7 8 U 0 . 0 7 8 U 0 . 0 7 8 U 0 . 0 7 8 U 0 . 0 7 8 1 0 1 0 1 0 Ba r i u m 1 5 µg/ L 24 8 2 0 6 5 1 . 2 J ' 25 4 47 . 3 J ' 51 . 2 J ' 0. 1 U 0 . 1 1 0 0 700 2,000 Bo r o n 42 8 µg/ L 24 8 24 5 3,1 8 0 79 . 8 18 . 1 J 13 . 7 J 14 J 3.3 N E 700 NE Ca d m i u m 34 µg/ L 24 8 0.1 1 3 J 0.1 0 1 U 0 . 1 0 1 U 0 . 1 0 1 U 0 . 1 0 1 U 0 . 1 0 1 U 0 . 1 0 1 1 2 5 Ch l o r i d e 45 5 µg/ L 24 8 9 2 , 1 0 0 4 , 9 6 0 9 , 0 7 0 2 , 0 9 0 3 , 0 2 0 2 2 U 2 2 N E 2 5 0 , 0 0 0 2 5 0 , 0 0 0 * Ch r o m i u m 5 1 µg/ L 24 8 5 . 3 5 J ' 0. 5 U 0 . 9 6 3 J 1. 8 4 J 0.5 U 0. 5 U 0 . 1 1 0 10 100 Co p p e r 54 µg/ L 24 8 1 U 1 U 1 . 2 3 J 1 U 1 . 4 6 J 1 U 1 1 0 1 , 0 0 0 1 , 0 0 0 * Flu o r i d e 31 2 µg/ L 24 8 79 . 2 J 20 2 J 68 . 9 J 82 . 9 J 17 U 17 U 1 7 2 , 0 0 0 2 , 0 0 0 2 , 0 0 0 * Iro n 34 0 µg/ L 24 8 15 4 J ' 14 J ' 17 . 5 J ' 11 3 J ' 24 . 2 J ' 1.4 9 J 1.3 3 0 0 300 300* Le a d 13 1 µg/ L 24 8 0.1 0 4 J 0.0 6 5 U 0 . 0 7 0 6 J 0.0 6 5 U 0 . 0 6 5 U 0 . 0 6 5 U 0 . 0 6 5 1 0 15 15 Ma n g a n e s e 34 2 µg/ L 24 8 22 . 8 J ' 15 . 1 J ' 49 . 7 J ' 2. 6 6 J 4.8 7 J 0. 2 U 0 . 2 5 0 50 50* Me r c u r y 1 3 2 µg/ L 24 8 0 . 0 3 3 4 U 0 . 0 3 3 4 U 0 . 0 3 3 4 U 0 . 0 3 3 4 U 0 . 0 3 3 4 U 0 . 0 3 3 4 U 0 . 0 3 3 4 0 . 2 1 2 Nic k e l 15 2 µg/ L 24 8 1. 7 1 J 0. 5 U 1.9 8 J 0.6 5 8 J 0.5 U 0. 5 U 0 . 5 5 0 100 NE Nit r a t e a s N i t r o g e n 30 3 µg/ L 24 8 26 8 J ' 46 5 J ' 4,8 4 0 J ' 15 . 9 J 5.4 U 5. 4 U 5 . 4 1 0 , 0 0 0 1 0 , 0 0 0 1 0 , 0 0 0 Se l e n i u m 18 3 µg/ L 24 8 0.9 3 4 J 33 . 7 0.0 9 2 U 0 . 0 9 2 U 0 . 0 9 2 U 0 . 0 9 2 U 0 . 0 9 2 1 0 2 0 5 0 Si l v e r 1 8 4 µg/ L 24 8 0 . 7 U 0 . 7 U 0 . 7 U 0 . 7 U 0 . 7 U 0 . 7 U 0 . 7 1 0 2 0 1 0 0 * Su l f a t e 3 1 5 µg/ L 24 8 1 7 , 3 0 0 J ' 19 9 , 0 0 0 J ' 20 1 J ' 13 8 J ' 66 . 4 J 18 U 1 8 2 5 0 , 0 0 0 2 5 0 , 0 0 0 2 5 0 , 0 0 0 * To t a l D i s s o l v e d S o l i d s 31 1 µg/ L 24 8 2 6 3 , 0 0 0 2 9 4 , 0 0 0 34 , 0 0 0 3 1 , 0 0 0 3 6 , 0 0 0 16 , 7 0 0 N E 5 0 0 , 0 0 0 5 0 0 , 0 0 0 * Zin c 21 3 µg/ L 24 8 9. 5 3 J ' 5.6 2 J ' 17 . 1 18 . 6 2.6 U 2. 6 U 2 . 6 1 0 1 , 0 0 0 5 , 0 0 0 * No t e s : 1 . C o n c e n t r a t i o n s p r e s e n t e d i n m i c r o g r a m s p e r l i t e r ( µ g / L ) . 2 . S U i n d i c a t e s S t a n d a r d U n i t s . 3 . µ Լ /c m i n d i c a t e s m i c r o m h o s p e r c e n t i m e t e r . 4 . S W S I D i s t h e S o l i d W a s t e S e c t i o n I d e n t i f i c a t i o n N u m b e r . 5 . M D L i s t h e l a b o r a t o r y m e t h o d d e t e c t i o n l i m i t . T h e M D L v a l u e s p r e s e n t e d a r e f o r s a m p l e s n o t d i l u t e d b y t h e l a b o r a t o r y d u r i n g a n a l y s i s . 6 . S W S L i s t h e S o l i d W a s t e S e c t i o n L i m i t . N C D E Q d e f i n e s t h e S W S L a s t h e l o w e s t a m o u n t o f a n a l y t e i n a s a m p l e t h a t c a n b e q u a n t i t a t i v e l y d e t e r m i n e d w i t h s u i t a b l e p r e c i s i o n a n d a c c u r a c y . 7 . 1 5 A N C A C 2 L S t a n d a r d r e f e r s t o C l a s s G A S t a n d a r d s a s f o u n d i n 1 5 A N C A C 0 2 L . 0 2 0 2 G r o u n d w a t e r Q u a l i t y S t a n d a r d s , l a s t a m e n d e d o n A p r i l 1 , 2 0 1 3 . 8 . M C L i s t h e F e d e r a l M a x i m u m C o n t a m i n a n t L e v e l a s f o u n d i n 4 0 C F R , S u b p a r t G , § 1 4 1 . 6 2 . 9 . * C o n c e n t r a t i o n l i s t e d i s a s e c o n d a r y m a x i m u m c o n t a m i n a n t l e v e l ( S M C L ) . S M C L s a r e e s t a b l i s h e d b y E P A i n t h e N a t i o n a l S e c o n d a r y D r i n k i n g W a t e r R e g u l a t i o n s a s f o u n d i n 4 0 C F R § 1 4 3 . 3 . 10 . N E i n d i c a t e s n o t e s t a b l i s h e d . N A i n d i c a t e s n o t a n a l y z e d . B l a n k c e l l s i n d i c a t e t h a t t h e r e i s n o i n f o r m a t i o n r e l e v a n t t o t h e r e s p e c t i v e r o w . 11 . G r a y e d v a l u e s i n d i c a t e v a l u e s t h a t e q u a l o r a r e g r e a t e r t h a n t h e S W S L . 12 . B o l d v a l u e s i n d i c a t e v a l u e s t h a t a t t a i n o r e x c e e d t h e 1 5 A N C A C 2 L S t a n d a r d . 13 . Q u a l i f i e r s i n n o n - i t a l i c i z e d t e x t a r e l a b o r a t o r y d a t a q u a l i f i e r s o r " f l a g s " . " U " i s u s e d t o i d e n t i f y r e s u l t s n o t d e t e c t e d a t c o n c e n t r a t i o n s w h i c h e q u a l t h e l a b o r a t o r y ' s M D L . " J " i s u s e d t o i d e n t i f y e s t i m a t e d c o n c e n t r a t i o n s w h i c h e q u a l o r a r e g r e a t e r t h a n t h e M D L b u t a r e l e s s t h a n t h e l a b o r a t o r y ' s m e t h o d r e p o r t i n g l i m i t ( M R L ) . A n i t a l i c i z e d J' -f l a g i s a d a t a q u a l i f i e r , a d d e d b y H D R t o i n d i c a t e c o n c e n t r a t i o n s w h i c h e q u a l o r a r e g r e a t e r t h a n t h e l a b o r a t o r y ' s M R L b u t a r e l e s s t h a n t h e S W S L . 14 . A n a l y t i c a l r e s u l t s o b t a i n e d f r o m E l e c t r o n i c D a t a D e l i v e r a b l e ( E D D ) p r o v i d e d b y T i m H u n s u c k e r o f D u k e E n e r g y C a r o l i n a s o n A u g u s t 2 4 , 2 0 1 6 . 15 . A c c o r d i n g t o t h e C o n s t i t u e n t L o o k - u p w e b p a g e o n t h e N C D E N R D i v i s i o n o f W a s t e M a n a g e m e n t w e b p a g e , t h e r e i s n o S W S L o r 2 L S t a n d a r d f o r c h o r i d e a s s o c i a t e d w i t h C A S n u m b e r 1 6 8 8 7 - 0 0 - 6 , w h i c h i s t h e C A S r e p o r t e d b y t h e l a b o r a t o r y f o r t h e a n a l y s e s c o m p l e t e d . T h e r e f o r e , t h e S W S L a n d 2 L S t a n d a r d l i s t e d a r e f o r t h e c h l o r i d e w i t h C A S n u m b e r S W 3 0 1 a s s p e c i f i e d o n t h e C o n s t i t u e n t L o o k - u p w e b p a g e ( l a s t u p d a t e d J u n e 1 3 , 2 0 1 1 ) . 18 0 4 M W - 5 17 . 0 4 465. 7 4.9 81 15 . 6 5 Laboratory Certificate Codes: Du k e E n e r g y C a r o l i n a s F i e l d # 5 1 9 3 Du k e E n e r g y A n a l y t i c a l L a b o r a t o r y # 2 4 8 Federal MCL 15 A N C A C 2 L St a n d a r d SW S L Sa m p l e D a t e : A u g u s t 3 , 2 0 1 6 Fie l d S a m p l i n g p e r f o r m e d b y D u k e E n e r g y C a r o l i n a s , L L C Pa r a m e t e r SW S I D U n i t s Ce r t i f i c a t e Co d e 18 0 4 M W - 1 MD L Fi e l d Bla n k 18 0 4 M W - 2 1 8 0 4 M W - 3 Mo n i t o r i n g W e l l s 18 0 4 M W - 4 NA--- 82 3 . 7 0 81 3 . 0 7 79 7 . 2 2 86 7 . 3 8 30 . 7 1 50 . 2 0 28 . 1 5 35 . 1 0 78 . 7 5 ---- 82 2 . 6 9 5. 3 36 15 . 8 2 5.6 38 0 15 . 9 2 26 . 0 9 79 6 . 6 0 16 . 0 8 41 5 5.4 83 0 . 6 3 36 . 7 5 8.9 0 80 4 . 1 7 78 9 . 9 6 7.2 6 51 . 3 1 77 2 . 3 9 Ta b l e 5 - F i e l d a n d A n a l y t i c a l R e s u l t s t h a t E q u a l o r E x c e e d 15 A N C A C 2 L G r o u n d w a t e r Q u a l i t y S t a n d a r d s Du k e E n e r g y C a r o l i n a s , L L C / M a r s h a l l S t e a m S t a t i o n Dr y A s h L a n d f i l l - P e r m i t N o . 1 8 0 4 Pa r a m e t e r S a m p l e I D Un i t s 15 A N C A C 2L S t a n d a r d His t o r i c a l C o n c e n t r a t i o n s Ca u s e a n d S i g n i f i c a n c e MW - 1 5. 2 - 6 . 2 pH i s c o n s i s t e n t w i t h h i s t o r i c a l r e a d i n g s a t M W - 1 . MW - 2 5. 1 - 6 . 1 pH i s c o n s i s t e n t w i t h h i s t o r i c a l r e a d i n g s a t M W - 2 . M W - 2 i s l o c a t e d w i t h i n t h e r e v i e w b o u n d a r y . MW - 3 4. 4 - 5 . 4 pH i s c o n s i s t e n t w i t h h i s t o r i c a l r e a d i n g s a t M W - 3 . M W - 3 i s l o c a t e d w i t h i n t h e r e v i e w b o u n d a r y . MW - 4 5. 1 - 6 . 3 pH i s c o n s i s t e n t w i t h h i s t o r i c a l r e a d i n g s a t M W - 4 . MW - 5 5. 1 - 5 . 8 pH i s c o n s i s t e n t w i t h h i s t o r i c a l r e a d i n g s a t M W - 5 . Bo r o n MW - 2 µg / L 70 0 2,1 7 5 - 3 , 2 3 0 B o r o n c o n c e n t r a t i o n i s c o n s i s t e n t w i t h h i s t o r i c a l r e a d i n g s a t M W - 2 . M W - 2 i s l o c a t e d w i t h i n t h e r e v i e w b o u n d a r y . Se l e n i u m M W - 2 µg / L 20 <1 - 4 4 . 1 Se l e n i u m c o n c e n t r a t i o n i s c o n s i s t e n t w i t h h i s t o r i c a l r e a d i n g s a t M W - 2 . M W - 2 i s l o c a t e d w i t h i n t h e r e v i e w b o u n d a r y . No t e s : 1 . 1 5 A N C A C 2 L S t a n d a r d r e f e r s t o C l a s s G A S t a n d a r d s a s f o u n d i n 1 5 A N C A C 0 2 L . 0 2 0 2 G r o u n d w a t e r Q u a l i t y S t a n d a r d s , l a s t a m e n d e d o n A p r i l 1 , 2 0 1 3 . 2 . µ g / L i n d i c a t e s m i c r o g r a m s p e r l i t e r . 3 . S U i n d i c a t e s S t a n d a r d U n i t s . 4 . H i s t o r i c a l c o n c e n t r a t i o n s b a s e d o n d a t a i n D u k e E n e r g y C a r o l i n a s , L L C ( D u k e E n e r g y ) a n a l y t i c a l r e s u l t s d a t a b a s e . 5 . A n a l y t i c a l r e s u l t s o b t a i n e d f r o m E l e c t r o n i c D a t a D e l i v e r a b l e ( E D D ) p r o v i d e d b y T i m H u n s u c k e r o f D u k e E n e r g y C a r o l i n a s o n A u g u s t 2 4 , 2 0 1 6 . 3, 1 8 0 33 . 7 Sa m p l e D a t e : A u g u s t 3 , 2 0 1 6 Fi e l d s a m p l i n g p e r f o r m e d b y D u k e E n e r g y C a r o l i n a s , L L C pH Re s u l t SU 6 . 5 - 8 . 5 5. 6 5. 4 4. 9 5. 7 5. 3 A Appendix A Field Sampling Forms ANALYZER SERIAL #: WEATHER CONDITIONS: DATE:TIME:DATE:TIME: Calibation Instrument Standard Instrument Standard Standard Value Value Value Value SS 0.0 ▬▬►0.0 0.0 ▬/▬►0.0 SS 352.4 ▬▬►350 346.6 ▬/▬►350 SS 72.9 ▬/▬►75 74.6 ▬/▬►75 SS ▬/▬►1410 ▬/▬►1410 B (7.00)7.01 ▬▬►7.02 6.99 ▬/▬►7.02 B (4.00)4.01 ▬▬►4.00 3.97 ▬/▬►4.00 B (10.00)10.01 ▬/▬►10.06 10.00 ▬/▬►10.06 20.45 20.49 pH Check B (7.00)▬▬►7.13 Time:0.00 439 ▬▬►440 439 ▬/▬►440 N/A ▬/▬►N/A N/A ▬/▬►N/A Zobell's 20.27 20.29 TEMP (CO) BP (mmHg) COND 100 % mg/L 8.94 ▬▬►8.92 8.92 ▬/▬►8.92 After Cal 8.93 100.12 8.90 99.73 LCS 8.96 100.46 8.95 100.29 LCSD 8.92 -0.45 8.97 0.22 SS 53.0 ▬/▬►54.5 53.8 ▬/▬►54.5 NIST N/A ▬/▬►N/A N/A ▬/▬►N/A KEY: NOTES: SS = Standard solution AW = Average Winkler ▬/▬►= Not Adjusted To (mmHg) B = Buffer W = Winkler ▬▬► = Adjusted To N/A = Not Applicable Replaced DO electrolyte See Notes Field Barometric Pressure Beginning BP 742.4 (mmHg)Ending BP 743.4 Tested - OK See Notes Tested - OK See Notes Dissolved Oxygen Subsystem Replaced Teflon Membrane Cleaned Electrode Tested - OK See Notes Oxidation Reduction Subsystem Temperature Subsystem Cleaned Electrode Cleaned Electrode Tested - OK Replaced ref Electrode KCL See Notes Replaced Ref. Electrode Tip INSTRUMENT MAINTENANCE DATE / TIME Conductance Subsystem pH Subsystem Cleaned Electrodes Cleaned Electrodes Temp Cert Device # TEMP (deg C)Adjustment Not Available Adjustment Not Available TURB (ntu)CALIBRATION ACCEPTED CALIBRATION ACCEPTED CALIBRATION PASS CALIBRATION PASS DO (mg/L) 19.75 19.79 742.41 743.40 90.5 CALIBRATION PASS CALIBRATION PASS CALIBRATION ACCEPTED CALIBRATION ACCEPTED After Cal % SAT After Cal % SAT 90.7 ORP Temp.ORP Temp. ORP CALIBRATION ACCEPTED CALIBRATION ACCEPTED Buffer Temp. CALIBRATION ACCEPTED CALIBRATION ACCEPTED Buffer Temp.Buffer Temp. pH (units) CALIBRATION ACCEPTED CALIBRATION ACCEPTED CALIBRATION ACCEPTED CALIBRATION ACCEPTED Specifc conductance checkpoint (used if sampled well is outside of initial calibration range). SPEC. COND. CHECK (uS/cm) SPEC. COND. (uS/cm)CALIBRATION ACCEPTED CALIBRATION ACCEPTED INSTRUMENT ZEROED INSTRUMENT ZEROED CALIBRATION ACCEPTED CALIBRATION ACCEPTED Parameter Calibration Results Calibration Results CALIBRATION BP (mmHg)742.41 CALIBRATION BP (mmHg)743.40 Calibration Date / Time 3-Aug-16 520 4-Aug-16 610 PROCEDURE #:HYDROLAB 3210.6 VALIDATED BY: FIELD SAMPLING CALIBRATION FORM STUDY:MARSHALL STEAM STATION - DRY ASH LANDFILL GROUNDWATER MONITORING DATE (s):August 3, 2016 SURFACE UNIT READER:LDC OTHER EQUIPMENT:TURBIDIMETER NO.2 - 3260-GW Clouds, calm, 75 to 80 deg F COLLECTORS:LDC SURFACE UNIT SERIAL #:3858 ANALYZER MODEL#:MS5 66120 68.75 78.75 40 (psi)11 (sec)(sec) (gal) 4.48 (gal) @ QC By:< 2.0 DATE TIME DISSOLVED OXYGEN 4.3 366 0.45 0.47368 (recalculates on current water level) 8/3/2016 0750 Sample preservation verified to pH (units) ORP (ft)(YES/NO) 4.50 NO 15.89 372 5.51 15.91 VOLUME EVACUATION COND. (gal) PURGE METHOD Conventional DISCHARGERECHARGEPRESSURE 9 PUMP CONTROLLER SETTINGS 0.1631CONVERSION FACTOR Well Volume = water column X conversion factor (Conversion factor dependent on well diameter and selected well volume units) 4.48WELL VOLUME FIELD CREW LDC MONITORING WELL INFORMATION 2 N/A PROCEDURE NO 3175.4DUKE ENERGY GROUNDWATER MONITORING DATA SHEET FOR CONVENTIONAL SAMPLING SITE NAME MARSHALL STEAM STATION PERMIT #18-04 SITE ID PROJECT NAME DRY ASH LANDFILL SAMPLING DATE(s)3-Aug-2016 73.75 77.80PUMP INTAKE DEPTH (ft TOC)78.75 TOC ELEV (ft msl) GS ELEV (ft msl) 823.70 821.20 WELL/LOCATION NAME MW-1 SCREEN LENGTH (ft)10.00 ELEV REF NAVD 88 WELL DEPTH (ft TOC) WELL DIAMETER (in)MIDDLE OF WETTED SCREEN (ft toc) WELL VOL SCREEN INTERVAL (ft TOC)TO SAMPLING INFORMATION INITIAL DEPTH TO WATER (ft TOC)51.31 WATER COLUMN (ft)27.44 EQUIPMENT INFORMATION LEVEL METER SERIAL#28652 SAMPLING EQUIPMENT TUBING DIAMETER (in)1/2 OD QED T1200 PURGE COMPLETE TEMP SPECIFIC pH TURBIDITY WATER ELEVATION (ft msl)772.39 APPEARANCE DETECTED ODOR None Normal WATER LEVEL AFTER PURGE * (deg C)(umho/cm)(SU)(NTU)(mV-NHE)(mg/L) 8.8 366 0.79 4.50 NO 4.50 NO 15.92 380 5.55 384 5.53 6.9 COLLECT SAMPLE - SAMPLE CRITERIA SATISFIED CHLORINE (mg/l)SAMPLE COLLECTED BY LDC 0 TOTAL PURGE VOLUME 13.50 * Optional measurement to recalculate well volume when purging results in substantial drawdown of water column WELL CASING WELL CONDITION PROTECTIVE CASING WELL PAD WELL TAG Good Condition Good Condition Good Condition Good Tag SAMPLING NOTES ADDITIONAL WELL CONDITION NOTES 25.10 35.10 20 (psi)6 (sec)(sec) (gal) 4.54 (gal) @ QC By: SAMPLING NOTES PROTECTIVE CASING Good Condition WELL PAD Good Condition WELL CASING Good Condition WELL TAG Good Tag WELL CONDITION ADDITIONAL WELL CONDITION NOTES Sample preservation verified to pH (units)< 2.0 TOTAL PURGE VOLUME * Optional measurement to recalculate well volume when purging results in substantial drawdown of water column COLLECT SAMPLE - SAMPLE CRITERIA SATISFIED CHLORINE (mg/l)SAMPLE COLLECTED BY DATE TIME 14.25 LDC 8/3/2016 0940 0 4.75 NO 16.08 415 5.36 2.8 423 0.51 4.75 NO 16.02 415 5.36 2.6 424 0.52 OXYGEN (recalculates on current water level)(mV-NHE)(mg/L) 4.75 NO 16.03 412 5.35 3.0 427 (ft)(YES/NO)(deg C)(umho/cm)(SU)(NTU) 0.52 PURGE WATER LEVEL AFTER PURGE * COMPLETE TEMP SPECIFIC pH TURBIDITY ORP DISSOLVED WELL VOL VOLUME EVACUATION COND. (gal) DETECTED ODOR None CONVERSION FACTOR 0.1631 APPEARANCE Normal SAMPLING INFORMATION INITIAL DEPTH TO WATER (ft TOC)7.26 WATER COLUMN (ft)27.84 Well Volume = water column X conversion factor (Conversion factor dependent on well diameter and selected well volume units) WATER ELEVATION (ft msl)789.96 WELL VOLUME 4.54 PUMP CONTROLLER SETTINGS PRESSURE RECHARGE DISCHARGE 9 28652 SAMPLING EQUIPMENT QED T1200 PURGE METHOD TUBING DIAMETER (in)1/2 OD Conventional MONITORING WELL INFORMATION WELL DIAMETER (in)2 TOC ELEV (ft msl)797.22 MIDDLE OF WETTED SCREEN (ft toc)30.10 SCREEN LENGTH (ft)10.00 ELEV REF NAVD 88 SCREEN INTERVAL (ft TOC)TO EQUIPMENT INFORMATION LEVEL METER SERIAL# WELL DEPTH (ft TOC)35.10 GS ELEV (ft msl)794.90 PUMP INTAKE DEPTH (ft TOC)34.10 PROJECT NAME DRY ASH LANDFILL FIELD CREW LDC SAMPLING DATE(s)3-Aug-2016 WELL/LOCATION NAME MW-2 SITE NAME MARSHALL STEAM STATION PERMIT #18-04 SITE ID N/A DUKE ENERGY PROCEDURE NO 3175.4 GROUNDWATER MONITORING DATA SHEET FOR CONVENTIONAL SAMPLING 18.15 28.15 18 (psi)8 (sec)(sec) (gal) 3.14 (gal) @ QC By: SITE NAME MARSHALL STEAM STATION PERMIT #18-04 SITE ID N/A DUKE ENERGY PROCEDURE NO 3175.4 GROUNDWATER MONITORING DATA SHEET FOR CONVENTIONAL SAMPLING PROJECT NAME DRY ASH LANDFILL FIELD CREW LDC SAMPLING DATE(s)3-Aug-2016 WELL/LOCATION NAME MW-3 MONITORING WELL INFORMATION WELL DIAMETER (in)2 TOC ELEV (ft msl)813.07 MIDDLE OF WETTED SCREEN (ft toc)23.15 SCREEN LENGTH (ft)10.00 ELEV REF NAVD 88 SCREEN INTERVAL (ft TOC)TO EQUIPMENT INFORMATION LEVEL METER SERIAL# WELL DEPTH (ft TOC)28.15 GS ELEV (ft msl)811.00 PUMP INTAKE DEPTH (ft TOC)27.20 PUMP CONTROLLER SETTINGS PRESSURE RECHARGE DISCHARGE 7 28652 SAMPLING EQUIPMENT QED T1200 PURGE METHOD TUBING DIAMETER (in)1/2 OD Conventional DETECTED ODOR None CONVERSION FACTOR 0.1631 APPEARANCE Normal SAMPLING INFORMATION INITIAL DEPTH TO WATER (ft TOC)8.90 WATER COLUMN (ft)19.25 Well Volume = water column X conversion factor (Conversion factor dependent on well diameter and selected well volume units) WATER ELEVATION (ft msl)804.17 WELL VOLUME 3.14 (gal) PURGE WATER LEVEL AFTER PURGE * COMPLETE TEMP SPECIFIC pH TURBIDITY ORP DISSOLVED WELL VOL VOLUME EVACUATION COND.OXYGEN (recalculates on current water level)(mV-NHE)(mg/L) 3.25 NO 15.59 81 5.03 10.6 424 (ft)(YES/NO)(deg C)(umho/cm)(SU)(NTU) 1.68 3.25 NO 15.65 81 4.93 2.2 455 2.41 3.25 NO 15.66 82 4.94 2.5 449 2.24 CHLORINE (mg/l)SAMPLE COLLECTED BY DATE TIME 9.75 LDC 8/3/2016 1030 0 TOTAL PURGE VOLUME * Optional measurement to recalculate well volume when purging results in substantial drawdown of water column COLLECT SAMPLE - SAMPLE CRITERIA SATISFIED WELL CONDITION ADDITIONAL WELL CONDITION NOTES Sample preservation verified to pH (units)< 2.0 PROTECTIVE CASING Good Condition Ants all over well cap. WELL PAD Good Condition WELL CASING Good Condition WELL TAG Good Tag SAMPLING NOTES 40.20 50.20 25 (psi)14 (sec)(sec) (gal) 2.19 (gal) @ QC By: SITE NAME MARSHALL STEAM STATION PERMIT #18-04 SITE ID N/A DUKE ENERGY PROCEDURE NO 3175.4 GROUNDWATER MONITORING DATA SHEET FOR CONVENTIONAL SAMPLING PROJECT NAME DRY ASH LANDFILL FIELD CREW LDC SAMPLING DATE(s)3-Aug-2016 WELL/LOCATION NAME MW-4 MONITORING WELL INFORMATION WELL DIAMETER (in)2 TOC ELEV (ft msl)867.38 MIDDLE OF WETTED SCREEN (ft toc)45.20 SCREEN LENGTH (ft)10.00 ELEV REF NAVD 88 SCREEN INTERVAL (ft TOC)TO EQUIPMENT INFORMATION LEVEL METER SERIAL# WELL DEPTH (ft TOC)50.20 GS ELEV (ft msl)864.50 PUMP INTAKE DEPTH (ft TOC)49.20 PUMP CONTROLLER SETTINGS PRESSURE RECHARGE DISCHARGE 6 28652 SAMPLING EQUIPMENT QED T1200 PURGE METHOD TUBING DIAMETER (in)1/2 OD Conventional DETECTED ODOR None CONVERSION FACTOR 0.1631 APPEARANCE Normal SAMPLING INFORMATION INITIAL DEPTH TO WATER (ft TOC)36.75 WATER COLUMN (ft)13.45 Well Volume = water column X conversion factor (Conversion factor dependent on well diameter and selected well volume units) WATER ELEVATION (ft msl)830.63 WELL VOLUME 2.19 (gal) PURGE WATER LEVEL AFTER PURGE * COMPLETE TEMP SPECIFIC pH TURBIDITY ORP DISSOLVED WELL VOL VOLUME EVACUATION COND.OXYGEN (recalculates on current water level)(mV-NHE)(mg/L) 2.25 44.64 NO 16.76 45 5.72 14.6 414 (ft)(YES/NO)(deg C)(umho/cm)(SU)(NTU) 6.59 0.91 1.00 NO 17.02 47 5.79 7.4 392 7.53 1.00 NO 17.00 46 5.84 13.1 394 7.49 1.00 NO 17.04 46 5.74 4.7 394 7.52 CHLORINE (mg/l)SAMPLE COLLECTED BY DATE TIME 5.25 LDC 8/3/2016 1150 0 TOTAL PURGE VOLUME * Optional measurement to recalculate well volume when purging results in substantial drawdown of water column COLLECT SAMPLE - SAMPLE CRITERIA SATISFIED WELL CONDITION ADDITIONAL WELL CONDITION NOTES Sample preservation verified to pH (units)< 2.0 PROTECTIVE CASING Good Condition WELL PAD Good Condition WELL CASING Good Condition WELL TAG Good Tag SAMPLING NOTES 20.71 30.71 20 (psi)7 (sec)(sec) (gal) 0.75 (gal) @ QC By: SITE NAME MARSHALL STEAM STATION PERMIT #18-04 SITE ID N/A DUKE ENERGY PROCEDURE NO 3175.4 GROUNDWATER MONITORING DATA SHEET FOR CONVENTIONAL SAMPLING PROJECT NAME DRY ASH LANDFILL FIELD CREW LDC SAMPLING DATE(s)3-Aug-2016 WELL/LOCATION NAME MW-5 MONITORING WELL INFORMATION WELL DIAMETER (in)2 TOC ELEV (ft msl)822.69 MIDDLE OF WETTED SCREEN (ft toc)28.40 SCREEN LENGTH (ft)10.00 ELEV REF NAVD 88 SCREEN INTERVAL (ft TOC)TO EQUIPMENT INFORMATION LEVEL METER SERIAL# WELL DEPTH (ft TOC)30.71 GS ELEV (ft msl)820.19 PUMP INTAKE DEPTH (ft TOC)29.70 PUMP CONTROLLER SETTINGS PRESSURE RECHARGE DISCHARGE 3 28652 SAMPLING EQUIPMENT QED T1200 PURGE METHOD TUBING DIAMETER (in)1/2 OD Conventional DETECTED ODOR None CONVERSION FACTOR 0.1631 APPEARANCE Normal SAMPLING INFORMATION INITIAL DEPTH TO WATER (ft TOC)26.09 WATER COLUMN (ft)4.62 Well Volume = water column X conversion factor (Conversion factor dependent on well diameter and selected well volume units) WATER ELEVATION (ft msl)796.60 WELL VOLUME 0.75 (gal) PURGE WATER LEVEL AFTER PURGE * COMPLETE TEMP SPECIFIC pH TURBIDITY ORP DISSOLVED WELL VOL VOLUME EVACUATION COND.OXYGEN (recalculates on current water level)(mV-NHE)(mg/L) 0.75 NO 15.74 37 5.34 2.7 395 (ft)(YES/NO)(deg C)(umho/cm)(SU)(NTU) 2.40 0.75 NO 15.82 36 5.34 2.8 401 2.64 0.75 NO 15.78 36 5.33 2.9 398 2.42 CHLORINE (mg/l)SAMPLE COLLECTED BY DATE TIME 2.25 LDC 8/3/2016 0840 0 TOTAL PURGE VOLUME * Optional measurement to recalculate well volume when purging results in substantial drawdown of water column COLLECT SAMPLE - SAMPLE CRITERIA SATISFIED WELL CONDITION ADDITIONAL WELL CONDITION NOTES Sample preservation verified to pH (units)< 2.0 PROTECTIVE CASING Good Condition WELL PAD Good Condition WELL CASING Good Condition WELL TAG Good Tag SAMPLING NOTES 107.14 122.14 (psi)(sec)(sec) (gal) (ft)=(in)@ QC By: SITE NAME MARSHALL STEAM STATION PERMIT #18-04 SITE ID N/A DUKE ENERGY PROCEDURE NO 3175.4 GROUNDWATER MONITORING DATA SHEET FOR LEVEL ONLY PROJECT NAME DRY ASH LANDFILL FIELD CREW LDC SAMPLING DATE(s)3-Aug-2016 WELL/LOCATION NAME MW-6 MONITORING WELL INFORMATION WELL DIAMETER (in)2 TOC ELEV (ft msl)919.65 MIDDLE OF WETTED SCREEN (ft toc)122.14 SCREEN LENGTH (ft)15.00 ELEV REF NAVD 88 SCREEN INTERVAL (ft TOC)TO EQUIPMENT INFORMATION LEVEL METER SERIAL# WELL DEPTH (ft TOC)122.14 GS ELEV (ft msl)917.18 PUMP INTAKE DEPTH (ft TOC)N/A WATER LEVEL ONLY PUMP CONTROLLER SETTINGS PRESSURE RECHARGE DISCHARGE 28652 SAMPLING EQUIPMENT PURGE METHOD TUBING DIAMETER (in)Level Only 0.00 DETECTED ODOR None CONVERSION FACTOR 0.1631 APPEARANCE SAMPLING INFORMATION INITIAL DEPTH TO WATER (ft TOC)122.14 WATER COLUMN (ft)0.00 Well Volume = water column X conversion factor (Conversion factor dependent on well diameter and selected well volume units) WATER ELEVATION (ft msl)797.51 WELL VOLUME TEMP SPECIFIC pH TURBIDITY ORP DISSOLVED TIME LDC 8/3/2016 LENGTH DEPTH (top)DEPLOYED COND.OXYGEN (inches)(ft TOC)(deg C)(umho/cm)(SU) HYDRASLEEVE DEPLOYED DATE (NTU)(mV-NHE)(mg/L) N/A N/A N/A N/A N/A N/A N/A 1052 N/A N/A N/A N/A Deployed Water Column In Screen Above Top Of Hydrasleeve NO PURGE SAMPLE CHLORINE (mg/l)Top Weight SAMPLE COLLECTED BY DATE WELL CONDITION ADDITIONAL WELL CONDITION NOTES Sample preservation verified to pH (units)N/A PROTECTIVE CASING Good Condition Dry well. WELL PAD Good Condition WELL CASING Good Condition WELL TAG Good Tag SAMPLING NOTES 42.25 57.25 (psi)(sec)(sec) (gal) (ft)=(in)@ QC By: SITE NAME MARSHALL STEAM STATION PERMIT #18-04 SITE ID N/A DUKE ENERGY PROCEDURE NO 3175.4 GROUNDWATER MONITORING DATA SHEET FOR LEVEL ONLY PROJECT NAME DRY ASH LANDFILL FIELD CREW LDC SAMPLING DATE(s)3-Aug-2016 WELL/LOCATION NAME MW-7 MONITORING WELL INFORMATION WELL DIAMETER (in)2 TOC ELEV (ft msl)859.16 MIDDLE OF WETTED SCREEN (ft toc)51.07 SCREEN LENGTH (ft)15.00 ELEV REF NAVD 88 SCREEN INTERVAL (ft TOC)TO EQUIPMENT INFORMATION LEVEL METER SERIAL# WELL DEPTH (ft TOC)57.25 GS ELEV (ft msl)856.56 PUMP INTAKE DEPTH (ft TOC)N/A WATER LEVEL ONLY PUMP CONTROLLER SETTINGS PRESSURE RECHARGE DISCHARGE 28652 SAMPLING EQUIPMENT PURGE METHOD TUBING DIAMETER (in)Level Only 2.02 DETECTED ODOR None CONVERSION FACTOR 0.1631 APPEARANCE SAMPLING INFORMATION INITIAL DEPTH TO WATER (ft TOC)44.88 WATER COLUMN (ft)12.37 Well Volume = water column X conversion factor (Conversion factor dependent on well diameter and selected well volume units) WATER ELEVATION (ft msl)814.28 WELL VOLUME TEMP SPECIFIC pH TURBIDITY ORP DISSOLVED TIME LDC 8/3/2016 LENGTH DEPTH (top)DEPLOYED COND.OXYGEN (inches)(ft TOC)(deg C)(umho/cm)(SU) HYDRASLEEVE DEPLOYED DATE (NTU)(mV-NHE)(mg/L) N/A N/A N/A N/A N/A N/A N/A 1044 N/A N/A N/A N/A Deployed Water Column In Screen Above Top Of Hydrasleeve NO PURGE SAMPLE CHLORINE (mg/l)Top Weight SAMPLE COLLECTED BY DATE WELL CONDITION ADDITIONAL WELL CONDITION NOTES Sample preservation verified to pH (units)N/A PROTECTIVE CASING Good Condition WELL PAD Good Condition WELL CASING Good Condition WELL TAG Good Tag SAMPLING NOTES 55.50 65.50 (psi)(sec)(sec) (gal) 3.11 (gal) @ QC By: SITE NAME MARSHALL STEAM STATION PERMIT #18-04 SITE ID N/A DUKE ENERGY PROCEDURE NO 3175.4 GROUNDWATER MONITORING DATA SHEET FOR LEVEL ONLY PROJECT NAME DRY ASH LANDFILL FIELD CREW LDC SAMPLING DATE(s)3-Aug-2016 WELL/LOCATION NAME OB-1 MONITORING WELL INFORMATION WELL DIAMETER (in)2 TOC ELEV (ft msl)825.85 MIDDLE OF WETTED SCREEN (ft toc)60.50 SCREEN LENGTH (ft)10.00 ELEV REF NAVD 88 SCREEN INTERVAL (ft TOC)TO EQUIPMENT INFORMATION LEVEL METER SERIAL# WELL DEPTH (ft TOC)65.50 GS ELEV (ft msl)PUMP INTAKE DEPTH (ft TOC)N/A PUMP CONTROLLER SETTINGS PRESSURE RECHARGE DISCHARGE 28652 SAMPLING EQUIPMENT PURGE METHOD TUBING DIAMETER (in)Level Only WATER LEVEL ONLY DETECTED ODOR None CONVERSION FACTOR 0.1631 APPEARANCE SAMPLING INFORMATION INITIAL DEPTH TO WATER (ft TOC)46.45 WATER COLUMN (ft)19.05 Well Volume = water column X conversion factor (Conversion factor dependent on well diameter and selected well volume units) WATER ELEVATION (ft msl)779.40 WELL VOLUME 3.11 PURGE WATER LEVEL AFTER PURGE * COMPLETE TEMP SPECIFIC pH TURBIDITY ORP DISSOLVED WELL VOL VOLUME EVACUATION COND.OXYGEN (recalculates on current water level)(mV-NHE)(mg/L) N/A N/A N/A N/A N/A N/A N/A (ft)(YES/NO)(deg C)(umho/cm)(SU)(NTU) N/A CHLORINE (mg/l)SAMPLE COLLECTED BY DATE TIME 0.00 LDC 8/3/2016 0715 N/A TOTAL PURGE VOLUME * Optional measurement to recalculate well volume when purging results in substantial drawdown of water column WELL CONDITION ADDITIONAL WELL CONDITION NOTES Sample preservation verified to pH (units)N/A PROTECTIVE CASING Good Condition WELL PAD Good Condition WELL CASING Good Condition WELL TAG Good Tag SAMPLING NOTES PERMIT # MW-1 MW-2 MW-3 MW-4 MW-5 OB-1 YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES N/A N/A N/A N/A N/A N/A YES YES YES YES YES YES Lacks required information - Total well depth Lacks required information - Depth to screen Lacks required information - Non potable tag NOTE: Lacks required information - Completion date FLUSH MOUNT WELLS Vault in good condition Water inside vault Vault bolt holes broken or stripped Bolts stripped Vault lid cracked or broken WELL ID TAGS Well tag in good condition Well tag missing Well tag damaged / illegible Lacks required information - Driller Reg # Replaced damaged well cap Fire ants around concrete pad WELL PROTECTIVE CASINGS Casing in good condition Damaged casing / still functional Damaged casing / repair required Broken hinge on protective lid Wasp nest inside protective casing Ants inside protective casing WELL CAPS Well cap in good conditon Damaged / needs replacement Undermined / washing out Lock in good condition Lock rusted, difficult to open / needs replacing Replaced damaged lock WELL CASINGS Casing in good condition Damaged casing / still functional Damaged casing / repair required CONCRETE PADS Pad in good condition Minor cracks Major cracks / broken / repair required WELL LOCK CONDITION PAGE 1 OF 1 ACCESS TO WELLS Access cleared into well Access cleared around well Tall grass or weeds - needs mowing Road washing out / muddy / needs grading Fallen tree blocking access WELL SECURITY Well found locked Well found unlocked SITE CONTACT Joseph La Sala, Chris Randazzo FIELD CREW LDC WEATHER Clouds, calm, 75 to 80 deg F NORTH CAROLINA GROUNDWATER SAMPLING SITE CHECKLIST LOCATION / SITE MARSHALL STEAM STATION - DRY ASH LANDFILL GROUNDWATER MONITORING 18-04 SAMPLE DATE August 3, 2016 WELL DEPTH TO WATER Purge AVG *WELL EVAC SPECIFIC WELL DEPTH WATER ELEV.Method PMP RATE VOL VOL EVAC TEMP CONDUCTANCE pH TURBIDITY ORP DO DATE NO.(feet-toc)(feet-toc)(feet)APPEARANCE ODOR (ml/min)(gal)(gal)(yes/no)(deg C)(umho/cm)(units)(NTU)(mV-NHE)(mg/l) 8/3/2016 MW-1 78.75 51.31 772.39 Normal None C N/A 4.48 13.50 NO 15.92 380 5.6 4.3 366 0.45 8/3/2016 MW-2 35.10 7.26 789.96 Normal None C N/A 4.54 14.25 NO 16.08 415 5.4 2.8 423 0.51 8/3/2016 MW-3 28.15 8.90 804.17 Normal None C N/A 3.14 9.75 NO 15.65 81 4.9 2.2 455 2.41 8/3/2016 MW-4 50.20 36.75 830.63 Normal None C N/A 2.19 5.25 NO 17.04 46 5.7 4.7 394 7.52 8/3/2016 MW-5 30.71 26.09 796.60 Normal None C N/A 0.75 2.25 NO 15.82 36 5.3 2.8 401 2.64 8/3/2016 OB-1 65.50 46.45 779.40 N/A N/A LO N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A 8/3/2016 MW-6 122.14 122.14 797.51 N/A None LO N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A 8/3/2016 MW-7 57.25 44.88 814.28 N/A None LO N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A Purge Methods LF = Low Flow LF(M) = Low Flow (Mod.) C = Connventional NP = No Purge EOP = Equip. Only Purge LO = Level Only * = Applicable to LF & LF(M) Purging Only MARSHALL STEAM STATION DRY ASH LANDFILL GROUNDWATER MONITORING FIELD DATA PERMIT #18-04 B Appendix B Laboratory Report and Chain-of-Custody Forms 13339 Hagers Ferry RoadHuntersville, NC 28078-7929 McGuire Nuclear Complex - MG03A2 Phone: 980-875-5245 Fax: 980-875-4349 Order Summary Report Analytical Laboratory Order Number:J16070637 Project Name:MARSHALL - Lab Contact: Anne Pridgeon Date:9/27/2016 Customer Address:8320 NC Hwy 150 East Customer Name(s):Chuck Campbell, Ed Sullivan, Tim Hunsucker Mail Code: Marshall Steam Station Terrell, NC 28682 Phone: 980-875-6610 Report Authorized By: (Signature) Program Comments: Report has been revised to include chain of custody document. Data Flags & Calculations: 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. Anne Pridgeon Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 1 of 18 Reason: I have reviewed this document. Date: 2016.09.27 09:25:42 -04'00' Sample ID's & Descriptions: Sample ID Plant/Station Collection Date and Time Collected By Sample Description 2016023172 MARSHALL 03-Aug-16 7:50 AM LDC MW-1 2016023173 MARSHALL 03-Aug-16 9:40 AM LDC MW-2 2016023174 MARSHALL 03-Aug-16 10:30 AM LDC MW-3 2016023175 MARSHALL 03-Aug-16 11:50 AM LDC MW-4 2016023176 MARSHALL 03-Aug-16 8:40 AM LDC MW-5 2016023177 MARSHALL 03-Aug-16 12:45 PM LDC FIELD BLANK 6 Total Samples Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 2 of 18 COC and .pdf report are in agreement with sample totals and analyses (compliance programs and procedures). All Results are less than the laboratory reporting limits. All laboratory QA/QC requirements are acceptable. Yes No Technical Validation Review Checklist: Yes No Yes No Report Sections Included: Job Summary Report Sub-contracted Laboratory Results Sample Identification Customer Specific Data Sheets, Reports, & Documentation Technical Validation of Data Package Customer Database Entries Analytical Laboratory Certificate of Analysis Analytical Laboratory QC Report Chain of Custody Reviewed By:Anne Pridgeon Date:8/19/2016 Electronic Data Deliverable (EDD) Sent Separatel Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 3 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 2016023172 Collection Date:03-Aug-16 7:50 AM Site:MW-1 Matrix:GW_RCRA Analyte Analysis Date/TimeMethodUnits Qualifiers RDLResult Sample #: AnalystDF LOW LEVEL ALKALINITY (FIXED END POINT) Alkalinity (mg/L CaCO3)9.3 mg/L (CaCO3) SM 2320B 08/10/2016 12:34 CJELLIO51 INORGANIC IONS BY IC Chloride 92 mg/L EPA 9056A 08/04/2016 12:07 BGN9034110 Fluoride < 0.1 mg/L EPA 9056A 08/04/2016 12:07 BGN90340.1 1 Nitrate 1.2 mg/L EPA 9056A 08/04/2016 12:07 BGN90340.1 1 Nitrate as N 0.27 mg-N/L EPA 9056A 08/04/2016 12:07 BGN90340.023 1 Sulfate 17 mg/L EPA 9056A 08/04/2016 12:07 BGN9034110 MERCURY (COLD VAPOR) IN WATER Mercury (Hg)< 0.05 ug/L EPA 7470A 08/08/2016 16:56 DMFRANC0.05 1 TOTAL RECOVERABLE METALS BY ICP Barium (Ba)0.206 mg/L SW 6010D 08/10/2016 10:03 MHH71310.005 1 Boron (B)0.245 mg/L SW 6010D 08/10/2016 10:03 MHH71310.05 1 Calcium (Ca)33.7 mg/L SW 6010D 08/10/2016 10:03B2 MHH71310.01 1 Chromium (Cr)0.005 mg/L SW 6010D 08/10/2016 10:03 MHH71310.005 1 Copper (Cu)< 0.005 mg/L SW 6010D 08/10/2016 10:03 MHH71310.005 1 Iron (Fe)0.154 mg/L SW 6010D 08/10/2016 10:03 MHH71310.01 1 Magnesium (Mg)8.60 mg/L SW 6010D 08/10/2016 10:03 MHH71310.005 1 Manganese (Mn)0.023 mg/L SW 6010D 08/10/2016 10:03 MHH71310.005 1 Nickel (Ni)< 0.005 mg/L SW 6010D 08/10/2016 10:03 MHH71310.005 1 Potassium (K)5.07 mg/L SW 6010D 08/10/2016 10:03 MHH71310.1 1 Silver (Ag)< 0.005 mg/L SW 6010D 08/10/2016 10:03 MHH71310.005 1 Sodium (Na)12.5 mg/L SW 6010D 08/10/2016 10:03 MHH71310.05 1 Zinc (Zn)0.010 mg/L SW 6010D 08/10/2016 10:03 MHH71310.005 1 TOTAL RECOVERABLE METALS BY ICP-MS Arsenic (As)< 1 ug/L SW 6020B 08/09/2016 17:53 CWSPEN311 Cadmium (Cd)< 1 ug/L SW 6020B 08/09/2016 17:53 CWSPEN311 Lead (Pb)< 1 ug/L SW 6020B 08/09/2016 17:53 CWSPEN311 Selenium (Se)< 1 ug/L SW 6020B 08/09/2016 17:53 CWSPEN311 TOTAL DISSOLVED SOLIDS TDS 260 mg/L SM2540C 08/08/2016 15:27 PARMSTR251 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 4 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 2016023173 Collection Date:03-Aug-16 9:40 AM Site:MW-2 Matrix:GW_RCRA Analyte Analysis Date/TimeMethodUnits Qualifiers RDLResult Sample #: AnalystDF ALKALINITY (FIXED END POINT 4.5) Alkalinity (mg/L CaCO3)23 mg/L (CaCO3) SM 2320B 08/08/2016 13:08 CJELLIO201 INORGANIC IONS BY IC Chloride 5.0 mg/L EPA 9056A 08/04/2016 12:24 BGN90340.5 5 Fluoride < 0.5 mg/L EPA 9056A 08/04/2016 12:24 BGN90340.5 5 Nitrate 2.1 mg/L EPA 9056A 08/04/2016 12:24 BGN90340.5 5 Nitrate as N 0.47 mg-N/L EPA 9056A 08/04/2016 12:24 BGN90340.023 1 Sulfate 200 mg/L EPA 9056A 08/04/2016 12:24 BGN9034550 MERCURY (COLD VAPOR) IN WATER Mercury (Hg)< 0.05 ug/L EPA 7470A 08/08/2016 16:36 DMFRANC0.05 1 TOTAL RECOVERABLE METALS BY ICP Barium (Ba)0.051 mg/L SW 6010D 08/10/2016 10:15 MHH71310.005 1 Boron (B)3.18 mg/L SW 6010D 08/10/2016 10:15 MHH71310.05 1 Calcium (Ca)30.3 mg/L SW 6010D 08/10/2016 10:15B2 MHH71310.01 1 Chromium (Cr)< 0.005 mg/L SW 6010D 08/10/2016 10:15 MHH71310.005 1 Copper (Cu)< 0.005 mg/L SW 6010D 08/10/2016 10:15 MHH71310.005 1 Iron (Fe)0.014 mg/L SW 6010D 08/10/2016 10:15 MHH71310.01 1 Magnesium (Mg)12.4 mg/L SW 6010D 08/10/2016 10:15 MHH71310.005 1 Manganese (Mn)0.015 mg/L SW 6010D 08/10/2016 10:15 MHH71310.005 1 Nickel (Ni)< 0.005 mg/L SW 6010D 08/10/2016 10:15 MHH71310.005 1 Potassium (K)2.68 mg/L SW 6010D 08/10/2016 10:15 MHH71310.1 1 Silver (Ag)< 0.005 mg/L SW 6010D 08/10/2016 10:15 MHH71310.005 1 Sodium (Na)29.7 mg/L SW 6010D 08/10/2016 10:15 MHH71310.05 1 Zinc (Zn)0.006 mg/L SW 6010D 08/10/2016 10:15 MHH71310.005 1 TOTAL RECOVERABLE METALS BY ICP-MS Arsenic (As)< 1 ug/L SW 6020B 08/09/2016 17:34 CWSPEN311 Cadmium (Cd)< 1 ug/L SW 6020B 08/09/2016 17:34 CWSPEN311 Lead (Pb)< 1 ug/L SW 6020B 08/09/2016 17:34 CWSPEN311 Selenium (Se)33.7 ug/L SW 6020B 08/09/2016 17:34 CWSPEN311 TOTAL DISSOLVED SOLIDS TDS 290 mg/L SM2540C 08/08/2016 15:27 PARMSTR251 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 5 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 2016023174 Collection Date:03-Aug-16 10:30 AM Site:MW-3 Matrix:GW_RCRA Analyte Analysis Date/TimeMethodUnits Qualifiers RDLResult Sample #: AnalystDF LOW LEVEL ALKALINITY (FIXED END POINT) Alkalinity (mg/L CaCO3)< 5 mg/L (CaCO3) SM 2320B 08/10/2016 12:34 CJELLIO51 INORGANIC IONS BY IC Chloride 9.1 mg/L EPA 9056A 08/04/2016 12:41 BGN90340.5 5 Fluoride < 0.1 mg/L EPA 9056A 08/04/2016 12:41 BGN90340.1 1 Nitrate 21 mg/L EPA 9056A 08/04/2016 12:41 BGN90340.5 5 Nitrate as N 4.8 mg-N/L EPA 9056A 08/04/2016 12:41 BGN90340.023 1 Sulfate 0.20 mg/L EPA 9056A 08/04/2016 12:41 BGN90340.1 1 MERCURY (COLD VAPOR) IN WATER Mercury (Hg)< 0.05 ug/L EPA 7470A 08/08/2016 16:39 DMFRANC0.05 1 TOTAL RECOVERABLE METALS BY ICP Barium (Ba)0.254 mg/L SW 6010D 08/10/2016 10:19 MHH71310.005 1 Boron (B)0.080 mg/L SW 6010D 08/10/2016 10:19 MHH71310.05 1 Calcium (Ca)0.686 mg/L SW 6010D 08/10/2016 10:19B2 MHH71310.01 1 Chromium (Cr)< 0.005 mg/L SW 6010D 08/10/2016 10:19 MHH71310.005 1 Copper (Cu)< 0.005 mg/L SW 6010D 08/10/2016 10:19 MHH71310.005 1 Iron (Fe)0.018 mg/L SW 6010D 08/10/2016 10:19 MHH71310.01 1 Magnesium (Mg)3.67 mg/L SW 6010D 08/10/2016 10:19 MHH71310.005 1 Manganese (Mn)0.050 mg/L SW 6010D 08/10/2016 10:19 MHH71310.005 1 Nickel (Ni)< 0.005 mg/L SW 6010D 08/10/2016 10:19 MHH71310.005 1 Potassium (K)2.34 mg/L SW 6010D 08/10/2016 10:19 MHH71310.1 1 Silver (Ag)< 0.005 mg/L SW 6010D 08/10/2016 10:19 MHH71310.005 1 Sodium (Na)6.00 mg/L SW 6010D 08/10/2016 10:19 MHH71310.05 1 Zinc (Zn)0.017 mg/L SW 6010D 08/10/2016 10:19 MHH71310.005 1 TOTAL RECOVERABLE METALS BY ICP-MS Arsenic (As)< 1 ug/L SW 6020B 08/09/2016 17:59 CWSPEN311 Cadmium (Cd)< 1 ug/L SW 6020B 08/09/2016 17:59 CWSPEN311 Lead (Pb)< 1 ug/L SW 6020B 08/09/2016 17:59 CWSPEN311 Selenium (Se)< 1 ug/L SW 6020B 08/09/2016 17:59 CWSPEN311 TOTAL DISSOLVED SOLIDS TDS 34 mg/L SM2540C 08/08/2016 15:27 PARMSTR251 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 6 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 2016023175 Collection Date:03-Aug-16 11:50 AM Site:MW-4 Matrix:GW_RCRA Analyte Analysis Date/TimeMethodUnits Qualifiers RDLResult Sample #: AnalystDF LOW LEVEL ALKALINITY (FIXED END POINT) Alkalinity (mg/L CaCO3)18 mg/L (CaCO3) SM 2320B 08/10/2016 12:34 CJELLIO51 INORGANIC IONS BY IC Chloride 2.1 mg/L EPA 9056A 08/05/2016 08:33 BGN90340.2 2 Fluoride < 0.1 mg/L EPA 9056A 08/05/2016 08:33 BGN90340.1 1 Nitrate < 0.1 mg/L EPA 9056A 08/05/2016 08:33 BGN90340.1 1 Nitrate as N < 0.023 mg-N/L EPA 9056A 08/05/2016 08:33 BGN90340.023 1 Sulfate 0.14 mg/L EPA 9056A 08/05/2016 08:33 BGN90340.1 1 MERCURY (COLD VAPOR) IN WATER Mercury (Hg)< 0.05 ug/L EPA 7470A 08/08/2016 16:41 DMFRANC0.05 1 TOTAL RECOVERABLE METALS BY ICP Barium (Ba)0.047 mg/L SW 6010D 08/10/2016 10:23 MHH71310.005 1 Boron (B)< 0.05 mg/L SW 6010D 08/10/2016 10:23 MHH71310.05 1 Calcium (Ca)3.68 mg/L SW 6010D 08/10/2016 10:23B2 MHH71310.01 1 Chromium (Cr)< 0.005 mg/L SW 6010D 08/10/2016 10:23 MHH71310.005 1 Copper (Cu)< 0.005 mg/L SW 6010D 08/10/2016 10:23 MHH71310.005 1 Iron (Fe)0.113 mg/L SW 6010D 08/10/2016 10:23 MHH71310.01 1 Magnesium (Mg)0.727 mg/L SW 6010D 08/10/2016 10:23 MHH71310.005 1 Manganese (Mn)< 0.005 mg/L SW 6010D 08/10/2016 10:23 MHH71310.005 1 Nickel (Ni)< 0.005 mg/L SW 6010D 08/10/2016 10:23 MHH71310.005 1 Potassium (K)1.98 mg/L SW 6010D 08/10/2016 10:23 MHH71310.1 1 Silver (Ag)< 0.005 mg/L SW 6010D 08/10/2016 10:23 MHH71310.005 1 Sodium (Na)4.17 mg/L SW 6010D 08/10/2016 10:23 MHH71310.05 1 Zinc (Zn)0.019 mg/L SW 6010D 08/10/2016 10:23 MHH71310.005 1 TOTAL RECOVERABLE METALS BY ICP-MS Arsenic (As)< 1 ug/L SW 6020B 08/09/2016 18:06 CWSPEN311 Cadmium (Cd)< 1 ug/L SW 6020B 08/09/2016 18:06 CWSPEN311 Lead (Pb)< 1 ug/L SW 6020B 08/09/2016 18:06 CWSPEN311 Selenium (Se)< 1 ug/L SW 6020B 08/09/2016 18:06 CWSPEN311 TOTAL DISSOLVED SOLIDS TDS 31 mg/L SM2540C 08/08/2016 15:27 PARMSTR251 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 7 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 2016023176 Collection Date:03-Aug-16 8:40 AM Site:MW-5 Matrix:GW_RCRA Analyte Analysis Date/TimeMethodUnits Qualifiers RDLResult Sample #: AnalystDF LOW LEVEL ALKALINITY (FIXED END POINT) Alkalinity (mg/L CaCO3)12 mg/L (CaCO3) SM 2320B 08/10/2016 12:34 CJELLIO51 INORGANIC IONS BY IC Chloride 3.0 mg/L EPA 9056A 08/05/2016 08:49 BGN90340.2 2 Fluoride < 0.1 mg/L EPA 9056A 08/05/2016 08:49 BGN90340.1 1 Nitrate < 0.1 mg/L EPA 9056A 08/05/2016 08:49 BGN90340.1 1 Nitrate as N < 0.023 mg-N/L EPA 9056A 08/05/2016 08:49 BGN90340.023 1 Sulfate < 0.1 mg/L EPA 9056A 08/05/2016 08:49 BGN90340.1 1 MERCURY (COLD VAPOR) IN WATER Mercury (Hg)< 0.05 ug/L EPA 7470A 08/08/2016 16:44 DMFRANC0.05 1 TOTAL RECOVERABLE METALS BY ICP Barium (Ba)0.051 mg/L SW 6010D 08/10/2016 10:27 MHH71310.005 1 Boron (B)< 0.05 mg/L SW 6010D 08/10/2016 10:27 MHH71310.05 1 Calcium (Ca)1.34 mg/L SW 6010D 08/10/2016 10:27B2 MHH71310.01 1 Chromium (Cr)< 0.005 mg/L SW 6010D 08/10/2016 10:27 MHH71310.005 1 Copper (Cu)< 0.005 mg/L SW 6010D 08/10/2016 10:27 MHH71310.005 1 Iron (Fe)0.024 mg/L SW 6010D 08/10/2016 10:27 MHH71310.01 1 Magnesium (Mg)0.707 mg/L SW 6010D 08/10/2016 10:27 MHH71310.005 1 Manganese (Mn)< 0.005 mg/L SW 6010D 08/10/2016 10:27 MHH71310.005 1 Nickel (Ni)< 0.005 mg/L SW 6010D 08/10/2016 10:27 MHH71310.005 1 Potassium (K)0.861 mg/L SW 6010D 08/10/2016 10:27 MHH71310.1 1 Silver (Ag)< 0.005 mg/L SW 6010D 08/10/2016 10:27 MHH71310.005 1 Sodium (Na)4.67 mg/L SW 6010D 08/10/2016 10:27 MHH71310.05 1 Zinc (Zn)< 0.005 mg/L SW 6010D 08/10/2016 10:27 MHH71310.005 1 TOTAL RECOVERABLE METALS BY ICP-MS Arsenic (As)< 1 ug/L SW 6020B 08/09/2016 18:12 CWSPEN311 Cadmium (Cd)< 1 ug/L SW 6020B 08/09/2016 18:12 CWSPEN311 Lead (Pb)< 1 ug/L SW 6020B 08/09/2016 18:12 CWSPEN311 Selenium (Se)< 1 ug/L SW 6020B 08/09/2016 18:12 CWSPEN311 TOTAL DISSOLVED SOLIDS TDS 36 mg/L SM2540C 08/08/2016 15:27 PARMSTR251 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 8 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 2016023177 Collection Date:03-Aug-16 12:45 PM Site:FIELD BLANK Matrix:GW_RCRA Analyte Analysis Date/TimeMethodUnits Qualifiers RDLResult Sample #: AnalystDF ALKALINITY (FIXED END POINT 4.5) Alkalinity (mg/L CaCO3)< 20 mg/L (CaCO3) SM 2320B 08/08/2016 13:08 CJELLIO201 INORGANIC IONS BY IC Chloride < 0.1 mg/L EPA 9056A 08/04/2016 12:58 BGN90340.1 1 Fluoride < 0.1 mg/L EPA 9056A 08/04/2016 12:58 BGN90340.1 1 Nitrate < 0.1 mg/L EPA 9056A 08/04/2016 12:58 BGN90340.1 1 Nitrate as N < 0.023 mg-N/L EPA 9056A 08/04/2016 12:58 BGN90340.023 1 Sulfate < 0.1 mg/L EPA 9056A 08/04/2016 12:58 BGN90340.1 1 MERCURY (COLD VAPOR) IN WATER Mercury (Hg)< 0.05 ug/L EPA 7470A 08/08/2016 17:03 DMFRANC0.05 1 TOTAL RECOVERABLE METALS BY ICP Barium (Ba)< 0.005 mg/L SW 6010D 08/10/2016 10:31 MHH71310.005 1 Boron (B)< 0.05 mg/L SW 6010D 08/10/2016 10:31 MHH71310.05 1 Calcium (Ca)0.017 mg/L SW 6010D 08/10/2016 10:31B2 MHH71310.01 1 Chromium (Cr)< 0.005 mg/L SW 6010D 08/10/2016 10:31 MHH71310.005 1 Copper (Cu)< 0.005 mg/L SW 6010D 08/10/2016 10:31 MHH71310.005 1 Iron (Fe)< 0.01 mg/L SW 6010D 08/10/2016 10:31 MHH71310.01 1 Magnesium (Mg)< 0.005 mg/L SW 6010D 08/10/2016 10:31 MHH71310.005 1 Manganese (Mn)< 0.005 mg/L SW 6010D 08/10/2016 10:31 MHH71310.005 1 Nickel (Ni)< 0.005 mg/L SW 6010D 08/10/2016 10:31 MHH71310.005 1 Potassium (K)< 0.1 mg/L SW 6010D 08/10/2016 10:31 MHH71310.1 1 Silver (Ag)< 0.005 mg/L SW 6010D 08/10/2016 10:31 MHH71310.005 1 Sodium (Na)< 0.05 mg/L SW 6010D 08/10/2016 10:31 MHH71310.05 1 Zinc (Zn)< 0.005 mg/L SW 6010D 08/10/2016 10:31 MHH71310.005 1 TOTAL RECOVERABLE METALS BY ICP-MS Arsenic (As)< 1 ug/L SW 6020B 08/09/2016 18:19 CWSPEN311 Cadmium (Cd)< 1 ug/L SW 6020B 08/09/2016 18:19 CWSPEN311 Lead (Pb)< 1 ug/L SW 6020B 08/09/2016 18:19 CWSPEN311 Selenium (Se)< 1 ug/L SW 6020B 08/09/2016 18:19 CWSPEN311 Qualifiers: B2 Target analyte was detected in blank(s) at a concentration greater than ½ the reporting limit but less than the reporting limit. Analyte concentration in sample is valid and may be used for compliance purposes. Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 9 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 Q16080244 ALK_FIX4.5 ALKALINITY (FIXED END POINT 4.5) Level II QC Summary Final QualifierDilMeasuredUnits:Parameter Duplicate # 1 RPD Parent Sample: J16080182 -- 2016024734 Alkalinity (mg/L CaCO3)0.823mg/L (CaCO3)-143.9 Final QualifierDilMeasuredUnits:Parameter LCS # 1 % Recovery LCL UCLSpike Alkalinity (mg/L CaCO3) 98.8 97.2mg/L (CaCO3)-12080196.1 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 10 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 Q16080331 ALK_LL_Fix LOW LEVEL ALKALINITY (FIXED END POINT) Level II QC Summary Final QualifierDilMeasuredUnits:Parameter Duplicate # 1 RPD Parent Sample: J16070637 -- 2016023172 Alkalinity (mg/L CaCO3)1.42mg/L (CaCO3)-19.46 Final QualifierDilMeasuredUnits:Parameter LCS # 1 % Recovery LCL UCLSpike Alkalinity (mg/L CaCO3) 8.81 86.8mg/L (CaCO3)-1208017.64 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 11 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 Q16080122 Dionex INORGANIC IONS BY IC Level II QC Summary Final QualifierDilMeasuredUnits:Parameter Blank # 1 RDL Relative Concentration Chloride 0.0339 mg/L -10.0339 0.1 < 1/2 RDL Fluoride 0.0307 mg/L -10.0307 0.1 < 1/2 RDL Nitrate 0.0178 mg/L -10.0178 0.1 < 1/2 RDL Sulfate -0.0025 mg/L -1-0.0025 0.1 < 1/2 RDL Final QualifierDilMeasuredUnits:Parameter IS # 1 % Recovery LCL UCLSpike Chloride 5.13 5 100mg/L -1208015.13 Fluoride 4.96 5 98.6mg/L -1208014.96 Nitrate 5.02 5 99.8mg/L -1208015.02 Sulfate 8.38 5 88mg/L -1208018.38 Final QualifierDilMeasuredUnits:Parameter ISD # 1 RPD% Recovery LCL UCLSpike Chloride 5.13 5 99.9 0.076mg/L -1208015.13 Fluoride 4.95 5 98.4 0.169mg/L -1208014.95 Nitrate 5.02 5 99.8 0.016mg/L -1208015.02 Sulfate 8.38 5 88 0.0205mg/L -1208018.38 Final QualifierDilMeasuredUnits:Parameter LCS # 1 % Recovery LCL UCLSpike Chloride 5 5 100mg/L -1208015 Fluoride 4.94 5 98.8mg/L -1208014.94 Nitrate 5.14 5 103mg/L -1208015.14 Sulfate 5.2 5 104mg/L -1208015.2 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 12 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 Q16080251 HG 7470 MERCURY (COLD VAPOR) IN WATER Level II QC Summary Final QualifierDilMeasuredUnits:Parameter Blank # 1 RDL Relative Concentration Mercury (Hg) -0.013 ug/L -1-0.013 0.05 < 1/2 RDL Final QualifierDilMeasuredUnits:Parameter LCS # 1 % Recovery LCL UCLSpike Mercury (Hg) 1.85 2 92.5ug/L -1158511.85 Final QualifierDilMeasuredUnits:Parameter MS # 1 % Recovery LCL UCLSpike Parent Sample: J16070637 -- 2016023172 Mercury (Hg) 0.931 1 94.3ug/L -1257510.931 Final QualifierDilMeasuredUnits:Parameter MSD # 1 RPD% Recovery LCL UCLSpike Parent Sample: J16070637 -- 2016023172 Mercury (Hg) 0.946 1 95.8 1.58ug/L -1257510.946 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 13 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 Q16080171 ICP_TRM TOTAL RECOVERABLE METALS BY ICP Level II QC Summary Final QualifierDilMeasuredUnits:Parameter Blank # 1 RDL Relative Concentration Barium (Ba) -0.000011 mg/L -1-0.000011 0.005 < 1/2 RDL Boron (B) -0.000669 mg/L -1-0.000669 0.05 < 1/2 RDL Calcium (Ca) 0.00878 mg/L -10.00878 0.01 > 1/2 RDL Chromium (Cr) 0.000188 mg/L -10.000188 0.005 < 1/2 RDL Copper (Cu) 0.000218 mg/L -10.000218 0.005 < 1/2 RDL Iron (Fe) 0.000495 mg/L -10.000495 0.01 < 1/2 RDL Magnesium (Mg) -0.000349 mg/L -1-0.000349 0.005 < 1/2 RDL Manganese (Mn) 0.000033 mg/L -10.000033 0.005 < 1/2 RDL Nickel (Ni) 0.00033 mg/L -10.00033 0.005 < 1/2 RDL Potassium (K) -0.00597 mg/L -1-0.00597 0.1 < 1/2 RDL Silver (Ag) -0.000672 mg/L -1-0.000672 0.005 < 1/2 RDL Sodium (Na) 0.00594 mg/L -10.00594 0.05 < 1/2 RDL Zinc (Zn) 0.000763 mg/L -10.000763 0.005 < 1/2 RDL Final QualifierDilMeasuredUnits:Parameter LCS # 1 % Recovery LCL UCLSpike Barium (Ba) 5 5 100mg/L -1208015 Boron (B) 4.91 5 98.3mg/L -1208014.91 Calcium (Ca) 5.05 5 101mg/L -1208015.05 Chromium (Cr) 4.9 5 98mg/L -1208014.9 Copper (Cu) 4.94 5 98.9mg/L -1208014.94 Iron (Fe) 5.08 5 102mg/L -1208015.08 Magnesium (Mg) 4.99 5 99.9mg/L -1208014.99 Manganese (Mn) 4.99 5 99.9mg/L -1208014.99 Nickel (Ni) 5.02 5 100mg/L -1208015.02 Potassium (K) 4.89 5 97.8mg/L -1208014.89 Silver (Ag) 0.469 0.5 93.9mg/L -1208010.469 Sodium (Na) 4.94 5 98.8mg/L -1208014.94 Zinc (Zn) 5.01 5 100mg/L -1208015.01 Final QualifierDilMeasuredUnits:Parameter MS # 1 % Recovery LCL UCLSpike Parent Sample: J16070637 -- 2016023172 Barium (Ba) 5.12 5 98.3mg/L -1257515.12 Boron (B) 5.09 5 97mg/L -1257515.09 Calcium (Ca) 38.9 5 104mg/L -12575138.9 Chromium (Cr) 4.78 5 95.6mg/L -1257514.78 Copper (Cu) 4.83 5 96.7mg/L -1257514.83 Iron (Fe) 5.15 5 99.9mg/L -1257515.15 Magnesium (Mg) 13.6 5 100mg/L -12575113.6 Manganese (Mn) 4.88 5 97.1mg/L -1257514.88 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 14 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 Q16080171 ICP_TRM TOTAL RECOVERABLE METALS BY ICP Level II QC Summary Final QualifierDilMeasuredUnits:Parameter MS # 1 % Recovery LCL UCLSpike Parent Sample: J16070637 -- 2016023172 Nickel (Ni) 4.84 5 96.7mg/L -1257514.84 Potassium (K) 10 5 98.8mg/L -12575110 Silver (Ag) 0.46 0.5 92.3mg/L -1257510.46 Sodium (Na) 17.2 5 95.4mg/L -12575117.2 Zinc (Zn) 4.84 5 96.7mg/L -1257514.84 Final QualifierDilMeasuredUnits:Parameter MSD # 1 RPD% Recovery LCL UCLSpike Parent Sample: J16070637 -- 2016023172 Barium (Ba) 5.22 5 100 2.03mg/L -1257515.22 Boron (B) 5.17 5 98.4 1.47mg/L -1257515.17 Calcium (Ca) 39.3 5 112 6.85mg/L -12575139.3 Chromium (Cr) 4.87 5 97.3 1.8mg/L -1257514.87 Copper (Cu) 4.91 5 98.2 1.5mg/L -1257514.91 Iron (Fe) 5.21 5 101 1.33mg/L -1257515.21 Magnesium (Mg) 13.7 5 102 1.93mg/L -12575113.7 Manganese (Mn) 4.97 5 98.9 1.84mg/L -1257514.97 Nickel (Ni) 4.92 5 98.3 1.62mg/L -1257514.92 Potassium (K) 10.1 5 101 2.52mg/L -12575110.1 Silver (Ag) 0.467 0.5 93.7 1.52mg/L -1257510.467 Sodium (Na) 17.4 5 99.6 4.25mg/L -12575117.4 Zinc (Zn) 4.92 5 98.3 1.64mg/L -1257514.92 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 15 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 Q16080179 IMS_TRM TOTAL RECOVERABLE METALS BY ICP-MS Level II QC Summary Final QualifierDilMeasuredUnits:Parameter Blank # 1 RDL Relative Concentration Arsenic (As) -0.012 ug/L -1-0.012 1 < 1/2 RDL Cadmium (Cd) 0.0078 ug/L -10.0078 1 < 1/2 RDL Lead (Pb) 0 ug/L -10 1 < 1/2 RDL Selenium (Se) 0.012 ug/L -10.012 1 < 1/2 RDL Final QualifierDilMeasuredUnits:Parameter LCS # 1 % Recovery LCL UCLSpike Arsenic (As) 48.5 50 97.1ug/L -12080148.5 Cadmium (Cd) 50.4 50 101ug/L -12080150.4 Lead (Pb) 43.9 50 87.7ug/L -12080143.9 Selenium (Se) 49.6 50 99.3ug/L -12080149.6 Final QualifierDilMeasuredUnits:Parameter MS # 1 % Recovery LCL UCLSpike Parent Sample: J16070637 -- 2016023173 Arsenic (As) 48.8 50 97.4ug/L -12575148.8 Cadmium (Cd) 50.3 50 100ug/L -12575150.3 Lead (Pb) 50.6 50 101ug/L -12575150.6 Selenium (Se) 81 50 94.5ug/L -12575181 Final QualifierDilMeasuredUnits:Parameter MSD # 1 RPD% Recovery LCL UCLSpike Parent Sample: J16070637 -- 2016023173 Arsenic (As) 50.1 50 100 2.62ug/L -12575150.1 Cadmium (Cd) 50.9 50 102 1.19ug/L -12575150.9 Lead (Pb) 50.7 50 101 0.263ug/L -12575150.7 Selenium (Se) 82.8 50 98.1 3.74ug/L -12575182.8 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 16 of 18 Certificate of Laboratory Analysis This report shall not be reproduced, except in full. Order # J16070637 Q16080219 TDS TOTAL DISSOLVED SOLIDS Level II QC Summary Final QualifierDilMeasuredUnits:Parameter Blank # 1 RDL Relative Concentration TDS mg/L -1-1 25 < 1/2 RDL Final QualifierDilMeasuredUnits:Parameter Blank # 2 RDL Relative Concentration TDS mg/L -1-1 25 < 1/2 RDL Final QualifierDilMeasuredUnits:Parameter Duplicate # 1 RPD Parent Sample: J16070637 -- 2016023172 TDS 2.31mg/L -1257 Final QualifierDilMeasuredUnits:Parameter Duplicate # 2 RPD Parent Sample: J16070637 -- 2016023173 TDS 0.678mg/L -1296 Final QualifierDilMeasuredUnits:Parameter Duplicate # 3 RPD Parent Sample: J16070637 -- 2016023174 TDS 2.9mg/L -135 Final QualifierDilMeasuredUnits:Parameter Duplicate # 4 RPD Parent Sample: J16070637 -- 2016023175 TDS 3.17mg/L -132 Final QualifierDilMeasuredUnits:Parameter LCS # 1 % Recovery LCL UCLSpike TDS 100 99mg/L -11090199 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 17 of 18 Duke Energy Analytical Lab Revision 1: 9/27/2016 Page 18 of 18