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HomeMy WebLinkAbout2019_11_27 Coal Pile Assessment Tech Memo - Cliffside - AddendumL� synTerra TECHNICAL MEMORANDUM Date: November 27, 2019 File: 1026.21.060 To: Ryan Czop (Duke Energy) Cc: Kathy We7.,OPJ-- From: Scott Spinner Subject: Soil and Groundwater Assessment Addendum - Coal Pile - Cliffside Steam Station Duke Energy Carolinas, LLC (Duke Energy) owns and operates the Rogers Energy Complex (henceforth referred to as the Cliffside Steam Station (CSS), or the site), which is located in Mooresboro, Rutherford and Cleveland Counties, North Carolina. CSS began operation in 1940 as a coal-fired generating station. Units 1 through 4 were retired in October 2011, and currently only Units 5 and 6 are in operation at CSS. Coal used for electricity generation is transported to the Site by railroad and stored on approximately 22 acres northeast of the the Unit 5 power generation plant and north of the Unit 6 power generation plant. The coal ash residue and other liquid discharges from coal combustion processes at CSS have historically been managed in CSS ash basins, which consist of the active ash basin, the former Units 1-4 ash basin, and the Unit 5 inactive ash basin. An initial soil and groundwater assessment of the coal pile was conducted from May 2019 through July 2019. Thirteen (13) monitoring wells were installed in general accordance with the Soil and Groundwater Assessment — Coal Pile — Cliffside Steam Station Technical Memorandum dated June 29, 2018 (workplan). The workplan was approved by NCDEQ in a July 31, 2018 letter from Jon Risgaard, Chief, Animal Feeding Operations and Groundwater Section to Paul Draovitch, Senior Vice President, with Duke Energy. The monitoring well locations and well identifications for the installed assessment wells are presented on Figure 1. A well construction table is provided as Table 1. An initial round of sampling and analysis of groundwater from the coal pile assessment wells was conducted in July 2019. The analytical results have been previously submitted to NCDEQ in the August 2019 quarterly comprehensive data submittal. Based on the analytical results from the coal pile wells, the horizontal and vertical extent of groundwater impacts around the CSS coal pile have not been delineated. P:\Duke Energy Carolinas \ 21. CLIFFSIDE \ 06.EHS-CAMA Compliance Support and Corrective Action\ Assessment\ Coal Pile Assessment\Coal Pile Assessment Workplan - Addendum\Coal Pile Assessment Tech Memo - Cliffside - Addendum.docx Soil and Groundwater Assessment Addendum — Coal Pile November 27, 2019 Cliffside Steam Station Page 2 of 4 Additional groundwater and soil assessment activities for the coal pile to delineate the horizontal and vertical extent of groundwater impacts are described herein. Regulatory Background In 2014, The North Carolina General Assembly passed the Coal Ash Management Act (CAMA). CAMA required owners of a coal combustion residuals (CCR) surface impoundment to conduct detailed assessment of site groundwater within and around the CCR surface impoundment. Groundwater monitoring wells were not installed near the coal pile during CAMA- associated fieldwork. Duke Energy understands the soils beneath the coal pile may be a potential "secondary source" of inorganic constituents that will be assessed apart from CAMA. Station Description Coal-fired power generation operations began at CSS in 1940. Coal is transported on - site by rail and offloaded onto the coal pile area where it is stored until burned by the coal -powered energy generating units. The coal pile area is approximately 22 acres and is located northeast of the the Unit 5 power generation plant and north of the Unit 6 power gerneration plant. A liner is located beneath approximately four acres of the eastern end of the coal pile. Coal Pile Area Additional Assessment Objectives Objectives of the coal pile area additional assessment activities include the following: • Characterize inorganic constituents associated with coal pile area soils • Characterize the horizontal and vertical extent of inorganic constituent concentrations in groundwater surrounding the coal pile area • Compare inorganic constituent concentrations in coal pile area groundwater and site background groundwater Soil Assessment Coal pile area soils are proposed to be sampled and analyzed for inorganic parameters to determine if the soil may be a secondary source of coal pile constituents that could leach into underlying groundwater. Soil samples are proposed to be collected at proposed monitoring well locations (CP-7, CP-8, and CP-9) as part of well installation activities (Figure 1). Due to the coal pile being active, soil samples directly beneath the footprint of the coal pile will not be accessible. Soil samples will be collected at approximately 5-foot intervals to the top of the groundwater table. An additional P:\Duke Energy Carolinas\21. CLIFFSIDE\06.EHS-CAMA Compliance Support and Corrective Action \ Assessment \ Coal Pile Assessment \ Coal Pile Assessment Workplan - Addendum \ Coal Pile Assessment Tech Memo - Cliffside - Addendum.docx Soil and Groundwater Assessment Addendum — Coal Pile November 27, 2019 Cliffside Steam Station Page 3 of 4 shallow soil sample will be collected below the water table within the new well screened intervals. Samples of bedrock will not be collected for analysis. Soil samples will be analyzed for inorganic parameters as listed on Table 2. Soil samples will also be collected approximately 5-feet below ground surface and the interval immediately above the water table and analyzed for leachable inorganics using Synthetic Precipitation Leaching Procedures (SPLP) at each well cluster location. Groundwater Assessment Thirteen coal pile assessment (CP) groundwater monitoring wells are proposed to be installed to characterize the horizontal and vertical extent of coal pile area impacts to groundwater. Three shallow ("S"), three deep ("D"), and seven bedrock ("BR") groundwater monitoring wells (CP-1BR, CP-3BRL, CP-4BR/BRL, CP-7S/D/BR, CP- 8S/D/BR, and CP-9S/D/BR) are proposed to be installed. Proposed approximate additional CP well installation locations are shown on Figure 1 and proposed well details are provided as Table 3. Shallow groundwater monitoring wells will be installed approximately 5 feet below the water table. Specific well locations may be shifted depending upon access and field conditions at the time of installation. Groundwater samples will be analyzed for inorganic constituents as listed on Table 4. Groundwater samples from monitoring wells CP-3BRL, CP-4BR/BRL, CP-8S/D/BR, and CP-9S/D/BR will also be analyzed for total uranium, radium-226, and radium-228. Coal Pile Assessment Report A coal pile comprehensive site assessment report (CSA) will be prepared and submitted to NCDEQ by March 31, 2020. Groundwater data available by February 1, 2020 will be included in the CSA report. If data for the additional monitoring wells in not available in time for inclusion in the CSA report an addendum to the report may be necessary. Additional existing site data will be used in characterizing the coal pile soils and groundwater, including CAMA and CCR program data. The report will include the following components: 1) Site History and Source Characterization 2) Site Geology and Hydrogeology 3) Sampling Results 4) Site Conceptual Model 5) Conclusions and Recommendations P:\Duke Energy Carolinas\21. CLIFFSIDE\06.EHS-LAMA Compliance Support and Corrective Action \ Assessment \ Coal Pile Assessment \ Coal Pile Assessment Workplan - Addendum \ Coal Pile Assessment Tech Memo - Cliffside - Addendum.docx Soil and Groundwater Assessment Addendum - Coal Pile November 27, 2019 Cliffside Steam Station ATTACHMENTS: Table 1: Monitoring Well Construction Table 2: Soil Analytical Methods Table 3: Proposed Coal Pile Assessment Soil Samples and Monitoring Wells Table 4: Groundwater Analytical Methods Figure 1: Additional Coal Pile Assessment Proposed Monitoring Wells Page 4 of 4 P:\Duke Energy Carolinas\21. CLIFFSIDE\06.EHS-LAMA Compliance Support and Corrective Action \ Assessment \ Coal Pile Assessment \ Coal Pile Assessment Workplan - Addendum \ Coal Pile Assessment Tech Memo - Cliffside - Addendum.docx Soil and Groundwater Assessment — Coal Pile November 22, 2019 Cliffside Steam Station ATTACHMENTS P:\Duke Energy Carolinas \ 21. CLIFFSIDE \ 06.EHS-CAMA Compliance Support and Corrective Action\ Assessment\ Coal Pile Assessment\Coal Pile Assessment Workplan - Addendum\Coal Pile Assessment Tech Memo - Cliffside - Addendum.docx TABLE 1 MONITORING WELL CONSTRUCTION COAL PILE ASSESSMENT CLIFFSIDE STEAM STATION DUKE ENERGY CAROLINAS, LLC, MOORESBORO, NC Well ID Well Installed Outer Casing Depth (6-inch) (ft bgs) Well Screen Interval (ft bgs) ( S U.) Turbidity Flow Layer Surface Completion CP-1D 6/11/2019 N/A 39.1-49.1 3.84 7.3 Deep Stick-up CP-2S 6/4/2019 N/A 37-47 5.09 8.6 Shallow Flush Mount CP-2BRU 6/10/2019 48.0 57-67 6.91 9.1 Deep Flush Mount CP-2BR 6/11/2019 48.0 167-177 8.38 7.5 Bedrock Flush Mount CP-3S 5/31/2019 N/A 37-47 5.31 3.6 Shallow Flush Mount CP-3BR 5/31/2019 71.0 107-117 5.74 9.9 Bedrock Flush Mount CP-4S 5/29/2019 N/A 31-36 3.63 9.5 Shallow Stick-up CP-4BRU 5/29/2019 43.0 49-59 3.45 7.8 Deep Stick-up CP-SS 5/22/2019 N/A 39.9-49.9 5.32 7.6 Shallow Stick-up CP-5I 5/20/2019 110.0 113-123 5.49 7.8 Shallow Stick-up CP-5BR 5/22/2019 127.0 166-176 7.53 9.8 Bedrock Stick-up CP-6S 6/12/2019 N/A 42-47 5.67 8.9 Shallow Flush Mount CP-6BR 6/13/2019 49.0 117-127 7.64 9.5 Bedrock Flush Mount Notes: ft bgs - feet below ground surface S.U. - Standard Units NTU - Nephelometric Turbidity Units pH and turbidity readings were taken after well development Prepared by: TJG Checked by: SAS Page 1 of 1 TABLE 2 SOIL ANALYTICAL METHODS COAL PILE ASSESSMENT CLIFFSIDE STEAM STATION DUKE ENERGY CAROLINAS, LLC, MOORESBORO, NC INORGANIC COMPOUNDS UNITS METHOD Aluminum mg/kg EPA 6010D Antimony mg/kg EPA 6020B Arsenic mg/kg EPA 6020A Barium mg/kg EPA 6010C Beryllium mg/kg EPA 6020B Boron mg/kg EPA 6010C Cadmium mg/kg EPA 6020A Calcium mg/kg EPA 6010C Chloride mg/kg EPA 9056A Chromium mg/kg EPA 6010C Cobalt mg/kg EPA 6020A Copper mg/kg EPA 6010C Iron mg/kg EPA 6010C Lead mg/kg EPA 6020A Magnesium mg/kg EPA 6010C Manganese mg/kg EPA 6010C Mercury mg/kg EPA Method 7471B Molybdenum mg/kg EPA 6010C Nickel mg/kg EPA 6010C Nitrate as Nitrogen mg/kg EPA 9056A pH SU EPA 9045D Potassium mg/kg EPA 6010C Selenium mg/kg EPA 6020A Sodium mg/kg EPA 6010C Strontium mg/kg EPA 6010C Sulfate mg/kg EPA 9056A Thallium (low level) (SPLP Extract only) mg/kg EPA 6020A Total Organic Carbon mg/kg EPA 9060 Vanadium mg/kg EPA 6020A Zinc mg/kg EPA 6010C Prepared by: RBI Checked by: SRW/TCP Notes• 1. Soil samples to be analyzed for Total Inorganics using USEPA Methods 6010/6020 and pH using USEPA Method 9045; select soil samples will also be analyzed for leaching potential using SPLP Extraction Method 1312 in conjunction with USEPA Methods 6010/6020. 2. Analytical methods and reporting limits as presented were applicable at time of CSA field implementation in 2015. Analytical methods and reporting limits are updated periodically and applied as appropriate. meq/100g - millequivalents per 100 grams mg/kg - Milligrams per kilogram my - Millivolts S.U. - Standard Unit Page 1 of 1 TABLE 3 PROPOSED COAL PILE ASSESSMENT SOIL SAMPLES AND MONITORING WELLS COAL PILE ASSESSMENT CLIFFSIDE STEAM STATION DUKE ENERGY CAROLINAS, LLC, MOORESBORO, NC Monitoring Well I Estimated Well Depth (feet bgs) Soil Sample ID (Estimated Depth Interval in feet bgs) Comments C13-11311 120 CP-1SB (110-120) HAO/HFO sample CP-3BRL 200 CP-3SB (190-200) HAO/HFO sample C13-41311 120 CP-3SB (110-120) HAO/HFO sample CP-4BRL 200 CP-3SB (190-200) HAO/HFO sample -- -- CP-7SB (3.5-5) Near -surface unsaturated soil sample (water table —25 feet bgs) -- -- CP-7SB (8.5-10) Unsaturated soil sample -- -- CP-7SB (13.5-15) Unsaturated soil sample -- -- CP-7SB (18.5-20) Unsaturated soil sample -- -- CP-7SB (23.5-25) Unsaturated soil sample CP-7S 40 CP-7SB (33.5-35) Soil sample from shallow well screened interval, HAO/HFO sample CP-7D 60 CP-7SB (53.5-55) Soil sample from deep well screened interval, HAO/HFO sample CP-71311 130 CP-7SB (128.5-130) HAO/HFO sample -- -- CP-8SB (3.5-5) Near -surface unsaturated soil sample (water table "25 feet bgs) -- -- CP-8SB (8.5-10) Unsaturated soil sample -- -- CP-8SB (13.5-15) Unsaturated soil sample -- -- CP-8SB (18.5-20) Unsaturated soil sample -- -- CP-8SB (23.5-25) Unsaturated soil sample CP-8S 40 CP-8SB (33.5-35) Soil sample from shallow well screened interval, HAO/HFO sample CP-8D 60 CP-8SB (53.5-55) Soil sample from deep well screened interval, HAO/HFO sample CP-81311 130 CP-8SB (128.5-130) HAO/HFO sample -- -- CP-9SB (3.5-5) Near -surface unsaturated soil sample (water table —25 feet bgs) -- -- CP-9SB (8.5-10) Unsaturated soil sample -- -- CP-9SB (13.5-15) Unsaturated soil sample -- -- CP-9SB (18.5-20) Unsaturated soil sample -- -- CP-9SB (23.5-25) Unsaturated soil sample CP-9S 40 CP-9SB (33.5-35) Soil sample from shallow well screened interval, HAO/HFO sample CP-913 60 CP-9SB (53.5-55) Soil sample from deep well screened interval, HAO/HFO sample CP-9BR 130 CP-9SB (128.5-130) HAO/HFO sample Prepared by: SAS Checked by: TJG Notes: bgs = below ground surface — = Approximately SynTerra recommends hollow stem auger and air rotary or sonic methods for boring and well installation. Continuous cores from air rotary or sonic drilling provide sufficient material for soil sampling and lithologic description. Estimated well and soil sample depths based on data from the existing well clusters. Number of soil samples shown is approximate. A shallower water table will result in fewer samples, and a deeper water table will result in additional samples. SynTerra recommends the shallow monitoring wells be installed approximately 5 feet below the water table and have a length of at least 10 feet. Page 1 of 1 TABLE 4 GROUNDWATER ANALYTICAL METHODS COAL PILE ASSESSMENT CLIFFSIDE STEAM STATION DUKE ENERGY CAROLINAS, LLC, MOORESBORO, NC PARAMETER RL UNITS IMETHOD FIELD PARAMETERS pH NA SU Field Water Quality Meter Specific Conductance NA VS/CM Field Water Quality Meter Temperature NA 0C Field Water Quality Meter Dissolved Oxygen NA mg/L Field Water Quality Meter Oxidation Reduction Potential NA mV Field Water Quality Meter Eh NA mV Field Water Quality Meter Turbidity INA INTU Field Water Quality Meter INORGANICS Aluminum 0.005 mg/L EPA 200.7 or 6010D Antimony 0.001 mg/L EPA 200.8 or 6020B Arsenic 0.001 mg/L EPA 200.8 or 6020B Barium 0.005 mg/L EPA 200.7 or 6010D Beryllium 0.001 mg/L EPA 200.8 or 6020B Boron 0.05 mg/L EPA 200.7 or 6010D Cadmium 0.001 mg/L EPA 200.8 or 6020B Chromium 0.001 mg/L EPA 200.8 or 6020B Cobalt 0.001 mg/L EPA 200.8 or 6020B Copper 0.001 mg/L EPA 200.8 or 6020B Hexavalent Chromium 0.000025 mg/L EPA 218.7 Iron 0.01 mg/L EPA 200.7 or 6010D Lithium 1 mg/L EPA 200.7 or 6010D Lead 0.001 mg/L EPA 200.8 or 6020B Manganese 0.005 mg/L EPA 200.7 or 6010D Mercury 0.00005 mg/L EPA 245.1 or 7470A Molybdenum 0.001 mg/L EPA 200.8 or 6020B Nickel 0.001 mg/L EPA 200.8 or 6020B Selenium 0.001 mg/L EPA 200.8 or 6020B Strontium 0.005 mg/L EPA 200.7 or 6010D Thallium (low level) 0.0002 mg/L EPA 200.8 or 6020B Vanadium (low level) 10.0003 mg/L I EPA 200.8 or 6020B Zinc 10.005 mg/L I EPA 200.7 or 6010D RADIONUCLIDES Radium 226 1 pCi/L EPA 903.1 Modified Radium 228 1 pCi/L EPA 904.0/SW846 9320 Modified Uranium (233, 234, 236, 238) Varies by isotope µg/mL SW846 3010A/6020A ANIONS/CATIONS/OTHER Alkalinity (as CaCO3) 5 mg/L SM 2320B Bicarbonate 5 mg/L SM 2320B Calcium 0.01 mg/L EPA 200.7 Carbonate 5 mg/L SM 2320B Chloride 0.1 mg/L EPA 300.0 or 9056A Fluoride 0.1 mg/L EPA 300.0 or 9056A Magnesium 0.005 mg/L EPA 200.7 or 6010D Potassium 0.1 mg/L EPA 200.7 Sodium 0.05 mg/L EPA 200.7 Sulfate 0.1 mg/L EPA 300.0 or 9056A Sulfide 0.1 mg/L SM 4500 S2 D Total Dissolved Solids 25 mg/L SM 2540C Total Phosphorus 0.05 mg/L EPA 365.1 Total Organic Carbon 0.1 mg/L SM5310C/EPA9060A Total Suspended Solids 5 mg/L SM 2450D Notes: NA indicates not applicable. °C - Degrees Celsius mg/L - Milligrams per liter mV - Millivolts NTU - Nephelometric turbidity unit pCi/L - picocuries per liter RL = reporting limit S.U. - Standard Unit ug/mL - micrograms per milliliter µS/cm = micro -Siemens per centimeter Dissolved and total metals analysis Prepared by: HHS Checked by: RH] Page 1 of 1 Lt if I ,,. t'• err' 1, R GWA-32S/D/B - ` - ILI'_ - deb ' �._ y'` ,`Ik lik .. • L 1�f i • • 4 e `� " .. '4"s+ — CP-3S/BR e • _ L .i+ �r �' • t• y� , CP-4S/BRU i i r h . �r��{J' •d�i'k �CP-2S/BRU/BR ti. • r '• GWA-10S/D = 'SIt ' :. IL CCR-IB-3S/D/BR CP-1 D s CP-5S/I/BR Ilk .r _ .' LEGEND PROPOSED MONITORING WELL I ! MONITORING WELL e '' ', - `+.�A' - '--•s �_ ;,�_ " CP-6S/BR "�"+ ASH BASIN WASTE BOUNDARY " "" • ��• �`, t'~ �� ASH BASIN COMPLIANCE BOUNDARY : J. h 4 �,•4 rye . s " ♦ ;r �- A `''- )IN- STREAM (AMEC NRTR) . ' .. *.� �. - t NOTES: �S ,. �. f `.� ti• 1. THE WATERS OF THE US HAVE NOT BEEN APPROVED BY THE US ARMY CORPS OF •� - '.r , '< ",• }_! ,,, _ ENGINEERS AT THE TIME OF THE MAP CREATION. THIS MAP IS NOT TO BE USED FOR JURISDICTIONAL DETERMINATION PURPOSES. THE WETLANDS AND STREAMS .. = ti - BOUNDARIES WERE OBTAINED FROM AMEC FOSTER WHEELER ENVIRONMENTAL AND ♦� - INFRASTRUCTURE, INC NATURAL RESOURCE TECHNICAL REPORT (NRTR) FOR �' ,� f �'F ♦� ♦ _ CLIFFSIDE STEAM STATION DATED JUNE 19, 2015. k _ yl� ; '; r ' ♦', - - 2. AERIAL PHOTOGRAPHY OBTAINED FROM GOOGLE EARTH PRO ON SEPTEMBER 7, -``,� 2018. IMAGE COLLECTED ON APRIL 20, 2018. 3. DRAWING HAS BEEN SET WITH A PROJECTION OF NORTH CAROLINA STATE PLANE y COORDINATE SYSTEM RIPS 3200 (NAD83). 150 D 150 300 FIGURE 1 GRAPHIC SCALE IN FEET ADDITIONAL COAL PILE ASSESSMENT synTerra PROPOSED MONITORING WELLS DRAWN BY: C. DAVIS Date: 10/01/2019 ti CHECKREVISEDBY.C.DAVIS.GRA Date:11/13/2019 CLIFFSIDE STEAM STATION Y x - ♦ - ~ - '�~ �. "+� �' DUKE CHECKED BY. T. GRANT Date: 11/13/2019 , ' "�♦ r _ t R a-. ENERGY PROJECT MANAGER: S. SPINNER Date:11/13/2019 MOORESBORO, NORTH CAROLINA �-` CAROLINA S www.synterracorp.com