HomeMy WebLinkAboutAdditional Source Area Assessment Workplan3191 Pine Hall Road
Walnut Cove, NC 27052
336-445-0610
November 15, 2018
Ms. Shuying Wang
Division of Water Resources
North Carolina Department of Environmental Quality
Winston Salem Regional Office
450 West Hanes Mill Road, Suite 300
Winston-Salem, North Carolina 27105
Subject: Duke Energy Carolinas, LLC
Dan River Steam Station
Proposed Additional Source Area Assessment
Dear Ms. Wang:
Duke Energy submits this proposed work plan, prepared by SynTerra Corp., to assess additional sources of
groundwater exceedances at the Dan River Steam Station site. Pursuant to the September 8, 2017 DEQ letter
and agreed upon during the CSA Update Review comments meeting on June 28, 2018, Duke Energy
understands the former coal pile area, CT area, and construction warehouse area soils and underlying
groundwater to be a potential “secondary source” of inorganic constituents that will be assessed apart from
CAMA.
Duke Energy formally requests your concurrence to this Assessment Work Plan.
If you have any questions or concerns, please contact Melonie Martin at 336-445-0610 or at
Melonie.Martin@duke-energy.com
Sincerely,
Melonie Martin
Environmental Services
Electronic cc: John Toepfer, Duke Energy
Ed Sullivan, Duke Energy
Jerry Wylie, SynTerra Corp.
Sherri Knight, NCDEQ
Steve Lanter, NCDEQ
Eric Smith, NCDEQ
ADDITIONAL SOURCE AREA ASSESSMENT
DAN RIVER STEAM STATION
900 S. EDGEWOOD ROAD
EDEN, NC 27288
NOVEMBER 2018
PREPARED FOR
DUKE ENERGY CAROLINAS, LLC
Jerry A. Wylie, NC LG 1425
Project Manager
Erin N. Kinsey, EIT
Project Engineer
Additional Source Area Assessment Work Plan November 2018
Dan River Steam Station
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LIST OF FIGURES
Figure 1 Site Location Map
Figure 2 Proposed Monitoring Well & Soil Boring Location Map – South
Figure 3 Proposed Monitoring Well & Soil Boring Location Map – West
LIST OF TABLES
Table 1 Soil Sample Analytical Methods
Table 2 Proposed Coal Pile Assessment Soil Samples and Monitoring Wells
Table 3 Groundwater Analytical Methods
Additional Source Area Assessment Work Plan November 2018
Dan River Steam Station
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Introduction
Duke Energy Carolinas, LLC (Duke Energy) owns and operates the Dan River Energy
Complex on the site of the former Dan River Steam Station (Plant or Site) near the town
of Eden in Rockingham County, NC. The Site encompasses approximately 380 acres.
Coal-fired power generation operations began in 1949 with the construction of the first
of three power-generating units. All three coal-fired units along with three 28-
megawatt oil-fired combustion turbine units were taken offline in 2012. A Combined
Cycle Station was constructed on site and began operation in October 2012. Coal was
transported on site by rail and stored on approximately 6.5 acres that constituted the
former coal pile area, immediately north of the former steam station on the north bank
of the Dan River. Combustion turbines (CTs) were located north of the former coal pile,
near the southwest corner of the Combined Cycle Station. Following the retirement of
the coal- and oil-fired units, the coal pile and turbines were removed from the Site. A
construction warehouse was built where a former baseball field was located.
Groundwater and soil assessment activities for the former coal pile area, CT area, and
construction warehouse area are described herein.
The on-site Land Clearing and Inert Debris (LCID) Landfill, Permit 79B-LCID, is not
included in this assessment. The LCID landfill does not contain coal combustion
residual (CCR) material.
Regulatory Background
In 2014, The North Carolina General Assembly passed the Coal Ash Management Act
(CAMA). CAMA required owners of a CCR surface impoundment to conduct detailed
assessment of Site groundwater within and around the CCR surface impoundment.
As indicated in a letter from the North Carolina Department of Environmental Quality
(DEQ) dated September 8, 2017 (Zimmerman to Sullivan), it is understood that in
addition to CAMA requirements, Duke Energy is also bound by the rules and
requirements of the NC General Statutes and NC Administrative Code 02L. These
provide requirements for the assessment and abatement of soil and groundwater
impacts resulting from Site activities. Therefore, Duke Energy is required to address
soil and groundwater impacts resulting from all primary and secondary sources at the
coal ash facilities, not just the CCR surface impoundments. Pursuant to technical
direction provided by in the September 8, 2017 letter, Duke Energy understands the
former coal pile area, CT area, and construction warehouse area soils and underlying
groundwater to be a potential “secondary source” of inorganic constituents will be
assessed on a separate timeline apart from CCR surface impoundments covered under
CAMA.
Additional Source Area Assessment Work Plan November 2018
Dan River Steam Station
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Site Description
The Dan River Plant is situated on the north bank of the Dan River, which is the
south/southwest property line of the Plant (Figure 1). The Plant is bordered by an
unnamed tributary on the west side, which flows into the Service Water Settling pond.
Another tributary, locally known as Railroad Branch, flows through the Site east of the
Plant operations.
The former coal pile is located north of the former steam station (Figure 2). The steam
station and former coal pile were separated by a rail line that was used to transport coal
onto the Site. This area is south of what is now the Combined Cycle Station and is a
large, vacant grass-vegetated area. The land surface surrounding the coal pile is
generally flat and is at an elevation of approximately 530 feet North American Vertical
Datum of 1988 (NAVD 88).
The combustion turbine area is located at the southwest corner of the Combined Cycle
Station (Figure 2). The area is now a cleared, grassy area. The elevation of the area is
approximately 545 feet NAVD 88.
The construction warehouse area is located northeast of the Combined Cycle Station
(Figure 3). The area was graded to create a flat, paved area upon which the warehouse
and laydown areas were constructed. Beyond the paved area to the south and west, the
land surface slopes downward west toward the unnamed tributary on the west of the
Site and southwest along the west side of the Combined Cycle Station into a drainage
swale. The elevation of the construction warehouse area is about 600 feet NAVD 88.
Additional Source Area Assessment Objectives
Objectives of the additional source area assessment include the following:
• Characterize inorganic constituents associated with coal pile area, CT area, and
construction warehouse area soils;
• Compare inorganic constituent concentrations in coal pile area, CT area, and
construction warehouse area soils and Site background soils;
• Characterize inorganic constituent concentrations in groundwater underlying the
coal pile area, CT area, and construction warehouse area and just beyond the coal
pile area, CT area, and construction warehouse area perimeters; and
• Compare inorganic constituent concentrations in coal pile area, CT area, and
construction warehouse area groundwater and Site background groundwater.
Additional Source Area Assessment Work Plan November 2018
Dan River Steam Station
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Soil Assessment
Coal pile area, CT area, and construction warehouse area soils will be sampled and
analyzed for inorganic parameters to determine if they are a secondary source of CCR
constituents that may leach into underlying groundwater. Soil samples will be collected
at proposed monitoring well locations (CPA-1 through CPA-7; CTA-1, CTA-2 and
GWA-7BR; and CWA-1 through CWA-6 and GWA-12) as part of well installation
activities. The proposed locations of the monitoring wells are included as Figures 2 and
3. Proposed locations are approximate and may vary slightly based on field
observations and locations of underground utilities which will be determined prior to
initiation of boring activities.
Soil samples will be analyzed for inorganic parameters consistent with assessment of
areas used for coal and CCR management (Table 1). Soil samples will be collected from
the near ground surface (2 to 3 feet) and at approximately 2- to 5-foot intervals to the
top of the groundwater table or bedrock, whichever is encountered first. An additional
soil sample will be collected below the water table within the new well screened
intervals. SPLP samples will be collected at a frequency of two per well cluster location
with one unsaturated sample collected from near ground surface (2 to 3 feet) and a
saturated sample collected 2 to 3 feet below the water table (Table 2).
Soil samples will also be collected from depths that coincide with the screen intervals of
newly installed wells for analysis of metal oxy-hydroxide phases of iron and aluminum
(HFO and HAO) to support optimization of the geochemical model for the Site.
HFO/HAO samples will be collected at each well. Following the first round of
groundwater sampling, wells that are geochemically significant to the Site will be
selected for analysis at approximately 15 wells. HFO/HAO analysis will be used in a
geochemical modeling approach that combines an aqueous speciation model with a
sorption model under a thermochemical framework that will use the site-specific in-situ
HFO and HAO results as a proxy of constituent sorption capacity.
Groundwater Assessment
Groundwater conditions proximate to the three areas of further investigation will be
assessed by installing groundwater monitoring wells in and around of the coal pile
area, CT area, and construction warehouse and collecting/analyzing representative
groundwater samples from the wells.
A total of 21 coal pile assessment (CPA) groundwater monitoring wells are proposed to
be installed to characterize coal pile area groundwater conditions. Four shallow (“S”),
four deep (“D”), and four bedrock (“BR”) groundwater monitoring wells (CPA-
Additional Source Area Assessment Work Plan November 2018
Dan River Steam Station
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1S/D/BR, CPA-2S/D/BR, CPA-3S/D/BR, and CPA-4S/D/BR) are planned to be installed
as well clusters at the proposed locations shown on Figure 2.
A total of seven combustion turbine area assessment (CTA) groundwater monitoring
wells are proposed to be installed to characterize coal pile area groundwater. Three
shallow (“S”), three deep (“D”), and four bedrock (“BR”) groundwater monitoring
wells (CTA-1S/D/BR, CTA-2S/D/BR, and GWA-7BR) are planned to be installed as well
clusters at the proposed locations shown on Figure 2.
A total of 19 construction warehouse area assessment (CWA) groundwater monitoring
wells are proposed to be installed to characterize coal pile area groundwater. Seven
shallow (“S”), seven deep (“D”), and eight bedrock (“BR”) groundwater monitoring
wells (CWA-1S/D/BR, CWA-2S/D/BR, CWA-3S/D/BR, CWA-4S/D/BR, CWA-5S/D/BR,
CWA-6S/D/BR, and GWA-12BR) are planned to be installed as well clusters at the
proposed locations shown on Figure 3.
Well locations may be modified from those shown on Figures 2 and 3 based on field
constraints (e.g. underground utility locations, rig stability).
Well installation procedures and well construction materials and lengths will be
consistent with ongoing CAMA assessment activities in accordance with the approved
Proposed Groundwater Assessment Work Plan (Rev. 1) (HDR, 2014). Shallow wells are
proposed to be installed so that the top of the screened interval is positioned
approximately 5 ft. below the water table, where practical, to avoid potential issues
such as biofouling and introduction of artificial redox conditions which are common
among monitoring wells with screened intervals that bracket the water table.
Rotary sonic drilling will be employed as the primary drilling technology for soil
sampling, well drilling, and well installation. In some cases in the unconsolidated
surficial materials, hollow stem augers may be employed for borehole stability and
unsaturated soil sampling. Rotary sonic drilling allows continuous cores to be retained
for subsurface characterization purposes. Continuous soil and rock cores will be
collected from the ground surface to the bottom of the exploration to document the
underlying stratigraphy; identify the depth encountered and the thickness of the
transition zone; identify the depth encountered of competent bedrock; and identify
potential water-bearing fractures.
Anticipated well depths are provided in Table 2. Groundwater samples will be
analyzed for field parameters (e.g., pH, conductivity, and turbidity) and inorganic
constituents consistent with ongoing CAMA assessment activities (Table 3).
Additional Source Area Assessment Work Plan November 2018
Dan River Steam Station
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Additional Source Area Assessment Report
An additional source area assessment report will be prepared after soil and
groundwater sample analytical data is received, validated, and evaluated. Components
of the report will include:
1) Brief Site History
2) Description of Source Assessment Activities
3) Observations Concerning Geology and Hydrogeology in Areas of Additional
Assessment
4) Soil Analytical Results
5) Groundwater Analytical Results
6) Site Conceptual Model
7) Conclusions and Recommendation
Additional Source Area Assessment Work Plan November 2018
Dan River Steam Station
FIGURES
SOURCE:
USGS TOPOGRAPHIC MAP OBTAINED FROM NRCS GEOSPTIAL DATA GATEWAY AT
http://datagateway.nrcs.usda.gov/ ,, ROCKINGHAM COUNTY
synTena
FIGURE 1SITE LOCATION MAP DAN RIVER STEAM STATION DUKE ENERGY CAROLINAS, LLC EDEN, NORTH CAROLINA NORTHEAST & SOUTHEAST EDEN NC QUADRANGLE
DRAWN BY: A. ROBINSON
PROJECT MANAGER: JERRY WYLIE
LAYOUT: FIG 1-1 (2017 USGS MAP)
DATE: 12/14/2017
CONTOUR INTERVAL: 20 FEET 1000 MAP DATE: 2017
GRAPHIC SCALE 0 1000 2000
148 RIVER STREET, SUITE 220 GREENVILLE, SOUTH CAROLINA PHONE 864421-9999 www .synterracorp.com P: Duke Ene Carolinas 19. DAN RIVER 018 CSA U ate OWG DE DAN RIVER USGS TOPO MAPS.dw IN FEET
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DAN RIVERCOMBINEDCYCLE PLANT
FORMERSTEAMSTATION
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FORMER COMBUSTIONTURBINE AREA
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CPA-6S/D/BR
CPA-2S/D/BR
CTA-1S/D/BR
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CPA-4S/D/BR
CPA-7S/D/BR
CPA-1S/D/BR
AB-30S/D/BR
AB-35BR
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CCR-6S/D
MW-10*/D*
CCR-5S
CCR-4S/D
MW-310D*/BR*
BG-1D/DA
BG-5S/D
GWA-10S/D
GWA-20S/DGWA-6S/D/BR
GWA-7S/D
MW-22S/D/BR
CCR-3S/D
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FIGURE 2PROPOSED MONITORING WELL & SOIL BORING LOCATION MAP - SOUTH
DAN RIVER STEAM STATION DUKE ENERGY CAROLINAS, LLC EDEN, NORTH CAROLINADRAWN BY: A. FEIGLPROJECT MANAGER: J. WYLIECHECKED BY: E. KINSEY
DATE: 11/15/2018
148 RIVER STREET, SUITE 220GREENVILLE, SOUTH CAROLINA 29601PHONE 864-421-9999www.synterracorp.com
P:\Duke Energy Progress.1026\00 GIS BASE DATA\Dan River\MapDocs\MISC\DANRIVER_ProposedLocations_South_20181114.mxd
150 0 150 300
GRAPHIC SCALE IN FEET
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ASH BASIN WASTE BOUNDARY
ASH BASIN COMPLIANCE BOUNDARY
ASH STACK WASTE BOUNDARY
CCR LANDFILL BOUNDARY
LANDFILL COMPLIANCE BOUNDARY
DUKE ENERGY CAROLINAS DAN RIVER PLANTSITE BOUNDARY
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TOPOGRAPHIC CONTOURS (10' INTERVAL)
LEGEND
NOTES:
AERIAL PHOTOGRAPHY OBTAINED FROM GOOGLE EARTH PRO ONSEPTEMBER 11, 2017. IMAGE COLLECTED ON FEBRUARY 18, 2017.
DRAWING HAS BEEN SET WITH A PROJECTION OF NORTH CAROLINASTATE PLANE COORDINATE SYSTEM FIPS 3200 (NAD83).
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CWA-3S/D/BR
CWA-4S/D/BR
CWA-5S/D/BR
CWA-6S/D/BR
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GWA-10S/D
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FIGURE 3PROPOSED MONITORING WELL & SOIL BORING LOCATION MAP - WEST
DAN RIVER STEAM STATION DUKE ENERGY CAROLINAS, LLC EDEN, NORTH CAROLINADRAWN BY: A. FEIGLPROJECT MANAGER: J. WYLIECHECKED BY: E. KINSEY
DATE: 11/15/2018
148 RIVER STREET, SUITE 220GREENVILLE, SOUTH CAROLINA 29601PHONE 864-421-9999www.synterracorp.com
P:\Duke Energy Progress.1026\00 GIS BASE DATA\Dan River\MapDocs\MISC\DANRIVER_ProposedLocations_West_20181114.mxd
100 0 100 200
GRAPHIC SCALE IN FEET
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&<MONITORING WELL
&<ABANDONED MONITORING WELL
ASH BASIN WASTE BOUNDARY
ASH BASIN COMPLIANCE BOUNDARY
ASH STACK WASTE BOUNDARY
CCR LANDFILL BOUNDARY
LANDFILL COMPLIANCE BOUNDARY
DUKE ENERGY CAROLINAS DAN RIVER PLANTSITE BOUNDARY
<STREAM
TOPOGRAPHIC CONTOURS (10' INTERVAL)
LEGEND
NOTES:
AERIAL PHOTOGRAPHY OBTAINED FROM GOOGLE EARTH PRO ONSEPTEMBER 11, 2017. IMAGE COLLECTED ON FEBRUARY 18, 2017.
DRAWING HAS BEEN SET WITH A PROJECTION OF NORTH CAROLINASTATE PLANE COORDINATE SYSTEM FIPS 3200 (NAD83).
Additional Source Area Assessment Work Plan November 2018
Dan River Steam Station
TABLES
TABLE 1
SOIL SAMPLE ANALYTICAL METHODS
DAN RIVER STEAM STATION
DUKE ENERGY CAROLINAS LLC, EDEN NC
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INORGANIC COMPOUNDS UNITS METHOD
Aluminum mg/kg EPA 6010D
Antimony mg/kg EPA 6020B
Arsenic mg/kg EPA 6020B
Barium mg/kg EPA 6010D
Beryllium mg/kg EPA 6010D
Boron mg/kg EPA 6010D
Cadmium mg/kg EPA 6020B
Calcium mg/kg EPA 6010D
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 6020B
Magnesium mg/kg EPA 6010D
Manganese mg/kg EPA 6010C
Mercury mg/kg EPA 7471B
Molybdenum mg/kg EPA 6010D
Nickel mg/kg EPA 6010C
Nitrate as Nitrogen mg/kg EPA 9056A
pH SU EPA 9045D
Potassium mg/kg EPA 6010D
Selenium mg/kg EPA 6020B
Sodium mg/kg EPA 6010D
Strontium mg/kg EPA 6010C
Sulfate mg/kg EPA 9056A
Thallium (low level) (SPLP Extract only)mg/kg EPA 6020B
Total Organic Carbon mg/kg EPA 9060
Vanadium mg/kg EPA 6020B
Zinc mg/kg EPA 6010C
Notes:
meq/100g - millequivalents per 100 grams
mg/kg - Milligrams per kilogram
mV - Millivolts
S.U. - Standard Unit
Prepared by: RBI Checked by: SRW/TCP/VTV
3. 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.
2. Soil samples collected from near ground surface (2 to 3ft) and from just above water table (field determined) in each boring will also
be analyzed for leaching potential using SPLP Extraction Method 1312 in conjunction with USEPA Methods 6010/6020
1. Soil samples to be analyzed for Total Inorganics using USEPA Methods 6010/6020 and pH using USEPA Method 9045, as noted above.
TABLE 2
PROPOSED ADDITIONAL SOURCE AREA ASSESSMENT SOIL SAMPLES AND MONITORING WELLS
DAN RIVER STEAM STATION
DUKE ENERGY CAROLINAS LLC, EDEN NC
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Monitoring
Well ID
Estimated Well
Depth
(feet bgs)
Soil Sample ID
(Estimated Depth
Interval in feet bgs)
Comments
----CPA-SB1 (2-3)Unsaturated soil sample ; SPLP
----CPA-SB1 (5-6)Unsaturated soil sample
----CPA-SB1 (11-12)Unsaturated soil sample
----CPA-SB1 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CPA-SB1 (20-21)Saturated soil sample; SPLP
CPA-1S 30 CPA-SB1 (25-27)Soil sample from shallow well screened interval
CPA-1D 50 CPA-SB1 (45-47)Soil sample from deep well screened interval
CPA-1BR 100 CPA-SB1 (95-97)Rock sample from bedrock well screened interval
----CPA-SB2 (2-3)Unsaturated soil sample ; SPLP
----CPA-SB2 (5-6)Unsaturated soil sample
----CPA-SB2 (11-12)Unsaturated soil sample
----CPA-SB2 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CPA-SB2 (20-21)Saturated soil sample; SPLP
CPA-2S 30 CPA-SB2 (25-27)Soil sample from shallow well screened interval
CPA-2D 50 CPA-SB2 (45-47)Soil sample from deep well screened interval
CPA-2BR 100 CPA-SB2 (95-97)Rock sample from bedrock well screened interval
----CPA-SB3 (2-3)Unsaturated soil sample ; SPLP
----CPA-SB3 (5-6)Unsaturated soil sample
----CPA-SB3 (11-12)Unsaturated soil sample
----CPA-SB3 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CPA-SB3 (20-21)Saturated soil sample; SPLP
CPA-3S 30 CPA-SB3 (25-27)Soil sample from shallow well screened interval
CPA-3D 50 CPA-SB3 (45-47)Soil sample from deep well screened interval
CPA-3BR 100 CPA-SB3 (95-97)Rock sample from bedrock well screened interval
----CPA-SB4 (2-3)Unsaturated soil sample ; SPLP
----CPA-SB4 (5-6)Unsaturated soil sample
----CPA-SB4 (11-12)Unsaturated soil sample
----CPA-SB4 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CPA-SB4 (20-21)Saturated soil sample; SPLP
CPA-4S 30 CPA-SB4 (25-27)Soil sample from shallow well screened interval
CPA-4D 50 CPA-SB4 (45-47)Soil sample from deep well screened interval
CPA-4BR 100 CPA-SB4 (95-97)Rock sample from bedrock well screened interval
----CPA-SB5 (2-3)Unsaturated soil sample ; SPLP
----CPA-SB5 (5-6)Unsaturated soil sample
----CPA-SB5 (11-12)Unsaturated soil sample
----CPA-SB5 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CPA-SB5 (20-21)Saturated soil sample; SPLP
CPA-5S 30 CPA-SB5 (25-27)Soil sample from shallow well screened interval
CPA-5D 50 CPA-SB5 (45-47)Soil sample from deep well screened interval
CPA-5BR 100 CPA-SB5 (95-97)Rock sample from bedrock well screened interval
----CPA-SB6 (2-3)Unsaturated soil sample ; SPLP
----CPA-SB6 (5-6)Unsaturated soil sample
----CPA-SB6 (11-12)Unsaturated soil sample
----CPA-SB6 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CPA-SB6 (20-21)Saturated soil sample; SPLP
CPA-6S 30 CPA-SB6 (25-27)Soil sample from shallow well screened interval
CPA-6D 50 CPA-SB6 (45-47)Soil sample from deep well screened interval
CPA-6BR 100 CPA-SB6 (95-97)Rock sample from bedrock well screened interval
----CPA-SB7 (2-3)Unsaturated soil sample ; SPLP
----CPA-SB7 (5-6)Unsaturated soil sample
----CPA-SB7 (11-12)Unsaturated soil sample
----CPA-SB7 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CPA-SB7 (20-21)Saturated soil sample; SPLP
CPA-7S 30 CPA-SB7 (25-27)Soil sample from shallow well screened interval
CPA-7D 50 CPA-SB7 (45-47)Soil sample from deep well screened interval
CPA-7BR 100 CPA-SB7 (95-97)Rock sample from bedrock well screened interval
Former Coal Pile Area
TABLE 2
PROPOSED ADDITIONAL SOURCE AREA ASSESSMENT SOIL SAMPLES AND MONITORING WELLS
DAN RIVER STEAM STATION
DUKE ENERGY CAROLINAS LLC, EDEN NC
P:\Duke Energy Carolinas\19. DAN RIVER\Additional Source Areas\Work Plan\FINAL\Table 2 Dan River Addtl Source Area Asmt Page 2 of 3
Monitoring
Well ID
Estimated Well
Depth
(feet bgs)
Soil Sample ID
(Estimated Depth
Interval in feet bgs)
Comments
----CTA-SB1 (2-3)Unsaturated soil sample ; SPLP
----CTA-SB1 (5-6)Unsaturated soil sample
----CTA-SB1 (11-12)Unsaturated soil sample
----CTA-SB1 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CTA-SB1 (20-21)Saturated soil sample; SPLP
CTA-1S 30 CTA-SB1 (25-27)Soil sample from shallow well screened interval
CTA-1D 50 CTA-SB1 (45-47)Soil sample from deep well screened interval
CTA-1BR 100 CTA-SB1 (95-97)Rock sample from bedrock well screened interval
----CTA-SB2 (2-3)Unsaturated soil sample ; SPLP
----CTA-SB2 (5-6)Unsaturated soil sample
----CTA-SB2 (11-12)Unsaturated soil sample
----CTA-SB2 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CTA-SB2 (20-21)Saturated soil sample; SPLP
CTA-2S 30 CTA-SB2 (25-27)Soil sample from shallow well screened interval
CTA-2D 50 CTA-SB2 (45-47)Soil sample from deep well screened interval
CTA-2BR 100 CTA-SB2 (95-97)Rock sample from bedrock well screened interval
----GWA-SB7 (2-3)Unsaturated soil sample ; SPLP
----GWA-SB7 (5-6)Unsaturated soil sample
----GWA-SB7 (11-12)Unsaturated soil sample
----GWA-SB7 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----GWA-SB7 (20-21)Saturated soil sample; SPLP
----GWA-SB7 (25-27)Soil sample from shallow well screened interval
----GWA-SB7 (45-47)Soil sample from deep well screened interval
GWA-7BR 100 GWA-SB7 (95-97)Rock sample from bedrock well screened interval
----CWA-SB1 (2-3)Unsaturated soil sample ; SPLP
----CWA-SB1 (5-6)Unsaturated soil sample
----CWA-SB1 (11-12)Unsaturated soil sample
----CWA-SB1 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CWA-SB1 (20-21)Saturated soil sample; SPLP
CWA-1S 30 CWA-SB1 (25-27)Soil sample from shallow well screened interval
CWA-1D 50 CWA-SB1 (45-47)Soil sample from deep well screened interval
CWA-1BR 100 CWA-SB1 (95-97)Rock sample from bedrock well screened interval
----CWA-SB2 (2-3)Unsaturated soil sample ; SPLP
----CWA-SB2 (5-6)Unsaturated soil sample
----CWA-SB2 (11-12)Unsaturated soil sample
----CWA-SB2 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CWA-SB2 (20-21)Saturated soil sample; SPLP
CWA-2S 30 CWA-SB2 (25-27)Soil sample from shallow well screened interval
CWA-2D 50 CWA-SB2 (45-47)Soil sample from deep well screened interval
CWA-2BR 100 CWA-SB2 (95-97)Rock sample from bedrock well screened interval
----CWA-SB3 (2-3)Unsaturated soil sample ; SPLP
----CWA-SB3 (5-6)Unsaturated soil sample
----CWA-SB3 (11-12)Unsaturated soil sample
----CWA-SB3 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CWA-SB3 (20-21)Saturated soil sample; SPLP
CWA-3S 30 CWA-SB3 (25-27)Soil sample from shallow well screened interval
CWA-3D 50 CWA-SB3 (45-47)Soil sample from deep well screened interval
CWA-3BR 100 CWA-SB3 (95-97)Rock sample from bedrock well screened interval
----CWA-SB4 (2-3)Unsaturated soil sample ; SPLP
----CWA-SB4 (5-6)Unsaturated soil sample
----CWA-SB4 (11-12)Unsaturated soil sample
----CWA-SB4 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CWA-SB4 (20-21)Saturated soil sample; SPLP
CWA-4S 30 CWA-SB4 (25-27)Soil sample from shallow well screened interval
CWA-4D 50 CWA-SB4 (45-47)Soil sample from deep well screened interval
CWA-4BR 100 CWA-SB4 (95-97)Rock sample from bedrock well screened interval
Combustion Turbine Area
Construction Warehouse Area
TABLE 2
PROPOSED ADDITIONAL SOURCE AREA ASSESSMENT SOIL SAMPLES AND MONITORING WELLS
DAN RIVER STEAM STATION
DUKE ENERGY CAROLINAS LLC, EDEN NC
P:\Duke Energy Carolinas\19. DAN RIVER\Additional Source Areas\Work Plan\FINAL\Table 2 Dan River Addtl Source Area Asmt Page 3 of 3
Monitoring
Well ID
Estimated Well
Depth
(feet bgs)
Soil Sample ID
(Estimated Depth
Interval in feet bgs)
Comments
----CWA-SB5 (2-3)Unsaturated soil sample ; SPLP
----CWA-SB5 (5-6)Unsaturated soil sample
----CWA-SB5 (11-12)Unsaturated soil sample
----CWA-SB5 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CWA-SB5 (20-21)Saturated soil sample; SPLP
CWA-5S 30 CWA-SB5 (25-27)Soil sample from shallow well screened interval
CWA-5D 50 CWA-SB5 (45-47)Soil sample from deep well screened interval
CWA-5BR 100 CWA-SB5 (95-97)Rock sample from bedrock well screened interval
----CWA-SB6 (2-3)Unsaturated soil sample ; SPLP
----CWA-SB6 (5-6)Unsaturated soil sample
----CWA-SB6 (11-12)Unsaturated soil sample
----CWA-SB6 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----CWA-SB6 (20-21)Saturated soil sample; SPLP
CWA-6S 30 CWA-SB6 (25-27)Soil sample from shallow well screened interval
CWA-6D 50 CWA-SB6 (45-47)Soil sample from deep well screened interval
CWA-6BR 100 CWA-SB6 (95-97)Rock sample from bedrock well screened interval
----GWA-SB12 (2-3)Unsaturated soil sample ; SPLP
----GWA-SB12 (5-6)Unsaturated soil sample
----GWA-SB12 (11-12)Unsaturated soil sample
----GWA-SB12 (14-15)Unsaturated soil sample(water table ~15 feet bgs)
----GWA-SB12 (20-21)Saturated soil sample; SPLP
----GWA-SB12 (25-27)Soil sample from shallow well screened interval
----GWA-SB12 (45-47)Soil sample from deep well screened interval
GWA-12BR 100 GWA-SB12 (95-97)Rock sample from bedrock well screened interval
Prepared by: ENK Checked by: JAW
Notes:
bgs - below ground surface
Continuous cores from rotary sonic drilling provide sufficient material for soil sampling and lithologic description.
Estimated well and soil sample depths based on data from the GWA-8 and GWA-7 well clusters.
Number of soil samples shown is approximate. For example, a shallower water table will result in fewer samples, and a deeper water table will result in additional samples.
TABLE 3
GROUNDWATER ANALYTICAL METHODS
DAN RIVER STEAM STATION
DUKE ENERGY CAROLINAS LLC, EDEN NC
P:\Duke Energy Carolinas\19. DAN RIVER\Additional Source Areas\Work Plan\FINAL\Table 3 Dan River Addtl Source Area Asmt Page 1 of 1
PARAMETER RL UNITS METHOD
pH NA SU Field Water Quality Meter
Specific Conductance NA µS/cm Field Water Quality Meter
Temperature NA ºC Field Water Quality Meter
Dissolved Oxygen NA mg/L Field Water Quality Meter
Oxidation Reduction Potential NA mV Field Water Quality Meter
Turbidity NA NTU Field Water Quality Meter
Ferrous Iron NA mg/L Field Test Kit
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 6020A
Barium 0.005 mg/L EPA 200.7 or 6010C
Beryllium 0.001 mg/L EPA 200.8 or 6020A
Boron 0.05 mg/L EPA 200.7 or 6010C
Cadmium 0.001 mg/L EPA 200.8 or 6020A
Chromium 0.001 mg/L EPA 200.8 or 6010C
Cobalt 0.001 mg/L EPA 200.8 or 6020A
Copper 0.001 mg/L EPA 200.8 or 6020B
Iron 0.01 mg/L EPA 200.7 or 6010C
Lead 0.001 mg/L EPA 200.8 or 6020A
Manganese 0.005 mg/L EPA 200.7 or 6010C
Mercury (low level)0.005 ng/L 1631 ONLY
Molybdenum 0.001 mg/L EPA 200.8 or 6020B
Nickel 0.001 mg/L EPA 200.8 or 6020B
Phosphorus 0.005 mg/L EPA 365.1
Selenium 0.001 mg/L EPA 200.8 or 6020A
Strontium 0.005 mg/L EPA 200.7 or 6010C
Thallium (low level)0.0002 mg/L EPA 200.8 or 6020A
Vanadium (low level)0.0003 mg/L EPA 200.8 or 6020A
Zinc 0.005 mg/L EPA 200.7 or 6010C
Radium 226 1 pCi/L EPA 903.1 Modified
Radium 228 1 pCi/L EPA 904.0/SW846 9320 Modified
Total Uranium NA µg/mL Calculated
Alkalinity (as CaCO3)5 mg/L SM 2320B
Bicarbonate 5 mg/L SM 2320
Calcium 0.01 mg/L EPA 200.7
Carbonate 5 mg/L SM 2320
Chloride 0.1 mg/L EPA 300.0 or 9056A
Magnesium 0.005 mg/L EPA 200.7
Methane 0.01 mg/L RSK 175
Nitrate as Nitrogen 0.01 mg-N/L EPA 353.2
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 SM4500S2-D
Total Dissolved Solids 25 mg/L SM 2540C
Total Organic Carbon 0.1 mg/L SM 5310C/EPA9060A
Total Suspended Solids 2.5 mg/L SM 2450D
Prepared by: RBI Checked by: SRW/TCP
Notes:
ºC - Degrees Celsius
µS/cm = micro-Siemens per centimeter
mg/L - Milligrams per liter
mg - N/L - Milligrams nitrogen per liter
mV - Millivolts
NA - Not analyzed
NTU - Nephelometric turbidity unit
pCi/L - picocuries per liter
RL = reporting limit
S.U. - Standard Unit
ug/mL - micrograms per milliliter
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.
INORGANICS
FIELD PARAMETERS
1. Select constituents will be analyzed for total and dissolved concentrations.
ANIONS/CATIONS
RADIONUCLIDES