HomeMy WebLinkAbout20190199 Ver 1_17BP10R112_Anson_FINAL NRTM_October 2018_20190213NATURAL RESOURCES TECHNICAL MEMORANDUM
Replacement of Bridge No. 19 on SR 1710 (Allen Street) over Cedar Creek
Anson County, North Carolina
WBS Element No. 17BP.10.R.112
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THE NORTH CAROLINA DEPARTMENT OF TRANSPORTATION
Division of Highways — Highway Division 10
October 2018
TABLE OF CONTENTS
lAINTRODUCTION ...................................................................................................................1
2.0 METHODOLOGY ..................................................................................................................1
3.0 PROTECTED SPECIES ........................................................................................................1
3.1 Endangered Species Act Protected Species ................................................................................ l
3.2 Bald Eagle and Golden Eagle Protection Act ............................................................................ 2
4.0 WATER RESOURCES AND REGULATORY CONSIDERATIONS ..............................3
4.1 Water Resources ........................................................................................................................... 3
4.2 Clean Water Act Waters of the U.S ............................................................................................ 3
4,3 Construction Moratoria ............................................................................................................... 4
4.4 N.C. River Basin Buffer Rules ..................................................................................................... 4
4,5 Rivers and Harbors Act Section 10 Navigable Waters ............................................................. 4
5.0 REFERENCES ........................................................................................................................5
Appendix A. Figures
Figure 1. Vicinity Map
Figure 2. Project Study Area Map
Figure 3. Jurisdictional Features Map
Appendix B. Qualifications of Contributors
Appendix G Mussel Survey Report
LIST OF TABLES
Table 1. ESA federally protected species listed for Anson County ......................................... l
Table 2. Potential streams in the study area .............................................................................. 3
Table 3. Characteristics of potential jurisdictional streams in the study area ....................... 3
Table 4. Characteristics of potential jurisdictional wetlands in the study area ..................... 4
Natural Resources Technical Memorandum Project No. 17BP.IO.R.112, Anson Countv, N. C.
1.0 INTRODUCTION
The North Carolina Department of Transportation (NCDOT) proposes the replacement of
Bridge No. 19 on SR 1710 (Allen Street) over Cedar Creek in Anson County, NC (Figures
1-2). The following Natural Resources Technical Memorandum (NRTM) has been
prepared to assist in the preparation of a State Minimum Criteria Determination Checklist
(MCDC) in accordance with the State Environmental Policy Act (SEPA).
2.0 METHODOLOGY
This investigation was conducted in accordance with the NCDOT Environmental
Coordination and Permitting's (ECAP) Preparing Natural Resources Technical Reports
Procedure and references the latest ECAP NRTR Template (November 2017). Field work
was conducted on January 16, 2018, September 5, 2018, and September 25, 2018. Potential
jurisdictional areas identified in the study area are expected to be verified by the U.S. Army
Corps of Engineers (USACE) and the North Carolina Division of Water Resources
(NCDWR). It is anticipated that the USACE will cover the potential features associated
with this project under a Preliminary Jurisdictional Determination (PJD). The principal
personnel contributing to the field work and document are provided in Appendix B.
3.0 PROTECTED SPECIES
3.1 Endangered Species Act Protected Species
As of June 27, 2018, the U.S. Fish and Wildlife Service (USFWS) lists three federally
protected species, under the Endangered Species Act (ESA), for Anson County (Table 1).
For each species, a discussion of the presence or absence of habitat is included below along
with the Biological Conclusion rendered based on survey results in the study area.
Table 1. ESA federally protected species listed for Anson County
Scientific Name Common Name Federal Habitat Biological
Status Present Conclusion
Lasinigona decorata Carolina heelsplitter E Yes No Effect
Picoides borealis Red-cockaded woodpecker E Yes No Effect
Helianthus schweinitzii Schweinitz's sunflower E Yes No Effect
E — Endangered
Carolina heelsplitter
USFWS optimal survey window: year-round
Biological Conclusion: No Effect
Suitable habitat for the Carolina heelsplitter exists within the study area. Therefore,
surveys were completed on September 25, 2018 by Three Oaks biologists Tim
Savidge and Logan Williams. Please see the attached survey report (Appendix C)
for survey details.
October 2018
Natural Resources Technical Memorandum Proiect No. 17BP.10.R.112, Anson Countv, N.C.
Red-cockaded woodpecker
USFWS optimal survey window: year-round; November-early March (optimal)
Biological Conclusion: No Effect
Red-cockaded woodpecker (RCW) habitat evaluations were conducted on
September 5, 2018. While there are a few small pockets of marginal foraging
habitat present in study area (open to semi-open pine stands 30-60 years in age),
larger, more cohesive foraging and nesting habitat for RCW (open to semi-open
pine stands > 60 years in age) is not present within the study area. Thinned pine
plantations within the study area contain pines < 30 years in age. A review of the
July 2018 NCNHP database indicates no known RCW occurrences within 1.0 mile
of the study area.
Schweinitz's sunflower
USFWS optimal survey window: late August-October
Biological Conclusion: No Effect
Suitable habitat (e.g., dry, clayey, early successional roadsides and utility rights-of-
way) for Schweinitz's sunflower is present within the study area. Therefore,
surveys for Schweinitz's sunflower were conducted on September 5, 2018; no
plants were found. A review of the July 2018 NCNHP database indicates one
known Schweinitz's sunflower occurrence (Element Occurrence [EO] No. 80)
within 1.0 mile of the study area, approximately 1.0 mile away from the project.
Northern long-eared bat
Since this project is state-funded, the USACE will act as the lead agency for issues related
to the northern long-eared bat (NLEB). Therefore 4(d) does not apply. The USACE has
developed a Standard Local Operating Procedure for Endangered Species (SLOPES) to
address NLEB when they are the lead agency, which NCDOT will follow for this project.
The requirements of the SLOPES for NLEB will be completed prior to Let and will be
submitted to USACE. Survey/assessment data will be provided by Three Oaks; additional
project- and design-related information will be provided by Division 10.
3.2 Bald Eagle and Golden Eagle Protection Act
Habitat for the bald eagle primarily consists of mature forest in proximity to large bodies
of open water for foraging. Large dominant trees are utilized for nesting sites, typically
within 1.0 mile of open water.
A desktop-GIS assessment of the project study area, as well as the area within a 1.0-mile
radius of the project limits, was performed on January 15, 2018, using the most currently-
available orthoimagery. No water bodies large enough or sufficiently open to be
considered potential feeding sources were identified. Since there was no foraging habitat
within the review area, a survey of the proj ect study area and the area within 660 feet of
the project limits was not conducted. Additionally, a review of the July 2018 NCNHP
database revealed no known occurrences of this species within 1.0 mile of the proj ect study
area.
October 2018
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Natural Resources Technical Memorandum Project No. 17BP.IO.R.112, Anson Countv, N. C.
4.0 WATER RESOURCES AND REGULATORY CONSIDERATIONS
4.1 Water Resources
Water resources in the study area are part of the Yadkin — Pee Dee River Basin (U.S.
Geological Survey [USGS] Hydrologic Unit [HUC] 03040104). One potential stream was
identified in the study area (Table 2). The location of this stream is shown on Figure 3.
Table 2. Potential streams in the study area
NCDWR Bank Bankfull
Best Usage Depth
Stream Name Map ID Index Height width
Number Classification �ft) (ft) (in)
Cedar Creek Cedar Creek 13-21 C 15-20 40-60 3-24
There are no Outstanding Resource Waters (ORW), High Quality Waters (HQW), Water
Supply Watersheds (WS-I or WS-II), trout waters, designated anadromous fish waters,
Primary Nursery Areas (PNA), or streams listed on the North Carolina 2016 Final 303(d)
list of impaired waters within or within 1.0 mile of the project study area.
No potential surface waters (i.e., tributaries, ponds, or basins) were identified in the study
area.
4.2 Clean Water Act Waters of the U.S.
One potential jurisdictional stream was identified in the study area (Table 3). The location
of this stream is shown on Figure 3. Cedar Creek is depicted as a named blue-line channel
on USGS 7.5' topographic quadrangle mapping. Therefore, an NCDWR stream
identiiication form was not completed. Due to Cedar Creek's high ecological integrity, a
North Carolina Stream Assessment Method (NCSAM) form was also not completed.
Cedar Creek has been designated as a warm water stream for the purposes of stream
mitigation.
Table 3. Characteristics of potential jurisdictional streams in the study area
Map ID Length Classification Compensatory River Basin
(ft.) Miti ation Re uired Buffer
Cedar Creek 571 Perennial Yes Not Sub�ect
Total 571
One potential jurisdictional wetland was identified within the study area (Table 4). The
location of this wetland is shown on Figure 3. All wetlands in the study area are located
within the Yadkin — Pee Dee River Basin (USGS HUC 03040104). North Carolina
Wetland Assessment Method (NCWAM) forms and USACE wetland determination forms
for the site are included in a separate PJD Package.
October 2018
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Natural Resources Technical Memorandum Project No. 17BP.IO.R.112, Anson Countv, N. C.
Table 4. Characteristics of jurisdictional wetlands in the study area
Map ID NCWAM NCWAM Hydrologic Area (ac.) in
Classification Ratin Classification Stud Area
WA Flood lain Pool Hi h Ri arian 0.03
Total 0.03
4.3 Construction Moratoria
No moratoria are recommended at this time.
4.� N.C. River Basin Buffer Rules
This proj ect is located in the Yadkin — Pee Dee River Basin; therefore, streamside riparian
zones within the study area are not currently protected under provisions of any Riparian
Buffer Rules administered by NCDWR.
4.5 Rivers and Harbors Act Section 10 Navigable Waters
There are no streams within the study area designated by the USACE as a Navigable Water
under Section 10 of the Rivers and Harbors Act.
October 2018
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Natural Resources Technical Memorandum Proiect No. 17BP.10.R.112, Anson Countv, N.C.
5.0 REFERENCES
Environmental Laboratory.1987. Corps of Engineers Wetlands Delineation Manual.
Technical Report Y-87-1, U. S. Army Engineer Waterways Experiment Station.
Vicksburg, Mississippi.
Environmental Laboratory.1992. Clarification and Interpretation of the 1987 Manual,
memorandum from Major General Arthttr E. Williams.
NC Department of Natural Resources (NCDENR) - Division of Water Resources.2018.
Fina12016 North Carolina 303(d) List. https://files.nc.gov/ncdeq/Water%
20Quality/Planning/TMDL/303d/2016/2016 NC_Category_5_303d list.pdf.
North Carolina Natural Heritage Program (NCNHP).2018. Natural Heritage Data Explorer
[Web Application]. NCDNCR, Raleigh, NC. Available at www.ncnhp.org.
(Accessed September 13, 2018).
U.S. Army Corps of Engineers (USACE).2012. Regional Supplement to the Corps of
Engineers Wetland Delineation Manual: Eastern Mountains and Piedmont Region
Version 2.0, ed. J. F. Berkowitz, J. S. Wakeley, R. W. Lichvar, C. V. Noble.
ERDC/EL TR-12-9. Vicksburg, MS: U.S. Army Engineer Research and
Development Center.
United States Department of Agriculture (USDA), Natural Resources Conservation
Service (NRCS).1996. Soil Survey of Union County, North Carolina.
USDA, Natural Resources Conservation Service (NRCS).2017. Field Indicators of Hydric
Soils in the United States, Version 8.1 L.M. Vasilas, G.W. Hurt, and J.F. Berkowitz
(eds.). USDA, NRCS, in cooperation with the National Technical Committee for
Hydric Soils.
United States Fish and Wildlife Service (USFWS).2006. Optimal Survey Windows for
North Carolina's Federally Threatened and Endangered Plant Species.
http://www.fws.gov/nc-es/es/plant_survey.htmL (Accessed September 13, 2018).
USFWS. Threatened and Endangered Species in North Carolina: Anson County. Updated
June 27, 2018. https://www.fws.gov/raleigh/species/cntylist/union.html.
USFWS. Carolina heelsplitter (Lasmigona decorata).2011. Updated November 2012.
https://www.fws.gov/asheville/htmis/listed species/Carolina heelsplitter.html.
USFWS. Red-cockaded woodpecker (Picoides borealis).2017.
https://www.fws.gov/raleigh/species/es_red-cockaded woodpecker.html.
USFWS. Schweinitz's sunflower (Helianthus schweinitzii).2017.
https://www.fws.gov/raleigh/species/es_schweinitz sunflower.html.
October 2018
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Natural Resources Technical Memorandum Proiect No. 17BP.10.R.112, Anson Countv, N.C.
United States Geological Survey (USGS).1983. Ansonville, North Carolina, Topographic
Quadrangle (1:24,000 scale).
Weakley, Alan S. (Working Draft of September 2015). Flora of the Southern and Mid-
Atlantic States. University of North Carolina Herbarium (NCU), North Carolina
Botanical Garden. Chapel Hill, NC. 1,320 pp.
October 2018
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Appendix A
Figures
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Project Vicinity Map
Anson County, North Carolina
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Elevation Dataset, Geographic Names Information System, National
Hydrography Dataset, National Land Cover Database, National
Structures Dataset, and National Transportation Dataset; U.S. Census
Bureau - TIGER/Line; HERE Road Data
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Jurisdictional Features Map
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Jurisdictional Features Map
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Date:
August2018
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Appendix B
Qualifications of Contributors
Principal
Investigator:
Education:
Experience:
Chris Sheats
B.S. Botany, North Carolina State University, 2002
Environmental Scientist, Three Oaks Engineering, 2015-March 2018
Environmental Biologist, The Catena Group, 2005-2015
Staff Scientist, Arcadis G&M, 2003-2005
Responsibilities: Wetland and stream delineations, T&E surveys
Investigator: Nathan Howell
Education: B.S. Fisheries, Wildlife, and Conservation Biology, North Carolina
State University, 2013
M.S. Plant and Microbial Biology, North Carolina State University,
2015
Experience: Environmental Scientist, Three Oaks Engineering, 2015-Present
Responsibilities: Wetland and stream delineations, T&E surveys, and document
preparation
Investigator: Lizzy Stokes-Cawley
Education: B.S. Conservation Biology, St. Lawrence University, 2011
M.E.M. Water Resources, Duke University, 2016
Experience: Environmental Scientist, Three Oaks Engineering, Apri12017-Present
Responsibilities: Document preparation
Investigator:
Education:
Experience
Kate Montieth Sevick
M.S. Natural Resources Sciences, University of Rhode Island, 2004
B.A. Biology, Reed College, 2000
Environmental Scientist, Three Oaks Engineering, Apri12015-Present
Environmental Specialist and Graphics Coordinator, The Catena
Group, 2004-2015
Responsibilities: GIS mapping
Investigator: James Mason
Education: M.S. Biology/Ecology, LTNC-Charlotte 2004
B.A. Biology, Colby College, 2000
Experience: Environmental Senior Scientist, Three Oaks Engineering, Apri12018-
Present
Environmental Program Consultant, NCDOT, 2006-2018
Responsibilities: Document review and preparation
October 2018
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Investigator: Jacob Rosemond
Education: B.A. Environmental Science Western Carolina University 2017
Experience: Environmental Scientist, Three Oaks Engineering, June 2018-Present
Responsibilities: Document review and preparation, T&E surveys
Investigator: Mary Frazer
Education: M.E.M Resource Ecology, Duke University
B.S. Zoology, University of Wisconsin
Experience: Environmental Specialist, Three Oaks Engineering, July 2015-Present
Environmental Program Consultant, NCDOT, 2000-2015
Environmental Specialist, Wisc. Coastal Mgt Program, 1996-2000
Water Regulation Specialist, Wisconsin Dept Natural Resources, 1994-
1996
Biologist, Soil and Environmental Consultants, 1992-1994
Responsibilities: T & E Surveys
October 2018
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Appendix C
Mussel Survey Report
October 2018
10
Freshwater Mussel Survey Report
Replacement of Bridge No. 19 on SR 1710 (Allen Street)
over Cedar Creek
WBS Element # 17BP.l0.Rll2
Anson County, North Carolina
Prepared For:
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NC Department of Transportation
Contact Person:
Larry Thompson
Environmental Supervisor
North Carolina Department of Transportation
Division of Highways — Division 10
lthompson(a�ncdot.gov
716 W Main Street
Albemarle, NC 28001
October 3, 2018
Cedar Creek during the survey efforts
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Contact Person:
Tim Savidge
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919-732-1300
Table of Contents
1.0 Introduction .......................................................................................................................... 1
2.0 Waters Impacted .................................................................................................................. 1
2.1 303(d) Classification ........................................................................................................ 1
2.2 NPDES discharges ........................................................................................................... 1
3.0 Target Federally Protected Species Descriptions ................................................................ 2
3.1 Lasmigona decorata (Carolina Heelsplitter) .................................................................... 2
3.1.1. Species Characteristics .............................................................................................. 2
3.1.2. Distribution and Habitat Requirements .................................................................... 2
3.1.3. Threats to Species ..................................................................................................... 3
4.0 Other Target Species Descriptions ....................................................................................... 4
4.1 Alasmidonta varicosa (Brook Floater) ............................................................................. 4
4.1.1. Species Characteristics .............................................................................................. 4
4.1.2. Distribution and Habitat Requirements .................................................................... 4
4.1.3. Threats to Species ..................................................................................................... 5
4.1.4. Species Listing .......................................................................................................... 6
5.0 Survey Efforts ...................................................................................................................... 6
5.1 Stream Conditions at Time of Survey: Cedar Creek ........................................................ 6
5.2 Methodology .................................................................................................................... 6
5.2.1. Mussel Surveys ......................................................................................................... 6
6.0 Results ..................................................................................................................................7
6.1.1. Mussel Survey Results .............................................................................................. 7
7.0 Discussion/Conclusions ....................................................................................................... 7
8.0 Literature Cited .................................................................................................................... 8
Appendix A. Figures:
Figure 1: Project Vicinity & Survey Reach
Figure 2: NCNHP Element Occurrences
Figure 3: 303(d) Listed Streams and NPDES Discharges
1.0 INTRODUCTION
The North Carolina Department of Transportation (NCDOT) proposes the replacement of bridge
No. 19 over Cedar Creek on SR 1710 (Allen Street) in Anson County (Appendix A, Figure 1).
The project will impact Cedar Creek of the Yadkin — Pee Dee River Basin. The Federally
Endangered Carolina Heelsplitter (Lasmigona decorata) is listed by the U.S. Fish and Wildlife
Service (USFWS) for Anson County. The Brook Floater (Alasmidonta varicosa) is being
considered for listing by the USFWS and is also known to occur in Anson County.
Table 1 lists the nearest element occurrence (EO) for the targeted species in approximate river
miles (RM) from the project crossing. Data are from the NC Natural Heritage Program database
(NCNHP 2018) most recently updated in July 2018 (Figure 2).
Table 1. Element Occurrences
EO EO Distance from First Last EO
S ecies Name ID Waterbod crossin (river miles) Observed Observed Status*
Carolina 21454 Goose/Duck >50 August 1987 March 2017 C
Heelsplitter Creek
21776 Brown Creek 18 July 1987 July 1987 H
Brook Floater
20865 Rocky Creek 30 August 1993 August 1993 C
*: C-NCNHP Current; H —NCNHP Historic
As part of the federal permitting process that requires an evaluation of potential project-related
impacts to federally protected species, Three Oaks Engineering (Three Oaks) was contracted by
NCDOT to conduct aquatic surveys targeting the Carolina Heelsplitter and Brook Floater.
2.0 WATERS IMPACTED
Cedar Creek is located in the Upper Pee Dee River subbasin (HUC# 03040104) of the Pee Dee
River basin. Cedar Creek flows approximately 5.9 river miles (RM) to its confluence with the
Pee Dee River.
2.1 303(d) Classification
Cedar Creek is not listed on the North Carolina Department of Environmental Quality (NCDEQ)
- Division of Water Resources 2016 Fina1303(d) list of impaired streams. There are no 303(d)
listed streams within a five-mile radius of the subject bridge (NCDEQ 2016, Figure 3).
2.2 NPDES discharges
There are no NPDES dischargers upstream of the Cedar Creek survey area. There are no
NPDES discharges within a five-mile radius of the subject bridge (USEPA 2018, Figure 3).
Cedar Creek Freshwater Mussel Report October 2018
Three Oaks Job #18-601 Page 1
3.0 TARGET FEDERALLY PROTECTED SPECIES DESCRIPTIONS
3.1 Lasmigona decorata (Carolina Heelsplitter)
3.1.1. Species Characteristics
The Carolina Heelsplitter (Lasmigona decorata), originally described as Unio decoratus by (Lea
1852), synonymized with the Green Floater (Lasmigona subviridis) (Conrad 1835, Johnson
1970), and later separated as a distinct species (Clarke 1985), is a federally Endangered
freshwater mussel, historically known from several locations within the Catawba and Pee Dee
River systems in North Carolina and the Pee Dee, Savannah, and possibly the Saluda River
systems in South Carolina.
The Carolina Heelsplitter is characterized as having an ovate, trapezoid-shaped, un-sculptured
shell. The outer surface of the shell ranges from greenish brown to dark brown in color, with
younger specimens often having faint greenish brown or black rays. The shell's nacre is often
pearly white to bluish white, grading to orange in the area of the umbo (Keferl 1991). The hinge
teeth are well developed and heavy and the beak sculpture is double looped (Keferl and Shelly
1988). Morphologically, the shell of the Carolina Heelsplitter is very similar to the shell of the
Green Floater (Clarke 1985), with the exception of a much larger size and thickness in the
Carolina Heelsplitter (Keferl and Shelly 1988).
Prior to collections in 1987 and 1990 by Keferl (1991), the Carolina Heelsplitter had not been
collected in the 20th century and was known only from shell characteristics. Because of its
rarity, very little information of this species' biology, life history, and habitat requirements was
known until very recently. Feeding strategy and reproductive cycle of the Carolina Heelsplitter
have not been documented but are likely similar to other native freshwater mussels (USFWS
1996). Nearly all freshwater mussel species have similar reproductive strategies; a larval stage
(glochidium) becomes a temporary obligatory parasite on a fish.
Many mussel species have specific fish hosts, which must be present to complete their life cycle.
Until recently, nothing was known about the host species(s) for the Carolina Heelsplitter
(USFWS 1996, Bogan 2002). Starnes and Hogue (2005) identified the most likely fish host
candidates (15 species) based on fish community surveys in occupied streams throughout the
range of the Carolina Heelsplitter. McMahon and Bogan (2001) and Pennak (1989) should be
consulted for a general overview of freshwater mussel reproductive biology.
3.1.2. Distribution and Habitat Requirements
Currently, the Carolina Heelsplitter has a very fragmented, relict distribution. Until recently, it
was known to be surviving in only six streams and one small river (USFWS 1996); however,
recent discoveries have increased the number of known populations to eleven:
Pee Dee River Basin:
1. Duck Creek/Goose Creek — Mecklenburg/Union counties, NC
2. Flat Creek/Lynches River — Lancaster/Chesterfield/Kershaw counties, SC
Cedar Creek Freshwater Mussel Report October 2018
Three Oaks Job # 18-601 Page 2
Catawba River Basin:
3. Sixmile Creek (Twelvemile Creek Subbasin) — Lancaster County, SC
4. Waxhaw Creek — Union County, NC and Lancaster County, SC
5. Cane Creek/Gills Creek — Lancaster County, SC
6. Fishing Creek Subbasin — Chester County, SC
7. Rocky Creek Subbasin (Bull Run Creek/LTT Bull Run Creek/Beaverdam Creek) —
Chester County, SC
Saluda River Basin:
8. Redbank Creek — Saluda County, SC
9. Halfway Swamp Creek — Greenwood/Saluda County, SC
Savannah River Basin:
10. Little Stevens Creek/Mountain Creek/Sleep Creek/Turkey Creek (Stevens Creek
Subbasin) — Edgefield/McCormick counties, SC
11. Cuffytown Creek (Stevens Creek Subbasin) — Greenwood/McCormick counties, SC
Habitat for this species has been reported from small to large streams and rivers as well as ponds.
These ponds are believed to be millponds on some of the smaller streams within the species'
historic range (Keferl 1991). Keferl and Shelly (1988) and Keferl (1991) reported that most
individuals have been found along well-shaded streambanks with mud, muddy sand, or muddy
gravel substrates. However, numerous individuals in several of the populations have been found
in cobble and gravel dominated substrate, usually in close proximity to bedrock outcroppings
(Savidge, personal observations). The stability of stream banks appears to be very important to
this species (Keferl 1991).
3.1.3. Threats to Species
Habitat degradation, water quality degradation, and changes in stream flow (water quantity) are
the primary identified threats to the Carolina Heelsplitter. Specific types of activities that lead to
these threats have been documented by the USFWS in the Recovery Plan, Federal Register and
other publications (USFWS 1996, 2002, 2007, 2012). These specific threats include the
following:
• Siltation resulting from poorly implemented agricultural, forestry, and developmental
activities;
• Golf course construction;
• Road construction and maintenance;
• Runoff and discharge of municipal, industrial and agricultural pollutants;
• Habitat alterations associated with impoundments, channelization, dredging, and sand
mining operations; and
• Other natural and human-related factors that adversely modify the aquatic environment.
Cedar Creek Freshwater Mussel Report October 2018
Three Oaks Job #18-601 Page 3
These threats, alone and collectively, have contributed to the loss of the Carolina Heelsplitter in
streams previously known to support the species (USFWS 2002). In addition, many of the
remaining populations occur in areas experiencing high rates of urbanization, such as the
Charlotte, North Carolina and Augusta, Georgia greater metropolitan areas. The low numbers of
individuals and the restricted range of each of the surviving populations make them extremely
vulnerable to extirpation from a single catastrophic event or activity (USFWS 1996). The
cumulative effects of several factors, including sedimentation, water quality degradation, habitat
modification (impoundments, channelization, etc.), urbanization and associated alteration of
natural stream discharge, invasive species, and other causes of habitat degradation have
contributed to the decline of this species throughout its range (USFWS 1996).
4.0 OTHER TARGET SPECIES DESCRIPTIONS
4.1 Alasmidonta varicosa (Brook Floater)
4.1.1. Species Characteristics
The Brook Floater, described from the Schuylkill River in Philadelphia County, Pennsylvania,
by Lamarck (1819), is a small mussel reaching a maximum size of around 70 mm. The shells of
the Brook Floater are long rhomboid in outline with a yellowish to greenish smooth
perisotracum, which darkens to brown in adults, with green to black rays possible. The ventral
margin can be straight, but is frequently arcuate, especially in older individuals. The posterior
ridge is broad, somewhat inflated, and round. There is a second faint ridge above and together
the posterior ridges end in a biangulate margin. The posterior slope is flat to slightly concave,
usually with numerous short, low corrugations radiating toward the posterior margin. The
umbos are large, a little inflated, projecting little above the anterior margin, and are directed
anteriorly. Each valve has one small thin, triangular pseudocardinal tooth. Lateral teeth are
vestigial or lacking. The nacre is glossy, bluish white, and grades into pale orange in the umbo
cavity. The foot and mantle color are usually bright orange in color.
4.1.2. Distribution and Habitat Requirements
The Brook Floater ranges from the lower St. Lawrence River Basin in Canada south to the
Atlantic drainages of South Carolina. While still common in some areas, the species has
experienced significant declines throughout its range. In North Carolina, it is found in the
Roanoke, Neuse, Cape Fear, Pee Dee and Catawba River basins (Clarke 1981, Adams et al.
1990, Bogan 2002).
According to Ortmann (1919), the Brook Floater is most abundant in small streams with gravelly
bottoms, and prefers strong currents; thus, it is frequently found in and near riffles. Johnson
(1970) stated that the Brook Floater "lives among rocks on gravel substrates; also on sandy
shoals, especially in rapids and riffles of small rivers and creeks". According to Fuller (1977)
the characteristic habitat of the Brook Floater is the sand floors or gravel riffles of small, upland,
rapidly flowing, oxygen-rich streams in upper portions of river systems. Eugene Kefrel in
Adams et al. (1990) noted that the Linville River of the Catawba River Basin population of this
species occurred near the mouth of the Linville River and Lake James. Most of the naiades
collected or observed were found in a sandy or silt substrate in the cracks between medium to
Cedar Creek Freshwater Mussel Report October 2018
Three Oaks Job # 18-601 Page 4
large boulders along a steep bank in 1 to 3 feet of water. Habitat in the Chatuga River of the
Savannah River Basin is described as bedrock crevices in swift rapids (John Alderman, personal
observations). Williams et al. (1993) lists the Brook Floater as Threatened and it is considered
Endangered in NC.
4.1.3. Threats to Species
The cumulative effects of several factors, including sedimentation, point and non-point
discharge, stream modifications (impoundments, channelization, etc.) have contributed to the
decline of this species throughout its range. All of the populations are generally small in
numbers and restricted to short reaches of isolated streams. The low numbers of individuals and
the restricted range of most of the surviving populations make them extremely vulnerable to
extirpation from a single catastrophic event or activity, much like the endangered Dwarf
Wedgemussel (DWM, Alasmidonta heterodon, Strayer et al. 1996). Catastrophic events may
consist of natural events such as flooding or drought, as well as human influenced events such as
toxic spills associated with highways, railroads, or industrial-municipal complexes.
Siltation resulting from substandard land-use practices associated with activities such as
agriculture, forestry, and land development has been recognized as a major contributing factor to
degradation of mussel populations. Siltation has been documented to be extremely detrimental
to mussel populations by degrading substrate and water quality, increasing potential exposure to
other pollutants, and by direct smothering of mussels (Ellis 1936, Marking and Bills 1979).
Sediment accumulations of less than one inch have been shown to cause high mortality in most
mussel species (Ellis 1936). In Massachusetts, a bridge construction project decimated a
population of the DWM because of accelerated sedimentation and erosion (Smith 1981).
Sewage treatment effluent has been documented to significantly affect the diversity and
abundance of mussel fauna (Goudreau et al. 1988). Goudreau et al. (1988) found that recovery
of mussel populations may not occur for up to two miles below points of chlorinated sewage
effluent.
The impact of impoundments on freshwater mussels has been well documented (USFWS 1992a,
Neves 1993). Construction of dams transforms lotic habitats into lentic habitats, which results in
changes in aquatic community composition. The changes associated with inundation adversely
affect both adult and juvenile mussels as well as fish community structure, which could eliminate
possible fish hosts for upstream transport of glochidia. Muscle Shoals on the Tennessee River in
northern Alabama, once the richest site for naiads (mussels) in the world, is now at the bottom of
Wilson Reservoir and covered with 19 feet of muck (USFWS 1992b). Large portions of all of
the river basins within the Brook Floaters's range have been impounded and this could be a
major factor contributing to the decline of the species (Master 1986).
The introduction of exotic species such as the Asian Clam (Corbicula fluminea) and Zebra
Mussel (Dreissena polymorpha) has also been shown to pose significant threats to native
freshwater mussels. The Asian Clam is now established in most of the major river systems in the
United States (Fuller and Powell 1973) including those streams still supporting populations of
the Brook Floater. Concern has been raised over competitive interactions for space, food and
Cedar Creek Freshwater Mussel Report October 2018
Three Oaks Job # 18-601 Page 5
oxygen with this species and native mussels, possibly at the juvenile stages (Neves and Widlak
1987, Alderman 1995). The Zebra Mussel, native to the drainage basins of the Black, Caspian
and Aral Seas, is an exotic freshwater mussel that was introduced into the Great Lakes in the
1980s and has rapidly expanded its range into the surrounding river basins, including those of the
South Atlantic slope (O'Neill and MacNeill 1991). This species competes for food resources
and space with native mussels and is expected to contribute to the extinction of at least 20
freshwater mussel species if it becomes established throughout most of the eastern United States
(USFWS 1992b). The Zebra Mussel is not currently known from any river supporting Brook
Floater or the Pee Dee River Basin.
4.1.4. Species Listing
This species was petitioned for federal listing under the Endangered Species Act (ESA) of 1973,
as amended within the 2010 Petition to List 404 Aquatic, Riparian and Wetland Species from the
Southeastern United States by the Center for Biological Diversity (CBD 2010) and is listed as
Endangered in North Carolina by NCWRC.
5.0 SURVEY EFFORTS
Three Oaks personnel Tim Savidge (Permit # 18-ES0034) and Logan Williams conducted the
survey on September 25, 2018.
5.1 Stream Conditions at Time of Survey: Cedar Creek
The water was running low and clear at the time of the site visit; however, habitat in the
surveyed portion of Cedar Creek appears to have been considerably altered by the recent
flooding associated with tropical storm Florence. Based on wrack lines, it appears that water
levels in the creek were over the bridge. The channel averaged 12 to 18 feet wide for the
majority of the reach; however, there were several areas where the channel was considerably
wider as a result of bank scour. The widest (approximately 35 feet) being the scour pool just
below the bridge. The highly eroded banks were up to 12 feet high and had totally collapsed in
some areas. With the exception of a bedrock outcrop at the downstream extent of the reach, the
substrate consisted of newly deposited loose sand and gravel up to two feet thick. Instream
habitat consists of riffle and run sequences, with numerous pools created by large trees that have
recently fallen into the stream. Water depth ranged from six inches to three feet deep during the
site visit. The channel was bordered by forest on both sides of the stream.
5.2 Methodology
5.2.1. Mussel Surveys
Mussel surveys were conducted from approximately 1,312 feet (400 meters) downstream of the
respective bridge crossing to approximately 328 feet (100 meters) upstream of the crossing for a
total distance of approximately 1,640 feet (500 meters) (Figure 1). Areas of appropriate habitat
were searched, concentrating on the habitats preferred by the target species. The survey team
spread out across the creek into survey lanes. Visual surveys were conducted using bathyscopes.
Cedar Creek Freshwater Mussel Report October 2018
Three Oaks Job #18-601 Page 6
Tactile methods were employed, particularly in streambanks under submerged rootmats. All
freshwater bivalves were recorded and returned to the substrate. If present, the timed survey
efforts would provide Catch Per Unit Effort (CPUE) data for each mussel species encountered.
Additionally, if encountered, relative abundance for freshwater snails and freshwater clam
species was to be estimated using the following criteria:
➢(VA) Very abundant > 30 per square meter
➢(A) Abundant 16-30 per square meter
➢(C) Common 6-15 per square meter
➢(U) Uncommon 3-5 per square meter
➢(R) Rare 1-2 per square meter
➢(P-) Ancillary adjective "Patchy" indicates an uneven distribution of the species within the
sampled site.
6.0 RESULTS
6.1.1. Mussel Survey Results
No freshwater mussels were found during the 2.0 person-hours of survey time. No other mollusk
species were observed.
7.0 DISCUSSION/CONCLUSIONS
No freshwater mussel species were found during these surveys. Based on these results, it
appears that freshwater mussels, including the targeted Carolina Heelsplitter and Brook Floater,
do not occur within the surveyed portion of Cedar Creek. Based on these survey results, impacts
to these two species are not anticipated to occur as a result of project construction. Strict
adherence to erosion control standards should minimize the potential for any adverse impacts to
occur to the aquatic community of Cedar Creek. Biological conclusions on potential impacts
from the project to the target species are provided below.
The USFWS is the regulating authority for Section 7 Biological Conclusions and as such, it is
recommended that they be consulted regarding their concurrence with the finding of this
document.
Biological Conclusion Carolina Heelsplitter: No Effect
While the following species is not currently federally protected and biological conclusions are
not necessary at the time of the writing of this report, if this species were to receive federal
protection, the appropriate biological conclusion is as follows:
Biological Conclusion Brooke Floater: No Effect
Cedar Creek Freshwater Mussel Report October 2018
Three Oaks Job #18-601 Page 7
8.0 LITERATURE CITED
Adams, W. F., J. M. Alderman, R. G. Biggins, A. G. Gerberich, E. P. Keferl, H. J. Porter, and A.
S. Van Devender. 1990. A report on the conservation status of North Carolina's
freshwater and terrestrial molluscan fauna. N.C. Wildlife Resources Commission,
Raleigh. 246 pp, Appendix A, 37 pp.
Alderman, J. M., Personal Observations.
Alderman, J. M. 1995. Monitoring the Swift Creek Freshwater mussel community. Unpublished
report presented at the UMRCC symposium on the Conservation and Management of
Freshwater Mussels II Initiative for the Future. Rock Island, IL, UMRCC.
Bogan, A.E. 2002. Workbook and key to the freshwater bivalves of North Carolina. North
Carolina Freshwater Mussel Conservation Partnership, Raleigh, NC, 101 pp, 10 color
plates.
Center for Biological Diversity (CBD). 2010. Petition to List 404 Aquatic, Riparian and Wetland
Species from the Southeastern United States as Threatened or Endangered Under the
Endangered Species Act. Apri120, 2010, 1,145 pp. Available online at:
https://www. fws.gov/southeast/pdf/petition/404-aquatic.pdf
Clarke, A.H. 1981. The tribe Alasmidontini (Unionidae: Anodontinae), Part L• Pegias,
Alasmidonta, and Arcidens. Smithsonian Contributions to Zoology 326:1-101.
Clarke, A.H. 1985. The tribe Alasmidontini (Unionidae: Anodontinae), Part II: Lasmigona and
Simpsonaias. Smithsonian Contributions to Zoolo�v, 399: 75.
Conrad, T.A. 1835-1840. Monography of the Family Unionidae, or naiades ofLamarck, (fresh
water bivalve shells) or North America, illustrated by figures drawn on stone from
nature. 108 Chestnut Street, Philadelphia, Pennsylvania: J. Dobson.
Ellis, M. M. 1936. Erosion Silt as a Factor in Aquatic Environments. Ecology 17: 29-42.
Fuller, S.L.H. 1977. Freshwater and terrestrial mollusks. In: John E. Cooper, Sarah S.Robinson,
John B. Fundeburg (eds.) Endangered and Threatened Plants and Animals of North
Carolina. North Carolina State Museum of Natural History, Raleigh.
Fuller, S. L. H. and C. E. Powell. 1973. Range extensions of Corbicula manilensis (Philippi) in
the Atlantic drainage of the United States. Nautilus 87(2): 59.
Goudreau, S. E., R. J. Neves, and R. J. Sheehan. 1988. Effects of Sewage Treatment Effluents
on Mollusks and Fish of the Clinch River in Tazewell County, Virginia. USFWS: 128 pp.
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Johnson, R.I. 1970. The systematics and zoogeography of the Unionidae (Mollusca: Bivalvia) of
the southern Atlantic slope region. Bulletin of the Museum of Comparative Zoology.
140: 263-449.
Keferl, E.P. 1991. "A status survey for the Carolina heelsplitter (Lasmigona decorata). A
freshwater mussel endemic to the Carolinas." Unpublished report to US Fish and Wildlife
Service.
Keferl, E.P. and R.M. Shelly. 1988. The Final Report on a Status Survey of the Carolina
Heelsplitter, (Lasmigona decorata), and the Carolina elktoe, (Alasmidonta robusta),
Unpublished Report to the U.S. Dept of the Interior, Fish and Wildlife Service: 47.
Lamarck, J.B.P.A. 1815-1822. Histoire naturelle des Animaux sans Vertebres. 8 volumes.
Lea, I. 1852. Descriptions of new species of the family Unionidae. Transactions of the American
Philosophical Society, 10 (New Series): 253-294, 218 plates.
Marking, L.L., and T.D. Bills. 1979. Acute effects of silt and sand sedimentation on freshwater
mussels. Pp. 204-211 in J.L. Rasmussen, ed. Proc. of the UMRCC symposium on the
Upper Mississippi River bivalve mollusks. UMRCC. Rock Island IL. 270 pp.
Master, L. 1986. Alasmidonta heterodon: results of a global status survey and proposal to list as
an endangered species. A report submitted to Region 5 of the U.S. Fish and Wildlife
Service. 10 pp. and appendices.
McMahon, R. F. and A. E. Bogan. 2001. Mollusca: Bivalvia. Pp. 331-429. IN: J.H. Thorpe and
A.P. Covich. Ecology and classification of North American freshwater invertebrates.
2"aedition. Academic Press.
Neves, R.J. 1993. A state of the Unionids address. Pp. 1-10 in K.S. Cummings, A.C. Buchanan,
and L.M. Kooch, eds. Proc. of the UMRCC symposium on the Conservation and
Management of Freshwater Mussels. UMRCC. Rock Island IL.189 pp.
Neves, R. J. and J. C. Widlak. 1987. Habitat Ecology of Juvenile Freshwater Mussels (Bivalvia:
Unionidae) in a Headwater Stream in Virginia. American Malacological Bulletin 1(5): 1-
7.
North Carolina Department of Environmental Quality (NCDEQ) - Division of Water Resources.
2016. 2016 North Carolina 303(d) List. https://deq.nc.gov/about/divisions/water-
resources/planning/modeling-assessment/water-quality-data-assessment/integrated-
report-files
North Carolina Natural Heritage Program. 2018. Biotics Database. Division of Land and Water
Stewardship. Department of Natural and Cultural Resources, Raleigh, North Carolina.
July 2018 version.
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O'Neill, C. R., Jr., and D. B. MacNeill. 1991. The zebra mussel (Dreissena polymorpha): an
unwelcome North American invader. Sea Grant, Coastal Resources Fact Sheet. New
York Sea Grant Extension. 12 pp.
Ortmann, A.E. 1919. A monograph of the naiades of Pennsylvania. Part IIL• Systematic account
of the genera and species. Memoirs of the Carnegie Museum 8(1):xvi-384, 21 pls.
Pennak, R. W. 1989. Fresh-water Invertebrates of the United States, Protozoa to Mollusca. New
York, John Wiley & Sons, Inc.
Savidge, T. W., Personal Observations.
Smith, D. 1981. Selected freshwater invertebrates proposed for special concern status in
Massachusetts (Mollusca, Annelida, Arthropoda). MA Dept. of Env. Qual. Engineering,
Div. of Water Pollution Control. 26 pp.
Starnes, W.C. and G.M. Hogue. 2005. Investigations into potential fish hosts for the Carolina
Heelsplitter Mussel (Lasmigona decorata). Final Draft Unpub. Report to U.S. Fish and
Wildlife Service, Asheville, NC. 29 pp. plus appendices.
Strayer, D. L., S. J. Sprague and S. Claypool, 1996. A range-wide assessment of populations of
Alasmidonta heterodon, an endangered freshwater mussel (Bivalvia: Unionidae). J.N.
Am. Benthol. Soc., 15(3):308-317.
U.S. Environmental Protection Agency Office of Water. NPDES facilities by permit type.
NPDESPERMIT WMERC. Accessed September 19, 2018.
https://watersgeo. epa. gov/arcgis/rest/services/OWPROGRAM/NPDESPERMIT_WMER
C/MapServer
U.S. Fish and Wildlife Service (USFWS). 1992a. Special report on the status of freshwater
mussels.
U.S. Fish and Wildlife Service (USFWS). 1992b. Endangered and Threatened species of the
southeast United States (The Red Book). FWS, Ecological Services, Div. of Endangered
Species, Southeast Region. Govt Printing Office, Wash, DC: 1,070.
U.S. Fish and Wildlife Service (USFWS). 1996. Revised Technical/Agency Draft Carolina
Heelsplitter Recovery Plan, Atlanta, GA: 47.
U.S. Fish and Wildlife Service (USFWS). 2002. Endangered and Threatened Wildlife and
Plants; Designation of Critical Habitat for the Carolina Heelsplitter; Final Rule, Dept of
the Interior. Federal Register 67(127):44501-44522.
U.S. Fish and Wildlife Service (USFWS). 2007. Draft Carolina Heelsplitter (Lasmigona
decorata) 5-Year Review: Summary and Evaluation, Asheville, NC, 34 pp.
Cedar Creek Freshwater Mussel Report October 2018
Three Oaks Job #18-601 Page 10
U.S. Fish and Wildlife Service (USFWS). 2012. Carolina Heelsplitter (Lasmigona decorata) 5-
Year Review: Summary and Evaluation, Asheville, NC, 31 pp.
https://ecos.fws.gov/docs/five_year review/doc3992.pdf
Williams, J.D., M.L. Warren Jr., K.S. Cummings, J.L. Harris, and R.J. Neves. 1993.Conservation
status of the freshwater mussels in the United States and Canada. Fisheries 18(9):6-22.
Cedar Creek Freshwater Mussel Report October 2018
Three Oaks Job #18-601 Page 11
APPENDIX A
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Cedar Creek Freshwater Mussel Report October 2018
Three Oaks Job #18-601 Page 12
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