HomeMy WebLinkAbout20181640 Ver 1_Draft PCN Support Document Nov. 29.SD_20181129
USACE Nationwide Permit 12
DWQ Water Quality Certification #4133
PRE-CONSTRUCTION NOTIFICATION & SUPPORTING
DOCUMENTATION FOR PIEDMONT NATURAL GAS LINE 24
REPLACEMENT PROJECT
PITT COUNTY, NORTH CAROLINA
NOVEMBER 26, 2018
Prepared for:
Piedmont Natural Gas
Attn: Mr. Aaron Weldon
4720 Piedmont Row Drive
Charlotte, North Carolina 28210
Prepared by:
DRAMBY ENVIRONMENTAL CONSULTING, INC.
A WOMAN MINORITY BUSINESS ENTERPRISE (WMBE)
8801 Fast Park Drive, Suite 301
Raleigh, North Carolina 27612
(757) 894-1673
www.drambyenv.com
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TABLE OF CONTENTS
EXECUTIVE SUMMARY ....................................................................................................................................... 1
1. PROJECT INFORMATION AND HISTORY .................................................................................................. 1
1.1 PROJECT LOCATION ....................................................................................................................................... 1
1.2 EXISTING SITE CONDITIONS ...................................................................................................................... 1
1.3 PROJECT PURPOSE AND DESCRIPTION .................................................................................................. 2
2. JURISDICTIONAL IMPACTS AND AVOIDANCE AND MINIMIZATION MEASURES .................. 2
3. COMPENSATORY MITIGATION PLAN ....................................................................................................... 4
4. ENVIRONMENTAL INFORMATION ............................................................................................................. 5
4.1 STREAM AND WETLAND DELINEATION ....................................................................................... 5
4.2 THREATENED AND ENDANGERED SPECIES ................................................................................ 8
4.3 CULTURAL AND HISTORIC RESOURCES ..................................................................................... 12
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LIST OF FIGURES
FIGURES ARE LOCATED BEHIND FIGURE TAB, UNLESS OTHERWISE NOTED
LIST OF APPENDICES
APPENDIX A – PRE-CONSTRUCTION NOTIFICATION WITH PROJECT FIGURES
APPENDIX B – THREATENED AND ENDANGERED SPECIES DATABASE
INFORMATION
APPENDIX C – CULTURAL RESOURCES INFORMATION
APPENDIX D – WETLAND DELINEATION REPORT AND REQUEST FOR
PRELIMINARY JURISDICTIONAL DETERMINATION
APPENDIX E – COMPENSATORY MITIGATION AND RIPARIAN BUFFER CREDIT
AVAILABILITY LETTERS
APPENDIX F – HDD INADVERTENT RETURN CONTINGENCY PLAN
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EXECUTIVE SUMMARY
The applicant, Piedmont Natural Gas (PNG), a subsidiary of Duke Energy, is an energy services
company primarily engaged in the distribution of natural gas to more than 1 million residential,
commercial, industrial and power generation customers in portions of North Carolina, South
Carolina, and Tennessee including customers served by municipalities who are wholesale
customers. PNG proposes to install 19 miles of 12-inch natural gas transmission line to replace
an existing smaller transmission main to serve the Pitt County area (Figure 1, Appendix A). The
approximate 650-acre transmission line corridor is located within the Tar-Pamlico and Neuse
River Basins (Project Figures, Appendix A).
Sections 401 and 404 of the Clean Water Act (CWA) require that any discharges of dredge or fill
material into waters of the U.S. (WOUS), including wetlands, require a permit from the State and
the U.S. Army Corps of Engineers (USACE). Based on the project activity and proposed
impacts to jurisdictional resources, the applicant is required to submit a Pre-Construction
Notification for verification of a USACE Nationwide Permit 12 and associated N.C. Department
of Environmental Quality General Water Quality Certification #4133.
The design team has attempted to avoid and minimize impacts to jurisdictional resources to the
maximum extent practicable while still maintaining the project purpose and need. Despite
avoidance and minimization efforts, temporary construction impacts to 12.831 acres of wetlands,
8,783 linear feet of stream channel, 0.159 acres of open water, and 244,610.53 square feet of
riparian buffer are required. Additionally, permanent impacts within the maintained corridor are
required to 21.324 acres of wetlands and 150,822.04 square feet of riparian buffer. Mitigation is
proposed to offset unavoidable riparian buffer and forested wetland permanent conversion
impacts. Converted forested wetlands are proposed to be mitigated at a 1:1 ratio via the N.C.
Division of Mitigation Services State In-Lieu Fund. To mitigate for unavoidable permanent
impacts to 150,822.04 square feet of riparian buffer, the applicant proposes to purchase
354,597.30 square feet from the state in-lieu fee fund via the N.C. Division of Mitigation
Services (DMS) at the required ratios as depicted in the Pre-Construction Notification (PCN) in
Appendix A. A letter from DMS is located in Appendix E.
No federally threatened and/or endangered species or their habitats are known to exist within the
project site. Database searches have been completed and are attached in Appendix B to assist
with inter-agency coordination and review. Additionally, no known eligible historic structures or
archeological features exist within the project site. Appendix C includes the results of a detailed
Phase I Cultural Resources Survey completed by Circa Cultural Resources Management, LLC.
The applicant is seeking authorization under the General Water Quality Certification #4133 from
the NCDWQ and the USACE Nationwide Permit 12. The enclosed PCN and following sections
of this permit support document provide a detailed description of the project and avoidance and
minimization efforts. Also attached for review and approval is the detailed wetland delineation
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https://drambyenv.sharepoint.com/TeamSite/Documents/Greenville PNG PCN Package Documents/For PNG Review 1 1.21/Draft PCN Support Document Nov. 26.SD.doc
report and associated mapping and USACE data sheets completed by Dramby Environmental
Consulting (DEC) and Vanasse Hangen Brustlin (VHB) staff.
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1. PROJECT INFORMATION AND HIST ORY
1.1 PROJECT LOCATION
The project area is comprised of approximately 650 acres of land along a proposed 19-
mile project corridor in Pitt County, North Carolina in close proximity to the southern
extent of the City of Greenville. The corridor begins near Nash Joyner Road to the west
of the City and encircles southern Greenville from west to east before reaching the
corridor terminus at Sunny Side Road. The project area is located in both the Tar-Pamlico
and Neuse River Basins in HUC codes 03020202 and 03020103.
Pitt County is in the Middle and Upper Atlantic Coastal Plain physiographic province.
The project alignment runs through a broad, flat area with slopes generally less than 4
percent. The County spans the interstream divide separating the Tar-Pamlico and Neuse
River Basins, and the interstream divide separating the Middle Neuse and Contentnea sub
basins of the Neuse River Basin.
1.2 EXISTING SITE CO NDITIONS
Most of the study area is comprised of existing agricultural land interspersed with
residential developments, arterial and secondary roadways, utility lines, forested wood
lots, and natural vegetation communities. Natural areas are early successional
communities where previous land management occurred. The western portion of the
study area also intersects the Greenville Southwest Bypass project, construction activities
for which are ongoing.
The project area is located on the Greenville SW and Greenville SE USGS Quadrangles
(USGS 2018). The USGS maps show that more than half of the study area is com posed
of agricultural “open” lands between various tracts of forested cover, residential
development, or road networks. The study area crosses seven named streams and
swamps, identified as Juniper Branch, Fork Swamp, Swift Creek, Horsepen Swamp,
Indian Well Swamp, Gum Swamp, and the Tar River. Several unnamed headwater
streams are also depicted as perennially flowing (as indicated by a solid blue line on the
Quadrangles) tributaries to the above-referenced named systems.
Although USGS maps show contour elevations that range between approximately 10 feet
and 70 feet above mean sea level (msl), the higher end of that range is representative of
the majority of the Line 24 project. Elevation decreases as the study area crosses natural
drainageways, with the lowest elevation found along the expansive Tar River floodplain
intersecting the eastern end of the project corridor.
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1.3 PROJECT PURPOSE AND DESCRIPT ION
The project purpose is to replace an existing smaller diameter natural gas transmission
line (Line 24) with an approximate 19-mile, 12-inch natural gas transmission pipeline
(Line 439) to increase the capacity to meet the natural gas demands of the growing Pitt
County area. The Line 24 Replacement project consists of the installation of 19 miles of
new 12-inch natural gas transmission pipeline (Line 439) to serve the Pitt County area.
The project involves installing two valves settings along the route, tie-in's to Piedmont
Natural Gas existing facilities, and also includes abandoning approximately 4 miles of
existing smaller diameter transmission main (Line 24). A 4-mile portion of Line 24 will
be grouted and capped during construction of Line 439. Line 24 is a smaller diameter, 7-
mile transmission main, which will be fully retired in 2021 or 2022.
Multiple roads are required along the proposed project corridor to provide adequate
linkages to nearby roadways for construction equipment and machinery. The typical
access road corridor will be 50-feet wide and will vary in length depending on proximity
to main roads. Proposed access roads will utilize existing forest roads, farm roads, or
other unpaved pathways to minimize impacts to existing natural areas, croplands and
jurisdictional resources to the greatest extent possible. An upland 16.22-acre site was
chosen at the eastern end of the proposed corridor as a required laydown yard for
construction staging activities to avoid impacts to jurisdictional resources.
Once all appropriate approvals and permits are received, the project will begin by
clearing and grading the land. Then, crews will string, weld, and install the pipe via open
cut installation, laying it on a gravel bed in the trench and then covering it with soil to
natural grades. Pipelines typically are installed at a depth 3 feet or more in accordance
with federal, state and local regulations. The Tar River crossing will be installed via
HDD methods to avoid and minimize environmental impacts. Before operations begin,
the pipe is carefully inspected and tested, as required by U.S. Department of
Transportation regulations. The entire construction and installation process will be
monitored by inspectors and will proceed as quickly and with as little impact as possible
to the environment, landowners, and the community. State-approved erosion and
sediment controls will be installed and monitored during construction to avoid and
minimize erosion and sediment from leaving the site.
2. JURISDICTIONAL IMPAC TS AND AVOIDANCE AND
MINIMIZATION MEASURE S
Piedmont Natural Gas (PNG) carefully considers the following when planning a route:
safety and reliability, environmental and cultural impacts, disruption to existing homes,
businesses and local commuters. PNG is dedicated to finding the best possible route that
causes the least amount of disruption and committed to work with property owners well
in advance of construction to make as many reasonable accommodations as possible.
PNG is committed to protecting significant cultural sites, environmentally sensitive areas
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and endangered species, and works with appropriate federal and state agencies to fully
comply with all applicable laws and regulations. Beyond that, PNG has its own standards
designed to minimize the impact of construction activities on surrounding areas.
The design team has attempted to avoid and minimize impacts to WOUS to the maximum
extent practicable, while still maintaining the project purpose. Despite avoidance and
minimization efforts, the following jurisdictional impacts are required for this project:
Selected Site Design Impacts:
Impact Type Total
Temporary
Total Permanent
Conversion
Wetlands 12.831 acres 21.324 acres
Streams 8,783 linear ft 0 linear feet
Riparian Buffer 244,610.53 sq. ft 150,822.04 sq. ft
Open Water 0.159 acres 0 acres
Various design layouts were considered throughout the planning process in an attempt to
avoid and minimize impacts to jurisdictional features to the maximum extent practicable,
while maintaining an environmentally and economically feasible project. The applicant
has reviewed potential options to offer the least environmentally damaging practicable
alternative that still meets the project’s purpose and need. Initial design for the project
required a 75-feet permanently maintained corridor and resulted in impacts as detailed in
the table below.
Initial Site Design Impacts:
In an effort to reduce permanent impacts to wetlands and riparian buffers, the applicant
re-evaluated site design and reduced the permanently maintained corridor to a width of
50-feet. The corridor width is required to maintain site lines and for maintenance
protocols. In addition to reducing the permanent corridor width, temporary workspace
has been eliminated in forested wetlands to reduce overall wetland impacts. Based on
these site design changes, overall wetland impacts have been reduced by 8.975 acres and
riparian buffer impacts by 80,039.51 square feet.
Three horizontal directional drills (HDDs) have been included to avoid impacts to waters
of the U.S., especially crossing the Tar River. Included in Appendix F is the HDD
inadvertent return contingency plan. Permanent impacts to streams, rivers, or open water
Impact Type Total
Temporary
Total Permanent
Conversion
Wetlands 20.85 acres 22.28 acres
Streams 8,641.35 linear
feet
0 linear feet
Riparian Buffer 295,606.07 sq.
feet
179,886.01 sq. feet
Open Water 0.159 acres 0 acres
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is not anticipated as upon completion of the pipeline crossings, the sites will be returned
to pre-existing conditions and contours. Wetlands impacted, with the exception of
forested wetlands, will be restored to pre-existing conditions and contours. Forested
wetlands will be restored to pre-existing contours but converted to PEM wetlands;
however, will not result in permanent loss of wetlands.
Additional avoidance and minimization measures included choosing a single laydown
yard which does not impact any jurisdictional features. Additionally, proposed access
roads utilize existing forest roads, farm roads, or other unpaved pathways to minimize
new road construction within existing natural areas or croplands where feasible to avoid
and minimize impacts to jurisdictional resources to the greatest extent possible.
Further avoidance and minimization measures will be implemented during construction.
PNG’s contractor will install all soil erosion and sediment control measures at the
commencement of the project and provide maintenance and assure effectiveness
throughout the duration of the project. Care will be taken to minimize downstream
siltation. Raw banks will be seeded and mulched to prevent erosion and all spoils
including organic soils, vegetation and debris will be removed from the site and properly
disposed of in such a manner as to not erode into any body of water or wetland. Silt
fencing will be placed where necessary to prevent sediment from leaving the work area.
Wetland areas will have silt fencing and one layer of straw log installed no closer than 50
feet from point of wetland delineation. Topsoil stockpiles will be located to avoid erosion
of said stockpile onto offsite areas. All environmental measures shall be per PNG design
and construction standards.
This project is not expected to impact public water supply, any shellfish harvesting areas,
spawning grounds, waterfowl habitat; nor jeopardizes threatened or endangered species;
nor disrupt the movement of aquatic life. Therefore, this activity should not cause or
contribute to significant degradation of WOUS; adversely or substantially affect human
health or welfare; life stages of organisms dependent upon the aquatic ecosystem;
ecosystem diversity, productivity, or stability; or significantly degrade recreational,
aesthetic, or economic values.
3. COMPENSATORY MITIGAT ION PLAN
To offset unavoidable permanent conversion impacts to 21.324 -acres of PFO wetlands,
the applicant proposes to purchase credits from the state in-lieu fee mitigation fund at a
1:1 ratio. To offset unavoidable permanent impacts to 150,822.04 square feet of riparian
buffer, the applicant proposes to purchase 354,597.30 square feet from the state in-lieu
fee fund at the required ratios as depicted in the PCN in Appendix A. A letter from the
N.C. Division of Mitigation Services is attached in Appendix E.
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4. ENVIRONMENTAL I NFORMATION
4.1 STREAM AND WETLAND DELINEATION
A detailed wetland and stream investigation were conducted within the project study
area. The delineation report is located in Appendix D. The onsite delineation of potential
wetlands and other WOUS determined that non-tidal freshwater wetlands, perennial
streams and waterbodies (including the Tar River), intermittent streams, open water
features, and modified streams are present within the study area.
Non-tidal Freshwater Wetlands
Palustrine Forested (PFO) Wetlands
PFO wetlands were the most abundant type of aquatic resource encountered
within the Line 24 Project study area. PFO wetlands types were generally
associated with three types of natural communities: 1) pine-dominated flatwoods;
2) mixed hardwood floodplains; and, 3) black willow/cypress swamps.
Pine-dominated flatwoods with PFO wetlands were usually found on broad,
temporarily-flooded interfluves with little to no topographic relief. Vegetation
was typically characterized by trees such as loblolly pine (Pinus taeda), sweetgum
(Liquidambar styraciflua), and red maple (Acer rubrum). Understory species
consisted of sweet pepperbush (Clethra alnifolia), coastal doghobble (Leucothoe
axillaris), sweet bay (Magnolia virginiana), giant cane (Arundinaria gigantea),
black highbush blueberry (Vaccinium fuscatum), and roundleaf greenbrier (Smilax
rotundifolia).
At times, floodplain wetland systems had overstory tree species similar to wet
flatwoods, but with a higher abundance of red maple. Other hydrophytic trees
commonly observed in floodplains included black gum (Nyssa sylvatica), swamp
chestnut oak (Quercus michauxii), green ash (Fraxinus pennsylvanica), and
willow oak (Quercus phellos). Understory species included ironwood (Carpinus
caroliniana), sweet bay, lizard’s tail (Saururus cernuus), and smallspike false
nettle (Boehmeria cylindrica). Occasionally, floodplain systems encompassed
broadly sloping transition zones before reaching lower-elevation riparian wetlands
adjacent to perennial stream systems.
Several cypress swamp wetlands were also found in the Tar River floodplain in
the eastern portion of the project area. Conditions were very wet with deep
surface water inundation extending to the edges of the swamp. Based on
observations of stain lines 6 to 8 feet high along the bases of trees, overbank
flooding of the Tar River provides a substantial volume of water on a regular
basis to these floodplain wetlands. Dominant tree species include bald cypress
(Taxodium distichum) and black willow (Salix nigra), overtopping a variety of
sedges (Carex spp.) mixed with other herbaceous hydrophytes mentioned above.
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Palustrine Scrub-Shrub (PSS) Wetlands
PSS wetlands in the study area were occasionally observed in recently cleared
forest communities (e.g., cutovers) from 5 to 15 years in age, or as fringe
communities in larger wetland complexes. Community composition was
representative of that found in pine-dominated flatwoods, suggesting the eventual
regeneration and succession back to a forested condition. Dense, low-diversity
mixtures of loblolly pine, sweetgum, sweet bay, woolgrass (Scirpus cyperinus),
and common rush (Juncus effusus) were prevalent in cutover PSS wetlands. In
comparison, PSS wetland fringe communities had a higher diversity of
hydrophytic species with additions such as elderberry (Sambucus nigra), wingleaf
primrose-willow (Ludwigia decurrens), woolgrass, marsh seedbox (Ludwigia
palustris), and several smartweed species (Persicaria spp.)
Palustrine Emergent (PEM) Wetlands
PEM wetlands were typically found within land use types where vegetation had
been recently modified or clear-cut. For instance, several large PEM wetlands
were in expansive “cutover” sites dominated by herbaceous species, with some
vegetation regeneration (but usually less than 3 feet in height). Water was often
found pooling in micro depressions associated with minor elevation changes.
Examples of plant species observed in these recently cleared wetlands include
common rush, woolgrass, Maryland meadowbeauty (Rhexia mariana), sweet bay,
jewelweed (Impatiens capensis), arrowleaf tearthumb (Persicaria saggitata), cane
(Arundinaria tecta), and roundleaf greenbrier.
Other emergent wetlands were found as part of maintained yards or newly fallow
fields with little to no woody vegetation. Hydrology was present either from
groundwater discharge zones near the soil surface (via endosaturation), or from
ponded water collecting after rain events on restrictive soils, creating episaturated
conditions. Dominant hydrophytes observed to be present included rice cutgrass
(Leersia oryzoides), common rush, tall yelloweyed grass (Xyris platylepis), and
various beaksedges (Rhynchospora spp.). These areas are continually maintained
either via mowing or agricultural practices and connect to larger wetland
complexes.
Non-tidal Streams and Waterbodies
Palustrine Unconsolidated Bottom (PUB) Waterbodies
PUB wetlands were less abundant than other aquatic resources found within the
study area. These features were observed to be entirely unvegetated and had
substrate conditions that met the Cowardin et al. (1979) parameters applied to
open waterbodies under the PUB designation.
Riverine Perennial (R2 and R3) Stream Channels
Riverine upper perennial (R3) stream systems were usually found in association
with drainageways in which USGS maps show named stream or swamp systems.
As shown on the figure in Appendix A, these include Horsepen Swamp and Swift
Creek (Figure 4-5 to Figure 4-7), Fork Swamp (Figure 4-11), Indian Well Swamp
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(Figure 4-14), and Juniper Branch (Figure 4-16). The Tar River (Figure 4-22) is
classified as a riverine lower perennial (R2) system and is the only waterbody in
the project area listed as a navigable waterbody.
Most perennial streams onsite range from 5 to 15 feet in width and are found
within historically channelized systems with near-vertical banks. Stream bed
conditions in the thalweg are often dynamic (e.g., variable sediment deposition,
with increasingly embedded substrates) because of high volume flow events and
stream bank erosion. Nevertheless, stream flow was observed throughout summer
site visits in 2017 and 2018.
Riverine Intermittent (R4) Stream Channels
Riverine intermittent streams identified onsite were mostly limited to headwater
drainages between milepost 15 and milepost 19 (Figure 4-18 to Figure 4-21,
Appendix A of Wetland Delineation Report), where the seasonal water table and
base flow evidently drop below the stream bed during drier periods of the year.
However, instream conditions were reflective of persistent stream flow occurring
during spring-season increases in rainfall/water table levels. Similar to the
perennial streams within the study area, intermittent streams were observed with a
clearly defined OHWM reflective of physical characteristics associated with
regularly flowing water (e.g., bed and bank, sediment sorting, etc.). Intermittent
streams were assessed using the Identification Methods for the Origins of
Intermittent and Perennial Streams from the North Carolina Division of Water
Quality (NCDWQ). Scoresheets are provided in Appendix C of the Wetland
Delineation Report.
Modified Streams
Due to the active agricultural land use characteristic of the land within the
proposed corridor, modified stream features were frequently identified in ditches
that had connectivity to larger aquatic/wetland systems. The cumulative size of all
modified stream features across the study was approximately 13,224 linear feet.
Each modified stream identified was generally observed to have evidence of
conveyance of surface water between palustrine and/or riverine systems, and an
ordinary high water mark (OHWM). Modified streams were assessed using the
Identification Methods for the Origins of Intermittent and Perennial Streams from
the North Carolina Division of Water Quality (NCDWQ). Scoresheets for each
modified stream are provided in Appendix C of the Wetland Delineation Report.
Upland Communities
Upland community types identified within the study area predominantly consisted
of existing agricultural fields currently used for soybean, peanut, and corn
production. Residential areas scattered between agricultural land uses often had
maintained lawns or were bordered by upland forest communities buffering the
edges of wetlands. Occasional upland islands were located within wetlands where
high points have persisted over time, supporting dominant upland species such as
white oak (Quercus alba), black cherry (Prunus serotina), winged sumac (Rhus
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copallinum), and tulip tree (Liriodendron tulipifera). In recently cut forests,
upland conditions were indicated by a prevalence of dense winged sumac and
tulip tree growth in the shrub stratum, often densely intertwined with sawtooth
blackberry (Rubus argutus). In most cases, upland soil conditions were reflective
of aerobic substrate conditions in the upper 12 inches of the soil profile. With soil
colors typically in the brown chroma range near the soil surface and a lack of soil
saturation (and other wetland hydrology indicators) during normal precipitation
conditions.
DEC and PNG are requesting a Preliminary Jurisdictional Determination (PJD) of the
delineation as part of the permit application review. A detailed wetland delineation report
with USACE wetland determination data forms are provided in Appendix D.
4.2 THREATENED AND ENDANGERED SPECIES
The U. S. Fish and Wildlife Service Information, Planning and Conservation System
(IPaC System) and North Carolina Natural Hertiage Program (NHP) Data Explorer was
used to identify potential threatened and endangered species as well as critical habitats
that may occur in and around the proposed project area. The results of the database
search are included in Appendix B and a summary of the results is provided below.
Further coordination with resource agencies will be conducted during permit review to
determine if any surveys will be required.
Based on IPaC search, the following 3 species are listed as federally threatened or
endangered within or adjacent to the project study area:
• West Indian Manatee (Trichechus manatus): The West Indiant Manatee is listed as
a federally threatened species under the Endangered Species Act (ESA). Based on
the habitat requirements, this project is not likely to impact this species. Habitat
requirements are described by the USFWS as:
“Manatees live in marine, brackish, and freshwater systems in coastal and riverine
areas throughout their range. Preferred habitats include areas near the shore
featuring underwater vegetation like seagrass and eelgrass. They feed along grass
bed margins with access to deep water channels, where they flee when threatened.
Florida manatees can be found throughout Florida for most of the year. However,
they cannot tolerate temperatures below 68 degrees Fahrenheit for extended periods
of time, and during the winter months these cold temperatures keep the population
concentrated in peninsular Florida. Many manatees rely on the warm water from
natural springs and power plant outfalls.
During the summer manatees expand their range, and on rare occasions are seen as
far north as Massachusetts on the Atlantic coast and as far west as Texas on the
Gulf coast. Manatees may travel hundreds of miles during a year’s time, preferring
to travel along channels and shorelines.”
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• Red-cockaded Woodpecker (Picoides borealis): The Red-cockaded Woodpecker is
listed as a federally endangered species under the ESA. There are four historic Red-
cockaded Woodpecker (RCW) populations ranging from approximately 7 to 13
miles away from the project area. Historic populations are defined as ones where no
observation has been made for 25 years or greater. The RCW’s status for Pitt
County is Historic, so surveys will not likely be required for this species. The
habitat requirements are described by the USFWS as:
“The red-cockaded woodpecker makes its home in mature pine forests. Longleaf
pines (Pinus palustris) are most commonly preferred, but other species of southern
pine are also acceptable. While other woodpeckers bore out cavities in dead trees
where the wood is rotten and soft, the red-cockaded woodpecker is the only one
which excavates cavities exclusively in living pine trees. Cavities are excavated in
mature pines, generally over 80 years old. The older pines favored by the red-
cockaded woodpecker often suffer from a fungus called red heart disease which
attacks the center of the trunk, causing the inner wood, the heartwood, to become
soft. Cavity excavation takes one to six years.
The aggregate of cavity trees is called a cluster and may include 1 to 20 or more
cavity trees on 3 to 60 acres. The average cluster is about 10 acres. Cavity trees that
are being actively used have numerous, small resin wells which exude sap. The
birds keep the sap flowing apparently as a cavity defense mechanism against rat
snakes and possibly other predators. The typical territory for a group r anges from
about 125 to 200 acres, but observers have reported territories running from a low
of around 60 acres, to an upper extreme of more than 600 acres. The size of a
particular territory is related to both habitat suitability and population density.”
• Dwarf Wedgemussel (Alasmidonta heterodon): The Dwarf Wedgemussel is listed
as a federally endangered species under the ESA. Habitat requirements are
described by the USFWS as:
“The dwarf wedgemussel appears to be a generalist in terms of its preference for
stream size, substrate and flow conditions – it inhabits small streams less than five
meters wide to large rivers more than 100 meters wide; it is found in a variety of
substrate types including clay, sand, gravel and pebble, and sometimes in silt
depositional areas near banks; and it usually inhabits hydrologically stable areas,
including very shallow water along streambanks and under root mats, but it has also
been found at depths of 25 feet in the Connecticut River. Dwarf wedgemussels are
often patchily distributed in rivers.
Historically, the dwarf wedgemussel was found from the Petitcodiac River in New
Brunswick, Canada to the Neuse River in North Carolina, and was found in 15
major Atlantic slope river systems. It is now extinct in Canada, extirpated in the
Neuse River, and present in low densities through-out much of its former range. It
is known from 54 locations in 15 major watersheds, with the largest populations in
the Connecticut River watershed. North Carolina supports the greatest number of
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known sites: Neuse River Basin: Orange County, Wake County, Johnston County,
Wilson County, and Nash County; Tar River Basin: Person County, Granville
County, Vance County, Franklin County, Warren County, Halifax County, and
Nash County. Unfortunately, most of these populations are very small and
isolated.”
The NHP Data explorer (state listed species) was used to further examine potential
protected species. The nearest occurrence of listed species in the NHP Data Explorer
more than 1 mile away from the project area include:
• West Indian Manatee (see above for habitat description).
• Roanoke Slabshell (Elliptio roanokensis): The Roanoke Slabshell is listed as a state
threatened species. Habitat requirements are described by the North Carolina
Wildlife Resources Commission (NCWRC) as:
“In the Tar River, the Roanoke slabshell is usually found associated with the deeper
channels near shore in relatively fast flowing water. The substrate consists of coarse
to medium sized sands and small gravel. The species is also associated with coarser
substrates, such as a mix of gravel and cobble seen in the Cape Fear River in
Harnett County.”
• Yellow Lance (Elliptio lanceolata): The Yellow Lance is a state threatened species.
Habitat requirements are described by the USFWS as:
“The yellow lance is a sand-loving species often found buried deep in clean, coarse
to medium sand, although it can sometimes be found in gravel substrates. Yellow
lances often are moved with shifting sand and eventually settle in sand at the
downstream end of stable sand and gravel bars. This species depends on clean,
moderate flowing water with high dissolved oxygen. This species is found in
medium-sized rivers to smaller streams.”
• Tidewater Mucket (Leptodea ochracea): The Tidewater Mucket is a state
threatened species. Habitat requirements are described by the NCWRC as:
“The tidewater mucket appears to be somewhat of a generalist in that it has been
documented from lakes, ponds, canals, streams, and rivers. It is most often found in
sand/silt substrates; in Lake Waccamaw, the highest density of this species was
found in the "northwest shallow sand subregion" (Porter 1985).”
Species listed in the vicinity of project area (~0.25 miles east of project area) include:
• Star-nosed Mole (Condylura cristata): The Star-nosed Mole is a special concern
species in North Carolina. Habitat requirements are described by North Carolina
Parks as:
“Almost strictly in wetland habitats; swamps, bottomlands, bogs, marshes, wet
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thickets, moist meadows, etc., are favored habitats. They can also be found along
streams and springs in hilly topography, especially in the mountains.”
• The Bald Eagle (Haliaeetus leucocephalus) is protected under the Bald and Golden
Eagle Protection Act (BGPA) and may occur within or adjacent to the study area.
Summary of Recommendations for Federal and State Species
Species Status Habitat Conclusion
West Indian Manatee
(Trichechus
manatu)s
FT, ST
Manatees live in marine, brackish, and
freshwater systems in coastal and riverine
areas throughout their range. Preferred
habitats include areas near the shore
featuring underwater vegetation like
seagrass and eelgrass
No suitable habitat
Red-cockaded
Woodpecker (RBW)
(Picoides borealis)
FE
The red-cockaded woodpecker makes its
home in mature pine forests. Longleaf
pines (Pinus palustris) are most
commonly preferred, but other species of
southern pine are also acceptable. While
other woodpeckers bore out cavities in
dead trees where the wood is rotten and
soft, the red-cockaded woodpecker is the
only one which excavates cavities
exclusively in living pine trees
Historic Status in Pitt
County
Dwarf Wedgemussel
(Alasmidonta
heterodon)
FE
The dwarf wedgemussel appears to be a
generalist in terms of its preference for
stream size, substrate and flow conditions
– it inhabits small streams less than five
meters wide to large rivers more than 100
meters wide; it is found in a variety of
substrate types including clay, sand,
gravel and pebble, and sometimes in silt
depositional areas near banks; and it
usually inhabits hydrologically stable
areas.
Not present within Pitt
County
Roanoke Slabshell
(Elliptio
roanokensis)
ST
In the Tar River, the Roanoke slabshell is
usually found associated with the deeper
channels near shore in relatively fast
flowing water. The substrate consists of
coarse to medium sized sands and small
gravel.
Suitable habitat present-
nearest occurrence is
greater than one mile
from project area. Not
likely to adversely affect.
Yellow Lance
(Elliptio lanceolata) ST
The yellow lance is a sand-loving species
often found buried deep in clean, coarse
to medium sand, although it can
sometimes be found in gravel substrates.
Suitable habitat present-
nearest occurrence is
greater than one mile
from project area. Not
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Species Status Habitat Conclusion
This species is found in medium-sized
rivers to smaller streams.
likely to adversely affect.
Tidewater Mucket
(Leptodea ochracea) ST
The tidewater mucket appears to be
somewhat of a generalist in that it has
been documented from lakes, ponds,
canals, streams, and rivers. It is most
often found in sand/silt substrates.
Suitable habitat present-
nearest occurrence is
greater than one mile
from project area. Not
likely to adversely affect.
Star-nosed Mole
(Condylura cristata) SSC
Almost strictly in wetland habitats;
swamps, bottomlands, bogs, marshes, wet
thickets, moist meadows, etc., are favored
habitats. They can also be found along
streams and springs in hilly topography,
especially in the mountains
Not likely to adversely
affect.
Bald Eagle
(Haliaeetus
leucocephalus)
FP
The bald eagle prefers habitat near lakes,
large rivers, and shorelines of sounds and
bays. The bird requires tall, isolated trees
for perching and nesting.
Potential to occur;
During nesting season, a
buffer of at least 660ft
around any nests will be
maintained.
FE- Federally Endangered, FT- Federally Threatened, FP- Federally Protected, SE- State
Endangered, ST- State Threatened, SSC- State Species of Concern
4.3 CULTURAL AND HISTORIC RESOURCES
Historic maps and records housed at the Library of Congress, city direct ories, census
data, slave records, North Carolina site forms and reports and the County were reviewed
to determine if cultural and historic resources were located in the project area. The
background archives review indicated that there were not any previously identified
resources in the project area. A phase I cultural resource survey was recommended
following coordination with the North Carolina State Historic Preservation Office
(SHPO) (see Appendix C for letter). A Phase I Cultural Resources Survey was conducted
by Circa Cultural Resources Management, LLC (Circa) in the project area to determine if
cultural resources would be impacted by the project. The results of the Phase I Cultural
Survey (draft report) are provided in Appendix C and a summary of conclusions are
below. These findings are awaiting site numbers so the report can be finalized and
submitted for concurrence that no further work is required.
Architectural Resources
No architectural resources were identified within the project alignment.
Archaeological Resources
Thirty-five isolated finds were identified within the project area. By definition, an
isolated find is not eligible for inclusion in the National Register of Historic Places, and
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Circa~ recommends that no further archaeological testing within these areas are
warranted.
The Phase I survey identified 11 archaeological sites within the project alignment.
• Site PGN3
This domestic artifact scatter dates from the late-19th with occupation continuing
into the 1940s. The surface scatter and shovel testing indicate a light density of
artifacts recovered from a relic plowzone near a road. Circa~ recommends that the
site as not eligible for listing on the National Register of Historic Places under
Criterion D. Accordingly, no further archaeological investigations appear warranted
at the site, and it is recommended that the site be given clearance for any potential
development projects.
• Site PGN5
This domestic artifact scatter dates from the circa post 1920 with occupation
continuing into the 1940s. The surface scatter and shovel testing indicate a light
density of artifacts recovered from a plowzone. Circa~ recommends that the site
located as not eligible for listing on the National Register of Historic Places under
Criterion D. Accordingly, no further archaeological investigations appear warranted
at the site, and it is recommended that the site be given clearance for any potential
development projects.
• Site PGN6
This domestic artifact scatter dates from the circa post 1930 with occupation
continuing into the 1940s. The surface scatter and shovel testing indicate a light
density of artifacts recovered from a plowzone. Circa~ recommends that the site
located as not eligible for listing on the National Register of Historic Places under
Criterion D. Accordingly, no further archaeological investigations appear warranted
at the site, and it is recommended that the site be given clearance for any potential
development projects.
• Site PGN7
This domestic artifact scatter dates from the circa post 1900 with occupation
continuing into the 1940s. The surface scatter and shovel testing indicate a light
density of artifacts recovered from a plowzone. Circa~ recommends that the site
located as not eligible for listing on the National Register of Historic Places under
Criterion D. Accordingly, no further archaeological investigations appear warranted
at the site, and it is recommended that the site be given clearance for any potential
development projects.
• Site PGN8
This domestic artifact scatter dates from the circa post 1775 with occupation
continuing into the 1820s. The surface scatter and shovel testing indicate a light
density of artifacts recovered from a plowzone. Circa~ recommends that the site
located as not eligible for listing on the National Register of Historic Places under
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Criterion D. Accordingly, no further archaeological investigations appear warranted
at the site, and it is recommended that the portion of the site within the project area
be given clearance for any potential development projects.
• Site PGN10
This domestic artifact scatter dates from the circa post 1900 with occupation
continuing into the 1940s. The surface scatter and shovel testing indicate a
moderate density of artifacts recovered from a plowzone. Circa~ recommends that
the site located as not eligible for listing on the National Register of Historic Places
under Criterion D. Accordingly, no further archaeological investigations appear
warranted at the site, and it is recommended that the site be given clearance for any
potential development projects.
• Site PGN11
This domestic artifact scatter dates from the circa post 1900 with occupation
continuing into the 1940s. The surface scatter and shovel testing indicate a
moderate density of artifacts recovered from a plowzone. Circa~ recommends that
the site located as not eligible for listing on the National Register of Historic Places
under Criterion D. Accordingly, no further archaeological investigations appear
warranted at the site, and it is recommended that the site be given clearance for any
potential development projects.
• Site PGN13
This domestic artifact scatter dates from the circa post 1950 with occupation
continuing into the 1970s. The surface scatter and shovel testing indicate a light
density of artifacts recovered from a plowzone. Circa~ recommends that the site
located as not eligible for listing on the National Register of Historic Places under
Criterion D. Accordingly, no further archaeological investigations appear warranted
at the site, and it is recommended that the site be given clearance for any potential
development projects.
• Site PGN14
This domestic artifact scatter dates from the circa post 1900 with occupation
continuing into the 1950s. The surface scatter and shovel testing indicate a
moderate density of artifacts recovered from a plowzone. Circa~ recommends that
the site located as not eligible for listing on the National Register of Historic Places
under Criterion D. Accordingly, no further archaeological investigations appear
warranted at the site, and it is recommended that the site be given clearance for any
potential development projects.
• Site PGN32
This domestic artifact scatter dates from the circa post 1950 with occupation
continuing into the 1970s. The surface scatter and shovel testing indicate a light
density of artifacts recovered from a plowzone. Circa~ recommends that the site
located as not eligible for listing on the National Register of Historic Places under
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Criterion D. Accordingly, no further archaeological investigations appear warranted
at the site, and it is recommended that the site be given clearance for any potential
development projects.
• Site PGN44
This domestic artifact scatter dates from the circa post 1900 with occupation
continuing into the 1960s. The surface scatter and shovel testing indicate a light
density of artifacts recovered from a plowzone. Circa~ recommends that the site
located as not eligible for listing on the National Register of Historic Places under
Criterion D. Accordingly, no further archaeological investigations appear warranted
at the site, and it is recommended that the site be given clearance for any potential
development projects.
• Site PGN47
This site dates from the circa post 1920 with occupation continuing into the 1960s.
The surface scatter and shovel testing indicate a light density of artifacts recovered
from a plowzone. Circa~ recommends that the site located as not eligible for listing
on the National Register of Historic Places under Criterion D. Accordingly, no
further archaeological investigations appear warranted at the site, and it is
recommended that the site be given clearance for any potential development
projects.
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Summary of identified resources and recommendations
Site Type National Register
Eligibility Recommendation
IF-PGN1 Isolated find, c. post 1950 No No further work
IF-PGN2 Isolated find, c. post 1930 No No further work
IF-PGN4 Isolated find, c. post 1950 No No further work
IF-PGN9 Isolated find, 20th century No No further work
IF-
PGN12 Isolated find, c. 1940 No No further work
IF-
PGN15 Isolated find, 20th century No No further work
IF-
PGN16 Isolated find, c. 1870 No No further work
IF-
PGN17 Isolated find, 20th century No No further work
IF-
PGN18 Isolated find, 1970 No No further work
IF-
PGN19 Isolated find, 20th century No No further work
IF-
PGN20 Isolated find, c. 1970 No No further work
IF-
PGN21 Isolated find, c. 1900 No No further work
IF-
PGN22 Isolated find, c. 1880 No No further work
IF-
PGN23 Isolated find, 20th century No No further work
IF-
PGN24 Isolated find, c. post 1795 No No further work
IF-
PGN25 Isolated find No No further work
IF-
PGN26 Isolated find, 20th century No No further work
IF-
PGN27 Isolated find, c. 1950 No No further work
IF-
PGN28 Isolated find, c. 1960 No No further work
IF-
PGN29 Isolated find, c. 1970 No No further work
IF-
PGN30 Isolated find, c. 1950 No No further work
IF-
PGN31 Isolated find, 20th century No No further work
IF-Isolated find, 20th century No No further work
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Site Type National Register
Eligibility Recommendation
PGN33
IF-
PGN34 Isolated find, 20th century No No further work
IF-
PGN35 Isolated find, 20th century No No further work
IF-
PGN36 Isolated find, 20th century No No further work
IF-
PGN37 Isolated find, 20th century No No further work
IF-
PGN38 Isolated find, 20th century No No further work
IF-
PGN39 Isolated find, 20th century No No further work
IF-
PGN40 Isolated find, 20th century No No further work
IF-
PGN41 Isolated find, 20th century No No further work
IF-
PGN43 Isolated find, c. 1930 No No further work
IF-
PGN44 Isolated find, c. 1940 No No further work
IF-
PGN45 Isolated find, 20th century No No further work
IF-
PGN46 Isolated find, Native American No No further work
PGN3 Domestic, c. post 1880 No No further work
PGN5 Domestic, c. post 1920 No No further work
PGN6 Domestic, c. post 1930 No No further work
PGN7 Domestic, c. post 1900 No No further work
PGN8 Domestic, c. post 1775 No No further work
PGN10 Domestic, c. post 1900 No No further work
PGN11 Domestic, c. post 1900 No No further work
PGN13 Domestic, c. post 1970 No No further work
PGN14 Domestic, c. post 1900 No No further work
PGN32 Domestic, c. post 1950 No No further work
PGN44 Domestic, c. post 1900 No No further work
PGN47 Domestic, c. post 1920 No No further work