HomeMy WebLinkAbout20171193 Ver 2_Grants Creek-Jax Final no forms_20200709Grants Creek — Jacksonville 230kV Line
Onslow County, NC
Prepared for:
(� DUKE
ENERGY.
Prepared by:
ENVIRONMENTAL SERVICES, INC.
4901 Trademark Drive
Raleigh, North Carolina 27610
September 2016
Environmental Services, Inc.
Table of Contents
1.0
PROJECT DESCRIPTION & UNDERSTANDING............................................................. 1
2.0
METHODOLOGIES & QUALIFICATIONS........................................................................ 1
3.0
PHYSICAL RESOURCES....................................................................................................... 1
3.1
Topography............................................................................................................................. 1
3.2
Soils.........................................................................................................................................2
3.3
Water Resources...................................................................................................................... 2
4.0
JURISDICTIONAL ISSUES.................................................................................................... 2
4.1
Clean Water Act Waters of the U.S......................................................................................... 2
4.1.1
Wetland Data................................................................................................................... 3
4.1.2
Stream/Surface Water Data............................................................................................. 4
4.2
Clean Water Act Permits......................................................................................................... 6
4.3
Coastal Area Management Act................................................................................................ 6
4.4
Construction Moratoria........................................................................................................... 6
4.5
N.C. River Basin Buffer Rules................................................................................................ 6
4.6
Section 10 of the Rivers and Harbors Act............................................................................... 6
4.7
Endangered Species Act Protected Species............................................................................. 7
4.8
Bald and Golden Eagle Protection Act..................................................................................
14
4.9
Federal Species of Concern ...................................................................................................
14
4.10
State Protected Species......................................................................................................
15
4.11
Cultural / Archaeological Resources.....................................................................................
16
5.0
SUMMARY..............................................................................................................................16
Appendices
Appendix A
• Topographic and Aerial Figures
Appendix B
0 Data Forms
Environmental Services, Inc.
Grants Creek — Jacksonville 230kV Line
Onslow County, NC
September 2016
1.0 PROJECT DESCRIPTION & UNDERSTANDING
Duke Energy is evaluating a proposed transmission line corridor located north of Jacksonville in
Onslow County, North Carolina. The corridor is approximately 12.5 miles in length. The evaluated
corridor is 400 feet in width to account for the line and potential danger trees. The final proposed
right-of-way (ROW) is proposed to be 125 feet wide.
The study area is depicted on both a current U.S. Geological Survey (USGS) map (Figurel) and a
recent aerial photography (Figure 2) in Appendix A. The study area limits were provided by Duke
Energy.
Environmental Services, Inc., (ESI) was tasked by Duke to provide the following services for
the Grants Creek — Jacksonville 230kV Line:
• Jurisdictional wetland, stream, and surface water delineation,
• GPS data collection for any delineated wetlands or streams,
• Preliminary protected species habitat assessments for federally Endangered and Threatened
species,
• Preliminary cultural resources assessment, and
• Report and graphics preparation.
2.0 METHODOLOGIES & QUALIFICATIONS
Prior to the initiation of field efforts, available sources were reviewed, including the applicable U.S.
Geological Survey 7.5-minute topographic quadrangles of Jacksonville North and Kellum, NC
(NGS/ESRI 2011), and U.S. Department of Agriculture Soil Survey for Onslow County (USDA
1992). Additionally, records kept by the North Carolina Natural Heritage Program (NCNHP)
concerning any known occurrences of federally Threatened or Endangered species were reviewed
(NCNHP 2016).
3.0 PHYSICAL RESOURCES
The proposed new transmission line is located in the Coastal Plain physiographic province of North
Carolina. Specifically, the proposed transmission line is located in the River Bend Formation and the
Belgrade Formation, Undivided. (NCDENR 1985).
3.1 Topography
Topography in the study area is flat to gently sloping. Elevations range from a high of approximately
47 feet above mean sea level (MSL) down to approximately 25 feet above MSL through the study
area.
1
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
3.2 Soils
General soil associations occurring in the study area include the Norfolk-Goldsboro-Onslow
association. This association is described as nearly level and gently sloping, well drained, moderately
well drained, and somewhat poorly drained soils that have a loamy subsoil. There are also portions of
the study area that are included in the Muckalee-Dorovan association. This association is described as
nearly level, poorly drained soils that are loamy throughout and very poorly drained soils that are
muck throughout; occurs on flood plains.
3.3 Water Resources
Water resources in the study area are located within the White Oak River basin (USGS hydrologic unit
03020302) (NCCGIA 2001). A Best Usage Classification (BUC) is assigned to waters of North
Carolina based on the existing or contemplated best usage of various bodies of water. Table 1
contains the named water resources associated with features located within the study area, their Stream
Index Numbers, and their BUCs. The named streams represent the receiving waters of the individual
stream segments or tributaries that are located inside the study area. Unnamed streams and tributaries
carry the same BUC as their receiving waters, unless otherwise indicated by DWR.
Table 1. Named water resources and receiving waters (NCDWR 2013)
m Name
Stream Index #
BUC 91
Basin
Half Moon Creek
19-6
C;NSW
White Oak
Horse Swamp
19-16-2-1
C;NSW
White Oak
Little Northeast Creek
19-16-2
C;NSW
White Oak
Northeast Creek
19-16-(0.5)
SC;NSW
White Oak
Poplar Creek
19-16-2-3
C;NSW
White Oak
Wolf Swamp
19-16-1
C;NSW
White Oak
Class C waters are used as secondary recreation such as fishing, wildlife, fish consumption, and
agriculture. The NSW supplemental designation indicates nutrient sensitive waters, which require
limitations on nutrient inputs. Class SC waters are tidal salt waters used as secondary recreation such
as fishing, boating, and other activities involving minimal skin contact.
There are no Primary Nursery Areas (PNAs) or Outstanding Resource Waters (ORWs) within the
project study area (NCDMF 2011).
The New River, downstream of the study area in Onslow County, is considered an Anadromous Fish
Spawning Area (AFSA) by the North Carolina Division of Marine Fisheries (NCDMF 2007). The
proposed project should not have any effect on the New River.
4.0 JURISDICTIONAL ISSUES
4.1 Clean Water Act Waters of the U.S.
Section 404 of the Clean Water Act (CWA) requires regulation of discharges into "Waters of the
United States". Although the principal administrative agency of the CWA is the U.S. Environmental
Protection Agency (EPA), the U.S. Army Corps of Engineers (USACE) has major responsibility for
implementation, permitting, and enforcement of provisions of the Act. The USACE regulatory
2
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
program is defined in 33 CFR 320-330. Water bodies such as rivers, lakes, and streams are subject to
jurisdictional consideration under the Section 404 program. However, by regulation, wetlands are also
considered "Waters of the United States".
According to the Regional Supplement to the ACOE Wetland Delineation Manual for the Atlantic and
Gulf Coastal Plain (USACE 2010), areas must exhibit three distinct characteristics to be considered
jurisdictional wetlands: 1) prevalence of hydrophytic (water tolerant) plants; 2) presence of hydric
soils; and 3) sufficient wetland hydrology indicators within 12 inches of the ground surface. When
present, intermittent and perennial stream channels are also considered Waters of the United States
under Sections 404 and 401 of the CWA.
The USACE "Rapanos" decision allows USACE and EPA to establish CWA jurisdiction under one of
two standards. The first standard upholds CWA jurisdiction if the water body is "relatively
permanent", and its adjacent wetlands directly about the water body. The second standard upholds
jurisdiction if a water body, in combination with all wetlands adjacent to that water body, has a
"significant nexus" with traditional navigable waters.
Presence of an ordinary high water mark (OHWM) and a continuous bed and bank define streams and
tributaries to waters of the U.S. under current USACE guidance. Perennial and intermittent streams
are considered relatively permanent waters (RPWs) and are defined by hydrologic regime. Tributaries
can be natural or man-made (ditches), but they must possess an OHWM and bed and bank to be
considered by USACE. The delineation results described in the following sections are considered
preliminary until reviewed or otherwise approved by USACE. Note that any land alteration activities
occurring in the study corridor can alter the wetland jurisdiction boundaries and a re-evaluation could
be required.
4.1.1 Wetland Data
Thirty five (35) wetlands were delineated within the project study area. The wetland types were
classified pursuant to the N.C. Wetland Assessment Method (NCWAM). Figures 2a-2j depict the
approximate extent and approximate location of the wetlands that were delineated. These graphics are
not intended to be a replacement for a traditional survey and are not intended to be used as such.
Table 2 contains wetland data collected within the project study area. Wetlands were flagged with
sequentially numbered blue and pink -and -black striped flagging.
Table 2. Wetland Data for the Grants Creek — Jacksonville 230kV Line.
Wetland
ID
Figure
No.
NCWAM
Classification
Acreage
Within 400'
Corridor
Acreage Within
125' Proposed
ROW
W 1
2a
Headwater Forest
0.2
<0.1
W2
2a
Pine Flat
8.2
3.5
W3
2a
Headwater Forest
0.1
0.1
W4
2a
Headwater Forest
<0.1
--
W5
2a
Pine Flat
0.3
0.3
W6
2a-2b
Pine Flat
0.1
--
W7
2b
Headwater Forest
0.1
<0.1
W8
2b
Headwater Forest
19
6.6
3
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
Table 2. Continued.
Wetland
ID
Figure
No.
NCWAM
Classification
Acreage
Within 400'
Corridor
Acreage
Within 125'
Proposed
ROW
W9
2b
Headwater Forest
2.4
0.7
W 10a
2c
Headwater Forest
0.6
0.2
W 10b
2c
Headwater Forest
<0.1
--
W11
2c
Riverine Swamp Forest
1.4
0.3
W 12
2c
Pine Flat
0.2
--
W13
2c
Pine Flat
5.9
2.0
W14a
2e
Headwater Forest
0.2
--
W14b
2e
Headwater Forest
6.4
0.1
W15
2e
Pine Flat
9.8
3.1
W16
2f
Headwater Forest
1.2
0.1
W17
2f
Headwater Forest
4.5
1.3
W 18
2f-2g
Hardwood Flat
3.5
1.4
W 19
2g
Hardwood Flat
9.8
3.3
W20
2g
Hardwood Flat
4.2
1.7
W21
2g
Pine Flat
13.4
4.2
W22
2g
Headwater Forest
1.1
0.3
W23
2g-2h
Pine Flat
0.1
--
W24
2h
Headwater Forest
1.2
0.4
W25
2h
Headwater Forest
14.3
4.6
W26
2h
Pine Flat
1.9
0.1
W27
2h
Pine Flat
1.3
0.3
W28
2h-21
Headwater Forest
1.6
0.5
W29
21
Headwater Forest
0.5
0.1
W30
21
Riverine Swamp Forest
7.8
2.7
W31
21
Headwater Forest
0.2
<0.1
W32
21-2j
Pine Flat
0.2
0.1
W33
2j
Pine Flat
0.8
0.3
W34
2j
Pine Flat
2.2
0.9
W35
2j
Hardwood Flat
1.3
0.4
TOTAL:
126.2
39.6
4.1.2 Stream/Surface Water Data
Thirty four (34) stream channel segments and one (1) surface water occur within the project study
area. The streams were delineated with sequentially numbered solid blue and orange flagging. USACE
and NCDWR stream data forms were completed for the streams in the study area. Table 3 contains
the stream data collected within the project study area. Figures 2a-2j depicts the approximate extent
and approximate location of the stream channels and wetlands that were delineated. These graphics
are not intended to be a replacement for a traditional survey and is not intended to be used as such.
4
Grants Creek - Jacksonville 230kV Line
Environmental Services, Inc.
Table 3. Stream Data for the Grants Creek - Jacksonville 230kV Line.
Stream
ID
Figures
Perennial/
Intermittent
Approximate
Length (feet)
In Study Area
Approximate
Width (feet)
NCDWR
Stream ID
Form
Score
Subject
to Buffer
(y/�
400'
Corridor
125'
ROW
S1
2a
Intermittent
267
80
2
24.75
No
S2
2a
Intermittent
205
129
2
23.75
No
S3
2b
Perennial
907
126
12
42.5
No
S4
2b
Perennial
204
29
12
42.5
No
S5
2b
Perennial
885
476
12
42.5
No
S6
2b
Perennial
1380
625
12
42.5
No
S7
2b
Perennial
623
285
5
34.5
No
S8
2c
Intermittent
490
130
3
26.75
No
S9
2c
Ephemeral'
450
140
3
17.75
No
S10
2c
Ephemeral'
463
136
2
17.75
No
S11
2c
Intermittent
469
129
10
19.75
No
S12
2c
Intermittent
916
130
10
19.75
No
S13
2c-2d
Intermittent
3069
--
10
19.75
No
S14
2d
Ephemeral'
446
147
4
16.5
No
S15
2d
Perennial
61
--
10
30.5
No
S16
2d
Ephemeral'
158
--
2
16.75
No
S17
2e
Perennial
704
139
7
36.5
No
S18
2e
Ephemeral'
54
--
2
16.75
No
S19
2e
Intermittent
281
14
2
19.25
No
S20
2f
Perennial
388
--
5
31.75
No
S21
2f
Intermittent
46
3
2
26.75
No
S22
2f
Perennial
547
126
17
41.5
No
S23
2f
Intermittent
197
--
2.5
24.25
No
S24
2f
Intermittent
287
130
2.5
24.25
No
S25
2f
Intermittent
456
--
2.5
24.25
No
S26
2f
Intermittent
133
--
2.5
24.25
No
S27
2f-2g
Ephemeral'
431
120
2
17.25
No
S28
2g
Ephemeral'
863
226
2
17.25
No
S29
2g
Intermittent
671
206
4
20.25
No
S30
2g
Ephemeral'
733
362
3
16.75
No
S31
21
Perennial
527
163
3
34
No
S32
21
Ephemeral'
270
125
1
18.25
No
S33
21
Perennial
463
267
12
42
No
S34
21
Ephemeral'
267
117
1
15.25
No
TOTAL:
18,311
4,697
' Ephemeral channels may still be claimed as a jurisdictional tributary by USACE.
Grants Creek - Jacksonville 230kV Line
Environmental Services, Inc.
4.2 Clean Water Act Permits
Dredge and fill activities in "Waters of the United States" must be authorized by USACE as a
regulated discharge pursuant to Section 404 of the CWA and also by NCDWR pursuant to Section 401
of the CWA. Activities authorized by the USACE are subject to further water quality requirements
per Section 401 of the CWA. In North Carolina, the NCDWR administers the Section 401 Water
Quality Certification process, which also must include plans on how the applicant proposes to manage
storm water.
Coordination is recommended with USACE in order to determine the permitting requirements for this
project, if any. Section 404 permitting may not be necessary if all wetland and stream impacts are
avoided; however, concurrence from USACE should be obtained prior to beginning any activities.
Hand clearing in wetlands is typically not a regulated activity if there is no ground disturbance.
Mechanized clearing in wetlands may be viewed as a regulated activity if heavy equipment disturbs
the natural ground surface or contours and if stump removal or grubbing occurs.
Compensatory mitigation can be required by USACE if the proposed project is determined to have an
adverse effect on Waters of the United States, including wetlands, as a result of a regulated discharge.
Nationwide Permit 12-Condition 23(g) states that "where certain functions and services of waters of
the United States are permanently adversely affected, such as the conversion of forested or scrub -shrub
wetlands to a herbaceous wetland in a permanently maintained utility right-of-way, mitigation may be
required to reduce the adverse effect of the project to a minimal level". Consultation with USACE is
recommended to determine if this condition is going to apply to this project. If it is determined that an
Individual Permit be required, this same USACE consultation should occur regarding the USACE
position on the wetland conversion resulting from the proposed project.
4.3 Coastal Area Management Act
North Carolina Division of Coastal Management (NCDCM) regulates certain wetlands and water
bodies in the twenty coastal counties of North Carolina under the Coastal Area Management Act
(CAMA). Areas subject to CAMA are identified as Areas of Environmental Concern (AECs). There
are no AECs in the study area that are subject to CAMA regulations
4.4 Construction Moratoria
It is anticipated that no in -water construction moratoria will apply to this project.
4.5 N.C. River Basin Buffer Rules
The study area is located in the White Oak River basin. No riparian buffer rules apply to this basin,
this study area is not subject to any riparian buffers.
4.6 Section 10 of the Rivers and Harbors Act
Section 10 of the Rivers and Harbors Act requires authorization from the USACE for the excavation
of material, alteration, obstruction, or construction of any structure in or over any "navigable water" of
the United States (33 U.S.0 410 et seq.). "Navigable water" is defined as waters that are subject to the
ebb and flow of the tide shoreward to the mean high water mark and/or waters that are presently used,
have been used in the past, or are susceptible for use to transport interstate or foreign commerce (33
CFR part 329). The study area is not subject to Section 10 regulations.
6
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
4.7 Endangered Species Act Protected Species
Species with the federal classifications of Endangered (E), Threatened (T) or Proposed (P) are
protected under the Endangered Species Act (ESA) of 1973, as amended (16 U.S.C. 1531 et seq.).
The U.S. Fish and Wildlife Service (USFWS) list fifteen species for Onslow County as of March 25,
2015 (USFWS 2015). NCNHP data updated in July 2016 was accessed to determine if any of these
species have been documented inside of or within 0.5 mile of the study area.
Table 4. Federal listed species for Onslow County, NC.
Potential
Federal
Biological
Scientific Name
Common Name
e
Status
Habitat
Conclusion
Present
Alligator
American alligator
T (S/A)
Yes
Not Required
mississippiensis
Chelonia mydas
Green sea turtle
T
No
No Effect
Eretmochelys
Hawksbill sea turtle
E
No
No Effect
imbricata
Lepidochelys
Kemp's ridley sea turtle
E
No
No Effect
kempii
Dermochelys coriacea
Leatherback sea turtle
E
No
No Effect
Caretta caretta
Loggerhead sea turtle
T
No
No Effect
Charadria melodus
Piping plover
T
No
No Effect
Red -cockaded
Picoides borealis
E
Yes
Unresolved
woodpecker
Trichechus manatus
West Indian manatee
E
No
No Effect
Thalictrum cooleyi
Cooley's meadowrue
E
No
No Effect
Carex lutea
Golden sedge
E
No
No Effect
Lindera melissifolia
Pondberry
E
No
No Effect
Lysimachia
Rough -leaved loosestrife
E
Yes
No Effect
asperulaefolia
Amaranthus pumilus
Seabeach amaranth
T
No
No Effect
Calidris canutus rufa
Red knot
T
No
No Effect
'E — Endangered
T —Threatened
T (S/A) —Threatened due to Similarity of Appearance
7
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
American alligator - In North Carolina, alligators have been recorded in nearly every coastal county,
and many inland counties to the fall line. The alligator is found in rivers, streams, canals, lakes,
swamps, and coastal marshes. Adult animals are highly tolerant of salt water, but the young are
apparently more sensitive, with salinities greater than 5 parts per thousand considered harmful. The
American alligator remains on the protected species list due to its similarity in appearance to the
Endangered American crocodile (Crocodylus acutus) (USFWS 2016a).
Habitat Present: Yes
Species listed as threatened due to similarity of appearance do not require Section 7
consultation with the USFWS. Suitable habitat for this species is present within the study
area. However, construction activities are not expected to have any permanent impacts to this
species or its habitat within the study area. A review of NCNHP records, updated July 2016,
indicates no known occurrence of American alligator within 0.5 mile of the study area.
BIOLOGICAL CONCLUSION: Not Required
Green sea turtle - The green sea turtle is found in temperate and tropical oceans and seas. Nesting in
North America is mostly limited to small communities on the east coast of Florida requiring beaches
with minimal disturbances and a sloping platform for nesting. The green sea turtle can be found in
shallow waters. They are attracted to lagoons, reefs, bays, mangrove swamps and inlets where an
abundance of marine grasses can be found, as this is the principle food source for the green sea turtle
(USFWS 2016b).
Habitat Present: No
Suitable habitat for the green sea turtle does not exist within the study area. The study area is
too far inland and lacks ocean/beach habitat associated with this species. A review of
NCNHP records, updated July 2016, indicates no known occurrence of green sea turtle within
0.5 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
Hawksbill sea turtle — Hawksbill sea turtles are found in tropical and subtropical oceans. Sightings
have been reported on the east coast of the U.S. as far north as Massachusetts, although rarely north of
Florida. Sightings have been recorded from a handful of counties in North Carolina, but the turtle is
not known to breed here. Adult hawksbills are found in coastal waters, especially around coral reefs,
rocky outcrops, shoals, mangrove bays, and estuaries. Juveniles are often seen offshore, in floating
mats of seaweed. This species nests on a wide range of beach types and substrates, using both low -
and high-energy beaches on islands and mainland sites. The nest is typically placed near or under
some vegetation (USFWS 2015c).
Habitat Present: No
The study area does not contain suitable habitat for this species. The study area lacks the
beach, bay, and estuary habitat associated with this species. NCNHP data from July 2016
indicates no occurrences of the Hawksbill sea turtle within 0.5 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
8
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
Kemp's ridley sea turtle — Kemp's ridley sea turtle is the smallest of the sea turtles that visit North
Carolina's coast, and has been sighted in most coastal counties. While the majority of this sea turtle's
nesting occurs in Mexico, the species is known to nest on North Carolina beaches infrequently.
Kemp's ridley sea turtle can lay eggs as many as three times during the April to June breeding season.
This species prefers beach sections that are backed up by extensive swamps or large bodies of open
water having seasonal narrow ocean connections and a well-defined elevated dune area. The species
prefers neritic area with sandy or muddy bottoms (USFWS 2015d).
Habitat Present: No
The study area does not contain suitable habitat for this species. The study area lacks the
beach, bay, and estuary habitat associated with this species. NCNHP data from July 2016
indicates no occurrences of the Kemp's ridley sea turtle within 0.5 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
Leatherback sea turtle - The leatherback sea turtle is distributed world-wide in tropical waters of the
Atlantic, Pacific, and Indian oceans. They are generally open ocean species, and may be common off
the North Carolina coast during certain times of the year. However, in northern waters leatherback sea
turtles are reported to enter into bays, estuaries, and other inland bodies of water. Major nesting areas
occur mainly in tropical regions. In the United States, primary nesting areas are in Florida, however,
nests are known from Georgia, South Carolina, and North Carolina as well. Nesting occurs from April
to August. Leatherback sea turtles need sandy beaches backed with vegetation in the proximity of
deep water and generally with rough seas. Beaches with a relatively steep slope are usually preferred
(USFWS 2016e).
Habitat Present: No
Suitable habitat for the leatherback sea turtle does not exist within the study area. The study
area is too far inland and lacks ocean/beach habitat associated with this species. A review of
NCNHP records, updated July 2016, indicates no known occurrence of leatherback sea turtle
within 0.5 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
Loggerhead sea turtle - The loggerhead sea turtle is widely distributed within its range, and is found
in three distinct habitats during their lives. These turtles may be found hundreds of miles out in the
open ocean, in neritic areas, or on coastal beaches. In North Carolina, this species has been observed
in every coastal county. Loggerhead sea turtles occasionally nest on North Carolina beaches, and are
the most common of all sea turtles that visit the North Carolina coast. They nest nocturnally, at two to
three year intervals, between May and September, on isolated beaches that are characterized by fine-
grained sediments. In near shore areas, loggerhead sea turtles have been observed in bays, lagoons,
salt marshes, creeks, ship channels, and the mouths of large rivers. Coral reefs, rocky places, and
shipwrecks are often used as foraging areas (USFWS 2016f).
Habitat Present: No
9
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
Suitable habitat for the loggerhead sea turtle does not exist within the study area. The study
area is too far inland and lacks ocean/beach habitat associated with this species. A review of
NCNHP records, updated July 2016, indicates no known occurrence of loggerhead sea turtle
within 1.0 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
Piping plover - The piping plover breeds along the entire eastern coast of the United States. North
Carolina is uniquely positioned in the species' range, being the only State where the piping plover's
breeding and wintering ranges overlap and the birds are present year-round. They nest most
commonly where there is little or no vegetation, but some may nest in stands of beach grass. The nest
is a shallow depression in the sand that is usually lined with shell fragments and light-colored pebbles
(USFWS 2016g).
Habitat Present: No
Suitable habitat for the piping plover does not exist within the study area. The study area
lacks beach habitat associated with this species. A review of NCNHP records, updated July
2016, indicates no known occurrence of piping plover within 0.5 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
Red -cockaded woodpecker - The red -cockaded woodpecker (RCW) typically occupies open, mature
stands of southern pines, particularly longleaf pine, for foraging and nesting/roosting habitat. The
RCW excavates cavities for nesting and roosting in living pine trees, aged 60 years or older, which are
contiguous with pine stands at least 30 years of age to provide foraging habitat. The foraging range of
the RCW is normally no more than 0.5 mile (USFWS 2016h).
Habitat Present: Yes
There is potentially suitable foraging habitat within the study area and throughout the
surrounding areas. The study area is dominated by loblolly pine timber tracts in varying
stages of succession and maturity. The study area also goes through, and borders, the
Hofmann Forest and various Weyerhaeuser tracts with Camp Lejeune and the Croatan
National Forest being in close proximity. The opportunity for foraging habitat within the
study area is vast and well connected to surrounding areas. Several of the areas evaluated
were estimated to be in 25+ year class and had recently been thinned. These areas provide a
suppressed understory which affords an open bole on the older pines left standing.
Consultation with Hofmann Forest staff indicates that there are pine stands with an age class
of 30 years throughout their holdings. Large older stands of pine are infrequent throughout
the study area thus limiting the nesting potential. However, given the volume of pine timber
managed in the immediate surrounding area, it is probable that nesting habitat could exist
within the nearby vicinity of the study area. Aerial surveys are recommended to document the
presence/absence of nesting habitat within 0.5 mile of the study area. A review of NCNHP
records, updated July 2016, indicates no known occurrence of RCW within 0.5 mile of the
study area.
BIOLOGICAL CONCLUSION: Unresolved
10
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
West Indian manatee - West Indian manatees have been observed in all the North Carolina coastal
counties. West Indian manatees are found in canals, sluggish rivers, estuarine habitats, salt water bays,
and as far off shore as 3.7 miles. They utilize freshwater and marine habitats at shallow depths of 5 to
20 ft. In the winter, between October and April, manatees concentrate in areas with warm water.
During the other time of the year habitats for the manatee are those with sufficient water depth, an
adequate food supply, and in proximity to freshwater. West Indian manatees require a source of
freshwater to drink. West Indian manatees are primarily herbivores, feeding on any aquatic vegetation
present, but they may occasionally feed on fish (USFWS 20161).
Habitat Present: No
Suitable habitat for the West Indian manatee does not exist within the study area. The study
area is too far inland and lacks the direct open water connections to downstream coastal areas..
A review of NCNHP records, updated July 2016, indicates no known occurrence of West
Indian manatee within 0.5 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
Cooley's meadowrue - Cooley's meadowrue, documented in the Pine Savanna natural community,
occurs in circumneutral soils in sunny, moist to wet grass -sedge bogs, wet -pine savannas over
calcareous clays, and savannah -like areas, often at the ecotones of intermittent drainages or non-
riverine swamp forests. This rhizomatous perennial herb is also found along plowed firebreaks,
roadside ditches and rights -of -way, forest clearings dominated by grass or sedge, and power line or
utility rights -of -way. The species requires some type of habitat disturbance (e.g., mowing, clearing,
periodic fire) to maintain its open habitat. The plant typically occurs on slightly acidic (pH 5.8-6.6)
soils that are loamy fine sand, sandy loam, or fine sandy loam; at least seasonally moist or saturated;
and mapped as Foreston, Grifton, Muckalee, Torhunta, or Woodington series (USFWS 1994).
Habitat Present: No
Suitable habitat for Cooley's meadowrue is not present within the study area. Wet areas
within the existing powerline right-of-way have a thick shrub layer, are not frequently
maintained, and do not exhibit the wet savanna -like conditions that could provide suitable
habitat for Cooley's meadowrue. Forested wetlands in the study area also do not exhibit the
wet savanna -like conditions that could provide suitable habitat for Cooley's meadowrue. A
review of NCNHP records, updated July 2016, indicates no known occurrences of Cooley's
meadowrue within 0.5 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
Golden sedge - Golden sedge, a very rare endemic of the Atlantic Coastal Plain, grows in sandy soils
overlying calcareous deposits of coquina limestone, where the soil pH, typically between 5.5 and 7.2,
is unusually high for this region. The perennial prefers the ecotone between the pine savanna and
adjacent wet hardwood or hardwood/conifer forest. Most plants occur in the partially shaded
savanna/swamp where occasional to frequent fires favor an herbaceous ground layer and suppress
shrub dominance. Soils supporting the species are very wet to periodically shallowly inundated.
11
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
Other occurrences may occur on disturbed areas such as roadside and drainage ditches or power line
rights -of -way, where mowing and/or wet conditions suppress woody plants. Poorly viable
occurrences may occur in significantly disturbed areas where ditching activities that lowers the water
table and/or some evidence of fire suppression threatens the species (USFWS 2002).
Habitat Present: No
Suitable habitat for golden sedge is not present within the study area. Wet areas within the
existing powerline right-of-way have a thick shrub layer, are too frequently flooded, are not
frequently maintained, and do not exhibit the wet savanna -like conditions that could provide
suitable habitat for golden sedge. Wetlands outside of the powerline right-of-way are forested
and also do not exhibit the wet savanna -like conditions that could provide suitable habitat for
golden sedge. A review of NCNHP records, updated July 2016, indicates no known
occurrences of golden sedge within 0.5 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
Pondberry - Pondberry occurs in seasonally flooded wetlands, sandy sinks, pond margins, and
swampy depressions. This deciduous, aromatic shrub occurs in bottomland hardwood forests with
perched water tables along inland areas of the southeastern United States. In the Coastal Plain of the
Carolinas, the species occurs at the margins of limestone sinks and ponds and in undrained, shallow
depressions of longleaf pine (Pious palustris) and pond pine (Pinus serotina) forests. Known
occurrences in North Carolina occur in the Small Depression Pocosin natural community, grow in
soils with sandy sediments and high water table, contain high peat content in the subsurface, and
include a prevalence of shrubs due to historically frequent or intense fires. It generally grows in
somewhat shaded areas, but can tolerate full sun (USFWS 1993).
Habitat Present: No
Suitable habitat for pondberry does not exist within the study area. The study area lacks
limestone sinks and ponds or undrained, shallow depressions associated with this species. A
review of NCNHP records, updated July 2016, indicates no known occurrence of pondberry
within 0.5 mile of the study area. No areas designated as Critical Habitat occur in the study
area.
BIOLOGICAL CONCLUSION: No Effect
Rough -leaved loosestrife - Rough -leaved loosestrife, endemic to the Coastal Plain and Sandhills of
North and South Carolina, generally occurs in the ecotones or edges between longleaf pine uplands
and pond pine pocosins in dense shrub and vine growth on moist to seasonally satuarated sands and on
shallow organic soils overlaying sand (spodosolic soils). Occurrences are found in such disturbed
habitats as roadside depressions, maintained power and utility line rights -of -way, firebreaks, and trails.
The species prefers full sunlight, is shade intolerant, and requires areas of disturbance (e.g., clearing,
mowing, periodic burning) where the overstory is minimal. It can, however, persist vegetatively for
many years in overgrown, fire-supressed areas. Blaney, Gilead, Johnston, Kalmia, Leon, Mandarin,
Murville, Torhunta, and Vaucluse are some of the soil series that the plant occurs on (USFWS 1995).
12
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
Habitat Present: Yes
Potentially suitable habitat for rough -leaved loosestrife is present within the study area. Some
larger wetlands within the corridor are managed, recently thinned pine stands that provide the
disturbed habitat and sunlight preferred by this species. Other wetlands within the study area
are maintained powerline rights -of -way and regenerating areas of emergent/successional
vegetation that exhibit pocosin like characteristics. Sandy soils and organic soils were
observed within the aforementioned wetland habitats. ESI biologists Stuart Bryan and Wil
Vaughan surveyed areas of potential habitat for rough -leaved loosestrife August 15-16, 2016.
A reference population was reviewed prior to conducting the survey. No specimens of rough -
leaved loosestrife were identified. A review of NCNHP data, updated July 2016, indicates no
known occurrence of rough -leaved loosestrife within 0.5 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
Seabeach amaranth - Seabeach amaranth occurs on barrier island beaches where its primary habitat
consist of overwash flats at accreting ends of islands, lower foredunes, and upper strands of
noneroding beaches (landward of the wrack line). In rare situations, this annual is found on sand spits
160 feet or more from the base of the nearest foredune. It occasionally establishes small temporary
populations in other habitats, including sound -side beaches, blowouts in foredunes, interdunal areas,
and on sand and shell material deposited for beach replenishment or as dredge spoil. The plant's
habitat is sparsely vegetated with annual herbs (fortis) and, less commonly, perennial herbs (mostly
grasses) and scattered shrubs. It is, however, intolerant of vegetative competition and does not occur
on well -vegetated sites. The species usually is found growing on a nearly pure silica sand substrate,
occasionally with shell fragments mixed in. Seabeach amaranth appears to require extensive areas of
barrier island beaches and inlets that function in a relatively natural and dynamic manner. These
characteristics allow it to move around in the landscape, occupying suitable habitat as it becomes
available (USFWS 2016j).
Habitat Present: No
Suitable habitat for the seabeach amaranth does not exist within the study area. The study area
lacks beach/dune habitat associated with this species. A review of NCNHP records, updated
July 2016, indicates no known occurrence of seabeach amaranth within 0.5 mile of the study
area.
BIOLOGICAL CONCLUSION: No Effect
Red knot — The rufa red knot is one of the six recognized subspecies of red knots, and is the only
subspecies that routinely travels along the Atlantic coast of the United States during spring and fall
migrations. It is known to winter in North Carolina and to stop over during migration. Habitats used
by red knots in migration and wintering areas are similar in character: coastal marine and estuarine
habitats with large areas of exposed intertidal sediments. In North America, red knots are commonly
found along sandy, gravel, or cobble beaches, tidal mudflats, salt marshes, shallow coastal
impoundments and lagoons, and peat banks. Ephemeral features such as sand spits, islets, shoals, and
sandbars, often associated with inlets can be important habitat for roosting (USFWS 2016k).
13
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
Habitat Present: No
Suitable habitat for the red knot does not exist within the study area. The study area lacks
beach/dune habitat associated with this species. A review of NCNHP records, updated July
2016, indicates no known occurrence of red knot within 0.5 mile of the study area.
BIOLOGICAL CONCLUSION: No Effect
4.8 Bald and Golden Eagle Protection Act
Bald eagles typically feed on fish but may also consume birds and small mammals. In the Carolinas,
nesting season extends from December through May (Potter et al. 1980). Bald eagles typically nest in
tall, living trees in a conspicuous location near water and forage over large bodies of water with
adjacent trees available for perching (Hamel 1992).
The bald eagle was officially delisted and removed from the federal Endangered Species List on
August 9, 2007, but they are still protected under the federal BGPA and the MBTA. The National
Bald Eagle Management Guidelines (Guidelines) prohibit disturbance to a bald eagle. The Guidelines
define disturb as "to agitate or bother a bald or golden eagle to a degree that causes, or is likely to
cause, based on the best scientific information available: 1) injury to an eagle; 2) a decrease in its
productivity, by substantially interfering with normal breeding, feeding, or sheltering behavior; or 3)
nest abandonment, by substantially interfering with normal breeding, feeding, or sheltering behavior."
The definition also covers impacts that result from human -caused alterations initiated around a
previously used nest site during a time when eagles are not present, if, upon the eagles return, such
alterations agitate or bother an eagle to a degree that injures an eagle or interferes with normal
breeding, feeding, or sheltering behavior.
Under the current Guidelines, USFWS recommends the following measures for roads, trails, canals,
power lines, and other linear utilities. If the eagle nest can be seen from the project site and there is no
similar activity within 660 feet, then USFWS recommends that the project: 1) maintain a buffer of at
least 660 feet between your activities and the nest; 2) maintain any established landscape buffers; and
3) if possible, create additional landscape buffers to screen the new activity from the nest. If these
recommendations cannot be adopted for the project, then coordination is recommended with the local
USFWS office. ESI did not identify any evidence of bald eagle activity while working inside the study
area. NCNHP data from July 2016 indicates no documented occurrences of bald eagle within 0.5 mile
of the study area.
4.9 Federal Species of Concern
The March 25, 2015 USFWS list for Onslow County also includes a category of species designated as
"Federal Species of Concern" (FSC). Federal species of concern are not afforded federal protection
under the Endangered Species Act and are not subject to any of its provisions, including Section 7,
until they are formally Proposed (P) or listed as Threatened (T) or Endangered (E). However, the
status of these species is subject to change, and so should be included for consideration. FSC are
defined as species that are under consideration for listing for which there is insufficient information to
support listing. The presence of potential habitat is based on the following NCNHP documents: List
14
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
of Rare Plant Species of North Carolina (NCNHP 2014a) and List of Rare Animal Species of North
Carolina (NCNHP 2014b).
4.10 State Protected Species
Some species that are listed as FSC by USFWS also receive limited state protection. Those species
that are listed as both FSC and as North Carolina state -listed Endangered (E), Threatened (T), and
Special Concern (SC) are identified in Table 5. These species receive limited protection under the
North Carolina Endangered Species Act (G.S. 113-331 et seq.) and the North Carolina Plant
Protection Act of 1979 (G.S. 106-202.12 et seq.).
Table 5. Federal Species of Concern for Onslow County, NC
N.C.
Potential
NCNHP
Common Name
Scientific Name
Status'
0.5-Mile
T, E, SC
Habitat
Occurrence
American eel
Anguilla rostrata
--
No
No
Bachman's sparrow
Aimophila aestivalis
SC
No
No
Black rail
Laterallus jamaicensis
SC
No
No
Carolina gopher frog
Rana capito capito
T
No
No
Eastern henslow's
Ammodramus henslowii
SC
No
No
sparrow
susurrans
Eastern painted
Passerina ciris ciris
SC
No
No
bunting
Mimic glass lizard
Ophisaurus mimicus
SC
No
No
Southern hognose
Heterodon simus
SC
No
No
snake
Bucholz's dart moth
Agrotis bucholzi
--
No
No
A skipper
Atrytonopsis sp. 1
--
No
No
Awned
Rhexia aristosa
SC-V
No
No
meadowbeauty
Boykins lobelia
Lobelia boykinii
E
Yes
No
Carolina grass -of-
Parnassia caroliniana
T
No
No
parnassus
Carolina trillium
Trillium pusillum var. pusillum
E
Yes
No
Coastal beaksedge
Rhynchospera pleiantha
T
Yes
No
Coastal goldenrod
Solidago villosicarpa
E
No
No
Grassleaf arrowhead
Sagittaria weatherbiana
E
No
No
Loose watermilfoil
Myriophyllum laxum
E
No
No
Many -flowered
Calopogon multijlorus
E
No
No
grass -pink
Pineland plantain
Plantago sparsijlora
T
No
No
Pondspice
Litsea aestivalis
SC-V
No
No
15
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
Table 5. Continued.
N.C.
Potential
NCNHP
Common Name
Scientific Name
Status l
Habitat
0.5-Mile
T, E, SC
Occurrence
Savanna onion
Allium sp. I
__
No
No
Smooth -seeded hairy
Scleria sp. 1
--
No
No
nutrush
Spring -flowering
Solidago verna
--
Yes
No
goldenrod
Swamp forest
Rhynchospera decurrens
T
Yes
No
beakrush
Thorne's beakrush
Rhynchospera thornei
SC-V
No
No
Venus' fly -trap
Dionaea muscipula
SC-V
No
No
Wagner's spleenwort
Asplenium heteroresiliens
E
No
No
A quillwort
Isoetes microvela
T
No
No
' T=Threatened, E=Endangered; SC=Special Concern; SC-V=Special Concern -Vulnerable
4.11 Cultural / Archaeological Resources
Research conducted by ESI at the Survey and National Register Branch of the North Carolina State
Historic Preservation Office (SHPO) on 29 March 2016 revealed that no previously recorded historic
properties listed in, eligible, or potentially eligible for listing in the National Register of Historic
Places (National Register) are located directly within the proposed project area. Research conducted
by ESI at the North Carolina Office of State Archaeology (OSA) on 29 March 2016 revealed that no
previously recorded archaeological sites are located directly within or immediately adjacent to the
proposed project area.
5.0 SUMMARY
The project study area contains thirty-five wetlands, thirty-four stream channels, and one surface
water. Impacts to jurisdictional areas should be avoided and minimized as much as practicable.
Potential habitat is present in the study area for the federally listed rough -leaved loosestrife. Surveys
were conducted for this species but none was observed within the study area. RCW foraging habitat is
present and aerial surveys are recommended to resolve this issue. Unavoidable impacts must be
coordinated with the applicable resource agency and permitting and mitigation could be required for
regulated discharged. No issues regarding cultural or archaeological resources were identified.
16
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
References
Hamel, P.B. 1992. Land Manager's Guide to the Birds of the South. The Nature Conservancy,
Southeastern Region, Chapel Hill, NC. 437 pp.
National Geographic Society/ESRI. 2011. I -cubed seamless USGS quadrangle (Jacksonville North
and Kellum, NC).
N.C. Center for Geographic Information and Analysis. 2001. State of North Carolina Hydrologic Unit
Map.
N.C. Department of Environment and Natural Resources. 1985. Geologic Map of North Carolina.
N.C. Division of Marine Fisheries. 2007. Anadromous Fish Spawning Areas, White Oak River Area
and New River Area, Map 1. http://portal.ncdenr.org/web/mf/ (Accessed August 2016).
N.C. Division of Marine Fisheries. 2011. Fishery Nursery Areas. http://portal.ncdenr.org/web/mf/
(Accessed August 2016).
N.C. Division of Water Resources. 2013. NC Water Quality Classifications by NC River Basin.
http://portal.ncdenr.org/web/wq/ps/csu/classifications (Accessed August 2016).
N. C. Natural Heritage Program. 2014a. List of Rare Plant Species of North Carolina 2014. North
Carolina Natural Heritage Program. 138 pp.
N. C. Natural Heritage Program. 2014b. List of Rare Animal Species of North Carolina 2014. North
Carolina Natural Heritage Program. 172 pp.
N. C. Natural Heritage Program. 2016. July 2016 NHP Element Occurrences. Raleigh, NC.
(Accessed July 2016).
Potter, E.F., J.F. Parnell, and R.P. Teulings 1980. Birds of the Carolinas. The University of North
Carolina Press, Chapel Hill, NC. 408 pp.
U.S. Army Corps of Engineers. 2010. Regional Supplement to the Corps of Engineers Wetland
Delineation Manual: Atlantic and Gulf Coastal Plain Region (Version 2.0). Vicksburg, MS.
180 pp.
U.S. Department of Agriculture. 1992. Soil Survey of Onslow County, North Carolina. U.S.
Department of Agriculture, Soil Conservation Service. 139 pp. + maps
U.S. Fish and Wildlife Service. 1993. Pondberry Recovery Plan. Atlanta, GA. 56 pp.
U.S. Fish and Wildlife Service. 1994. Cooley's Meadowrue Recovery Plan. Atlanta, Georgia. 29 pp.
U.S. Fish and Wildlife Service. 1995. Rough -leaved Loosestrife Recovery Plan. Atlanta, GA. 32pp.
U.S. Fish and Wildlife Service. 2002. Endangered and Threatened Wildlife and Plants; Endangered
Status for Carex lutea (Golden Sedge). 67 FR 3120-3126.
17
Grants Creek — Jacksonville 230kV Line
Environmental Services, Inc.
U.S. Fish and Wildlife Service. 2007. National Bald Eagle Management Guidelines
U.S. Fish and Wildlife Service. 2015. T&E species listed for Onslow County.
http://www.fws.gov/raleigh/species/cntylist/nc_counties.html (Accessed August 2016).
U.S. Fish and Wildlife Service. 2016a. American alligators in North Carolina.
Http://www.fws.gov/nces/reptile/alligat.html (Accessed July 2016).
U.S. Fish and Wildlife Service. 2016b. Green Sea Turtles in North Carolina.
Http://www.fws.gov/nces/reptile/greensea.httnl (Accessed July 2016).
U.S. Fish and Wildlife Service. 2016c. Hawksbill Sea Turtles in North Carolina.
Http://www.fws.gov/nces/reptile/hawksbill.html (Accessed July 2016).
U.S. Fish and Wildlife Service. 2016d. Kemp's Ridley Sea Turtles in North Carolina.
Http://www.fws.gov/nces/reptile/ridley.html (Accessed July 2016).
U.S. Fish and Wildlife Service. 2016e. Leatherback Sea Turtles in North Carolina.
Http://www.fws.gov/nces/reptile/leather.html (Accessed July 2016).
U.S. Fish and Wildlife Service. 2016f. Loggerhead Turtles in North Carolina.
Http://www.fws.gov/nces/reptile/logger.html (Accessed July 2016.)
U.S. Fish and Wildlife Service. 2016g. Piping plover (Charadrius melodus) Species Profile.
Http:Hecos.fws.gov/speciesProfile/profile/speciesProfile.action?spcode=B079 (Accessed July
2016.)
U.S. Fish and Wildlife Service. 2016h. Red -cockaded Woodpecker (Picoides borealis).
http://www.fws.gov/rcwrecovery/rcw.html (Accessed August 2016).
U.S. Fish and Wildlife Service. 20161. West Indian Manatees in North Carolina.
http://www.fws.gov/nc-es/mammal.html (Accessed August 2015).
U.S. Fish and Wildlife Service. 2016j. Seabeach Amaranth (Amarathus pumilus).
http://www.fws.gov/nc-es/plant/scabamaranth.html (Accessed August 2016).
U.S. Fish and Wildlife Service. 2016k. Rufa Red Knot (Calidris canutus rufa).
https://www.fws.gov/northeast/redknot/pdf/Redknot_BWfactsheet092013.pdf (Accessed
August 2016).
U.S. Geologic Survey. 2011. http://mrdata.usgs.gov/mrds/ (Accessed August 2016).
Webster, W.D., J.F. Parnell, and W.C. Biggs, Jr. 1985. Mammals of the Carolinas, Virginia, and
Maryland. Chapel Hill: The University of North Carolina Press. 255 pp.
18
Grants Creek — Jacksonville DOW Line
Environmental Services, Inc.
Appendix A
Figures
19
Grants Creek — Jacksonville DOW Line
1 '1-, 0, Ilk
1 -
I $de N
s NAl
•• � ♦ �'� % f tab. � Aso
J -
INI
m
ero
lilt' 0
_.;
ra, •. ea �—f �. i
w
�
Q
Project Study Area
LL
{
0 1,000 2,000
f
J
Feet
+Aw � -
- ��� t
Cfl
o m
O
N
>
Q�
N
U)
Y
3
2,
0-0
W
E
°�
U
O
0 0
E
�Cr
U
OA O
>+ C 3
C tll 0)
O
O 2
N 0 O
O
._U 7
_ �
Q N .0
7 O_
af
U
O_ O
0
O >
IL
O m
oU
i5E�
oU)
c/) Z
o 0
E
C
0 �,
oY
N vi.0
=
a)
�0 0
Qa
>
3 0
0) M
zCO
0 0
N
N
0o
c
EL �
m o
2
3
0 0 0
CO
•� U
O
N
u'
O m
o
O
0)U
E
�
O O
y Z
(n
~
O
�
N
(1) o
U
Z:)
E C
a 1
�
U
4-1
i
00
Val
on
x� Ei3
Z
� v
Or
W
3
p
r ••
a �� � / r� u . � I • •
r a
r � I •.•
s• pARy f �■ T � 11 r• � r / r � •• • ,tea . �-ti�� .; b--
'P A~• ��i� r @ 17
J J f � y .a_• � '
1 a �
r
pt'•} � - I i'r' •• 1
���{; • OO � $ �� M •� � 'Sim � ►~' 069
s - Mo4.le Home PWk
L y '�'• •r
ti
� •,
o �
�y 4 �
f c� ' 1 i � M _ �, a ■• a
f + �
t Um. 0�1;I�
� � R
R
b y• I P 1
Jk
_•• a lJ n 'y�ffl f 1� IP
IL
� rl f; � • �a o � a` +rt �
_ • �` � rya
i f .,G -} s� 4 vim• �. e
r ♦ AL u
It
41,
D— � `Jl5 •��� • .... �� _ �S _ --Tf O •«i7 - . r� . _ems} _� � v
y%��Q
�f i � �� �� � { 17� r � •'e' ■ _' � �14i1 + •err *a ��► .R==- _ - _ _
�•e �a� �. i I 1
QProject Study Area �, o, `• •~ _ ems:,: ; ,•• �. r �41i"I
0 1,000 2,000 �T
Feet
w
cs7
=
o (U
O
N
LO
Y
Q�
U)
Y
o
W
E
O
°�
U
O
IL
0
0
LL
�0
�M
�M
U _0
aa))°?O
O
_ 7
U)
Q (n.0
O
U
QQ
0
O
a)
d
0
_ N
o U
6 E
o
U) Z
o
� E
Q �
m
�
off m
ai
� Y
.N vi .o
(6
Q 0
w Qa
O O
� 0)z
z 2
0
0C
a'�0
N CO
N O
U
��
E��
m o
3
C O O
CO
'� U
O
ul
0
O m
�0)O
_
rn
E
U 0 O
O y Z
Cr
(D� u)
s o
+J
U)
~
U
N
Z
E C
d
0
U
4-1
� o
LEJ
3
1 •vv �' � ti � ti7 f
* Y N• .4 ` Y 1427 �J .. ranw s
1427. ` v •l i x;-- _ .:s I;
/ t1 .1423 !
0 r ��L-0-0-0-0-0-0......"''''ssssss"""""�y�TT�C���CVU�TT��� CVU� . C_ ' M • � _ � - -� - � . h
Ilk
■ u _� _ram � 1
51 et
•e.
1423
a
r
n ,,`'
■ + n �
■ n . <d u
A403
�- N.• - �. _ — � +{ Q _ t�-. "r, • � is a � ' '�� as �t1 ''.,
r� q _ �� a � ❑ '� aA ' _
+ •o A ~ � � I f�:y. L � rl
y�` .. _ _ g '*■ �.' • = r� r�� �u IN
Ilk
f. - ti 4 .• ° A ' B u rH/Lr-r__r. p+ r r',' - _- -__ rss�
til U -
�. rr ifof
ce r �•.
AO
do
to
7 q
■ 4
�_ a �_:=��=s=x=• au n
-60
0 J T�(
QProject Study Area --� i� - Lis` / C�
0 1,000 2,000 °
I
Feet
V\ f
m
co
_
v
om
O
N
o
a
Y
LU
>
Q2
a)
Cn
Y
3
2 2,
0-0
W
E
� a)
t
U
o
lu >
0
a)
C
7
a)
-o o
0
0
LL
Cr
mom
U
fOn O
> C 3
C to �
-O N
�
O N
-0
U
�o
O
_ 7
U)
2-n .0
7 N Q
Q Q
2
'L
o U
o U
U) Z
o 0
L
CL
a)
oCD
.0
0
0 O
N U)
J
as
rn52
C
fn EL
\
0 0
Z
Z 2
CO
N O
U
a)!�
m 0
2�
3
C O O
CO
•� U
O
u) rn
O m
�o)
0 =
0
rn
U 0 0
as
o00
0 y z
C
a
a) n
+J
U)
~
U
�
n
°� o
U
C
a 1
iR
0
0
Ate,
O
UW
i
IN
IN
0
IN
�
y o
011 0 0
W�
�LLJ1.1
ss
Jr-
3
016
jPF
{ . r -•tea �` .a F��4 R '�._' '
.. c+ *RF
r' ti i kti5
•f
lop
y
f 10 r .
AJ *
*F �
oEvaluation Area A
�J 125ft Easement -
® Jurisdictional Wetland
® Jurisdictional Surface Water* "I % _
Jurisdictional Stream*
'Location and extent is approximate.
� Y. I LN
Feet17
`* #
Note: Vegetation removal or alteration of soils or hydrology �} 4 f
after initial site evaluation can affect jurisdictional status
and may require re-evaluation of wetland boundaries. 'i { f f� ` ' f s+ _ _. _-'3
0
M
oM
� �
CL
2
o- o
o�
M 2 >
� -
�o�
o
0
m
0
LO
w
0
o
co
�
Z)
Q
�;
o
_
Y
U
o
N
L
0
�LJ
U
O N
O 3
N
N 2.2
CL
OE
C
Q
N
Q
O
=
.3 aTi
O N '
Cr
E
_0U
m
.S
Z m
N
N
oQ
� _
o�
m
C
= O
N .'O
N
O '
U)
N a)N
3 U)
J
�2-o
i
L W
0
N Qd
CL
2 O
N
0
0
U N
a)
CO
O Q
E
U.�O
N c
v7(D
U
EL N
o
-o
�F0
O CO
°� U
O
L
CO r L
O
li0
U) Z
aD -0 N
m
-a
s
CO
o
U
O
a�
le o
N
i O
4-0
'Ln
V
o
C w y�o N
az�
W
w aim
3
3
r
o M
O
N
�
Y
N
t
l
i .
i>
O
LO
0
Z)
Q
N
� .#4k 4
CL
o
Oz
0
��
# * - .:���
0
iL
.-
w
N 0
•
•
W8
y
#
.0 Y
O
U) C
O N
o
QQ
i
i
zM
N
m �
U13
U)
Eon
o
A.
/S6 r
'
H +
o<
g
MU)
o
N�o
aU)
0
d%
_J
r
rr ' P
r-
rnw
D Qa
o .�
52
O
00, f
U N
N T
O O
M
CO
F
c '
U)
Q 0)0
C N
Qi O
.,. L*''
C ate,
LL NZ
he
S3CO
OC
„
*
®
X t
er
.N
O
-
- + _y "*� Jam, '
'
f• f F
�+
dr
.
•~
-�
Y
FF!
_
+
}. r k7
cot'
�R
`1
: '
V
W 6Ab
y
.C-
IL
Evaluation Area
Pff �� y#.4#
125ft Easement
,'�
z •_
® Jurisdictional Wetland*
® Jurisdictional Surface Water
Jurisdictional Stream
VIA
' r : tV11,11 .14o
E
*Location and extent is approximate.
0 250 500
w
W
Feet
Note: Vegetation removal or alteration of soils or hydrology
after initial site evaluation can affect jurisdictional status
boundaries.
s,�.'t ;* ;_4, 14
N �� ~ " ti ` .-'} # ; + 4 t ...:
.,� F
*� err
pip3
y`
yL
Ow swab
and may require re-evaluation of wetland
r- ," ,k _ ��"
l
O1
S13
_ � 1
Ye
V. `�.
f
E
'4 `+
oEvaluation Area
�,. 41
�J 125ft Easement
-S14
® Jurisdictional Wetland*--
® Jurisdictional Surface Water*
Jurisdictional Stream*
'Location and extent is approximate.
0 250 500
Feet
Note: Vegetation removal or alteration of soils or hydrology
after initial site evaluation can affect jurisdictional status
and may require re-evaluation of wetland boundaries.
f S16
S15 '
-may
co _
O N
N Y
O Z
Lt7 Q
LU O
Y
L
t U
2 0)
- 0 0 ii
W
J
O
M CO
*4
(D 0
U) (0
U
N C O
L.L U) Z
CO 7
0
N �
C, Ate, O
W �
L O
N
V
a
0
i
" Y
S19
OS17
k rS
oEvaluation Area
125ft Easement
® Jurisdictional Wetland*
® Jurisdictional Surface Water*
Jurisdictional Stream*
'Location and extent is approximate.
0 250 500
Feet
Note: Vegetation removal or alteration of soils or hydrology
after initial site evaluation can affect jurisdictional status
and may require re-evaluation of wetland boundaries.
-- ----- -- -- H- ----
W
CO
O
M
N
m o
U
CO r
(2) p o
LL U) Z
CO 7
0
N �
Ate, O
W 5
i O
N
C
M
'Ln
V
h
oEvaluation Area
125ft Easement
® Jurisdictional Wetland*
® Jurisdictional Surface Water*
Jurisdictional Stream*
'Location and extent is approximate.
0 250 500
Feet
Note: Vegetation removal or alteration of soils or hydrology
after initial site evaluation can affect jurisdictional status
and may require re-evaluation of wetland boundaries.
7
t
W
M
N
m .o
� U
� �
N Z
N �
C, Ate, O
W �
i O
N
V
g
10
r i
J r A
oEvaluation Area
125ft Easement
® Jurisdictional Wetland*
® Jurisdictional Surface Water*
Jurisdictional Stream*
'Location and extent is approximate.
0 250 500
Feet
Note: Vegetation removal or alteration of soils or hydrology
after initial site evaluation can affect jurisdictional status
and may require re-evaluation of wetland boundaries.
S27a
S27b
I'l
O M
m >
Q�
a�
o `O
O (6
U rn>
2 2
o 2-
0
� o �
U
O o
U�
a�
N O
O N
Q U O
7 O Q
Q Q i
(6 0
� O N
O
m E
E O U
O C
t U J
L -
U
N O
�U)U
=0�
� CL
Qa
o �
0
U 'iceO
Q C a)
0 0 U)
0 o 0
o
)
O � N
N U
L �6 'U
-
.. U
a�
E O
m w
U
Mn -o
co =
O N
N Yo 0)
LO Q
W
t
t U
W
0
M CO
N
m o
U
N C O
L.L U) Z
CO 7
U
N �
Ate, O
W U
C
i O
N
M
'Ln
V
y
'k
1$ * � "11�
2h"'
AL
F -
oEvaluation Area
�J 125ft Easement
® Jurisdictional Wetland*
® Jurisdictional Surface Water*
Jurisdictional Stream*
'Location and extent is approximate.
0 250 500
Feet
Note: Vegetation removal or alteration of soils or hydrology
after initial site evaluation can affect jurisdictional status
and may require re-evaluation of wetland boundaries. r
w =R��+ r - .r t ...... 7 . � wF: 4 ' wi � T� �� �7s.� �.'� .'''''. - - . mow!••' �
ik
Ll4� �.. , 'r.# F:- ti•.ti .. �- f4*'-n{ S':4
V
CIF *_1��� .t` •n��r4,'��':�"�titi'`,'-•'�`�' 1�y `�
' ►�,+, 4s 4# # 4 '�4- -}'R_ Fky.:� � -� ..:.■' _ T rY �}r i 7'7 - •IL4
i+�iT,"S ���� w�.'y' �J' ��� �*•fiY'k`"_'4 ': i�''4* � i'--'+��r .�4*��+�k4x 'T1+3 ti� - � "
. t � r .b. ,�'� � � JJ�+ � "* 1.�':• '�' +•.}* 4� k`. Lam., r41 �Y s'' •1'- � � y•P'_'•� S it;t
r j' r. �,a�ti'C .�
w _* * � i , w: #a ti'� :-'� �`-� •� *;'� i��. .J; _ .'!.r _ . 'lx � -: , .'4y�y.� soh. ?'M rr ��-•.'. i �'+..�_i�- � � ir- rt. } f.
'. rk'`:.�, -_
'.`','
.k '•rw .. •.' �- 't .''~` +,_ tilt +�' T'rr•_' •' V',ti
y4`�. 5: f /+4.' `x,7 �: '{y �'C.' .+.� µ�'� �.' �t _ � ; ♦.•y... n` ter` � :�' �.- �i'r, 44 y
��, jy. # i• � 4 � _ ` {i+�i � ., +-w i \ 4 . � +l ,A_';•'+'rt '� � isti - } M1" � * �
'T}` '`}�f x.•
S ,+ i }_. r V _ 4.'�,~'- F. 1' Nam, T 4 .*lt ti _. - i •' -'�'k '%�. ��f * _.i `..f[Y
�x � � - 1 • i'x'.',v �
��
r
L
r
O M
a) N
(6 >
Q
a) T
CL `o
o m �
D
u) rn'L
M
-0 o
� o �
C Ul
o' o
u,
a�
a)� O
O a)
Q N O
7 O Q
Q Q i
a5 C: 0
O N
O
m E
E O U)
O E
N J
L —
O � Lp
N '0
N.O
a� a) rn
3oaa)
O-O
Mn Ca
0 .S
O �
E
U .0O
Q � a)
O N 7
0 O o
o —
t 0)
Ea'o
a� D
s as '—
.. U)a`)
E O
as w
U'
N
L
Ez
LU
W
\J
CD
M CO
*4
(D 0
U) (0
U
N C O
LL U) Z
CO
0
N �
O
� O
L O
U
C
M
'Ln
V