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October 31, 2005
Mac Haupt
North Carolina Ecosystem Enhancement Program
1652 Mail Service Center
Raleigh, NC 27699-1652
Michael F. Easley, Governor
William G. Ross Jr., Secretary
North Carolina Department of Environment and Natural Resources
Alan W. Klimek, P.E. Director
Division of Water Quality
Re: Roquist Wetland Restoration Plan Phase I, Bertie County, NC (DWQ# 20051680)
Dear Mr. Haupt:
DWQ has reviewed the "Roquist Wetland Restoration Plan Phase I, Final Plan August 2005"
prepared by Hayes, Seay, Mattern and Mattern (HSMM). Several questions or concerns arose
upon review of the document.
1. The monitoring plan (p.19) should read, "Monitoring of wetland restoration efforts
will be performed for five years or until success criteria are satisfied, whichever is
longer."
2. Figure 2 depicts several logging staging areas. These areas are usually heavily
compacted and laden with logging debris. These areas will need work to receive any
mitigation credits. It may be possible to receive restoration credit for these areas if
logging debris is removed, the soil is ripped to remove the compacted areas, and
vegetation is planted.
3. The mitigation credits received for Preservation areas are determined based on the
quality of the preservations areas. Early succession sites, like the areas clear-cut in
2003, will not receive high mitigation credits. These credits could be greatly
increased by planting favorable species to enhance these areas.
4. The majority of the proposed well locations are located in close proximity to each
other and in the areas with the lowest elevation on the site. Some of the well
locations need to be placed in areas with higher elevations where hydrologic success
may be more of an issue (e.g. end of B1 and B3). Spreading out the wells will also
give abetter indication of how various areas of the site are doing. Please propose a
modified well location plan to address this issue.
5. It is not necessary to have numerous reference wells in the same type of reference
wetland. It is necessary to have one or two reference wells in mature reference
wetlands of each type. Please modify your plans accordingly.
6. Vegetation monitoring should be done during the growing season, not afterwards.
This will allow for a more accurate assessment of the percent cover of each species
and the health of the vegetation.
401 Oversight/Express Review Permits Unit
1650 Mail Service Center, Raleigh, North Carolina 27699.1650
2321 Crabtree Boulevard, Suite 250, Raleigh, North Carolina 27604
Phone: [phone] FAX [phone]/ Internet: httn://h2o.em•.state.nc.us/newetlands
one
N Carolina
Nt ura!!y
An Equal Opportunity/Affirmative Action Employer- 50% Recycled/10% Post Consumer Paper
7. The number and location of the vegetation plots should be specified. Also, discuss
what information will be collected at each vegetation monitoring location and how it
will be reported.
These comments are made with the hope of establishing a successful wetland mitigation project.
Please contact Amanda Mueller of my office [phone] should you have any questions or
need further assistance.
Cc: Hayes, Seay, Mattern and Matte
Kyle Barnes DWQ-Washington
File Copy
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Regional Office

ROQUIST WETLAND RESTORATION PLAN2 0 0 5 1 6 8 0
PHASE I
BERTIE COUNTY
NORTH CAROLINA
RECEIVED
AUG Z R 2005
NCECOSYSTEM
EM ANCEME fPROGRAM
Prepared for:
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NORTH CAROLINA DEPARTMENT OF ENVIRONMENT
AND NATURAL RESOURCES
ECOSYSTEM ENHANCEMENT PROGRAM
RALEIGH, NORTH CAROLINA
FINAL PLAN
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i
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
TABLE OF CONTENTS
1.0 INTRODUCTION .............................................................................................................1
2.0 GOALS AND OBJECTIVES ...........................................................................................1
2.0 LOCATION INFORMATION ........................................................................................ 3
3.0 EXISTING CONDITIONS .............................................................................................. 3
3.1 PHYSIOGRAPHY, SITE HISTORY, AND LAND USE ............................................................. 3
3.2 WATER RESOURCES ......................................................................................................... 5
3.2.1 Streams ....................................................................................................................5
3.2.2 Wetlands ..................................................................................................................5
3.3 SOILS ............................................................................................................................... 5
3.4 PLANT COMMUNITIES ...................................................................................................... 7
3.4.1 Nonriverine Swamp Forest ...................................................................................... 9
3.4.2 Nonriverine Wet Hardwood Forest ...................................................................... 10
3.4.3 Mesic Mixed Hardwood Forest (Coastal Plain Subtype, Upland Flat Variant).. 10
3.4.4 Pine Plantation ..................................................................................................... 11
3.4.5 Old-Field ...............................................................................................................11
3.4.6 Clear-Cut (Early Succession) ............................................................................... 12
3.5 FEDERALLY PROTECTED SPECIES .................................................................................. 12
3.6 FEDERAL SPECIES OF CONCERN ..................................................................................... 13
4.0 REFERENCE WETLANDS .......................................................................................... 13
4.1 VEGETATION .................................................................................................•................13
4.2 HYDROLOGY ..................................................................................................................13
5.0 RESTORATION PLAN .................................................................................................14
5.1 WETLAND RESTORATION ............................................................................................... 14
5.1.1 Hydrology ............................................................................................................. 14
5.1.2 Soils .......................................................................................................................14
5.1.3 Vegetation ............................................................................................................. 17
5.2 WETLAND PRESERVATION ............................................................................................. 19
5.3 UPLAND PRESERVATION ................................................................................................ 19
6.0 MONITORING PLAN ...................................................................................................19
6.1 HYDROLOGY .................................................................................................................. 19
6.1.1 Hydroligic Monitoring .......................................................................................... 20
6.1.2 Hydrologic Success Criteria ................................................................................. 20
6.2 VEGETATION ..................................................................................................................20
6.2.1 Vegetation Monitoring .......................................................................................... 20
6.2.2 Vegetation Success Criteria .................................................................................. 20
6.3 REPORT SUBMITTALS ..................................................................................................... 22
6.4 CONTINGENCY ............................................................................................................... 22
7.0 MITIGATION VALUES ............................................................................................... 22
8.0 REFERENCES ................................................................................................................23
EEP 1 August 2005
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
LIST OF FIGURES
FIGURE 1 SITE MAP ......................................................................................................................... 2
FIGURE 2 PROPERTY BOUNDARY AND SOILS MAP .......................................................................... 4
FIGURE 3 WETLAND BOUNDARY .................................................................................................... 6
FIGURE 4 PLANT COMMUNITIES ...................................................................................................... 8
FIGURE 5 PHASE I RESTORATION AREAS ....................................................................................... 15
FIGURE 6 CROSS SECTION SURVEY LOCATIONS ............................................................................ 16
FIGURE 7 PROPOSED PLANT COMMUNITY LOCATIONS .................................................................. 18
FIGURE 8 GROUNDWATER GAUGE LOCATIONS ............................................................................. 21
LIST OF TABLES
TABLE 1. ROQUIST WETLAND RESTORATION SITE MAPPED SOILS ................................................. 7
TABLE 2. ROQUIST WETLAND RESTORATION SITE PLANT COMMUNITIES ....................................... 9
TABLE 3. FEDERAL SPECIES OF CONCERN FOR BERTIE COUNTY, NC ............................................ 13
TABLE 4. PHASE I MITIGATION ACREAGES FOR THE ROQUIST WETLAND RESTORATION SITE ...... 23
LIST OF APPENDICES
Appendix A ....................................................................................................................Photographs
Appendix B ....................................................................._........_._.._ -...Jurisdictional Determination
EEP ii August 2005
ROQUIST RESTORATION SITE WETLAND RESTORATION PLAN

1.0 INTRODUCTION
The North Carolina Ecosystem Enhancement Program (EEP) is developing a regional wetlands
mitigation site in eastern North Carolina. The Roquist Wetland Restoration Site (hereafter
referred to as "the Roquist Wetland Restoration Site" or "the Site") is located in western Bertie
County south of Lewiston-Woodville, North Carolina within Hydrologic Unit 03010107 of the
Roanoke River Basin (Figure 1).
The Roquist Wetland Restoration Site is a unique ecosystem hosting prime examples of
nonriverine wetland communities in large, nearly intact tracts. The Site encompasses 3,926 acres
(ac) positioned on the interstream divide of the Roanoke and Cashie Rivers. Historically, the
Site was known as a pocosin primarily for its geologic setting rather than its vegetative
composition. The Site is almost entirely comprised of Nonriverine Swamp Forest and Wet
Hardwood Forest Communities with relatively smaller portions of Mesic Mixed Hardwood
Forest Communities (Schafale and Weakly 1990) positioned along the margins of the vast flat.
Historic activities in the Site include intensive logging and some conversion of wetland
hardwood forests into pine plantation. These efforts required constructing elevated roads for
access into the area in addition to ditching in order to drain the site for ease of timber removal.
Although the Roquist Wetland Restoration Site has been heavily timbered for nearly a century,
there remains approximately 390 ac of high quality old growth forest harboring specimens of a
rare 95+ years of age. The old growth forest forms a contiguous Nonriverine Swamp and Wet
Hardwood (Schafale and Weakly 1990) stand that is uncommon to be of this age and size.
2.0 GOALS AND OBJECTIVES
Due to the magnitude of the restoration effort for the Roquist Wetland Restoration Site, the
project will be divided into two major phase's (hereafter referred to as Phase I and Phase II).
Restoration components planned for Phase I of the Roquist Wetland Restoration Site consist of
restoring ditched and filled wetlands, and preserving existing Nonriverine Swamp Forest,
Nonriverine Wet Hardwood Forest, and Mesic Mixed Hardwood Forest Communities.
Restoration components planned for Phase II of the Roquist Wetland Restoration Site will
consist of restoring the remaining (53 ac) ditched and filled wetlands. Specifically the proposed
mitigation credits for Phase I consist of.
• restoration of 52 ac of previously ditched and filled nonriverine wetlands
• preservation of 3,776 ac of nonriverine wetlands
• preservation of 45 ac of uplands
EEP 1 August 2005
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SITE MAP
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 1
ROQUIST WETLAND RESTORATIONSITE WETLAND RESTORA TION PLAN
2.0 LOCATION INFORMATION
The Roquist Wetland Restoration Site is located in Bertie County within Hydrologic Unit
03010107 of the Roanoke River Basin along the interstream divide of the Cashie and Roanoke
Rivers (Figure 1). The Roquist wetland forms the headwater basin of Roquist Creek and Indian
Creek.
3.0 EXISTING CONDITIONS
3.1 Physiography, Site History, and Land Use
The Roquist wetland is a broad flat, elliptical in shape, and extending roughly 3.5 miles (mi)
wide by 4.0 mi long (14 mi2). The drainage area is approximately 13,700 ac. Land use
surrounding the wetland is mostly comprised of agriculture crops and pine plantations. The Site
itself lies almost entirely within the limits of the wetland with some portions extending to the
periphery (Figure 2). Ninety percent of the Site is 42 feet (ft) above mean sea level (msl) with a
gradual rise to 54 ft above msl forming the rim. The highest elevation reaches 78 ft above msl
and is located within the small stream basins (Jack's Branch) located in the northern portion of
the Site.
Timber records from International Paper indicate the Roquist Wetland Restoration Site has been
timbered for nearly a century with the oldest stands being established in 1905 and 1910.
However, the majority of the existing forest within the Site ranges from twelve to sixty years of
age. The most recent timbering activities occurred in 2003 with a final 927 ac harvested from
April to October. In addition, logging records reveal an 80-ac pine plantation was established
within timbered wetlands near the western entrance of the Site. Timbering in the Roquist
wetland required elevated logging roads to be constructed throughout the Site to aid in removal
of timber. Aerial photographs of the Site indicate that five miles of logging roads were present
as early as 1964. These roads include ditches located adjacent and perpendicular to the logging
roads ranging in width from 2 to 25 ft. Presently, 12 mi of logging roads traverse the Site
including a small segment in the north.
EEP 3 August 2005
1-11).11ci1 cl I lei It
PROPERTY BOUNDARY
& SOILS MAP
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 2
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
3.2 Water Resources
3.2.1 Streams
There are three jurisdictional streams located within the Site. These streams include Jack's
Branch (DWQ Index Number 24-2-7-1, Class "C Sw"), Roquist Creek (DWQ Index Number 24-
2-7, Class "C Sw"), and Indian Creek (DWQ Index Number 23-47, Class "C") (Figure 2,
Appendix A). On the USGS topographic map (Figure 1) Jack's Branch appears to have a
continuous channel through the Roquist wetland and connecting with Indian Creek. Historically
this may have been accurate but field investigations (2003) of Jack's Branch revealed no
continuous channel through the Roquist wetland. Non jurisdictional surface waters observed
within the Site include drainage ditches located adjacent to and perpendicular to the existing
logging roads.
3.2.2 Wetlands
The Roquist Wetland Restoration Site is almost entirely comprised of an extensive wetland
system. Specifically, the wetland accounts for 99%, or 3,881 ac of the Site. Based on field
observations, the wettest hydrology is localized within the center of the Site where the lowest
recorded elevations (41.5-42 ft above msl) occur. These areas experience more frequent and
deeper inundation when compared with the adjacent wetland areas. Presumably this is due to the
influx of water from the surrounding uplands. Relatively drier wetlands are located along the
margins of the Roquist wetland where elevations are slightly higher (43-45 ft above msl) than
elevations within the central flat. Environmental scientists of Hayes, Seay, Mattern and Mattern,
Inc. (HSMM) delineated the wetland/upland boundary along the proposed mitigation areas from
October 20 to 28, 2003 using the methods described in the 1987 U.S. Army Corps of Engineers
(USACE) Manual, Field Guide for Wetland Delineation (Figure 3). The jurisdictional
determination was received from the USACE on February 11, 2004 (Appendix B)
3.3 Soils
The Bertie County Soil Survey (USDA 1990) indicates the Site is underlain by nine soil series
(Figure 2). These soils include: Bibb and Johnston loam, Bonneau loamy sandy, Leaf sandy
loam, Lenoir fine sandy loam, Lynchburg sandy loam, Norfolk sandy loam, Pantego loam, Rains
sandy loam, and Roanoke fine sandy loam. Of the nine soil series, Leaf soil accounts for the
majority of the Site and is almost entirely confined to the central flat of the wetland. Soil series
EEP 5 August 2005
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WETLAND BOUNDARY
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 3
ROQUIST WETLAND RESTORATION SITE {WETLAND RESTORATION PLAN
mapped in the restoration areas were field verified by environmental scientist of HSMM on
December 3, 2003. Table 1 describes the drainage class and hydric classification for each of
these soils.
Table 1. Roquist Wetland Restoration Site Mapped Soils
Soil Name Map
Symbol Percent
Slope Drainage Class
b Hydric
Class
Bibb and Johnston loam BB 0 to 2 Poorly to very poorly drained Hydric
Bonneau loamy sandy BoB 0 to 6 Well drained
Leaf loam Lf - Moderately well to somewhat poorly drained Hydric
Lenoir fine sandy loam Ln - Somewhat poorly drained
Lynchburg sandy loam Ly - Somewhat poorly drained
Norfolk sandy loam NoB 2 to 6 Well drained I Non-Hydric
Pantego loam Pa - Very poorly drained Hydric
Rains sandy loam Ra - Poorly drained Hydric
Roanoke fine sandy loam Ro - Poorly drained Hydric
T ?)oiis navmg nyaric inclusions.
3.4 Plant Communities
The Classification of Natural Communities of North Carolina, Third Approximation (Schafale
and Weakley 1990) was used to categorize the Site's natural plant communities. Consequently,
the following natural communities were identified within the 3,926-ac Site: Nonriverine Swamp
Forest, Nonriverine Wet Hardwood Forest, and Mesic Mixed Hardwood Forest (Coastal Plain
Subtype). These communities are listed in the North Carolina Natural Heritage Program's
(NCNB?) database for Natural Communities within the Roquist Nvetland. Floristic communities
that could not be classified according to Schafale and Weakley (1990) included pine plantation,
old-field community, and clear-cut areas (early succession) (Figure 4, Table 2, and Appendix A).
EEP 7 August 2005
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PLANT COMMUNITIES
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 4
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
Table 2. Roquist Wetland Restoration Site Plant Communities

Plant Community
Acres Percent
of
Total Area
Nonriverine Swamp Forest 769 20
Nonriverine Wet Hardwood Forest 751 19
Mesic Mixed Hardwood Forest 23 1
Pine Plantation 46 1
Old-Field 981 25
Clear-Cut (Early Succession) 1,251 32
Logging Roads and Ditches* 105* 2*
Total 3,926 100
* Non-plant community accounting for the remaining area.
3.4.1 Nonriverine Swamp Forest
Nonriverine Swamp Forests observed in the Roquist Wetland Restoration Site comprise
approximately 20% or 769 ac of the property. Schafale and Weakley (1990) state that
Nonriverine Swamp Forest communities typically occur in very poorly drained upland flats but
the origin and dynamics of these communities are not well known. Presently, the Nonriverine
Swamp Forest community consists of a mosaic of forest stands varying in age due to historic
timbering activities. This community can be divided by stand age, including approximate
acreage, into three groups: 10 to 30 years (240 ac); 30 to 70 years (139 ac); and 70 to 100 years
of age (390 ac). Overall, the existing Nonriverine Swamp Forest community is centrally located
within the flat and is distinguished biotically and abiotically from the peripheral, slightly
elevated Nonriverine Wet Hardwood Forests. Nonriverine Swamp Forests differ from riverine
swamp communities by source of water and topographic position. In Nonriverine Swamp
Forests, upland run-off and water table fluctuations account for the majority of the flood source
rather than from river flooding events or back-water (Schafale and Weakley 1990).
Timbering activities have influenced Nonriverine Swamp Forest plant species composition
within the Roquist Wetland Restoration Site. Thus, stands of varying ages are dominated by
varying canopy, shrub, and/or herbaceous species. The following is a list of the dominant
vegetation for the mature Nonriverine Swamp Forest within the Site: CANOPY - bald cypress
(Taxodium distichum), black gum (Nyssa sylvatica var. biflora), green ash (Fraxinus
pennsylvanica), laurel oak (Quercus laurifolia), red maple (Acer rubrum), swamp tupelo (Nyssa
sylvatica var. biflora), sweet gum (Liquidambar styraciflua), water tupelo (Nyssa aquatica), and
willow oak (Quercus phellos); SUBCANOPY - iron wood (Carpinus caroliniana), red maple,
EEP 9 August 2005
'100 ROQUIST WETLAND RESTORA TION SITE WETLAND RESTORATIONPLAN
and sweet gum; SHRUBNINE - greenbriar (Smilax rotundifolia), muscadine grape (Vitis
rotundifolia), sweet pepperbush (Clethra alnifolia), and trumpet vine (Campsis radicans);
HERBACEOUS - lizard's tail (Saururus cernuus), netted chainfem (Woodwardia areolata), and
royal fern (Osmunda regalis).
3.4.2 Nonriverine Wet Hardwood Forest
Nonriverine Wet Hardwood Forests observed in the Roquist Wetland Restoration Site account
for approximately 751 ac, or 19% of the Site. This community was once common in Eastern
North Carolina but is now considered threatened due to logging and the ease of converting this
community to farmland or pine plantation by draining. Few of these communities are left, thus,
preservation is highly valued. The Site contains large tracts of high quality Nonriverine Wet
Hardwood stands adding to the importance of preservation.
Nonriverine Wet Hardwood Forests are located within the Site along the margin of the vast flat
and are distinguished from the central Nonriverine Swamp Forest by a gradual elevating
topography. Schafale and Weakley (1990) describe this palustrine community as occurring in
poorly drained interstream flats and having fine textured mineral soils. Specifically, these
communities commonly occur on the margins of wetlands. Nonriverine Wet Hardwood Forests
are distinguished from Nonriverine Swamp Forests by relatively drier conditions and by the
predominance of bottomland oaks or mixed hardwood species. Nonriverine Wet Hardwood
Forests are distinguished from Mesic Mixed Hardwood Forests (Coastal Plain Subtype) by
relatively wetter conditions and the presence but not dominance of swamp species (Schafale and
Weakley 1990).
The following is a list of the dominant vegetation found in Nonriverine Wet Hardwood Forests
within the Roquist Wetland Restoration Site: CANOPY - laurel oak, red maple, swamp chestnut
oak (Quercus michauxii), swamp tupelo, sweet gum, and willow oak; SUBCANOPY -
American holly (Ilex opaca), red maple, and sweet gum; SHRUBNINE - grape (Vitis spp.),
poison ivy (Toxicodendron radicans), and trumpet vine; HERBACEOUS - false nettle
(Boehmeria cylindrical), lizard's tail, and netted chainfern.
3.4.3 Mesic Mixed Hardwood Forest (Coastal Plain Subtype, Upland Flat Variant)
Mesic Mixed Hardwood Forests account for a small portion of the Roquist Wetland Restoration
Site, roughly 23 ac, or one percent of the total acreage. Mesic Mixed Hardwood communities
within the Site are considered of the upland flat variant, an ecotone to Nonriverine Wet
Hardwood Forest, consisting of both hydrophytic and upland mesic plant species (Frost 1990).
This community occurs near the margin of the Site surrounding Nonriverine Wet Hardwood
EEP 10 August 2005
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATIONPLAN
Communities. Schafale and Weakley (1990) describe this community as being distinguished
from Nonriverine Swamp Forests by relatively drier conditions and the dominance of upland
rather than wetland species. Mesic Mixed Hardwood Forests are distinguished from Nonriverine
Wet Hardwood Forests by relatively drier conditions and the dominance of upland mesic species
(Schafale and Weakley 1990). The vegetative distinction between Mesic Mixed Hardwood
Forest and Nonriverine Wet Hardwood Forest is most likely due to small differences in
microtopography between the two communities (Schafale and Weakley 1990). Within the
Roquist wetland, Mesic Mixed Hardwood Forests presumably undergo relatively drier conditions
than Nonriverine Wet Hardwood Forests.
The following is a list of the dominant vegetation found in Mesic Mixed Hardwood Forests
within the Roquist Wetland Restoration Site: CANOPY - laurel oak, red maple, tulip poplar
(Liriodendron tulipifera), and white oak (Quercus alba); SUBCANOPY - American beech
(Fagus grandifolia), American holly, red maple, and white oak; SHRUBNINE - greenbriar and
muscadine grape; HERBACEOUS - giant cane (Arundinaria gigantea) and sedge (Carex spp.).
3.4.4 Pine Plantation
Pine plantations represent a minimal portion (one percent, or 46 ac) of the total acreage within
the Roquist Wetland Restoration Site. The existing pine plantation was established in 1993 and
was presumably converted from Nonriverine Wet Hardwood Forest allowing loblolly pines
(Pinus taeda) to establish in relatively drier soil conditions. Roughly, 36 ac of the pine
plantation was bedded in order to elevate the loblolly roots above frequent inundation. Presently,
the occurrence of hardwood species occupying the canopy, subcanopy, and herbaceous layers,
and the presently low quality of the planted pines indicates that the plantation has not been
managed with herbicidal or fertilization treatments. These species included Japanese
honeysuckle (Lonicera japonica), muscadine grape, red maple, swamp chestnut oak, sweet gum,
and trumpet vine.
3.4.5 Old-Field
Old-field communities within the Site include early stages of Nonriverine Swamp and Wet
Hardwood Forests and account for approximately 25%, or 981 ac. These communities were
classified as those that have been intensively logged within 1 to 10 years of the investigation
(October 2003). This community was dominated by herbaceous and sapling species including
American sycamore (Platanus occidentalis), blackberry (Rubus spp.), common boneset
(Eupatorium perfoliatum), devil's walking stick (Aralia spinosa), Eastern false-willow
(Baccharis halimifolia), giant cane, meadow-beauties (Rhexia spp.), red maple, sweet gum, and
tulip poplar.
EEP 11 August 2005
ROQUIST WETLAND RESTORATION SITE
3.4.6 Clear-Cut (Early Succession)
WETLAND RESTORATION PLAN
Clear-cut communities were classified as areas that had been intensively logged within one year
of the Site investigation (October 2003). Clear-cut communities included approximately 32%, or
1,251 ac of the total 3,926 ac within the Site. At the time of the investigation, these communities
were in the earliest stages of forest succession. Plant species observed were those that can
tolerate long periods of inundation and soil anoxia due to the absence of mature canopy species
to aid in water uptake. The clear-cut communities were dominated by herbaceous species
including giant cane, soft rush (Juncus effusus), common reed (Phragmites australis), arrow-leaf
tearthumb (Polygonum sagittatum), wool-grass bulrush (Scirpus cyperinus), and cattails (Typha
spp.). The wettest areas, or areas of deepest inundation, were within skidder trails created by
heavy equipment during logging. Most of these linear pools were absent of vegetation or had
clumps of cattails. American sycamore, Eastern false-willow, red maple, and sweet gum were
the only woody species present within the clear-cut communities with stump sprouts accounting
for the majority of the stems.
3.5 Federally Protected Species
The red-cockaded woodpecker is the only species federally listed as threatened or endangered for
Bertie County, North Carolina. The red-cockaded woodpecker was listed as endangered
throughout its entire range on October 13, 1970. As of June 15, 2005, the NCNHP database for
threatened and endangered species revealed the red-cockaded woodpecker has been observed in
Bertie County within the last 20 years, though none have been observed within one mile of the
Roquist Wetland Restoration Site. The closest known observation of the red-cockaded
woodpecker in Bertie County is within seven miles of the Roquist Wetland Restoration Site near
Burden, NC.
Habitat
Habitat for the red-cockaded woodpecker consists of old-growth open stands of southern pines,
which are utilized for foraging and nesting grounds. The red-cockaded woodpecker shows a
particular affinity for stands of longleaf pine (Pinus palustris). Inhabited stands typically contain
more than 50 percent pine, lack a thick understory, and are contiguous with other suitable stands.
The red-cockaded woodpecker nests exclusively in living pine trees that are greater than 60 years
in age and are contiguous with pine stands that are at least 30 years in age.
Biological Conclusion No Effect
The majority of the habitat observed within the Site consists primarily of swamp hardwood
forests. Although there are pine stands within the Site, none harbor pines greater than 60 years
old, thus not meeting habitat requirements for the red-cockaded woodpecker. Additionally,
EEP 12 August 2005
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
construction activities will be limited to logging roads and roadside ditches in which red-
cockaded woodpecker habitat does not exist. Consequently, construction of the Roquist Wetland
Restoration Site will have "No Effect" on the red-cockaded woodpecker or its preferred habitat.
3.6 Federal Species of Concern
There are four species listed as Federal Species of Concern for Bertie County (Table 3). The
Roquist Wetland Restoration Site includes suitable habitat for three of the four species.
Specifically, habitat for the Eastern Henslow's sparrow includes clear-cut pocosins and other
damp weedy fields [breeding season only] in the North Carolina coastal plain. Habitat for the
Cerulean warbler includes mature hardwood swamp forest (breeding season only) in the North
Carolina coastal plain. Chowanoke crayfish habitat includes streams and rivers occurring in the
Roanoke River drainage (Indian Creek). The Rafinesque's big-eared bat roosts in caves, mines,
and old buildings, none of which occur on the site.
Table 3. Federal Species of Concern for Bertie County, NC
Common Name Scientific Name NC Status Habitat Present
Eastern Henslow's Sparrow Ammodramus henslowd SR Yes
Rafinesque's big-eared bat Corynorhinus ra inesquii SC* No
Cerulean Warbler Dendroica cerulea SR Yes
Chowanoke Crayfish Orconectes virginianus SC Yes
Any species of plant in iNorm uaronna which requires monitoring but which may be collected and sold under regulations
adopted under the provisions of [the Plant Protection and Conservation Act]" (GS 19B 106:202.12). (Special Concern
species that are not also listed as Endangered or Threatened may be collected from the wild and sold under specific
regulations. Propagated material only of Special Concern species which are also listed as Endangered or Threatened
may be traded or sold under specific regulations.)
"SR" A Significantly Rare species is one which is very rare in North Carolina, generally with 1-20 populations in the state,
generally substantially reduced in numbers by habitat destruction, direct exploitation or disease.
# Historic record - the species was last observed in the county more than 50 years ago.
4.0 REFERENCE WETLANDS
4.1 Vegetation
Each wetland community (Nonriverine Swamp and Nonriverine Wet Hardwood) proposed for
restoration has a representative undisturbed forested area as a reference wetland. Tree species
composition (qualitative) was inventoried in both reference communities and used as a guide for
the planting plan. Refer to Sections 3.4.1 and 3.4.2 for species composition information.
4.2 Hydrology
Hydrologic monitoring within reference wetlands will consist of groundwater elevation
observations using water gauges. Remote Data Systems, Inc. model Ecotone WM Series
EEP 13 August 2005
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
automated groundwater monitoring gauges were installed within reference wetlands on May 10,
2005 in accordance with specifications in the Corps of Engineers' Installing Monitoring
Wells/Piezometers in Wetlands (WRP Technical Note HY-IA-3.1, August, 1993). These gauges
will continuously record water level data along a 40-inch gradient once daily for five years.
Groundwater elevations within the reference wetland will be used as the target elevation for the
associated restoration communities.
5.0 RESTORATION PLAN
5.1 Wetland Restoration
Wetland restoration efforts for Phase I of the Roquist Wetland Restoration Site will include 52 ac
of nonriverine wetlands (Figure 5, Plan Sheets 4-8). The proposed restoration efforts will consist
of grading the existing logging roads and spoil areas to their original wetland elevations, filling
the existing roadside ditches to their original wetland elevations, and soil preparation
(ripping/disking) of the restoration areas. Phase II of the wetland restoration effort will involve
grading and filling the remaining roads and ditches (approx. 53 ac) to their original wetland
elevations.
5.1.1 Hydrology
Original hydrologic regime will be restored in the proposed restoration areas by filling roadside
ditches, grading road fill and spoil areas to the original wetland elevations, and soil preparation
(ripping/disking) of the restoration areas. Additionally, impervious dikes will be placed in select
locations within the restored ditch areas to restrict ground water movement through backfilled
ditches. In order to compare existing natural elevations to road, ditch, and spoil area elevations,
cross sections were surveyed approximately every 1,000 ft in the proposed restoration areas
(Figure 6). Natural wetland elevations determined by these cross sections will be used as the
target elevations in the restoration areas. Elevation surveys will be conducted throughout the
construction process in order to meet target elevations.
5.1.2 Soils
All soils utilized for construction within the restoration areas will consist of in situ soils. If there
is material that is unsuitable for backfilling, it will be disposed of offsite and imported soil will
be used to back fill the ditches. Additionally, if unsuitable materials exist in the soil below
original ground elevations, these materials will be removed and replaced with imported soil. The
restoration areas will be graded and ripped/disked following construction activities.
EEP 14 August 2005
tr'l`i
OSI'Stem
MITIGATION AREAS PHASE I
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 5
I•
rA?j
Ems I
CROSS SECTION LOCATIONS
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 6
•
ROQU1ST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
5.1.3 Vegetation
The proposed wetland restoration areas will be planted with trees in the form of bare-root stock.
Planting will be performed between December 1 and March 15 while stock is dormant using a
minimum stem count of 680 stems per acre. This translates to planting on approximately 8-foot
centers. The restoration areas will be planted with either a Nonriverine Swamp Community or
Nonriverine Wet Hardwood Community. The proposed plant community to be planted in the
restoration areas will be determined by the existing plant community surrounding that location
(Figure 7). In the restoration areas where the surrounding plant community is a clear cut or old
field community, the proposed plant community to be planted will be determined by the plant
community that existed prior to timbering. Tree species to be planted within the Nonriverine
Swamp Community will be consistent with those species located within the reference wetlands
(refer to section 5.0) and derived from the following list (as available):
• Fraxinus pennsylvanica (green ash)
• Nyssa sylvatica var. biflora (black gum)
• Quercus laurifolia (laurel oak)
• Quercus michauxii (swamp chestnut oak)
• Quercus phellos (willow oak)
• Taxodium distichum var. distichum (bald cypress)
Shrub species to be planted within the Nonriverine Swamp Community will be consistent with
those species located within the reference wetlands (refer to section 5.0) and derived from the
following list (as available):
• Carpinus caroliniana (iron wood)
• Clethra alnifolia (sweet pepperbush)
• Vaccinium conymbosum (highbush blueberry)
Tree species to be planted within the Nonriverine Wet Hardwood Community will be consistent
with those species located within the reference wetlands and derived from the following list (as
available):
• Nyssa aquatica (water tupelo)
• Quercus laurifolia (laurel oak)
• Quercus michauxii (swamp chestnut oak)
• Quercus pagoda (cherry bark oak)
• Omits Americana (American elm)
EEP 17 August 2 005
PROPOSED
PLANT COMMUNITY LOCATIONS
? FIGURE 7
c:o1,Vstcl.l1 Roquist Wetland Restoration Site
Bertie County, NC

ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
Shrub species to be planted within the Nonriverine Wet Hardwood Community will be consistent
with those species located within the reference wetlands and derived from the following list (as
available):
• Clethra alnifolia (sweet pepperbush)
• Itea virginica (Virginia willow)
• Leucothoe axillaris (coastal dog-hobble)
5.2 Wetland Preservation
The wetland preservation component for the Roquist Wetland Restoration Site will consist of
preserving 3,776 ac (Figure 5). Of this, 390 ac are high quality wetland preservation. The total
acreage proposed for preservation includes areas that contain stands established before 1993
(1,520 ac), areas that have been logged since 1993 (2,210 ac), and a ten year old pine plantation
(established in 1993) (46 ac). Although the logged areas are absent of mature vegetation, they
are considered an essential part of the existing high quality forests. These areas will ultimately
contribute to the formation of an extensive wilderness area through the discontinuation of timber
practices and the process of natural regeneration within the Site.
5.3 Upland Preservation
The upland preservation component for the Site will consist of preserving 45 ac of existing
Mesic Mixed Hardwood Forests and clear-cut uplands. These areas are located along the
western and northern boundaries of the Site (Figure 5).
6.0 MONITORING PLAIN
Monitoring of wetland restoration efforts will be performed for five years or until success criteria
are satisfied. Monitoring is proposed for t-,vo wetland components, hydrology and vegetation.
6.1 Hydrology
Automated monitoring gauges utilized to monitor the Site's groundwater hydrology will be
designed and placed in accordance with specifications in the Corps of Engineers' Installing
Monitoring Wells/Piezometers in Wetlands (WRP Technical Note HY-IA-3.1, August, 1993).
The monitoring gauges installed will consist of Remote Data Systems, Inc. model Ecotone TM
WM Series automated groundwater monitoring gauges. These gauges will continuously record
water level data along a 40-inch gradient.
EEP 19 August 2005
ROQUIST JVETLAND RESTORATION SITE H ETLAND RESTORATION PLAN
6.1.1 Hydroligic Monitoring
Thirteen Ecotone TM WM Series (40-in) automated groundwater monitoring gauges will be
installed throughout five locations within the site (Figure 8). At least two gauges will be
installed at each location with one gauge positioned in the restoration area and one gauge
positioned in the adjacent reference wetland. Following installation, the automated groundwater
gauges will be adjusted to record data once daily. The gauges will be in operation throughout the
year, and data will be retrieved twice a year (at the beginning and end of the growing season) to
provide effective monitoring and assessment of success criteria for wetland hydrology.
6.1.2 Hydrologic Success Criteria
Wetland hydrology success criterion will be satisfied in the restoration areas during average
climatic conditions when saturated soil conditions occur within 12 in of the round's surface for
a minimum of 12.5% of the growing season, or if the hydroperiod in the restoration areas is
within 20% of the reference wetland's hydroperiod during drought conditions.
6.2 Vegetation
After HSMM completes first year vegetation monitoring EEP will be responsible for monitoring
and loner term management of the Site.
6.2.1 Vegetation Monitoring
Quantitative sampling plots (10 meter (m) x 10 m) for vegetation will be established in the
wetland restoration areas. The number of vegetation plots will be specified by EEP in the
Mitigation Plan. Vegetation plots will be inventoried after each growing season until vegetation
success criteria is achieved. Floristic inventories will begin within the first growing season
following completion of construction. Permanent photography stations will be established for
each sampling plot at selected vantage points to provide a visual record of vegetation
development over time. All vegetation monitoring plots will be correlated with hydrological
monitoring sites where possible to allow for point-source data of hydrologic and vegetation
parameters.
6.2.2 Vegetation Success Criteria
Wetland vegetation success criterion is defined by a minimum mean density of 320 trees per acre
of approved target species surviving for the first three years (USACE 1995). The required
success criteria will decrease by 10% per year after the third year to 290 stems per acre for year
four and 260 stems per acre for year five. Vegetation success criteria apply to the Nonriverine
EEP 20 August 2005
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.? { "f'y? ,,•?? "?"Lr . .Y t :r ?J ? ?1 a 1 r? J r.. F,. ??rY _
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Property Boundary
Wetland Restoration
Monitoring Station
? ? r r rI
2000 0 2000 4000 ?r
Scale (ft)
GROUNDWATER MONITORING
y STATIONS
FIGURE 8
F??c)system Roquist Wetland Restoration Site
Bertie County, NC
0
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
Swamp Community and the Nonriverine Wet Hardwood Community to be planted within the
Roquist Wetland Restoration Site.
6.3 Report Submittals
As-built plans will be submitted within 90 days following the completion of mitigation
construction. The as-built plans will show final site grading along with a description of post-
construction site conditions. The report will also provide a map of groundwater monitoring
gauge locations, proposed photographic monitoring stations and proposed vegetation sampling
areas.
The first year monitoring report will be submitted to EEP in pdf format. Subsequent monitoring
reports will be submitted by EEP annually to the resource agencies following each growing
season. Submitted reports will include (1) sample plot data, (2) water level data from automated
groundwater monitoring gauges, and (3) a discussion of substantiated problems and proposed
recommendations for problem resolution. Density, survival and percent composition of targeted
tree species will be reported. The duration of wetland hydrology during the growing season will
also be calculated at each monitoring gauge location and extrapolated to each restored
community.
6.4 Contingency
In the event that vegetation and/or hydrology success criteria are not fulfilled, appropriate
contingency measures will be implemented in coordination with the Resource Agencies.
Examples of such actions include replanting and extension of the monitoring period if
community mitigation types do not fulfill minimum species density and distribution
requirements. If exotic invasive plant species are of concern, appropriate measures will be used
to control for them. Hydrologic contingency will require consultation with hydrologists and the
Resource agencies in the event that predicted hydrology is not achieved during the monitoring
period. Recommendations for altering hydrology to establish wetland hydrology will be
implemented and monitored until the hydrology success criteria are achieved.
7.0 MITIGATION VALUES
The objective of the Roquist Wetland Restoration Site is to enhance and preserve 3,926 ac of the
Roanoke and Cashie Rivers' headwater ecosystems. The proposed mitigation components
should be viewed from the perspective of their cumulative contribution to the overall value of the
ecosystem rather than their individual values. The nonriverine ecosystem to be protected in
perpetuity not only provides valuable habitat to a diverse assemblage of flora and fauna but also
EEP 22 August 2005
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
serves as a contiguous wildlife corridor. Wetland values that will be increased by the mitigation
efforts proposed for the Site include water storage, pollutant removal, aquatic/wildlife habitat,
recreation, and education. The types of natural communities available for mitigation within the
Site are listed in Table 4.
The Roquist Wetland Restoration Site will be managed by EEP. All mitigation credits and the
credit release schedule for the Roquist Wetland Restoration Site will be consistent with the July
22, 2003 MOA between the NCDENR, NCDOT, and USACE.
Table 4. Phase I Mitigation acreages for the Roquist Wetland Restoration Site
Mitigation Type Acres'
Wetlands
Restoration 52
Preservation
Existing Forest 1,520
Pine Plantation 46
Clear-Cut Areas 2,210
Total 3,776
Uplands
Preservation
Existing Forest 23
Clear-Cut Areas 22
Total 45
8.0 REFERENCES
Cobb B. 1984. Peterson Field Guides: A Field Guide to the Ferns and their Related Families of
Northeastern and Central North America. Houghton Mifflin Company, New York. 281 pp.
Conant R, Collins JT. 1991. Peterson Field Guides: A Field Guide to Reptiles and Amphibians.
Houghton Mifflin Company, New York. 450 pp.
Frost CC, LeGrand Jr. HE, and Schneider RE. 1990. Regional inventory for critical natural areas,
wetland ecosystems, and endangered species habitats of the Albermarle-Pamlico Estuarine
Region. Phase 1. E.P.A. Albermale-Pamlico Esturaine Study Project No. 90-01.
Godfrey RK and Wooten JW. 1979. Aquatic and Wetland Plants of Southeastern United States:
Monocotyledons. University of Georgia Press, Athens. 712 pp.
EEP 23 August 2005
ROQUIST WETLAND RESTORATION SITE
WETLAND RESTORATION PLAN
Harrar ES, Harrar JG. 1962. Guide to Southern Trees. Dover Publications, Inc., New York. 709
PP.
Horton, Jr. JW and Zullo VA. 1991. The Geology of the Carolinas, Carolina Geological Society
Fiftieth Anniversary Volume. University of Tennessee Press, Knoxville.
Little EL 1996. National Audubon Society Field Guide to North American Trees: Eastern
Region. Alfred A. Knopf, Inc., New York. 714 pp.
Maptech®, Terrain Navigator 2001. South Mid-Atlantic Region: Raleigh/Chapel Hill, CD-ROM.
Martof BS, Palmer WM, Bailey JR, Harrison III JR. 1980. Amphibians and Reptiles of the
Carolinas and Virginia. The University of North Carolina Press, Chapel Hill. 261 pp.
Murie OJ. 1982. Peterson Field Guides: A Field Guide to Animal Tracks. Houghton Mifflin
Company, New York. 375 pp.
North Carolina Department of Environment, Health, and Natural Resources, Division of
Environmental Management, Water Quality Section. Guidance for Rating the Values of
Wetlands in North Carolina: Fourth Version. January 1995.
Radford AE, Ashles HE, and Bell CR. 1968. Manual of the Vascular Flora of the Carolinas.
University ofNorth Carolina Press, Chapel Hill.
Schafale MP and Weakley AS. 1990. Classification of the Natural Communities of North
Carolina: Third Approximation. North Carolina Department of Environmental Management,
Division of Parks and Recreation, Natural Heritage Program.
U.S. Department of Agriculture, Natural Resources Conservation Service in Cooperation with
the North Carolina Agricultural Experiment Station. Soil Survey of Bertie County, North
Carolina. 1984.
U.S. Department of the Army, Corps of Engineers. Branch Guidance for Wetland
Compensation, Permit Conditions and Performance Criteria. 7 December 1995.
U. S. Environmental Protection Agency Region IV. Restoration Banking Guidance. Atlanta,
Georgia.
U.S. Fish and Wildlife Service. National Wetlands Inventory Map - Bertie, North Carolina 7.5
Minute Quadrangle. Newton Corners, Massachusetts. 1994.
Wetland Training Institute, Inc. 1999. U.S. Field Guide for Wetland Delineation: 1987 Corps of
Engineers Manual. Glenwood, NM. WTI 99-1. 143 pp.
EEP 24 August 2005
ROQUIST WETLAND RESTORATION SITE
WETLAND RESTORATION PLAN
APPENDIX A
ROQUIST WETLAND RESTORATION SITE
PHOTOGRAPHS
EEP 25 August 2005
ROQUIST WETLAND RESTORATION SITE
JAL,
A

r. "yam o ,? ? ti.

t

v a
WETLAND RESTORATION PLAN

Photo: A) Jack's Branch; B) Nonriverine Swamp Community; C) Nonriverine 'Wet Hardwood
Community; D) Mesic Mixed Hardwood Community; E) old-field community; F) clear-cut
community; G) clear-cut community.
ROQUIST WETLAND RESTORATION SITE

WF_ TLAND RESTORATION PLAN
r f? ti -
h
ty

?
r

?4g e;
ht

Photo: H) Logging road, roadside ditch, and spoil; I) new logging road and ditch; J) restoration
corridor with adjacent mature stand (seed source); K) timber processing area - low pile; L) ditch
effect - surface water drainage; M) example cross section location.
R0QUIST WETLAND RESTORATION SITE
WETLAND RESTORATION PLAN
APPENDIX B
ROQUIST WETLAND RESTORATION SITE
JURISDICTIONAL DETERMINATION
EEP 26 August 2005
MAR 1 6 2004 r` • r- _;
HAYES,sEnr,MA IcrtN&MAI FERN, INC. U.S. ARMY CORPS OF ENGINEERS
RALEOH,N.C. WILMINGTON DISTRICT
Action ID 200411232 County Bertie
NOTIFICATION OF JURISDICTIONAL DETERMINATION
Property Ow er/Agent: NCDOT, Gregorv J. Thorpe, Ph.D.
Address: Environmental Management Director, PDEA
1548 Mail Service Center
Raleigh. North Carolina 27699-1548
Telephone No.: [phone]
Size and location of property (waterbody, highway name/number, town. etc.) The project area
is approximately 3,936 acres located on the east side of NC Highwav 11 just north of NCSR
1108 and south of Woodville/Levyiston adjacent to Roquist Pocosin. Roouist Creek. Jack's
Branch. and Indian Creek.
Indicate «'hich of the Following Apply:
There are waters of the U.S. and or wetlands, on the above described property which we strongly
suggest should be delineated and surveyed. The surveyed wetland lines must be verified by our staff
before the Corps will make a final jurisdictional determination on your property.
Because of the size of your property and our present workload, our identification and delineation of
your wetlands cannot be accomplished in a timely manner. You may wish to obtain a consultant to
obtain a more timely delineation of the wetlands. Once the consultant has flagged a wetland line on
the property, Corps staff will review it, and, if it is accurate, we strongly recommend that you have the
line surveyed for final approval by the Corps. The Corps will not make a final jurisdictional
determination on your property without an approved survey.
X The waters of the U.S. and/or wetlands, within the construction corridor limits, have been delineated
by your consultant, the delineation has been reviewed in the field by the Corps on February 11, 2004,
and the delineation as shown in the submission by your consultant, dated February 18 and 1-3, 2004,
has been determined by the Corps to be accurate, based on the information at this time. Unless there is
a change in the law or our published regulations, this determination may be relied upon for a period not
to exceed five years from the date of this notification.
_ There are no waters of the U.S., to include wetlands; present on the above described property which
are subject to the permit requirements of Section 404 of the Clean Water Act (33 USC 1344). Unless
there is a change i-: the law or our published regulations, this deternnation may be relied upon for a
period not to exceed five years from the date of this notification.
X The proper is lo:ared in one ofthe'0 Coastal Counties subject to regulation under the Coastal Area
Management AZ Z! LAMA). You should contact the Division of Coastal Management in Elizabeth
Citv. NC. at (2=?) 2164-3901 to determine their requirements.
Placement of dredged or fill material in Waters of the US and/or wetlands on this property
without a Department of the Army permit may constitute a violation of Section 301 of the Clean
Water Act (33 L: SC 1311). A permit is not required for work restricted entirely to existing non-
wetland area. If you have any questions regarding this determination and/or the Corps of
Engineers regulatory program, please contact Bill Biddlecotne at [phone] ext. 31.
Basis For Deten:linanon: The wetlands are a broad continuum to Roquist Pocosin. Roquist
Creek. Indian Creek. and Jack's Branch which are tributaries to the Roanoke River.
Owner,-Authorized Agent Signature
Corps Regulatory Official :y%`' J 41`. ?-?
Date 2/5,'2004 f Expiration Date 2/5/2009
SURVEY PLAT OR FIELD SKETCH OF THE DESCRIBED PROPERTY AND THE
WETLAND DELINEATION FORM MUST BE ATTACHED TO THE FILE COPY OF THIS
FORM
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INDEX OF SHEETS
R f z,~os ~
SHEET NO. SHEET 1U~ ~D
q ,"~s9'~wQ~~,
~7~q ~Y
lA TITLE SHEET
q~ 5 R4'~
1B CONVENTIONAL SYMBOLS
2 MISCELLANEOUS DETAILS
4 THRU 8 PLAN SHEETS
P~
X-1 THRU X-17 CROSS SECTION SHEETS
INCOMPLETE PLANS
DO NOT VSB FOR R/F ACQUISI'IRON
PRELIMINARY PLANS
OO NOT V88 POR CONBTRVCf10N

l~l
HYDRAULICS EXGINEER
V GRAPHIC SCALES DESIGN DATA PROJECT LENGTH
0 200
~,o PLANS
t~'~„~ 0 P.E.
SIGN.477JRG:

~~w
~~a O PROFILE (HORIZONTAL)
N~z >s,~
v~taw p
~ PROFILE (VERTICAL)

_

PROJECT REFERENCE N0. SHEET N0.
16
N S M M
ARCHITECTS - ENGIf~ERS -PLANNERS
1305 NAVAHO DR. SUITE 303 RALEIGH, NC 27609
Ed a of Pavement - - - - -
9
Curb Buildin s 9
c MINOR
Pro . Slo a Stakes Cut P p Foun ations ~
Pro . Slo a Stakes Fill F Head & End Wall
_ P P coNC Hw . . Utili Power Line • Area Outline rver Line Connects to Traffic Si nal
Pro .Woven Wire Fence - J Pi a Cu vert 9 ~
P - - - - - - , Lines Cut Into the Into the Pavement TS Ts Gate
Pro .Chain Link Fence P
9 ~ Footbrid e { Water Line e w w Gas Pum Vent or USG Tank Ca p p
Pro .Barbed Wire Fence P
Drains a Boxes g ca Sancta Sewer Pro .Wheelchair Ram ry ' Church sewer ss ss
~ . P P ~
Paved Ditch Gutter • - - - - - - Santa Sewer Foi ry }ewer Force ain ---f - - School SS FSS
Exist. Guardrail r r r
Rock Cross Vane . Gas Line Park - - - o o ~ - - ~
Pro .Guardrail P T 7 T
Lo Vane 9 Storm Sewer..-..---.. ewer s s Cemete - - - ry-------------------------------------------------------------------------- t
E uali S mbol ° Q Y ~__J
Power Line Roadwa Removal e P P Dam
Y
Tele hone Cable P Cable Si n T T g 0
S
Exi t Pol l~G Tele hone C~ • s. e p Baseline Control Pont • hone Conduit Well o P TC TC W
- - Small Mine -
Existin Ri ht of Wa .Marker Exist. Power Pole ' ' Unknown Utili 9 9 Y ~ ty ty ?U L-~U L Utlll T T
Exist. Ri ht of Wa Line w/Marker - - - - Pro .Power Pole Television Cable 9 Y P b Cable TV TV-
Swimmin Poo 9
Pr . Ri h Exist. Tele hone Pole Fiber 0 tics Cable o t of Wa Line with Pro osed P 9 Y P P + P FO FO ics Ca e - -
R1W Marker Iron Pin & Ca Pro . Tele hone Pole p ' P P -o- Exist. Water Meter
gr Meter Loose Surface
Pro . Ri ht of Wa line with Pro osed Exist. Joint Use Pole
P 9 Y p -l- Drawn Accordm g Hard Surface :cordm to I,VG Records g DATUR -
Concrete or Granite RAW Marker Pro .Joint Use Pole
P - -b- Abandoned Accorc :d Records AAT Chan a in Road Surface Accordin to USG UR 9 9
Exist. Control of Access line ~c~ Tele hone Pedestal
~ P T End Of Information D ~A, iformation E.o.l. Curb
Pro .Control of Access Line c Cable N Pedestal
P c A ? Ri ht of Wa S bol 9 Y Ym R/W
Exist. Easement Line H Brant E Y Guard Post p GP
Pro .Tem .Construction Easement Line Satellite Dish P P E Paved Walk
Pro .Tem . Drains a Easement Line Exist. Water Valve P P g TDE - - - I Brid e 9
Pro .Perm. Drains a Easement Line Sewer Clean Out State Line P 9 PDE Box Culvert or Tunnel - . ~
i
Power Manhole ' oun Line ie Fer rY -
Stream or Bod of Water _ _ Tele hone Booth ~ Townshi line Y P o P Line Culvert
Flow Arrow - Water Manhole . Ci Line - . ~ w 0 - - Foot ri e 9
Disa earin Stream--------------------------------------------------- - Li ht Pole Reservation Line . PP 9 9 0 n Line - - - - - Trail Foot ath
p ~
S rin H-Frame Pole Pro a Line P 9 ~ p ine
L~ ht House 9 .
Environmental) Sensitive Area Power Line Tower Pro a Line S k Y P Ym ine S bol Ym
Shoreline ' Pole with Base Exist. Iron Pin ? Pin 0 . aP Sin le Tree
9
Falls Ra ids P Gas Valve Pro a Corner P ~Y ,orner +
Sin le Shrub 9 a
Pro Ditches and Pro Tulula Creek P P Gas Meter Pro a Monumen P rtY Monument
Hed a 9
Existin Ch nn i tin Tele hone Manhole Pro a Number a el Ex s Relic P rtY ~umber
9 ~ 9 P T 0 123 Woods Line
' Power Transformer Parcel Number Backfill Exist Pond or Channel nber
0 6 Orchard
Soil Removal Area Sancta Sewer Manhole Fence Line P ry 0 Vine and -X X-X-
ww & isew y - - - VINEYARD
Root Wad Bank Protection Storm Sewer anhole Existin Wetland B M s • ~____J Wetland Boundaries _ _ _
0 g - WLB Trans lant p
Groundwater Water auge Tank Water Gas Oil Pro osed Wetland
- P Wetland Boundaries WLB
Im ermeable Cla Plu P Y 9
® Water Tank With Les Existin Endan ere 9 9 9 ~dan ered Animal Boundaries............ _ _ 9 EAB - - Standard Gau e 9
CSX TRANSPoRTATION
Traffic Si nal Juncti n B x Existin Endan ere z g o o s 9 9 D ~dan ered Plant Boundaries • 9 - - - - RR Si nal Mile ost EPB 9 p o
~o~ pfLEPt7ST 35
Fiber 0 tic S lice Box P P F MAJOR D Switch
~~w Television or Radio Tower Brid a Tunnel or Box Culvert g ~ i CONC revised 03/26/97
~Q
`~Z Bri ' d e Win Wall Head Wall ~~w 9 9
and En coNC ww d Wall

PROJECT REFERENCE NO. SHEET NO.
2
INCOMPLETE FLANS
~ ~ DO NOT V8B FOR R/ W AC~UISl770N
PRELIMINARY PLANS
DETA DO NOT VSB POR CONSTRVGTION
EXCAVATE SPOIL PILES
TO ELEV. OF ADJACENT H S M M
WETLANDS ARCHITECTS -ENGINEERS -PLANNERS
1305 NAVAHO DR. SUITE 303 RALEIGH, NC 27609
EXCAVATE LOGGING ROAD
TO ELEV. OF ADACENT
WETLANDS
PROPOSED 'ROPOSED WETLAND
- EXISTING WETLAND ELEVATIO \ i / ELEVATION :LEVATION EXISTING WETLAND
ELEVATION
~ `i ce.

r--
BACKFILL EXIST. DITCH BACKFILL EXIST. DITCH
TO ELEV. OF ADJACENT TO ELEV. OF ADJACENT
WETLANDS WETLANDS
3' (MIN)
IMPERVIOUS BLOCK -PLAN LO (NOT TO SCALE) LOGGING ROAD TYPICAL SECTION 1
(NOT TO SCALE)
PROPOSED WETLAND EXIST. WETLAND
ELEVATION ELEVATION
_ ~c_ _
I~ y ~Y ~i ~ ~ Y yr •C
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