20051680 Ver 1_COMPLETE FILE_20050831

Office Use Only: Form Version October 2001
USACE Action ID No. DWQ No. ? 0 0 5 1 8 8 0
If any particular item is not applicable to this project, please enter "Not Applicable" or "N/A" rather than
leaving the space blank.
1. Processing
1. Check all of the approval(s) requested for this project: A?? 1 2005
® Section 404 Permit oEN? WATER QUxoly
? Section 10 Permit
pSaNDS?
® 401 Water Quality Certification
? Riparian or Watershed Buffer Rules
2. Nationwide, Regional or General Permit Number(s) Requested: Nationwide 27
3. If this notification is solely a courtesy copy because written approval for the 401 Certification
is not required, check here: ?
4. If payment into the North Carolina Wetlands Restoration Program (NCWRP) is proposed for
mitigation of impacts (see section VIII - Mitigation), check here: ?
II. Applicant Information
1. Owner/Applicant Information
Name: NC Ecosystem Enhancement Program
Mailing Address: 1652 Mail Service Center Raleigh, NC 27699-1652
Telephone Number: 919-715-7571 Fax Number: 919-715-2219
E-mail Address: lin.xu(d,)ncmail.net
2. Agent Information (A signed and dated copy of the Agent Authorization letter must be
attached if the Agent has signatory authority for the owner/applicant.)
Name: N/A
Company Affiliation: N/A
Mailing Address: N/A
Telephone Number: N/A
E-mail Address: N/A
Page 5 of 13
Fax Number: N/A

III. Project Information
Attach a vicinity map clearly showing the location of the property with respect to local
landmarks such as towns, rivers, and roads. Also provide a detailed site plan showing property
boundaries and development plans in relation to surrounding properties. Both the vicinity map
and site plan must include a scale and north arrow. The specific footprints of all buildings,
impervious surfaces, or other facilities must be included. If possible, the maps and plans should
include the appropriate USGS Topographic Quad Map and NRCS Soil Survey with the property
boundaries outlined. Plan drawings, or other maps may be included at the applicant's discretion,
so long as the property is clearly defined. For administrative and distribution purposes, the
USACE requires information to be submitted on sheets no larger than 11 by 17-inch format;
however, DWQ may accept paperwork of any size. DWQ prefers full-size construction
drawings rather than a sequential sheet version of the full-size plans. If full-size plans are
reduced to a small scale such that the final version is illegible, the applicant will be informed that
the project has been placed on hold until decipherable maps are provided.
1. Name of project: Roquist Wetland Restoration Project
2. T.I.P. Project Number or State Project Number (NCDOT Only): N/A
3. Property Identification Number (Tax PIN): N/A
4. Location
County: Bertie Nearest Town: Woodville
Subdivision name (include phase/lot number): N/A
Directions to site (include road numbers, landmarks, etc.): Follow Hwy 64 East Past
Tarboro to Hwy 11 North. Follow 11 North through Oak City towards Lewiston -
Woodville. Cross the Roanoke River, pass Apple Tree Rd two times (on the left) and then
Indian Woods Rd on your right. The very next road to the right is a short spur leading to a
road parallel to Hwy 11. The short spur leads directly to a gate that is the access to Roquis
sitet.
5. Site coordinates, if available (UTM or Lat/Long): N/A
(Note - If project is linear, such as a road or utility line, attach a sheet that separately lists the
coordinates for each crossing of a distinct waterbody.)
6. Describe the existing land use or condition of the site at the time of this application:
Agriculture and forest
7. Property size (acres): 3,920 acres
Nearest body of water (stream/river/sound/ocean/lake): Jack's Branch, Roquist Creek and
Indian Creek
9. River Basin: Roanoke
Page 6 of 13
(Note - this must be one of North Carolina's seventeen designated major river basins. The
River Basin map is available at http://h2o.enr.state.nc.us/admin/maps/.)
10. Describe the purpose of the proposed work: Restoration of 52 acres of Previously ditched
and filled nonriverine wetlands, preservation of 3,776 acres of existing nonriverine
wetlands, and preservation of 45 acres of existing uplands
11. List the type of equipment to be used to construct the project: Track Hoes, loaders
12. Describe the land use in the vicinity of this project: Agriculture and forest
IV. Prior Project History
If jurisdictional determinations and/or permits have been requested and/or obtained for this
project (including all prior phases of the same subdivision) in the past, please explain. Include
the USACE Action ID Number, DWQ Project Number, application date, and date permits and
certifications were issued or withdrawn. Provide photocopies of previously issued permits,
certifications or other useful information. Describe previously approved wetland, stream and
buffer impacts, along with associated mitigation (where applicable). If this is a NCDOT project,
list and describe permits issued for prior segments of the same T.I.P. project, along with
construction schedules.
N/A
V. Future Project Plans
Are any future permit requests anticipated for this project? If so, describe the anticipated work,
and provide justification for the exclusion of this work from the current application:
NIA
VI. Proposed Impacts to Waters of the United States/Waters of the State
It is the applicant's (or agent's) responsibility to determine, delineate and map all impacts to
wetlands, open water, and stream channels associated with the project. The applicant must also
provide justification for these impacts in Section VII below. All proposed impacts, permanent
and temporary, must be listed herein, and must be clearly identifiable on an accompanying site
plan. All wetlands and waters, and all streams (intermittent and perennial) must be shown on a
delineation map, whether or not impacts are proposed to these systems. Wetland and stream
evaluation and delineation forms should be included as appropriate. Photographs may be
included at the applicant's discretion. If this proposed impact is strictly for wetland or stream
Page 7 of 13
mitigation, list and describe the impact in Section VIII below. If additional space is needed for
listing or description, please attach a separate sheet.
1. Wetland Impacts (No Impact)
Wetland Impact
Site Number
(indicate on ma)
Type of Impact* Area of
Impact
(acres) Located within
100-year Floodplain**
(es/no) Distance to
Nearest Stream
(linear feet)
Type of Wetland***

* List each impact separately and identify temporary impacts. Impacts include, but are not limited to: mechanized clearing, grading, fill,
excavation, flooding, ditching/drainage, etc. For dams, separately list impacts due to both structure and flooding.
** 100-Year floodplains are identified through the Federal Emergency Management Agency's (FEMA) Flood Insurance Rate Maps
(FIRM), or FEMA-approved local floodplain maps. Maps are available through the FEMA Map Service Center at 1-800-358-9616, or
online at http:/hvww.fema.aov.
*** List a wetland type that best describes wetland to be impacted (e.g., freshwater/saltwater marsh, forested wetland, beaver pond,
Carolina Bay, bog, etc.)
List the total acreage (estimated) of existing wetlands on the property: 3,881 acres
Total area of wetland impact proposed: 0.0 acres
2. Stream Impacts, including all intermittent and perennial streams (no impact)
Stream Impact
Site Number
(indicate on ma)
Type of Impact* Length of
Impact
(linear feet)
Stream Name** Average Width
of Stream
Before Impact Perennial or
Intermittent?
(please seci )

* List each impact separately and identify temporary impacts. Impacts include, but are not limited to: culverts and associated rip-rap,
dams (separately list impacts due to both structure and flooding), relocation (include linear feet before and after, and net loss/gain),
stabilization activities (cement wall, rip-rap, crib wall, gabions, etc.), excavation, ditching/straightening, etc. If stream relocation is
proposed, plans and profiles showing the linear footprint for both the original and relocated streams must be included.
** Stream names can be found on USGS topographic maps. If a stream has no name, list as UT (unnamed tributary) to the nearest
downstream named stream into which it flows. USGS maps are available through the USGS at 1-800-358-9616, or online at
wwnv.uses.gov. Several internet sites also allow direct download and printing of USGS maps (e.g., www.topozone.com,
wwlv.mapquest.com, etc.).
Cumulative impacts (linear distance in feet) to all streams on site: 0.0 LF
Page 8 of 13
3. Open Water Impacts, including Lakes, Ponds, Estuaries, Sounds, Atlantic Ocean and any
other Water of the U.S. (No Impact)
Open Water Impact
Site Number
indicate on ma
(' )
Type of Impact* Area of
Impact

(acres) Name Waterbody
(if applicable) Type of Waterbody
(lake, pond, estuary, sound,

bay, ocean, etc.)

* List each impact separately and identify temporary impacts. Impacts include, but are not limited to: fill, excavation, dredging,
flooding, drainage, bulkheads, etc.
4. Pond Creation
If construction of a pond is proposed, associated wetland and stream impacts should be
included above in the wetland and stream impact sections. Also, the proposed pond should
be described here and illustrated on any maps included with this application.
Pond to be created in (check all that apply): ? uplands ? stream ? wetlands
Describe the method of construction (e.g., dam/embankment, excavation, installation of
draw-down valve or spillway, etc.): N/A
Proposed use or purpose of pond (e.g., livestock watering, irrigation, aesthetic, trout pond,
local stormwater requirement, etc.): N/A
Size of watershed draining to pond: N//A Expected pond surface area: N/A
VII. Impact Justification (Avoidance and Minimization)
Specifically describe measures taken to avoid the proposed impacts. It may be useful to provide
information related to site constraints such as topography, building ordinances, accessibility, and
financial viability of the project. The applicant may attach drawings of alternative, lower-impact
site layouts, and explain why these design options were not feasible. Also discuss how impacts
were minimized once the desired site plan was developed. If applicable, discuss construction
techniques to be followed during construction to reduce impacts.
The aroiect is involved with nreservina and restorine wetlands in the Roauist wetland site
in Bertie_County to serve EEP's prollram objective and mitillation needs. The project is a
mitigation effort and does not impact adjacent streams and wetlands. See Roquist wetland
restoration plan for specific information regarding the restoration design.
Page 9 of 13
VIII. Mitigation
DWQ - In accordance with 15A NCAC 2H .0500, mitigation may be required by the NC
Division of Water Quality for projects involving greater than or equal to one acre of impacts to
freshwater wetlands or greater than or equal to 150 linear feet of total impacts to perennial
streams.
USACE - In accordance with the Final Notice of Issuance and Modification of Nationwide
Permits, published in the Federal Register on March 9, 2000, mitigation will be required when
necessary to ensure that adverse effects to the aquatic environment are minimal. Factors
including size and type of proposed impact and function and relative value of the impacted
aquatic resource will be considered in determining acceptability of appropriate and practicable
mitigation as proposed. Examples of mitigation that may be appropriate and practicable include,
but are not limited to: reducing the size of the project; establishing and maintaining wetland
and/or upland vegetated buffers to protect open waters such as streams; and replacing losses of
aquatic resource functions and values by creating, restoring, enhancing, or preserving similar
functions and values, preferable in the same watershed.
If mitigation is required for this project, a copy of the mitigation plan must be attached in order
for USACE or DWQ to consider the application complete for processing. Any application
lacking a required mitigation plan or NCWRP concurrence shall be placed on hold as
incomplete. An applicant may also choose to review the current guidelines for stream restoration
in DWQ's Draft Technical Guide for Stream Work in North Carolina, available at
http://h2o.enr.state.nc.us/ncwetlands/strmgide.html.
Provide a brief description of the proposed mitigation plan. The description should provide
as much information as possible, including, but not limited to: site location (attach directions
and/or map, if offsite), affected stream and river basin, type and amount (acreage/linear feet)
of mitigation proposed (restoration, enhancement, creation, or preservation), a plan view,
preservation mechanism (e.g., deed restrictions, conservation easement, etc.), and a
description of the current site conditions and proposed method of construction. Please attach
a separate sheet if more space is needed.
The restoration plan is attached. The plan indicates the conservation easement
acquired by the state, plan views, cross section view and proposed method of
preservation and restoration.
2. Mitigation may also be made by payment into the North Carolina Wetlands Restoration
Program (NCWRP) with the NCWRP's written agreement. Check the box indicating that
you would like to pay into the NCWRP. Please note that payment into the NCWRP must be
reviewed and approved before it can be used to satisfy mitigation requirements. Applicants
will be notified early in the review process by the 401/Wetlands Unit if payment into the
NCWRP is available as an option. For additional information regarding the application
process for the NCWRP, check the NCWRP website at bqp://1120.enr.state.ne.us/wrp/index.htm. If
use of the NCWRP is proposed, please check the appropriate box on page three and provide
the following information:
Page 10 of 13
Amount of stream mitigation requested (linear feet): N/A
Amount of buffer mitigation requested (square feet): N/A
Amount of Riparian wetland mitigation requested (acres): N/A
Amount of Non-riparian wetland mitigation requested (acres): N/A
Amount of Coastal wetland mitigation requested (acres): N/A
IX. Environmental Documentation (DWQ Only)
Does the project involve an expenditure of public funds or the use of public (federal/state/local)
land?
Yes ® No ?
If yes, does the project require preparation of an environmental document pursuant to the
requirements of the National or North Carolina Environmental Policy Act (NEPA/SEPA)?
Note: If you are not sure whether a NEPA/SEPA document is required, call the SEPA
coordinator at [phone] to review current thresholds for environmental documentation.
Yes ? No
If yes, has the document review been finalized by the State Clearinghouse? If so, please attach a
copy of the NEPA or SEPA final approval letter.
Yes ? No
X. Proposed Impacts on Riparian and Watershed Buffers (DWQ Only)
It is the applicant's (or agent's) responsibility to determine, delineate and map all impacts to
required state and local buffers associated with the project. The applicant must also provide
justification for these impacts in Section VII above. All proposed impacts must be listed herein,
and must be clearly identifiable on the accompanying site plan. All buffers must be shown on a
map, whether or not impacts are proposed to the buffers. Correspondence from the DWQ
Regional Office may be included as appropriate. Photographs may also be included at the
applicant's discretion.
Will the project impact protected riparian buffers identified within 15A NCAC 2B .0233
(Meuse), 15A NCAC 2B .0259 (Tar-Pamlico), 15A NCAC 2B .0250 (Randleman Rules and
Water Supply Buffer Requirements), or other (please identify Catawba Buffer Requirement )?
Yes ? No ® If you answered "yes", provide the following information:
Identify the square feet and acreage of impact to each zone of the riparian buffers. If buffer
mitigation is required calculate the required amount of mitigation by applying the buffer
multipliers.
Page 11 of 13
Zone* Impact
(square feet) Multiplier Required
Mitigation
1 0 3
2 0 1.5
Total 0
* Zone 1 extends out 30 feet perpendicular from near bank of channel; Zone 2 extends an
additional 20 feet from the edge of Zone 1.
If buffer mitigation is required, please discuss what type of mitigation is proposed (i.e., Donation
of Property, Conservation Easement, Riparian Buffer Restoration / Enhancement, Preservation or
Payment into the Riparian Buffer Restoration Fund). Please attach all appropriate information as
identified within 15A NCAC 2B .0242 or .0260.
N/A
XI. Stormwater (DWQ Only)
Describe impervious acreage (both existing and proposed) versus total acreage on the site.
Discuss stormwater controls proposed in order to protect surface waters and wetlands
downstream from the property.
N/A
XII. Sewage Disposal (DWQ Only)
Clearly detail the ultimate treatment methods and disposition (non-discharge or discharge) of
wastewater generated from the proposed project, or available capacity of the subject facility.
N/A
XIII. Violations (DWQ Only)
Is this site in violation of DWQ Wetland Rules (15A NCAC 2H.0500) or any Buffer Rules?
Yes ? No
Is this an after-the-fact permit application?
Yes ? No
XIV. Other Circumstances (Optional):
It is the applicant's responsibility to submit the application sufficiently in advance of desired
construction dates to allow processing time for these permits. However, an applicant may
choose to list constraints associated with construction or sequencing that may impose limits on
work schedules (e.g., draw-down schedules for lakes, dates associated with Endangered and
Threatened Species, accessibility problems, or other issues outside of the applicant's control).
Page 12 of 13
N/A

-alwos
Applicant/Agent's Signature
Date
(Agent's signature is valid only if an authorization letter from the applicant is provided.)
Page 13 of 13
1
SITE MAP
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 1

PLANT COMMUNITIES
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 4
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ROQUIST WETLAND RESTORATION PLAN
PHASE I
BERTIE COUNTY
NORTH CAROLINA
I 10V *? 14 kyj 11,4 C
AUG G 6 2005
NCECOSYSTEM
ENHwMwPROGRAM
Prepared for:
NORTH CAROLINA DEPARTMENT OF ENVIRONMENT
AND NATURAL RESOURCES
ECOSYSTEM ENHANCEMENT PROGRAM
RALEIGH, NORTH CAROLINA
Ecas stem
PROGRAM
FINAL PLAN
August 2005

t[R@[l5lwl9
AUG 3 7 2005
DENK • WA1 ER QUALITY
WETLANDS AND STOR M 0AW
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 ..............................................................................
6.1.1 Hydroligic Monitoring ......................................................
6.1.2 Hydrologic Success Criteria .............................................
6.2 VEGETATION ..............................................................................
6.2.1 Vegetation Monitoring ...................................................
6.2.2 Vegetation Success Criteria ...........................................
61 REPORT SUBMITTALS
.................................... 19
.................................... 20
.................................... 20
.................................... 20
.................................... 20
....................................... 20
..................................................................................................... 22
6.4 CONTINGENCY ............................................................................................................... 22
7.0 MITIGATION VALUES ............................................................................................... 22
8.0 REFERENCES ................................................................................................................23
EEP I August 2005
ROQ UIST 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 ................................
Appendix B ................................
............................................................................Photographs
..........................................,........Jurisdictional Determination
EEP ii August 2005
ROQUIST RESTORATION SITE
1.0 INTRODUCTION
WETLAND RESTOR4TIONPLAN
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 11 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
_L
L01b.-d'al
Stem
SITE MAP
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 1
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION 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 mi) . 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
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;: Jack's Branch i
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Property Boundary
N
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Sods r

Streams
2000 0 2000 4 000 i_

Scale (ft)

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PROPERTY BOUNDARY
& SOILS MAP
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE

ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATIONPLAN
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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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 Hydric

Class
Bibb and Johnston loam BB 0 to 2 Poorly to very poorly drained Hydri c
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 Non-Hydric
Pantego loam Pa - Very poorly drained Hydric
Rains sandy loam Ra - Poorly drained Hydric
Roanoke fine sandy loam Ro - Poorly drained Hydric
* Soils having hydric 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
(NCNHP) database for Natural Communities within the Roquist wetland. 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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2000 0 2000 4000
Scale (ft)

PLANT COMMUNITIES
Roquist Wetland Restoration Site
Bertie County, NC

FIGURE 4
0
ROQUIST WETLAND RESTORATION SITE
Table 2. Roquist Wetland Restoration Site Plant Communities
WETLAND RESTORATION PLAN

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 styraciua), water tupelo (Nyssa aquatica), and
willow oak (Quercus phellos); SU 3CANOPY - iron wood (Carpinus caroliniana), red maple,
EEP 9 August 2005
ROQUIST WETLAND RESTORA TION SITE WETLAND RESTORA TION PLAN
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 (Osnzunda 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; SHRUB/VINE - 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
ROQ UIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
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 -Arith 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 WETLAND RESTORATION PLAN
3.4.6 Clear-Cut (Early Succession)
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 henslowii SR Yes
Rafinesque's bi- eared bat Co norhinus ra ines uii SC* No
Cerulean Warbler Dendroica cerulea SR Yes
Chowanoke Crayfish Orconectes virginianus SC Yes
Any species or plant in iNortn 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 If 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 backfrlling, 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
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MITIGATION AREAS PHASE I
Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 5

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•
FIGURE 6
• ?r;c?te?? Roquist Wetland Restoration Site
• Bertie County, NC
0
ROQUIST WETLAND RESTORA TION SITE WETLAND RESTORA TION 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 corymbosum (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)
• Ulmus Americana (American elm)
EEP 17 August 2005
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PROPOSED
PLANT COMMUNITY LOCATIONS
FIGURE 7
a; s 'stc m Roquist Wetland Restoration Site
°.,s..I Bertie County, NC
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORA TION 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 PLAN
Monitoring of wetland restoration efforts will be performed for five years or until success criteria
are satisfied. Monitoring is proposed for two 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
WM Series automated groundwater monitoring gauges. These gauges will continuously record
water level data along a 40-inch gradient.
EEP 19 August 2005
ROQUIST WETLAND RESTORATION SITE WETLAND RESTORATION PLAN
6.1.1 Hydroligic Monitoring
Thirteen Ecotone 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 ground'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 long-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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Roquist Wetland Restoration Site
Bertie County, NC
FIGURE 8
ROQUIST WETLAND RESTORATIONSITE WETLAND RESTORATIONPLAN
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 of North 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, Pen-nit 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
WETLAND RESTORATION PLAN

7: t

'3 ..+i ?{ c iP wy ''9Td!t. ?X.? ?s?.j; ? # ~?a. R2

ell
kk ? f
- 4
r !lam}??`'`Eo ?+7
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.
ROQU/ST WETLAND RESTORATION SITE

_ . h 4 555
` qr i ;:3L,

W ; y
VOW
'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 - log-pile; L) ditch
effect - surface water drainage; M) example cross section location.

ROQUIST WETLAND RESTORATION SITE
APPENDIX B
ROQUIST WETLAND RESTORATION SITE
JURISDICTIONAL DETERMINATION
WETLAND RESTORATION PLAN
EEP 26 August 2005
-3 0
D "312g
VMAYR .16 2004' °
•? ,,MWUEnNBMATTEM,WC. U.S. ARMY CORPS OF ENGINEERS
ME0,N.C. WILMINGTON DISTRICT
Action ID 200411232 County Bertie
NOTIFICATION OF JURISDICTIONAL DETERMINATION
• Property Owner/Agent: NCDOT, Gregory 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 3,926 acres located on-the east side of NC Highwav 11 just north of NCSR
1108 and south of Woodville/Lewiston adjacent to Roquist Pocosin. Roquist Creek, Jack's
Branch, and Indian Creek.
• Indicate Which of the Following Applv:
_ 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,
a
and the delineation as shown in the submission by your consultant, dated February 18 and 23, 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 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.
X The property is located in one of the 20 Coastal Counties subject to regulation under the Coastal Area
Management Act (CANLA). You should contact the Division of Coastal Management in Elizabeth
City, NC, at [phone] to determine their requirements. v
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 USC 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 Biddlecome at [phone] ext. 31.
• Basis For Determination: 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
Date 2/5/2004 ' 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
m 8TA'IS 81'A'IS PROlB(.T RBPBIBNCB NQ ~T ~'v' NQ 8619
m ~~~1~1~ CIF N R OQ UIS T WETLAII t PH A ( ~ ~p s Jl ~ ~~~~~~d V ~ a~o ~dll
8TAT6 PRp1.NQ P.A%IOI.N¢ pBHCgV1'pN
1 ~D RESTORA T101~ SITE
RASE l
m sos ' ~ - LOCATION: NC 1U42 ~ „
1U42 LEWIST011t WDODVILLE
m
F 42 BERTIE :TIE COU11tTY
o u ~ TYPE OF WORK: GR
P„~, - sos GRADI11lG AVID DRAINAGE
Ha/ifax Co
Be ~ ~o ~ ROQU/ST
M/T/GATION~
.SITE
~ ROQU
~ ~ ~ ~ a PoCOSI \ 42 a
_ ~
~ ' G1'
uz~ (3 M
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z
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VICINITY MAP 0
s
B,
m? Auc r Zoos D
INDEX OF SHEETS ~ ~W'~~
~s
SHEET NO. SHEET ns 4
lA TITLE SHEET
q~ 5
1 B CONVENTIONAL SYMBOLS
2 MISCELLANEOUS DETAILS
4 THRU 8 PLAN SHEETS
X-1 THRU X-17 CROSS SECTION SHEETS P~
INCOMPLETE 1DLANS
UO NOT VSB POR R/N AODUI9ITION
PRELIMINARY PLANS
DO Ndf USB POR CONBTRVCI'ION

l~1
HYDRAULICS E1~GINEER
V GRAPHIC SCALES DESIGN DATA PROJECT LE11lGTH
~ 0 200
~,o ~ PLANS
P.B.
0 SIGNATURH:

'-'~~w
~~a O PROFILE (HORIZONTAL) N~z
r+~~
v~+»w Q

~ PROFILE (VERTICAL)

PROJECT REFERENCE N0. SHEET N0.
r
1B
m N S M M
ARCI4TECTS - ENGINEERS - PLANNgtS
1305 NAVAHO OR. SURE 303 RALgGH, NC 27604
Ed a of Pavement - - - - - -
9
Curb - - - - - Buildin s 9
c MINOR
Pro . Slo a Stakes Cut P P Foun ations
Fill Head & En Wa
Pro . Slo a Stakes coNC Hw . . _ P P Utili Po • • Area Outline nnects to Traffic Si nal Utili Power Line Co 9 ~
Pro .Woven ire ence ~ - - - - - , P Pi a Culvert - - - - -
P ~ Lines Cui Lines Cut Into the Pavement TS rs Gate
Pro .Chain Link Fence P i
Footbr d e 9 > { Water Lir Water Line Gas Pum Vent or UiG Tank Ca o w w p p
Pro .Barbed Wire Fence P
Drama a Boxes 9 ca nit Sa a ry Sanita Sewer Church rY ss ss
Pro .Wheelchair Ram ~ . P P c
Paved Ditch Gutter . . Sancta ry Sanita Sewer Force Main - - School ry -fss Fss
Exist. Guardrail r T r
Rock Cross Vane ' Gas Line G G Gas Line Park - - -
Pro .Guardrail T T T P
Lo Vane Storm S~ 9 0 Storm Sewer s s Cemete rY t ~__J
E uali S mbol q Y
Power Lir Power Line P P Dam
Roadwa Removal Y
Tele hon P Tele hone Cable Si n . P T T g o s
LVG Tele • Exist. Pole Baseline Control Pornt------------------------------------------------ • LVG Tele hone Conduit Well o P TC TC W
Small Mine
' Exist. Power Pole Unknown Existin Ri ht of Wa .Marker----------------------------------- 1 9 9 Y Unknown Utili - T T - ty ?U L~U L
Te evisior ht of Wa Line w/Marker - - - - Pro .Power Pole Exist. Ri p b 9 Y TV TV- Television Cable Swimmin Poo 9
Fiber 0 1 Pr sed Exist. Tele hone Pole P Pro . Ri ht of Wa line with o o 9 Y P P Fiber 0 tics Cable - - p Fo Fo
P
er Iron Pin & Ca .Pro . Tele hone Pole ' R1W Mark p p -o- Exist. Wa'J P Loose Surface Exist. Water Meter
' ht of Wa Line with Pro osed Exist. Joint Use Pole Pro . Ri p Drawn A ' Hard Surface Drawn Accordin to USG Records
P 9 Y g QATUR
or Granite R1W Marker Pro .Joint Use Pole Concrete p Abandon t0 R@COrdS AATUR Chan a in Road Surface Abandoned Accordm l~G
9 g
f A s 'c~ Tee one Pedesta T End Of li ' Line Exist. Contro o cces , p End Of Information E.o.I. Curb
~A.
Line c Cabie N Pedestal Ri ht of Wa S mbol
Pro .Control of Access P 9 Y Y R/W
Guard Post
ment Line H rant Exist. Ease E Y Q GP
Paved Walk
.Construction Easement Line Satellite Dish Pro .Tem P P E ~
r in Easement Line Exist. Water Valve Pro .Tem .Da ae p p 9 TDE 9 ~ Bride -
State Line
n State Lini r in a Easement Line Sewer Clea Out Pro . Perm. D a a PoE P 9 + Box Culvert Or Tunnel L_______________J
r / noun Line
Powe Ma a tY r nhol - - Coun Li tY Fer ry
Townshi ~ownshi Line
- - Tele hone Booth ® P Stream or Bod of Water p Y p Culvert
Wa a Man o t r h le Ci Line Flow Arrow _ w ~ 0 :i Line - - Footbr~d a g
' _ i ht Pol . Reservatic Disa earn Stream 9 a PP 9 Teservation Line Trail Foot ath ~ _ - p _
H-Frame Pole ro erty S rin tr~--~ P P 9 0'1 Pro a Line p Li ht House
9 •
' ' ' P r Lin To er Environmental) Sensitive Area J~ owe e w rope Y Pro a Line S mbol P Y
' Pole with Base Exist. Iror Shoreline _ Exist. Iron Pin o • aP Sin a Tree
9
Falls Ra ids _ Pro e ~ - Gas Valve P rtY P Pro a Corner . P rtY + Sin le Shrub
9 ~
Pro Ditches and Pro Tulula Creek Pro e ~ Gas Meter P rtY P P Pro a Monument P rtY Hed a
9
• Pro e Tele hone Manhole P rtY Existin Channel Existin Relic p T Pro a Number . P rtY 123
9 ~ 9 0 Woods Line
Parcel Nu • Power Transformer Parcel Number 6 Orchard
Backfill Exist Pond or Channel
• Fence Lir Area Sancta Sewer Manhole S oil Remova ry 0 Fence Line - x x-x- Vine and
~ p ww & isaw • ~ VINEYARD
r nho - Existin ~ Root Wad Bank Protection Storm Sewe Ma le s 9 Existin Wetland Boundaries _ _ _ _ g WLB
0 Trans lant P
Groundwater Water Gau e Tank• Water Gas Oil Pro osed 9 - P Pro osed Wetland Boundaries p wL6
Im ermeable Cla Plu ' Y 9 t r T nk ith L Existm E P ® Wa e a W e s 9 . . Existm Endan ered Animal Boundaries.....-...... _ _ _ _
9 9 9 EAB Standard Gau e 9
• CSX TRANSP3RTATION Existin Endan ered Plant Boundaries •
Traffic Si nal Junction Box istm s 9 z 9 ? 9 9 - - RR Si nal Mile ost EPB 9 p o YIiEPOST 35

Fiber 0 tic S lice Box P P F Switch
MAJOR SWlfCN
w~W • Television or Radio Tower Bnd a Tunnel or Box Culvert g i i CONC revised 03/26/97
~»a
Brid a Win Wall Heod Wall 9 9
and End Wall coNC ww

PROJER REFERENCE NO. SHEEP NO.
N 2
INCOMPLETE PLANS
PRELIMINARY PLANS
DO NOT U5B POR CONSTRVC170N
D ET EXISTING WETLAND TA I L S ~ NOT O86 FOR R/ W ACQ[IIS1T[ON
EXCAVATE SPOIL PILES H S M M
TO ELEV. OF ADJACENT
WETLANDS ARCHITECTS -ENGINEERS -PLANNERS
1305 NAVAHO OR. SUITE 303 RALEIGH, NC 27609
EXCAVATE LOGGING ROAD
TO ELEV. OF ADACENT
WETLANDS
PROPOSED WETLAND
p ELEVATION EXISTING WETLAND
ELEVATION
i ELEVATION
z `i_

r--
BACKFILL EXIST. DITCH / ~ TO ELEV. OF ADJACENT f. DITCH BACKFILL EXIST. DITCH
IJACENT TO ELEV. OF ADJACENT
WETLANDS WETLANDS
3' fMIM
IMPERVIOUS BLOCK -PLAN LOGGING ROAD TYPICAL SECTION 1
(NOT TO SCALE)
(NOT TO SCALE)
PROPOSED WETLAND EXIST. WETLAND
ELEVATION ELEVATION

~v y v
EXCAVATE LOGGING ROAD
h < ~~~i~~~ ~i~~~~%i~ ~ a Y d i~ ~C <n ~C ~i~ L v v v TO ELEV. OF ADJACENT
~Yx ~~(~4 i~ n~<~~4i~~~~ ~ v WETLANDS
~ ~ xK ~ { fi/~ i~~ i4~ ~ PROPOSED WETLAND
~%~y~~xX'~~'~ T T~J~~\T~~~~~~/ EXISTING DITCH EXISTING WET TING WETLAND ELEVATION EXISTING WETLAND
` ~r,~y 7h7>yx'~5y ~ ELEVATION ATION ELEVATION
~ Y T~~ rc ~`'Skkyyy~i
"y'~ Xyv'~u ,c'~~ v ~ IMPERVIOUS SELECT
%v~~ v~'~ ~ ~~~v BACKFILL
3' (MIM
LOGGING ROAD TYPICAL SECTION 2
IMPERVIOUS BLOCK -SECTION
WOT TO SCALE) (NOT TO SCALE)
BACKFILL AREA
EXCAVATION AREA
v~`„v,~v IMPERVIOUS BLOCK
~ BACKFILL AREA
Z
- - - - EXISTING ELEVATION

W
PROPOSED WETLAND
rM N~ ELEVATION
r~ V1W

~N

11 11 1 11 '11 • . • µ R ~ y

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