HomeMy WebLinkAbout20111042 Ver 1_Public Notice_20111130 20 � 1 1042
Dennison, Laurie
From Fauser Anna E SAW[Anna E Fauser@usace army mil]
Sent Wednesday November 30 2011 10 44 AM
Sub�ect US Army Corps of Engmeers Public Notice
As you requested you are hereby notified that the Wilmmgton District United States Army Corps of Engineers
has issued a Public Notice The Text of this document can be found on the Public Notices portion of the
Regulatory Drvision Home Page Each Public Notice is available in ADOBE ACROBAT ( pd� format for
viewing printing or download at www saw usace army mil/wetlands As with all e mail attachments be sure to
check for viruses prior to opening the attachment The current notice involves The establishment of a stream
and wetland mitigation bank known as the New River Stream and Wetland Mitigation Bank within a 31 acre
tract owned by the Thompson and Troldahl families and being developed by Restoration Systems LLC c/o Mr
Worth Creech The tract is located within the floodplain of the New River on the north side of NC Hwy 24
west of Richlands Onslow County North Carolina
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US Army Corps PU�LIC NOTICE
Of Engmeers 2 � 1 1 1 0 4 2
Wilmmgton Distnct
Issue Date November 30 2011
Comment Deadlme December 30 2011
Corps Action ID# SAW 2011 02198
The Wilmmgton Distnct Corps of Engmeers(Corps)has received a prospectus
proposmg to establish a stream and wetland mitigation bank known as the New River
Stream and Wetland Mitigation Bank withm a 31 acre tract owned by the Thompson and
Troldahl families and bemg developed by Restoration Systems LLC c/o Mr Worth
Creech The tract is located withm the floodplam of the New River on the north side of
NC Hwy 24 west of Richlands Onslow County North Carolma
Specific plans and location mformation are descnbed below and shown on the attached
plans The Public Notice and the prospectus are available on the Wilmmgton Distnct �
Web Site at http//www saw usace army miUWetlands/Notices/Current not�ces html
Sponsor Restorahon Systems LLC
c/o Mr Worth Creech
1101 Haynes Street Suite 211
Raleigh North Carolma 27604
Landowners Mr and Mrs Ronald Thompson
302 Jesse Williams Road
Richlands North Carolma 28574
Mr and Mrs Moms Thompson
113 Westside Lane
Richlands North Carolina 28574
.
Mr and Mrs Richard Troldahl
314 Jesse Williams Road
Richlands North Carolma 28574
Authority
The Corps will evaluate this prospectus and the establishment of the mitigation bank in
accordance with the procedures outlmed m 33 CFR Part 332 Additionally tlus proposal
will also be reviewed pursuant to the permittmg authorriy under Section 404 of the Clean
Water Act if construction work mvolves the discharge of fill matenal in waters and/or
wetlands of the Ututed States
Location
The current proposed bank is positioned wrthm the floodplam of the New River and the
site s western boundary encompasses the New River It is located at 34° 55 19 34 N
77°37 02 38 W north of NC Hwy 24 and Jesse Williams Road intersection west of
Richlands Onslow County North Carolma The site is srtuated within the Hydrologic
Umt Code(HIJC) 03020302 of the Onslow Bay Watershed Boundary River Basm
formerly the HUC 0303001 (New)of the White Oak River Basm
Ezishng Site Condit�ons
The proposed 31 acre New River bank pro�ect site is compnsed of(2) separate parcels
and is located in a rural community with low density housmg agnculture and
timberlands The property has been histortcally cleared stumped and ditched and is
presently maintamed as pastureland An approximate 0 2 acre pond is located withm the
southeast corner of the tract
The proposed bank is positioned within the 100 year floodplam of the New River
Hydrology from the site flows through a series of ditches that empty directly mto the
nver Due to extensive pastwYng the ma�onty of the tract is void of canopy trees and
understory bemg predommantly vegetated with grasses and other herbaceous cover
Several soil types are mcluded witlun the bank boundanes but mostly consist of
Muckalee loam a hydnc soil that is a level to nearly level poorly dramed soil located on
floodplams All other mapped soil types are non hydric and are the followmg Craven
fine sandy loam which may have hydric soil mclusions Norfolk loamy fine sand with 0
2 percent slopes Norfolk loamy fine sand with 2 6 percent slopes which may have
hydnc soil mclusions and Pactolus fine sand wluch also may have hydnc soil
mclusions
Pro,ect Purpose
The purpose of the proposal is to establish a stream and wetland mitigation bank witivn
the 31 acre tract m order to provide compensatory mitigation for stream and ripanan
wetlands tmpacts associated wrth Department of the Army authorizations made pursuant
to Section 404 of the Clean Water Act
Pro�ect Descript�on
The bank srte is an extensively ditched floodplain of the New River Restoration and
enhancement activities for perenmal streams mtermittent streams and riparian wetlands
are proposed on the tract Ex�stmg ditches are being characterized as G type (gully)
channels and based on undisturbed zero to first order streams m the area historic
conditions for the onsite drainage ways would characterize them as D type (multi stem)
channels that grade to smgle stem E type channels in their pre converted conditions
Prelimmary plans show the construction of two stream types The upstream reach of
Tnbutary 1 and the entire length of Tnbutary 2 are proposed for D type(mult� stem or
braided) channels and the lower reach of Tnbutary 1 and the entire length of Tributary 3
will be designed for E type channel construction The existing ditches v�nll be back filled
m order to facilitate the construction of the proposed channels After stream construction
�s completed subsequent vegetation plantmgs will occur m order to reestabl�sh a coastal
plam bottom land hardwood forest
The Sponsor proposes to accomplish the followmg within the bank 1)Restore�2 000
lmear feet of perenmal stream �9951mear feet of interm�ttent stream and�15 2 acres of
npanan wetlands and 2) Enhance�2 2 acres of ripanan wetlands The work is intended
to generate approximately 2,995 linear feet of stream credits and approximately 16 3
credits of npanan wetlands to be used for compensatory mitigation The implementation
of the plan is expected to remove nonpomt source pollution reduce downstream sediment
load reestablish stream stability for transportmg watershed flows and sediment promote
floodwater attenuation improve aquat�c and terrestrial habitat and restore and reestablish
natural commuruty structure diversity and functional contmurty
The proposed Geographical Service Area(GSA)is withm the Onslow Bay River Basm
and mcludes the 03020302 8 Digit HLJC which extends from the headwaters of the New
River to its mouth at the New River Inlet The sponsor who has a contract to purchase
the land fee simple plans to transfer a perpetual conservation easement for long term
protection and management to a potential holder At tlus point the sponsor antic�pates
that the North Carolina Wildlife Habitat Foundation will hold the easement
Evaluahon and Commenhng Information
The Corps is solicitmg comments from the public Federal State and local agencies and
officials includmg any consolidated State Viewpomt or wrrtten position of the Governor
Indian Tnbes and other interested parties in order to consider and evaluate the
establishment of the New River Stream and Wetland Mitigation Bank Any comments
received vv�ll be considered by the Corps of Engineers in evaluatmg the approval of this
bank To make this decision all factors which may be relevant to the proposal will be
considered mcludmg the cumulative effects thereof among those are conservation
economics aesthetics general environmental concerns wetlands histonc properties fish
and wildlife values flood hazards flood plam values (in accordance with Executive
Order 11988) land use navigation shoreline erosion and accretion recreation water
supply and conservation water quality energy needs safety food and fiber production
mmeral needs considerations of property ownership and m general the needs and
welfare of the people
The Corps has reviewed the prospectus and has exammed all mformation provided by the
sponsors Our prelimmary review mdicate the following 1)An Environmental Impact
Statement will not be required 2)No listed species of fish wildlife and/or plant species
(or Cnhcal Habrtat) under the Endangered Species Act of 1973 is expected to be
impacted by the construchon of the bank and 3)There are no cultural or historic
resources located withm the proposed pro�ect srte A no effect detertrunation for
threatened and endangered species and for cultural and/or lustonc resources has been
made at this time Any additional or new information may change any of these
preliminary findmgs
Written comments pertment to the proposed work as outlined above will be received by
the Corps of Engineers Wilmmgton Distnct until Spm December 30 2011 Comments
should be submitted to Mr Mickey Sugg 69 Darlington Avenue Wilmmgton North
Carolma 28403 or via mternet at mickey t su�g�(a�usace army mil If you have any
questions or in need of a copy of the bank prospectus please contact Mr Sugg at(910)
251 4811
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Proposed wetlanC restoration = 15.6 acres {
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Prepared for: ProjecC Titie: Drawn by: SGD �
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� NEW RIVER Proposed
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,.�^ .,u��r � Onslow County, NC Projecr. 09-002.11
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PROSPECTUS
New River Stream and Wetland Mitigation Bank
BANK SPONSOR: RESTORATION SYSTEMS, LLC
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Submitted To:
U. S. Army Corps of Engineers, Wilmington District
� � � . , �
November 22, 2011
TABLE OF CONTENTS
1 Descnpt�on of the Mrtigatton Bank 1
2 Goals and Ob�ectives 1
3 Establ�shment of the Mit�gation Bank 2
4 Operation of the M�tigation Bank 2
5 Descrtptton of the Serv�ce Area for the Mitigation Bank 3
6 Need for the Mit�gation Bank 3
7 Technical Feasibil�ty of the Mitigation Bank 3
8 M�tigatton Bank Ownershtp/Long term management Strategy 3
9 Qualificat�ons of Sponsor to Successfully Complete Bank 4
10 Ecolog�cal Suitab�lity of the Bank to Achieve its ObJect�ves 5
11 Assurances of Sufficient Water Rights to Support the
Long term sustainabil�ty of the Proposed Bank 5
Append�x A Supplemental Technical Report A 1 A 15
Appendix B Site F�gures
Figure 1 Pro�ect Location Map
Figure 2 Hydrologic Unit Map
Figure 3a Topography& Drainage Area
Figure 3b Deta�led Topography
F�gure 4 Existing Condrtions
F�gure 5 Proposed Condrt�ons
F�gure 6 NRCS Soils
New Rrver Stream and Wetland M�uganon Bank Table of Contents
Prospectus
i
Th�s Prospectus has been prepared m conformance with the gu�dance given �n the federal m�t�gation rule
which can be found at http//www epa gov/owow/wetlands/pdf/wetlands_mit�gatton_final_rule_4_10_08 pdf
1 Descr�ption of the M�tigat�on Bank
The Bank is a 31 acre composite of two land parcels owned by the Thompson fam�ly The Bank �s
predominately pasture and is situated approximately 8 9 miles east from the center of Beulav�lle and
approx�mately 4 2 miles northwest from the center of Richlands in northwest Onslow County (Figures 1 5)
The Bank encompasses portions of three unnamed tr�butar�es to the New R�ver which have been assigned a
Best Usage Class�fication of C NSW The Bank has been cleared of nat�ve forest vegetation streams have
been relocated ditched and stra�ghtened and groundwater hydrology has been lowered due to ditch�ng and
channel�zmg of Bank streams and their floodplains Based on prel�m�nary analyses the Bank is best suited
for the removal of agricultural practices followed by restorat�on of Bank streams wh�ch w�ll �n turn restore
histortcal groundwater hydrology to the dra�ned r�partan hydr�c soils stream profiles will be elevated to
restore overbank flooding capacities followed by reestabl�shing of forested wetland vegetat�on These
efforts w�ll result �n the establishment of functional ecologically relevant streams and assoc�ated r�panan
r�ver�ne wetland communrttes
The land is located within 14 digit Hydrologic Unit and (DWQ) Targeted Local Watershed
03030001010010 (North Carolina D�vis�on of Water Qual�ty Subbasin 03 OS 02) of the White Oak R�ver
Bastn and will service the USGS 8 digrt CU 03030001
�
Almost 3000 stream m�tigation units (SMU s) and more than 16 wetland m�t�gat�on un�ts (WMU s) will
result from these mrtigat�on efforts(See Table 1)
Table 1 Summary of Stream and Wetland M�t�gat�on Un�ts
Streams Wetlands
T e Restorat�on Len th SMU's T e M�t� at�on Area ac WMU's
Braided Perennial 2000 2000 Restoration 15 2 15 2
Intermittent 995 995 Enhancement 2 2 1 1
Total 2995 2995 Total 17 4 16 3
2 Goals and Ob�ectrves
The primary goals of this stream and wetland restoration pro�ect focus on �mprov�ng water quality
enhanc�ng flood attenuation and restor�ng wildlife habitat and will be accomplished by the following
1 Remov�ng nonpo�nt sources of pollution assoc�ated w�th agr�cultural production �nclud�ng a)
removal of lrvestock b) cessation of broadcasting fertilizer pest�c�des and other agr�cultural
materials into and ad�acent to Bank streams/wetlands and c) restoration of forested riparian
wetlands ad�acent to streams to treat surface runoff
2 Reducing sedimentation w�thin on site and downstream receiving waters through a) reductton of
bank eros�on vegetation maintenance plowing and hoof shear to Bank streams and wetlands b)
removal of livestock from the Bank and c) restoration of forested ripanan wetlands ad�acent to
Bank streams
3 Reestablishing stream stability and the capacity to transport watershed flows and sediment loads by
restortng stable dtmension pattern and profile supported by natural in stream habitat and
grade/bank stabilization structures
New River Stream and Wetland Mitigat�on Bank pg I
Prospectus
4 Promoting floodwater attenuation by a) reconnecting bank full stream flows to the abandoned
floodplatn b) restor�ng secondary entrenched tr�butaries thereby reducing floodwater velocrties
wrthin smaller catchment basms c) restormg depressional floodpla�n and side slope wetlands to
increase the floodwater storage capacity w�thm the Bank and d) re vegetating Bank floodplams to
increase frictional resistance on floodwaters crossing Bank floodplains
5 Improv�ng aquat�c habrtat by enhanc�ng streambed var�abilrty and the use of in stream structures
6 Prov�ding a terrestrial wildl�fe corridor and refuge m an area extensively developed for agr�cultural
product�on
7 Restormg and reestablishing natural commun�ty structure hab�tat divers�ty and functional
cont►nu�ty
8 Enhanc�ng and protecting the Bank s full potential of stream and wetland functions and values �n
perpeturty
3 Establ�shment of the Bank
Following a per�od of m house and field invest�gattons of stream channels and the biolog�cal chem�cal and
phys�cal character�stics of the Bank s sotls hydrology and vegetation the Sponsor entered mto an
agreement with the land owner(s) establishing a conservation easement to protect the aquat�c resources �n
perpeturty
After the new mrtigation Bank has been fully approved by the IRT including the execution of the
M�tigat�on Banking Instrument the approved des�gn will be implemented by a m�t�gation construct�on
company using the latest techmques in mitigat�on�mplementation
The Bank will be established followmg complehon of a sertes of processes that are considered to be
standard pract�ces m the mit�gat�on banking industry(green=tasks already successfully completed)
• GIS landscape level Bank evaluat�on
• Landowner contact
• Techn�cal �nvestigations of
• Soils Bank hydrology drainage features plant and an�mal commun�ties rare species rare hab�tats
etc
�
� Bank restoration/enhancement/preservation potenttal
• Land Acquisrt�on ..
• Preparat�on of mrtigation plan mcluding conceptual design
• Submit prospectus to the [RT for review and approval
• Complete des�gn and subm�t Mitigation Plan and MBI to [RT for approval
• Implementation and Monitortng
4 Operat�on of the Bank
Followmg �mplementation of the Bank design an As bu�lt drawmg will be completed which will establ�sh
details and dimensions of all constructed features in the new mitigatton Bank
The Sponsor w�ll mamta�n ownersh►p of the Bank for seven years beyond the Bank s tmplementat�on so
that annual momtor�ng activrties can be undertaken as specified in the pro�ect s Mrtigation Plan The
Sponsor will contract with one or more experienced technical firms to ensure that monitor�ng tasks are
performed m accordance w�th acceptable standards and pract�ces The firm w�ll be responsible for
collecting groundwater hydrology data us�ng dig�tal piezometers positioned at pre determined locat�ons
New Rrver Stream and Wetland Mitigation Bank pg 2
Prospectus
i
Vegetatton will also be monitored to ensure that sufficient trees and shrubs survrve throughout the areas
planted
Stream physical attributes includtng m stream structures w�ll be monrtored and documented usmg
photographic and other methods Where necessary macro benth�c samples will be taken and analyzed in
an attempt to determine how quickly the stream s aquat�c life rebounds from its history of agr�cultural
influences and from rts more recent mit�gat�on �mplementation
5 Descript�on of the Servue Area
The Bank ltes withtn 8 d�git cataloging unit 03030001 known as Wh�te Oak Ol The Bank �s found near
the upper limit of the catalog�ng unrt where Jones Dupl�n and Onslow Counttes �oin White Oak Ol �s
wedged between several Neuse and Cape Fear R�ver Basin catalog�ng units with Cape Fear 07 prominently
positioned along rts western per�meter and Neuse 04 to rts north It �s interest�ng to note that the Tar Pam
R�ver Basin boundary forms the eastern perimeter of White Oak Ol The catalog�ng un�t takes all of
Onslow County except the extreme west and the extreme east and rt also takes in the beachfront landscape
from Caroltna Beach to Brown s Inlet �n New Hanover and Pender Counties
The area of the catalogmg un�t near the proposed mitigation Bank �s rural agricultural sparsely interspersed
wrth res�dential sites This rural agricultural mix �s idenhcal throughout Jones Duplin and northern
Onslow Counties Land use in the highly developed Jacksonv�lle area and �n the narrow beachfront area to
the south are substantially different from the rural nature of the rest of the catalogmg unit
6 Need for the Bank
` A search of public records by the Sponsor �dent�fied one mrttgation bank proposed �n the 8 digrt cataloging
untt 03030001 (Wh�te Oak O1) the default serv�ce area for the proposed mitigation bank The proposed
New River Bank has a different ripar�an wetland credit type but will potenttally compete wtth stream
credits Furthermore �t is reasonable to predict even moderate growth w�ll occur in the geographic area
defined by thts hydrologic unit
7 Techmcal Feasib�hty of the Bank
The technical feasibil�tv of the Bank is constdered to be reasonably assured based on several factors
(1)the absence of fatal flaws such as hydrological trespass presence of rare species or thetr habitats and the
absence of nationally stgnificant historical or archaeological resources and (2)the presence of hydr�c soils
and the possess�on of knowledge of how best to restore suffic�ent hydrology to these areas to restore
funct�onality The feas�bilrty was determined from careful srte evaluat�ons by Ax�om Env�ronmental Inc
�nclud�ng b�olog�cal geotechn�cal and hydrological Furthermore the Sponsor �ntends to bring highly
skilled well experienced expert�se to bear on des�gn plamm�g and �mplementatton of the Bank
8 Mit�gation Bank Ownership/Long Term Management Strategy
I
The Sponsor has a contract to purchase the land underly�ng the Bank m fee simple Pr�or to the first cred�t
release the Sponsor will place a Conservation Easement over the proJect area The Conservat�on Easement
w�ll be m the form currently used by the Wilmington D�stnct Corps of Engmeers for the long term
protection of compensatory mitigat�on banks The easement will allow the Sponsor to complete all work
necessary to establish the proposed stream and wetland mitigation bank and to protect it in perpetu�ty The
Conservatton Easement preserves all natural areas and prohibits all use of the property inconststent with its
use as mrt�garion property tncluding any activrty that would matenally alter the biolog�cal �ntegrrty or
funct�onal and educational value of wetlands withm the Bank consistent with the mitigation plan The
New R�ver Stream and Wetland Mrtigahon Bank pg 3
Prospectus
purpose of the conservatton easement �s to assure that future use of the Bank will result m the restorat�on
protection mamtenance and enhancement of wetland and stream functions described m the mrtigation plan
Prior to execution of the MBI the Sponsor shall deliver a trtle opmion acceptable to the IRT cover�ng the
mitigatton property The property shall be free and clear of any encumbrances that would confl�ct with its
use as mitigation including but not l�m�ted to any liens that have prior�ty over the recorded preservat�on
mechamsm
Upon successful completion of all monitoring activ�ties on the Bank and the release of all cred�ts the
Sponsor will transfer ownershtp of the Conservat�on Easement to an appropriate long term steward At this
point the Sponsor ant�cipates that the North Carolina Wildl�fe Habitat Foundat�on w�ll hold the easement
The final determination of a long term conservat�on holder w�ll be made in con�unction wrth the [RT and
w�ll be responsible for per�odic rospection of the easement area to enforce the conservat►on provis�ons The
sponsor w�ll provide funding to the easement holder to enable such acttvrty
Throughout the pro�ect s l�fe cycle the Sponsor will be �mplementing principles of adaptive management
and continuously assessing the progress of the proJect as �t relates to the restoration plan construction
documents and monrtonng provis�ons described herein If at any t�me such plans need reviston or
modification to ensure a successful restorat�on the Sponsor will not�fy the Corps and work to approprtately
mod�fy pro�ect plans S�nce the primary goal of the pro�ect is to restore natural streams �n the Bank it �s not
ant�c�pated that long term management (other than oversight of human act�v�ty as described above) w�ll be
necessary beyond the monitoring pertod
9 Qual�ficat�ons of Sponsor
RS has been a preem�nent force in the development of successful aquat�c m�t�gat�on Banks �n North
Carolina for more than 15 years RS s quaLfications are best illustrated by rts track record �n selectmg
high quality sites and highly sktlled technical experts in srte evaluation design and �mplementation �s well
demonstrated RS has designed and implemented more than 25 wetland stream and ripartan buffer
mrt�gation srtes/banks in Maryland Texas Tennessee Louisiana Pennsylvanta and North Carolina
representing thousands of acres of wetlands and m�les of streams Furthermore RS prov�des financ�al
surety for every pro�ect through every phase of work and each s�te �s mspected by staff at least quarterly
follow�ng the completion of monitoring responsibil�ttes [ncluded among the stream and wetland mitigation
pro�ects completed or tn advanced plamm�g by RS are
Pro�ect State Status
Anderson NC Monitormg Year 5
Angola Bay NC [n Development
Bear Creek NC Post Monrtonng
Big Bull Creek NC Monrtormg Year 5
Brogdon Road NC Momtoring Year 5
Brown Marsh Swamp NC � Monrtoring Year 4
Burrows Cove TN Monrtoring Year 2 �
Cane Creek NC Monrtoring Year 4
Carbonton Dam NC Close Out
Casey Da�ry NC Close Out
Causey Farm NC Close Out
The Cliffs NC In Development
Columbus Swamp NC Momtoring Year 3
Cutawhiskie NC Monrtoring Year 4
New River Stream and Wetland Mit�gation Bank pg 4
Prospectus
Elk Shoals NC Momtoring Year 5
Fox Run NC Monitoring Year 2
Frog Hollow NC Close Out
Gatl►n Swamp NC Mon�toring Year 5
Gray Farm NC Monrtoring Year 5
Haw River NC Close Out
Herman Dairy NC Under Construction
Holly Grove NC Monrtor�ng Year 3
Jarman s Oak NC Monitormg Year 4
Lick Creek NC Monitormg Year 5
Lloyd NC Monitor�ng Year 5
Lowell Mill Dam NC Close Out
Morgan Creek NC Mon►toring Year 3
Salisbury W�comico MD Monrtor�ng Year 4
Sleepy Creek NC Monitortng Year 5
Summrt Seep NC Under Constructton
Three M�le Creek ! NC Monrtor�ng Year 3
Cranstons M�ll Pond � VA Under Construction
Cripple Creek I NC Monrtaring Year 1
Bass Mountatn I NC [n Development
Pancho , NC In Development
Salisbury III �I MD In Development
Jesuit Bend LA In Development
South Lafourche I LA In Development
Little Hazel I GA In Development
Katy Pra�rte ' TX [n Development
10 Ecolog�cal Suitabdity of the Bank to achieve the obJect�ves of the proposed mit�gat�on bank
The Bank is characterized by agricultural fields and historically modified streams and wetlands
Relatively modest alterations to site streams and other features will result �n measurable ecological gams in
aquatic funct�ons and values Hydrology,needed to sustain wetland functions will be restored by chang�ng
some of the morphometr�cs of the ad�acent stream channel reaches Furthermore l�vestock and agricultural
practices w�ll be precluded from any future encroachments into aquatic resources The Bank s ecolo��cal
suitabil� as a mttigation bank lies in the fact that its aquatic resources have been degraded over the
decades but its recovery through focused implementation of restoration and enhancement measures is
cons�dered to be relatively simple to ach�eve Proposed mttigation approaches are very ach�evable because
they do not oveneach but are guided b�y the likely h�stoncal pre agncultural attnbutes of the ex�sting
streams and wetland complexes
�
11 Assurance of suffic�ent water r�ghts to support the long term sustamabil�ty of the mit�gahon
bank
North Carol�na applies the concept of ripar�an r�ghts to water rather than water r�ghts as typ�cally
applted �n more arid parts of the United States As such npar�an owners are entrtled to reasonable use of
flow�ng water through their propert�es Any infr�ngement of such use may be addressed through c�vtl courts
(See North Carolina Department of Natural Resources D�vision of Water Qualrty — Instream Flow Unrt
Riparian Rights found at http//www ncwater org/Permrts_and_Registration/[nstream_Flow/mtroduct►on htm
(last visrted November 10 2011)
�
New Rrver Stream and Wetland Mit�gation Bank pg 5
Prospectus I
I
RS believes that the Bank s locat�on should ensure that natural processes w�ll cont�nue to provide sufficient
hydrology for the foreseeable future drought conditions notwithstanding Proposed modificat�ons to waters
�n the contr�buting watershed would have to meet ex�st�ng regulatory requirements which should �udge
such proposals in the context of impacts on downstream resources including mitigat�on banks Beyond a
rel�ance on normal weather patterns and exist�ng regulatory controls there �s nothing pract�cable that a bank
sponsor can do to assure perpetual ava�lability of sufficient water
J
l
J
New River Stream and Wetland Mitigat�on Bank pg 6
Prospectus
Append�x A
Supplemental Techntcal Report A 1 A 15
�
�
�
New River Stream and Wetland MrtigaUOn Bank Appenda A
Prospectus
SUPPLEMENTAL TECHIVICAL REPORT
1 Pro�ect Goals and Ob�ectrves �
This technical report details stream and wetland restoration potential at the proposed New R�ver Stream
and Wetland Mrtigat�on Bank (hereafter referred to as the Bank ) The Bank �s located wrthm 14 d�g►t
Catalog�ng Unit and NC Ecosystem Enhancement Program (NCEEP) Targeted Local Watershed
03030001010010 (NCEEP 2009) This is wrthin North Carol�na Divtsion of Water Qualrty Subbasm 03
OS 02 of the White Oak River Basm and will service the USGS 8 d►grt CU 03030001 The Bank is
situated approximately 8 9 miles east of Beulaville and approx�mately 4 2 mtles northwest of Richlands
in northwest Onslow County(Figures 1 and 2 Appendix B) The Bank encompasses approximately 31 0
acres of pasture land (F�gures 1 and 2 Appendtx B) Within the Bank existing streams have been
relocated ditched and stra�ghtened and riparian hydric soils have been cleared and dratned The Bank
encompasses portions of three unnamed tributaries (UTs) to the New R�ver [North Carolma Drvis�on of
Water Quality (NCDWQ) Stream Index Number 19 (1)] The Bank has been cleared of nat�ve forest
vegetat�on streams have been relocated d�tched and straightened and groundwater hydrology has been
lowered due to ditching of Bank streams and floodplains
The pr�mary goals of this stream and wetland restoration pro�ect focus on improv�ng water quality
enhancmg flood attenuation and restoring wildlife habitat and w�ll be accomplished by the followmg
1 Remov�ng nonpotnt sources of pollution assoc�ated wtth agricultural product�on �ncluding
a) removal of livestock b) cessat�on of broadcastmg fertilizer pest�cides and other agr�cultural
materials �nto and ad�acent to site streams/wetlands and c) restorat�on of forested r�parian
riverme wetlands ad�acent to streams to treat surface runoff
2 Reduc�ng sedimentat�on wrthm onsrte and downstream rece�ving waters through a) reduct�on of
bank erosion vegetatton mamtenance plowmg and hoof shear to Bank streams and wetlands
b) removal of livestock from the Bank and c)restoration of forested ripar�an wetlands ad�acent to
Bank streams
3 Reestablishmg stream stab�ltty and the capacity to transport watershed flows and sediment loads
by restormg stable dimension pattern and profile supported by natural in stream habitat and
grade/bank stabil�zation structures
4 Promoting floodwater attenuation by a) reconnect�ng bankfull stream flows to the abandoned
floodplam b) restoring secondary entrenched trtbutaries thereby reducing floodwater veloc�ttes
withm smaller catchment basins c) restormg depress�onal floodplam and s�de slope wetlands to
increase the floodwater storage capac�ty withm the Bank and d) revegetating Bank floodplams to
increase fr�cttonal resistance on floodwaters crossing Bank floodplatns
5 [mproving aquat�c habrtat by enhancing stream bed var�ab�lrty and the use of�n stream structures
6 Provtd�ng a terrestrial wildlife corrtdor and refuge in an area extensively developed for
agricultural product�on ,
7 Restormg and reestablishmg natural commurirty structure habitat diversity and functional
continuity
8 Protecttng the Bank s full potential of stream and wetland functions and values in perpetuity
These goals will be achieved by the followmg actions
• Provid�ng a mmimum of 2995 Stream M�tigatton Units by
o restormg approximately 1700 Imear feet of exist�ng perenmal stream channel through
construction of a stable stream valley to allow for natural creation of stable D type stream
systems cessat�on of current land use practices exclud�ng livestock planting with native
New R�ver Stream and Wedand M�Ugat�on Bank A I
Supplemental Techmcal Report
forest vegetation and plugging anc�llary�drtches currently used to dratn riparian soils for
agr�cultural purposes m order to restore h�storic ground water levels that �nfluence
perenn�al stream hydrology
o Restor�ng approximately 300 linear feet of perennial stream channel and 995 linear feet of
intermittent stream channel through construction of stable single thread channel (E type)at
the histonc floodpla�n elevat�on cessahon of current land use practices excluding
livestock and planting wrth nattve forest vegetat�on and pluggmg anctllary drtches
currently used to direct surface flow and ground water away from the h�stor�c interm�ttent
channel location for agr�cultural purposes
• Provtdmg 16 3 Ripar�an R�verme Wetland Mrtigation Unrts by
o Restormg approximately I S 2 acres of r�par�an wetland by restormg stream �nverts to
historic elevattons to rehydrate stream side wetlands el�mmatmg detrimental land use
pract�ces backfilling drtches and pond and planting with nat�ve forest vegetat�on
o Enhanc�ng approx�mately 2 2 acres of r�partan wetland elim�nating by el�m�nating
detrimental land use practtces removal of�nvasive spec�es and plant�ng with native forest
vegetahon
• Protecting the Bank in perpeturty wrth a conservat�on easement
Pro�ect Descr�ptton
The Bank �s encompassed within two parcels utilized as pasture land and is situated �n the floodplain of
the New River The Bank has been cleared of native forest vegetatton streams have been relocated
d�tched and stra�ghtened and groundwater hydrology has been lowered due to ditching of Bank streams
(Figure 4 Appendix B)
2 Physiography and Land Use
The Bank is located �n the Carolma Flatwoods ecoregion of North Carolina within Un�ted States
Geolog�cal Survey (USGS) Catalogmg Unrt 03030001 of the Whrte Oak R�ver Basin Regional
physiography �s characterized by flat plams on I�ghtly dissected mar�ne terraces The ecoregion is
characterized by Carolina bays swamps and low gradient streams with s�lty or sandy substrate This
port�on of North Caroltna was covered by shallow coastal waters durmg the Ple�stocene and the resultant
terraces and shoreline related landforms are covered typically by fine loamy and coarse loamy so�ls wrth
period�cally h�gh water tables (Gnffith et al 2002) Elevat�ons withm the Bank range from 42 52 feet
National Geodetic Vertical Datum [USGS Richlands NC 7 5 minute topographic quadrangle (2010) and
2 foot elevation contours generated from 2007 L�ght Distance and Rangmg (L�DAR) data] (F�gure 3b
Appendix B)
The primary hydrologic features of the Bank cons�st of three unnamed tnbutaries to the New Rrver and
associated floodplains s�de slopes and hydric soils (Figure 4 Appendix A) The Bank provides water
yual�ty functions to an approx�mately 66 acre (0 1 square mile) watershed at the Bank outfall (F�gure 3a,
Appendix B)
3 Water Qual�ty
The Bank is located wrthm the Cape Fear River Basin in 14 d�grt USGS Catalogmg Unrt
03030001010010 of the South Atlantic/Gulf Reg�on (NCDWQ subbasin number 03 OS 02) [F�gure 2
Appendix A]) The Bank is located ad�acent to the New River and contains unnamed tributartes to the
New River which have been assigned NCDWQ Stream Index Number 19 (1) and a Best Usage
Classtficahon of C NSW (NCDWQ 201 la) The reach of the New Rrver that receives waters from the
New Rrver Stream and Wetland Mrtigation Bank A 2
Supplemental Techmcal Report
)
Bank rece�ved a Good Fa�r rat�ng based on benth�c macromvertebrate sampling �n 2010 Sampling in
2004 also resulted m a Good Fa�r ratmg (NCDWQ 2011 b) This reach of the New R�ver is listed as
Fully Supporting its �ntended uses however �t was l�sted as [mpatred and Not Supportmg fish
consumption due to high levels of inercury from 2002 through 2008 (NCDWQ 2002 2004 2006 2008
and 2010b) The reach of the new R�ver located approx�mately 7 mtles downstream of the Bank is listed
as impaired due to h�gh pH and h�gh levels of chlorophyll a copper and Enterrococcus (NCDWQ 2010)
Streams classified as C are surtable for aquatic life propagatton and survtval fishing w�ldlife secondary
recreahon and agr�culture Secondary recreation mcludes wad�ng boat�ng and other uses not mvolvtng
human body contact with waters on an organized or frequent basis NSW ts a supplemental classification
denot�ng waters sub�ect to growth of microscop�c or macroscopic vegetation requ�ring limitations on
nutnent mputs
l
4 Soils and Land Form
Soils that occur wrthin the Bank accord�ng to the Soal Survey of Onslow Counry North Carolana(USDA
1992) and the Natural Resource Conservat►on Serv�ce (NRCS) Web So�l Survey (USDA 2011) are
� depicted�n F�gure 6(Append�x B)and are descr�bed�n Table 1
The maJorrty of the Bank �s underlatn by soils of the Muckalee series Bank soils have been �mpacted by
plowing land clear�ng and agr�cultural product�on in add�t�on to landscape alterat�ons associated wrth
floodplain d�tchmg and dredgmgJstratghtening of stream channels
Table 1 NRCS So�ls Ma ed withm the Bank
So�l Senes H dric Status Famil Descrt tion
Nonhydric Th�s series consists of gently slopmg
Craven fine but may � moderately well dra�ned so�ls with slow
sandy loam conta�n hydr�c Aquac Hapludults permeabiltty on the r�dges of marine terraces
inclusions The seasonal high water table occurs at a depth
of 24 to 36 mches
This sertes cons�sts of level to nearly level
Muckalee Hydric Typic Fluvaguents Poorly drained soils w�th moderate permeab�l�ty
loam on flood plams The seasonal htgh water table
occurs at a de th of 0 to 12 inches
This series consists of level to nearly level well
Norfolk loamy dramed soils wrth moderate permeabtlrty on
fine sand 0 2 Nonhydr�c Typic Kandiudults broad �nterstream d�vides and r�dges on manne
percent slopes terraces The seasonal high water table occurs
at a de th of 40 to 72 inches
Nonhydric Th�s series consists of gently slopmg well
Norfolk loamy dramed soils with moderate permeabiltty on
fine sand 2 6 but may Typic Kandaudults broad interstream divides and the ridges on
percent slopes contam hydr�c manne terraces The seasonal high water table
inclus�ons occurs at a de th of 40 to 72 �nches
Nonhydric Th�s series conststs of level to nearly level
Pactolus fine but may Aquic moderately well dra�ned so�ls wrth rap�d
sand contain hydric Quartzapsamments Permeabilrty on the ridges of marme terraces
inclusions The seasonal high water table occurs at a depth
of 18 to 36 mches
New River Stream and Wetland Mrtigation Bank A 3
Supplemental Techmcal Report
5 Protected Spec�es
Based on the most recently updated county by county database of federally listed spec�es in North
Carolma as posted by the Unrted States F�sh and Wildl�fe Serv�ce (USFWS 2011) 15 federally protected �
spec�es are l�sted for Onslow County Table 2 lists the federally protected spec�es and �nd►cates �f
potent�al habrtat ex�sts wrthin the Bank for each spec�es
Habttat is present withm or ad�acent to the Bank for American all�gator Cooley s meadowrue and
pondberry American alligator is listed as T(S/A)and is not sub�ect to Section 7 consultat►on Surveys�n
su�table habitat for Cooley s meadowrue and pondberry will be conducted during the summer of 2012
One des�gnated unrt of Cr�ttcal Habrtat far piping plover is located tn Onslow County on the Bogue Inlet
wh�ch �s greater than 30 miles southeast/seaward of the Bank(USFWS 2001)
Table 2 Federall Protected S ecies for Onslow Count
Common Name Sc�ent►fic Name Status* Hab►tat Present W�thin Bank
Vertebrates
American alltgator Alltgator mrsstsstpptensrs T(S/A) Yes
Bald eagle Haliaeetus leucocephalus BGPA No
Eastern puma Puma concolor couguar E No
Green sea turtle Chelonta mydas T No
Leatherback sea turtle Dermochelys coraacea E No
Loggerhead sea turtle Caretta caretta T No
P�ping plover Charadrrus melodus T No
Red cockaded woodpecker Picotdes borealts � E No
Shortnose sturgeon Acrpenser brevirostrum E No
West [nd�an manatee Trachelus manatus E No
Plants
Cooley s meadowrue Thakctrum cooleyi E Yes
Golden sedge Carex lutea E No
Pondberry Lindera melissrfolaa E Yes
Rough leaved loosestrife Lysrmachaa asperulaefolia E No
Seabeach amaranth Amaranthus pumilus T No
T(S/A) Th ten d d t S m I ty f App aran tax h Ih ten d d m lanty f app aran wi h an h I st d p ( ih as Am an d I (Cmcrxly!
)and I t d f prot ct
BGPA P aed by h B Id and Gold E gl Prot n Att
E E dang ed tax dang f xc t t}v gh t all g f an po f ang
T Th en d ta�c 1 k ly bec m dang d wi h h f se bl f ur h gh ut all g f an pom f t ang
New River Stream and Wetland Mrtigation Bank A 4
Supplemental Technical Report
Benthic macromvertebrate samplmg was undertaken at several locat�ons wrthm the Bank on 1/14/2011 to
ass�st m the hydrological classification of on s�te water resources Sampl�ng locat�ons are dep�cted on
Ftgure 4(Appendix B) Results of the survey are represented below in Table 3
Table 3 Benth�cs Study
�_ .—_
�_� ^ w z > >
�Stream Fomi and Assesment DaW_ 3 m o � � E o 0 0 �
� v 3 0
�' o h — � � a c � — in
o v
v
__ ` � t o a « � � � '�` m o
NCDWQ USACEStream � �o > °' E ° °° ° L
F o 0o m « x
Site eamlDFoAssessmentFortn ¢ � � o u° � m LL 3 � z° 3 �
� 1 29 33 24+ 24+ 3 1 1 6 to 12 1 1 4 to 6 6 ro 12
2 32 38 24+ 24+ 6 5 8to 12 12to 24 1 1
3 26 25 34 24+ 24+ 6 8 8 to 12 12 ta 24 2 1
�te lowtwns are depicted on Figure 4�Appendix B� 1 �_J � , � �— � �
� NCDWQ,USACE and Benth¢data collection forms are avadable upon request_ j � _ 1 �_ I _�_�_ �j _�
The Bank encompasses several unnamed tr�butaries to the New Rrver Table 4 g�ves characteristics of
Bank streams the locat�ons of each are deptcted in F�gure 4(Append�x B)
None of the UTs are depicted on the USGS 7 5 m�nute topographic quadrangle however UTs 1 and 2
exhibrted charactertsttcs of perenmal streams during field investigations Geomorphology scores for
these streams are generally low due to historical manipulation and disturbance UT3 �s a rel�ct channel
that has had water d�verted through a large ditch to flow to UT2 and has been subsequently abandoned
Currently UT3 only receives flow dur�ng large storm events and overbank events of the New River
Table 4 Exist�n Stream Character�stics
Stream Reach USGS USGS Stream *Field Stream NCDWQ Stream
Stream Order Classificat�on Classification Form Score
UT 1 0 not shown erenmal 29
UT2 0 not shown erenmal 26 25
UT3 0 not shown e hemeral
ZField Stream Classification and NCDWQ Stream Form Score These tributanes are not shown on the
USGS 7 5 mmute topographic quadrangle and received less than 30 points on the NCDWQ Stream
Identification Form however drtched and mcised streams exhibrted characteristics of perennial streams
dur�ng field investigat�ons and pr�marily lack geomorphology �ndicators due to disturbance and
ma�ntenance (see attached NCDWQ stream classification forms) In addrtion UT3 is a small drtch that
only receives flow dur�ng large storm events and overbank events of the New River [n order to avo�d
hydrologic trespass subsequent to restoratton activrt�es the reach of UT3 wrthm the Bank must be
restored to carry hydrology currently d�verted into UT2
On Bank streams have been drtched straightened and exhib�t character�st�cs of typical G type(gully)and
F type (widened gully) channels The lack of deep rooted nparian vegetation appears to have resulted m
additional bank eroston to`the Bank channel Continued erosion wtll eventually result m lateral extension
of the G type channels into F type (widened gully) channels The F type channels will cont�nue to wtden
laterally unt�l the channel �s wide enough to support a stable C type or E type channel at a lower elevation
and the original floodpla�n�s no longer sub�ect to regular flooding
New Rrver Stream and Wetland Mrtigation Bank A 5
Supplemental Technical Report
s
� �
Bank streams have been relocated d�tched and stra�ghtened and are currently unstable with little to no
r�par�an buffer Table 5 provides a summary of a prel�mmary estimate of potent�ally stable stream
attributes Prelimmary estimates of stable stream attr�butes are based primarily upon observations along
the exist�ng reaches and regional curves for the Coastal Plam of North Carolina(Geratz and Sweet 2003)
6 Hydrology
This hydro physiographic region �s characterized by moderate rainfall w�th prectprtation averag�ng
approximately 56 inches per year (USDA 1992) Bank d�scharge appears to be dommated by a
combinat�on of upstream basin catchment groundwater flow and prec�pitation Based on regtonal curves
(Geratz and Sweet 2003) the bankfull d�scharge for a 0 1 square mile watershed is expected to average
approximately 1 5 cub�c feet per second and occur approximately every 1 3 to 1 5 years (Rosgen 1996
Leopold 1994)
Stream Classificat�on
Stream geometry and substrate data have been evaluated to orient stream restorat�on based on a
class�ficat�on utilizing fluvial geomorphic pr�nciples (Rosgen 1996) Th�s classificat►on stratifies streams
into comparable groups based on pattern dimens�on profile and substrate character�st�cs Primary
components of the class�ficahon mclude degree of entrenchment width depth raho sinuosrty channel
slope and stream substrate composttion Stream classes currently associated wtth the Bank include F
and G type streams
Historic onsrte reaches most likely would have been classified as D type and E type stream morpholog�es
D type streams are multiple channel systems descnbed as braided streams occurr�ng wrthin broad alluvial
valleys D type streams are character�zed as sltghtly entrenched high w�dth/depth ratio streams
exhibrtmg low sinuosity (<1 2) 0.type streams typ�cally exh�brt a senes of closely spaced rapids and
scour pools formed by convergence/divergence processes Although D type channels are not typically
� considered stable in the Coastal Plain physiographic province of North Carolma these stream types are
cons�dered appropnate for mit�gation purposes as streams in th�s area would l�kely not support engmeered
stream channels due to the lack of slope and sandy terram (USACE et al 2005) E type streams are
characterized as slightly entrenched r�ffle pool channels exhibiting high sinuosity (1 3 to greater than
1 5) E type streams typ�cally exhibit a sequence of riffles and pools assoc�ated wrth a s�nuous flow
pattern In North Carolina, E type streams often occur in narrow to w�de valleys wrth well developed
alluvial floodplains (Valley Type VIII) E type channels are typically considered stable however these
streams are sensitive to upstream dramage basin changes and/or channel disturbance and may rap�dly
convert to other stream types
New Rrver Stream and Wedand Mmgauon Bank A 6
Supplemental Techmcal Report
Table 5 Stream Geomet and Classificat�on
Attribute Pro osed D T e* Pro osed E T e
DA O1 Ol
Abkf 1 6 1 6
A � 6 8 6 8
WbkF g� 4�
�bkf �2 �4
� /
D„� 03 07
Wbkfl�bkf 40 1�
FPA 60 60
ENT 7 5 15
LBH 03 07
BHR 10 � 10
Wbelt The proposed channel will consist 28 �
Wbelt�Wbkf of interconnected distr�butary 7
Lm channels consist�ng of a closely 40—56
Lm�Wbkf spaced series of rapids and scour l0— l4
L pools formed by 20—28
L Wbkf convergence/divergence processes $—'7
SIN 11 13
Stream T e D T e E T e
Pr po d D typ I ar m I f II han I ass at d with b a�d d st am morph I gy
DA Dramage basin area(square m�les) BHR Bank height ratio [low bank he�ghdDm�
Ab� Bankfull cross sect�onal area (r�ffle) (square (nffle)]
feet) Wb i, Belt width(feet)
A , � Ex�sting cross sectional area (riffle) (square Lm Meander wavelength(feet)
feet) LP P Length from pool to pool(feet)
Wb� Bankfull w�dth(r�ffle)(feet) SIN Smuosity (thalweg distance/stra�ght lme
Db� Average bankfull depth(r�ffle)(feet) distance)
Dm� Maximum bankfull depth(r�ffle)(feet) S W Slope of the water surface(r�se/run)
FPA Floodprone area(feet) S �ie,, Slope of the valley(r�se/run)
ENT Entrenchment rat�o(FPA/Wb�)
Onsrte streams h�storically were charactenzed by backwater slough mulh stem channels Currently
these systems have been cleared of vegetation and dredged resulting �n a drtched smgle thread channel
that exhibits characterist�cs of a G type (gully) channel Bra�ded backwater slough type channels
function for flood flow suppresston pollutant removal and reduced sed�mentation mto downstream
recerving waters The existmg dredged channel through the h�storic backwater slough has not only
hindered these �mportant water quality functions but lowered ad�acent groundwater tables thereby
reducmg the area of and/or degrading assoc�ated�urisdictional wetlands
D�mension
Regional curves (Geratz and Sweet 2003) were util�zed to determine bankfull channel cross sectional
areas of Bank stream reaches Using th�s method a departure from stabil�ty could be est�mated based on
a comparison of ex�sting and proposed/stable dimension var�ables
Undisturbed zero to first order streams m the area are character�zed by D type (multi stem) channels that
grade to single stem E type channels Existing stream channels are characterized by single thread
New River Stream and Wetland MrtigaUOn Bank A 7
Supplemental Technical Report
t i
overstzed and entrenched channels as �nd�cated by high bank he�ght ratios and oversized channels
Measures to reduce channel size (cross sectional area) reduce bank height ratios and restore braided
stream morphology should be targeted for th�s pro�ect
Profile
Based on LIDAR contours the onsite valley slope measures approximately 0 004 rise/run Estimated
valley slopes appear typ�cal for the Coastal Plain physiograph�c reg�on of North Carolina Onsrte streams
are character�zed by human man�pulation(drtching and stra�ghtening) which has resulted in water surface
slopes that are equal to the valley slope In add�t�on channel mod�fications have removed channel bed
morphology that supports hab�tat for aquatic l�fe survival and function Pools and riffles that support area
w�ldlife hab�tat also increase resistance of floodwaters and provide surface water storage mclud�ng vernal
pools wetland pockets coarse textured r�ffles and an enlarged hyporheic zone Measures designed to
restore braided channel complexes thereby promotmg stormwater dissipat�on benefihng water qual�ty
through improved wetland funct�on and increas�ng aquat�c and terrestrial w�ldlife habrtat are expected to
be targeted on these stream reaches
Plan Form
Bank streams have been dredged and stra�ghtened resultmg m s�nuosrty measur�ng approximately 1 0
(thalweg distance/valley distance) Due to channel ditching and straighten�ng act�vrt�es no dtst�nct
repetittve pattern of riffles and pools or bra�ded channels occurs tn the existmg channel Based on plan
form var�ables Bank streams contain reaches that have been degraded by 1) clearing floodplain
vegetatton 2) l�vestock trampl�ng and levelmg of rel�ct channels sloughs wetland pockets and other
bra�ded channel morphological features 3) straightening result�ng �n the loss of divergendconvergent
channel sequences and reduction m sinuosity and 4)a subsequent reduction m the overall length of Bank
channels Mrtigation efforts along degraded sections should target restoration of histor�c braided channel
morphology
7 Bank Design and Implementation Constramts
The presence of condittons or character�stics that have the potent�al to hmder restorat�on acttvmes on the
Bank was evaluated The evaluation focused pr�marily on the presence of hazardous matertals uttl�ttes
and restrictive easements rare/threatened/endangered species or crrtical hab�tats and the potential for
hydrologic trespass Existing information regardmg Bank constratnts was acquired and reviewed In
addition any Bank condittons that have the potenttal to restr�ct the restorat�on des�gn and �mplementat�on
were documented durmg the field mvest�gat�on
No evidence of natural and/or man made condirions was identified that has the potenhal to �mpede
proposed restorat�on activmes
8 Pro�ect Development
The primary goals of this restorat�on plan include 1) restoration of a mult� stem braided stream channel
2) restoration of riparian rtver�ne wetlands 3) enhancement of water quality funct�ons (reduce nonpomt
source sedimentation and nutr�ent mputs) 4) creahon of a natural forested r�parian buffer along onsrte
stream reaches 5) restorat�on of wildlife habitat associated with a rtpar�an corrtdor/stable stream system
and 6) establishment of a conservation easement which will encompass all restoration act�vities and
address landowner concerns
New Rrver Stream and Wetland Mit�gat�on Bank A 8
i Supplemental Techmcal Report
�
Pr�mary activ�ties designed to restore the stream and wetland complex �nclude 1) stream restoration 2)
wetland restoration and 3)vegetat�on planting(Figure 5 Appendtx B)
Stream Restoratton
Stream restorat�on is expected to entail 1) belt w�dth preparat�on and grading 2) spoil stockpiling 3)
channel stabilization 4) channel d�version 5) channel backfill and 6) vegetatton planting Minimal
channel excavation is proposed m assoc�ation with the D type streams It is ant�cipated that th�s stream
type will develop within the Bank without mtervent�on
Two stream types are proposed for restoration based upon physical features of the Bank The upstream
reach of UT1 and the entire length of UT2 are proposed for D type channel construction The lower
portion of UTl and the ent�re length of UT3 are proposed for E type channel construction D type
streams were determined to be appropr�ate for the low slope upstream reaches per guidance from the
NCDWQ(USACE et al 2005) UT3 and the downstream reach of UTl were selected for E type channel
construction due to channel slope and necessary elevatton drop to discharge to the New River
Beltwidth corridor preparation will entail cleanng and grubb�ng of the Bank Floodplains for E type
channels are expected to be approximately twice the w�dth of the channel (approximately 50 to 60 feet)
W�dths of the proposed valleys for D type stream channels are expected to be of a s�m�lar width
(averag�ng approximately 50 feet) Material w�ll be stockp�led ad�acent to any ditches to be backfilled or
will be d�str�buted to areas the landowner requests
After the backwater slough has been prepped through clear�ng and grubb�ng the location of channel
backfill areas and any bra�ded or single channel excavation areas will be staked and/or clearly marked
Once belt width corridor floodpla�n and valley preparat�ons are complete the proposed E type channels
will be excavated to the average w�dth depth and cross sectional area derived from reference reach
studies and detailed measurements of the onstte reach Stream banks and the belt width area of
constructed channels will be �mmed�ately planted w�th shrub and herbaceous vegetation Root mats may
also be selectively removed from ad�acent areas and placed as erosion control features on channel banks
and valley wall slopes
Once the proposed design valley has been excavated and stab�lized abandoned channels will be
backfilled util�zing spo�l matertal stockpiled from floodplain grad�ng and channel excavation Abandoned
channels will be backfilled to the maximum extent feas�ble however if a deficit of backfill matertal
occurs sect�ons of the abandoned channel may be left open to form closed ellipt�cal pools within the
floodplain that are expected to fill over t�me
Bra�ded channel construct�on w�ll be minim�zed to the max�mum extent feasible to reduce �mpacts to
exist�ng and future wetland surfaces However reaches that are devoid of surface roughness or potential
braided channel features may be altered through d�sking nppmg or the excavation of mult�ple channel
reaches Upon completion of channel excavation or soil surface roughening erosion control measures
such as seed�ng wrth erosion control vegetation andlor mulch�ng should be implemented Addit�onal
stabilization may be achieved through the use of erosion control matting where necessary �
�
New Rrver Stream and Wetland Mmgation Bank p 9
Supplemental Techmcal Report
[n stream Structures
The use of in stream structures for grade control and habitat are essent�al for successful stream
restoration part�cularly in the E type channels In stream structures may be placed in the channel to
elevate local water surface profiles m the channel potentially flattenmg the water energy slope or
grad�ent The structures would likely consist of boulder size rock vanes � hook vanes and/or step pool
dev�ces designed primarily to d�rect stream energy into the center of the channel and away from banks In
addit�on the structures would be placed in relatively stra�ght reaches to prov�de secondary(perpendicular)
flow cells durtng bankfull events In addit�on a TerraCell drop structure �s proposed at the Bank outfall to
lower Bank hydrology to �ts preconstruction elevation TerraCell is a light wetght flexible mat made of
htgh dens�ty polyethylene stnps that are bonded together to form a honeycomb configuratton that is fixed
�n place and filled w�th gravel or sand and planted w�th grasses and shrubs for add�tional eros�on
protection The TerraCell structure forms a nickpotnt that approx�mates geolog�c controls m stream beds
Wetlands
Wetlands are defined by the presence of three criteria hydrophyttc vegetation hydric soils and ev�dence
of wetland hydrology durmg the grow�ng season (Environmental Laboratory 1987) Portions of the Bank
support�ng hydric so�ls may have h�stor�cally been characterized as palustr�ne broadleaved dec�duous
pers�stent wetlands wh�ch were temporar�ly to seasonally flooded (Coward�n et al 1979) The hydrology
of these systems would have come from overbank flood�ng of stream channels in close proxim�ty of the
hydric soils These areas were likely to have supported Coastal Plain Bottomland Hardwoods Forest as
described in Classification of the Natural Communitres of North Carolina (Schafale and Weakley 1990)
However onsrte wetland areas have been �mpacted by livestock tramplmg deforestat�on groundwater
draw down from drtch�ng and �ncision of Bank streams and discharge of fill mater�al and debrts onto
wetland surfaces Hydr�c so�l ltm�ts w�thtn the Bank were mapped in December 2010 by a Licensed So�l
Sctentists and are depicted on Figure 4(Appendix B)
Riparian Wetlands The Bank conta�ns ripar�an hydric soils within floodpla�ns that have been cleared of
native forest vegetation and have been �mpacted by groundwater table alterations resultmg from ditchmg
dredgmg re routing of tr�butaries d�scharge of fill mater�al m the floodplam and channel �nc�sion
Groundwater table fluctuat�ons occur ad�acent to interfield ditches and inc�sed channels which have
effect�vely lowered the groundwater table below hydrologic thresholds outlined for wetland crrter�a
Prel�minary groundwater modeling has been conducted m order to quantify ►mpacts to the groundwater
table from Bank alterat�ons Approximately 17 4 acres of hydrtc soils are located with�n the Bank
Approximately 15 2 acres of ripar�an hydric sotls are currently drained or excavated for an �rr�gation
pond and are proposed for restoration and enhancement by filling d�tches restor�ng stream �nverts at the
histor�c floodplam elevation backfilling abandoned channels and plant�ng charactertstic wetland
vegetat�on Hydric soils are grey to gley m color and are highly impacted by channel �ncision and
clearmg of the floodplatn
Groundwater model simulations for existmg cond�tions mdicate that approximately 14 7 acres of hydric �
Muckalee soils within the Bank are below�urisdtctional wetland hydrology cr�teria and are cons�dered
effect�vely dra�ned due to the groundwater drawdown from relocat�on dredg�ng stra�ghtening and
rerouting of onsite streams ditchmg of fields plowing of agr�cultural fields and removal of vegetation
Approximately 5 acres are affected by pond excavation wrth the Muckalee so�ls and redistr�button of
these hydric soils surroundmg the pond (Figure 4 Appendix B)
Restoration efforts should focus on elevatmg groundwater tables through routing stream channels through
the histortc floodplain reconnecting hydrolog,y within abandoned floodplains filling agricultural field
New River Stream and Wetland Mit�gation Bank A 10
Supplemental Technical Report
�
d�tches removmg Itvestock and planttng with native forest vegetation Mitigation efforts should allow
the floodplain to perform wetland functions such as flood flow suppression nutr�ent cycl�ng pollutant
removal and prov�sion of native species habitat
Vegetation Planting
Deep rooted r�par�an vegetat►on may be restored withm the entire Bank Planting vegetat�on on cleared
stream banks is proposed to reestabl�sh vegetation community patterns withm the stream corr�dor
assoctated side slopes and transition areas Revegetating the floodplain and riparian wetland areas will
prov�de stream bank stab�lity shade and cool surface waters filter pollutants from ad�acent runoff and
provide hab�tat for area w�ldlife The Bank �s expected to be planted with natrve hardwood spectes
character►st�c of a Coastal Plain Bottomland Hardwoods Forest (Blackwater Subtype) as described tn
Classrficatton of the Natural Communrties of North Caroltna(Schafale and Weakley 1990)
Scar�fication of floodplam surfaces may be required prior to planting Var�ations m vegetative planting
may occur based on topographic locattons and hydraul�c conditions of the so�l Vegetat�ve species
compositton should mimic reference forest data and onBank observations Spec�es expected for this
pro�ect may include the follow�ng elements
amertcan elm(Ulmus americana) elderberry(Sambucus canadensis)
amer�can holly(Ilex opaca) g�ant cane(Arundrnarra grgantea)
american sycamore(Platanus occidentalrs) green ash(Fraxinus pennsylvanica)
bankers dwarf willow(Saltx cotteli) hackberry(Celtis laevigata)
b�tternut hickory(Carya cordtformis) �ronwood(Carpinus carolin�ana)
black gum(Nyssa sylvahca) paw paw(As�mana triloba)
`� black willow(Saltx ragra) r�ver birch(Betula n�gra)
buttonbush(Cephalanthus occrdentalis) tag alder(Alnus serrulata)
black walnut(Juglans nigra) water htckory(Carya aquatrca)
cherrybark oak(Quercus pogoda) water oak(Quercus nrgra)
dec�duous holly(Ilex decidua) willow oak(Quercus phellos)
9 Monitormg
Stream Monitorm�
E type streams w�ll require annual fall monitor�ng that wtll include development of channel cross sections
� on r�ffles and pools pebble counts and a water surface profile of the channel The data will be presented
in graphic and tabular format Data to be presented w�ll mclude 1)cross sect�onal area, 2)bankfull w�dth
3) average depth 4) max�mum depth 5) w�dth to depth ratio 6)water surface slope 7) smuosrty and 8)
stream substrate composition A photographic record of preconstruct�on and post construction condit�ons
will also be comp�led
Stream measurements are not proposed in associatton with D type streams due to typ�cal character�st�cs of
a D type stream as consist�ng of multiple braided channels D type stream systems are not conduc�ve to
measurement of pattern dtmens�on and profile therefore the stream will be visually assessed and
photographically documented annually to sem� annually and any potenttal problem area(s) will be
ident�fied if a problem area �s noted during the review the area will be evaluated to determine the
corrective action required to resolve the problem
�
New Rrver Stream and Wetland Mitiganon Bank A 11
Supplemental Techn�cal Report
� 1
Based on agency gu�del�nes (USACE et al 2005) success cntena for Coastal Plam streams should be
commensurate w�th the restoration of rtpar�an river�ne bottomland wetland commun�ty Th�s would entatl
restorat�on of hydrolog�cal characteristics �nclud�ng saturat�on or inundation for at least 12 5 percent of
the growmg season Therefore groundwater monitoring gauges will be installed to take measurements
after hydrolog�cal modificat�ons are performed at the Srte Hydrological sampling w�ll continue
throughout the growmg season at �ntervals necessary to sat�sfy the �ur�sd�ctional hydrology success
crrteria w►thtn the restorarion area(USEPA 1990)
Stream Success Crrtena
Success criteria for stream restoration will mclude 1) successful classification of the reach as a
functiomng stream system (Rosgen 1996) and 2) channel var�ables indicative of a stable stream system
(bank he�ght ratio not exceed�ng 1 2 and entrenchment ratio no less than 2 2)
Annual fall monitonng w�ll �nclude development of channel cross sections on r�ffles and pools The data
will be presented in graphtc and tabular format Data to be presented will include 1)cross sectional area
2) bankfull w�dth 3) average depth 4) maximum depth and 5) width to depth rat�o A photographic
record of preconstruct�on and post construction condit�ons wtll also be compiled
Visual assessment of in stream structures will be conducted to determ�ne if fa�lure has occurred Fa�lure
of a structure may be �ndicated by collapse of the structure undermm�ng of the structure abandonment of
the channel around the structure and/or stream flow beneath the structure In addit�on visual assessments
of the entire channel wtil be conducted �n each year of monitoring as outl�ned �n NCEEP Monitoring
Requrrements and Reporting Standards for Stream and/or Wetland Mitrgatron Areas of concern wtll be
depicted on a plan view figure identifytng the location of concern along wrth a written assessment and
photograph of the area
Hvdrolo�v Monitormg
Groundwater mon�tor�ng gauges w�ll be mstalled to take measurements after hydrological modifications
are performed at the Site Hydrological sampling wtll cont�nue throughout the grow�ng season at
intervals necessary to sat�sfy Jurisdictional hydrology success criteria (EPA 1990) The quant�ty and
location for monitoring wells will be approved by the IRT
Hvdrology Success Cr�teria
Target hydrological charactertst�cs mclude saturat�on or �nundat�on for 12 5 percent of the grow�ng
season dunng average climatic cond�tions Durtng grow�ng seasons w�th atypical climat�c conditions
groundwater gauges in reference wetlands may dictate threshold hydrology success criter�a These areas
are expected to support hydrophyt�c vegetat�on If wetland parameters are margmal as indicated by
vegetat�on and/or hydrology momtoring a Jurisdictional determmat�on will be performed
Ve�etation Monitoring
Durmg quant�tative vegetat�on sampl�ng sample plots(10 meter by 10 meter) will be installed wrthin the
Site as per guidelines establtshed �n CVS EEP Protocol for Recordrng Vegetatron Versron 4 0(Lee et al
2006) [n each sample plot vegetat�on parameters to be mon�tored mclude spectes compos�tion and
species density Visual observations of the percent cover of shrub and herbaceous species will also be
documented by photograph
New River Stream and Wedand MiUgation Bank A 12
Supplemental Technical Report
i
Ve�etation Success Cr�teria
After plant�ng has been completed m winter or early sprmg an m�tial evaluation will be performed to
venfy planting methods and to determine �nrtial spec�es composrt�on and densrty Supplemental planting
and addrt�onal Srte modificahons will be�mplemented �f necessary
During quantitative vegetation sampl�ng sample plots(10 meter by 10 meter)wtll be mstalled w�thin the
S�te as per guidelines establ�shed in CVS EEP Protocol for Recording Vegetation Versaon 4 0(Lee et al
2006) In each sample plot vegetat�on parameters to be mon�tored �nclude species composit�on and
spec�es densrty Visual observations of the percent cover of shrub and herbaceous species will also be
documented by photograph
An average density of 320 stems per acre of Character�st�c Tree Spec�es must be surviv�ng in the first
three monrtor�ng years Subsequently 290 Characteristic Tree Species per acre must be surv�v�ng m year
4 260 Character�stic Tree Species per acre m year 5 and 210 Characteristic Tree Species per acre�n year
7 In addit�on planted vegetation must average 10 feet m height in each plot at year 7 smce this Srte is
located in the Coastal Plain
10 Contmgency
Stream
In the event that stream success criterta are not fulfilled a mechanism for contingency will be
implemented Stream contingency may mclude but may not be l�mited to 1) structure repair and/or
installat�on 2) repatr of d�mension pattern and/or profile variables and 3) bank stabil�zation The
method of contmgency w�ll be dependent upon stream variables that are not in compl�ance wrth success
criteria Primary concerns which may�eopardize stream success �nclude 1) structure failure 2) headcut
migration through the Site and/or 3)bank erosion
Hydrolo��c Contingency
Hydrologic contmgency may include so�l surface modificat�ons such as constructton of ephemeral pools
and deep rippmg of the sotl profile installation of berms to retard surface flows and/or maintenance to
areas of the wetland Recommendations for contmgency to establ�sh wetland hydrology may be
�mplemented and monitored until Hydrology Success Criter�a are achteved In the event that beaver
become a nu�sance with�n the Srte beaver management will be inrtiated and continued on an as needed
bas�s in accordance wrth North Carol�na W�Idlife Resource Commission(NCWRC)rules and regulat�ons
Ve�etation Contin�ency
If vegetatton success critena are not achieved based on average density calculations from combined plots
over the entire restoration area supplemental plantmg may be performed with tree spec�es approved by
regulatory agencies Supplemental planting may be performed as needed until achievement of vegetat�on
success criter�a
New River Stream and Wetland MmgaUOn Bank A 13
Supplemental Techmcal Report
11 References
Cowardm Lewts M V Carter F C Golet and E T LaRoe 1979 Classificat�ons of Wetlands and
Deepwater Habrtats of the United States U S F�sh and Wildlife Service U S Government
Pnntmg Office Washington D C
Environmental Laboratory 1987 Corps of Engineers Wetlands Delineation Manual Tec,hnical Report
Y 87 1 Unrted States Army Engmeer Waterways Experiment Stat�on Vicksburg Mississippt
Geratz J W and W V Sweet 2003 Bankfull hydraul�c geometry relattonsh�ps and recurrence �ntervals
for North Carolma s Coastal Plam Journal of Amertcan Water Resources Associat�on Volume
3 No 4 pp 861 871 American Water Resources Assoc�ation
Griffith G E J M Omerntk J A Comstock M P Schafale W H McNab D R Lenat T F MacPherson
J B Glover and V B Shelbourne 2002 Ecoregions of North Carolina and South Carolma
U S Geolog�cal Survey Reston Virgima
Lee M T R K Peet S D Roberts and T R Wentworth 2006 CVS EEP Protocol for Recordmg
Vegetat�on Vers�on 4 0 North Carolina Department of Environment and Natural Resources
Ecosystem Enhancement Program Raleigh North Carol�na
Leopold L B 1994 A V�ew of the River Harvard Universrty Press Cambridge MA 298 pp
�
North Carol�na Divis�on of Water Quality(NCDWQ) 2011 a North Carol�na Water Bodies Report
(onlme) Available http//h2o enr state nc us/bims/reports/reportsWB html [January 24 2011]
North Carol�na Department of Environment and Natural Resources Rale�gh
North Caroltna Div�sion of Water Quality(NCDWQ) 2011b Basinwide Assessment Report White Oak
River Basin (onl�ne) Available http//portal ncdenr or web/wq/ess/re orts [January 24 2011]
North Carolma Department of Environment and Natural Resources Raleigh North Carolma
North Carolzna Divis�on of Water Quality(NCDWQ) 2010 Ftnal North Carolina 2010 Integrated
� Report Categor�es 4 and 5 Impaired Waters (2010 Integrated 305(b) and 303(d) Report) (online)
Available http//portal ncdenr or web/wq/ps/mtu/assessment [January 24 2011] North Carolma
Department of Environment and Natural Resources Raleigh North Carol�na
North Carolina Drvision of Water Qualrty(NCDWQ) 2008 Final North Carolina Water Qual�ty
Assessment and Impaired Waters L�st (2008 [ntegrated 305(b) and 303(d) Report) (online)
Ava�lable http//portal ncdenr or web/wq/ps/mtu/assessment [January 24 2011] North
Carolma Department of Env�ronment and Natural Resources Raleigh North Carolma
North Carolma Division of Water Qualrty(NCDWQ) 2006 Final North Carolina Water Qualrty
Assessment and [mpaired Waters List (2006 303(d) Report) (online) Ava�lable
http//portal ncdenr or�/web/wq/ps/mtu/assessment [January 24 2011] North Carolma
Department of Environment and Natural Resources Raleigh North Carolma
North Carolina D�vision of Water Quality(NCDWQ) 2004 Final North Carolma Water Qualrty
Assessment and [mpaired Waters List (2004 303(d) Report) (onlme) Available
ht�t //portal ncdenr or web/wc�/ps/mtu/assessment [January 24 2011] North Caroltna
Department of Environment and Natural Resources Raleigh North Carolina
New River Stream and Wetland Mitigation Bank A 14
Supplemental Techmcal Report
North Carolma Div�s�on of Water Quality(NCDWQ) 2002 Final North Carolina Water Qual�ty
Assessment and Impaired Waters List (2002 303(d) Report) (onlme) Available
http//portal ncdenr or web/wq/ps/mtu/assessment [January 24 2011] North Carol�na
Department of Env�ronment and Natural Resources Raleigh North Carolina
North Carolma Ecosystem Enhancement Program(NCEEP) 2009 EEP s Targeted Local Watersheds
(onl�ne) Available http//www nceep nedpa�es/lwp htm [January 24 2011] North Caroltna
Department of Environment and Natural Resources Rale�gh North Carolina
North Carolina Ecosystem Enhancement Program(NCEEP) 2001 Watershed Restorat�on Plan for the
White Oak River Basm(onlme) Available
http//www nceep net/services/restplans/white oak_2001 pdfhttp//www nceep net/services/lwps/
cape_fear/RBRP Cape Fear 2008 pdf[January 25 2011] North Carol�na Department of
Environment and Natural Resources Raleigh North Carol�na
Rosgen D 1996 Appl�ed R�ver Morphology W�Idland Hydrology(Publisher) Pagosa Spr�ngs Colorado
Schafale M P and A S Weakley 1990 Classification of the Natural Communmes of North Carolina
Th�rd Approximation North Carolina Natural Heritage Program D�vis�on of Parks and
Recreat�on N C Department of Env�ronment Health and Natural Resources Raleigh North
Carol�na
Skaggs R W 1980 Drainmod Reference Report Methods for Design and Evaluation of Dratnage
Water Management Systems for So�ls with H�gh Water Tables Prepared for the U S Department
of Agr�culture South National Techn�cal Center Fort Worth Texas
Skaggs R W and A Tabrtz� 1986 Des�gn Dra�nage Rates for Estimat�ng Dra�n Spactngs in North
Carolina ASAE Paper Number 84 2055
Skaggs R W D Amatya R O Evans and J E Parsons 1994 Characterizations and evaluation of
proposed hydrologic criteria for wetlands Journal of Sotl and Water Conservation 49 (5) 501
510
Skaggs R W et al 2002 Methods to Determine Lateral Effects of a Dra�nage Ditch on Wetland
Hydrology ASAE Annual International Meetmg/C[GR XVth Worid Congress Paper Number
020602
United States Department of Agriculture(USDA) 1992 So�l Survey of Onslow County North Carolma
Sotl Conservation Service
United States Department of Agriculture(USDA) 2011 Web Soil Survey(online) Available
http//webso�lsurvev nres usda�ov/app [January 25 2011] Soil Survey Staff Natural Resources
Conservation Servtce United States Department of Agr�culture
Unrted States Fish and W�ldlife Service (USFWS) 2011 Endangered Species Threatened Species
Federal Species of Concern and Cand�date Species Onslow County North Carohna (online
updated September 22 2010) Available http//www fws gov/nc es/es/countvfr html [January
24 2011] United States F�sh and W�ldlife Serv�ce
New Rrver Stream and Wetland Mmgauon Bank A 15
Supplemental Techmcal Report
Append�x B S�te F�gures
Figure 1 Pro�ect Locat�on Map
Figure 2 Hydrologic Unit Map
Figure 3a Topography& Drainage Area
F�gure 3b Detailed Topography
Figure 4 Ex�sting Condrtions
Figure 5 Proposed Condrt�ons
Figure 6 NRCS Soils
New River Stream and Wetland Mrtigation Bank Append�x B
Prospectus
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�New River Easement=31.0 acres �, y^ � � ' - �� �' } :. Ir��� ,��'� �- .
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—� Perennial stream resroration=2000 linear feet ' , »'' :yy� . a��t,! . Vl - �
�' Intermittent stream restoration=995 linear feet �"' �, ' y� 4+ 7 ' ��� '
�Wetland enhancement=2.2 acres = T . - .�_ �!, • � ��
�Wetland restoration=15.2 acres �' ~ � � _�� � , .'
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Proposed stream restoration =2,995 linear feet �
Stream Mitigation Units generated= 2,995 SMUs �
Proposed wetland restoration = 15.2 acres °'� '�°
,
-. Proposed wetland enhancement=2.2 acres 200 100 0 200
Wetland Mitigation Units generated= 16.3 WMUs Feet
Prepared for: Project: Title: Drawn by: SGD
�` � FIGURE
NEW RIVER Proposed �ate: NOV 2011
RESTORATION SITE Conditions Scale: 1:2400 5
"'"'"°"m"""�."` Project: 09-002.11
Onslow County, NC
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Au6 Alpin fine sand "i , � � , � .sr
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CrC Craven fine sandy loam w � +z
Mk Muckalee loam ,t � ` .� �ti''� .,=�_ ��,y�,;�••
NoA Norfolk loamy fine sand(0-2 percent slopes) � � �, �
NoB Norfolk loamy fine sand(2-6 percent slopes) �;.� ��
Pa Pactolus fine sand -
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Legend ��c � .a� �,� �No6
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Streams digitized from the Soil Suroey of Onstow County(1992) � X;" � '
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�1 Hydric soils ±� ���� ,t:{=f '����
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L 1 Soils that may include hydric inclusions
Feet
Prepared for: Project: Title: Drawn by: SGD
NRCS Date: NOV 2011 FIGURE
NEW RIVER Soils
RESTORATION SITE Map Scale: 1:3000 6'
"�""°�"'°"�"�""` Project: 09-002.11
Onslow County, NC