HomeMy WebLinkAbout20170919 Ver 1_UMBI Modification FINAL COMBINED_20170707RES Cape Fear 02 Umbrella Mitigation Bank
Walnut Wood Site
INSTRUMENT MODIFICATION
Cape Fear River Basin
HUC 03030002
Prepared by: Resource Environmental Solutions, LLC
Bank Sponsor: Environmental Banc & Exchange, LLC
302 Jefferson Street, Suite 110
Raleigh, NC 27605
919-209-1062
fires
July 2017
Table of Contents
1 INTRODUCTION.....................................................................................................................1
1.1 Project Description........................................................................................................................1
1.2 Project Location............................................................................................................................1
1.3 Service Area..................................................................................................................................1
1.4 Identified Watershed Needs..........................................................................................................1
1.5 Purpose and Objectives.................................................................................................................
2
1.6 Technical Feasibility.....................................................................................................................
2
1.7 Site Ownership..............................................................................................................................
2
2 QUALIFICATIONS..................................................................................................................3
2.1 Bank Sponsor................................................................................................................................3
2.2 Bank Sponsor Qualifications........................................................................................................
3
3 EXISTING CONDITIONS........................................................................................................4
3.1 Existing Reach Conditions............................................................................................................4
3.2 Existing Wetlands.........................................................................................................................
5
3.3 Soil Survey....................................................................................................................................5
3.3.1 General Physiographic and Geologic Characteristics......................................................... 5
3.3.2 Site Mapped Soil Series......................................................................................................... 5
3.4 Endangered/Threatened Species...................................................................................................
5
3.5 Vegetation and Wildlife................................................................................................................
6
3.6 Cultural Resources........................................................................................................................
6
3.7 Constraints....................................................................................................................................
6
3.8 Site Photographs...........................................................................................................................
7
...................................................................................................................................................................
8
...................................................................................................................................................................
8
4 PROPOSED BANK CONDITIONS..........................................................................................9
4.1 Conceptual Mitigation Plan..........................................................................................................
9
4.1.1 Project Development.............................................................................................................
9
4.1.2 Stream Restoration and Enhancement.................................................................................. 9
4.1.3 Monitoring..........................................................................................................................11
5 BANK ESTABLISHMENT AND OPERATION.....................................................................12
5.1 Establishment and Operation of the Bank...................................................................................12
5.2 Proposed Credit Release Schedule..............................................................................................12
5.2.1 Initial Allocation of Released Credits.................................................................................13
5.2.2 Subsequent Credit Releases................................................................................................14
5.3 Financial Assurances..................................................................................................................14
5.4 Proposed Ownership and Long -Term Management...................................................................14
5.5 Assurance of Water Rights.........................................................................................................14
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List of Figures
Figure 1. Project Vicinity Map
Figure 2. USGS Topographic Map
Figure 3. Aerial Photography Map
Figure 4. Landowner Map
Figure 5. Soils Map
Figure 6. NWI Wetlands Map
Figure 7. Constraints Map
Figure 8. Conceptual Design Plan
Appendix A — Landowner Authorization Form
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I INTRODUCTION
1.1 Project Description
The Walnut Wood Mitigation Site (the "Site") is located in Julian, NC and contains one parcel totaling 147 -
acres in Guilford County, NC. The Site will involve the restoration and enhancement of five unnamed
tributaries to the Cape Fear River. The Site was identified as having potential to help meet the compensatory
mitigation requirements for stream impacts in hydrologic unit code (HUC) 03030002 of the Cape Fear
River Basin. The Site provides 38.4 acres of proposed conservation easement.
The conceptual design presents 8,274 linear feet of stream mitigation generating 6,388 Stream Mitigation
Units (SMU).
1.2 Project Location
The Site is located in Guilford County in Julian, NC (Figures 1 and 2). The GPS coordinates of the Site
are 35.9808°N and -79.6446°W. To access the site from the town of Julian, take Old 2' Street for
approximately 0.1 miles then turn right onto Old Julian Road. Continue on Old Julian Road for
approximately 4.1 miles, and then turn left onto Coble Church Road for 2.3 miles then turn right onto
Alamance Church Road. The property at 3172 Alamance Church Road provides access to the Site.
1.3 Service Area
The Site is located within the Cape Fear River Basin (8 -digit USGS HUC 03030002, 14 -digit USGS
03030002040010). This proposed Site will result in significant ecological improvements including water
quality improvement, restoring hydrologic connectivity, and habitat restoration.
The Site's is located within a rural area, and land use within the watershed is comprised primarily of
agricultural and forested land uses (Figure 3). The Site is located on the former Walnut Wood golf course,
and at the present time is comprised of an inactive golf course, driving range, ponds, and forested areas.
Water quality stressors currently affecting the Site include stream impoundments and the burying of
headwater streams into a piped system. There are no current conservation easements or options that conflict
with the proposed mitigation bank.
The project stream reaches are tributaries that flow into the Haw River then into the Cape Fear River. The
Haw River is the major river in the HUC 03030002; this river and its tributaries flow to B. Everett Jordan
Lake, a drinking water supply. This supply has been designated a Nutrient Sensitive Water and NCDWR
has developed a set of rules to reduce non -point source pollution. Goals include promoting nutrient and
sediment reduction in agricultural and urban areas by restoring and preserving streams, wetlands, and
riparian buffers.
1.4 Identified Watershed Needs
The North Carolina Division of Mitigation Services (DMS) develops River Basin Restoration Priorities
(RBRP) to guide its restoration activities within each of the state's 54 cataloging units. The Cape Fear is
one of four river basins entirely contained within North Carolina's borders. The 2009 Cape Fear River
Basin RBRP identified several restoration needs for the entire Cape Fear River Basin, as well as for HUC
03030002, specifically.
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The proposed Site is designed to help meet these goals. The project will address stressors identified in the
watershed through nutrient removal, sediment removal, runoff filtration, and improved aquatic and
terrestrial habitat. These project goals will be achieved through stream enhancement and restoration.
1.5 Purpose and Objectives
The purpose of the proposed Site is to generate compensatory mitigation credits for inclusion in the RES
Cape Fear 02 Umbrella Mitigation Bank in HUC 03030002 of the Cape Fear River Basin.
The project goals address stressors identified in the watershed, and include the following:
• Nutrient removal,
• Sediment reduction,
• Invasive species treatment,
• Filtration of runoff,
• Restore hydrologic connectivity,
• Enhance flood attenuation
• Wildlife corridor enhancement and preservation, and
• Improved aquatic and terrestrial habitat.
The project goals will be addressed through the following project objectives:
• Dam breach and pond removal,
• Daylighting of headwater stream systems,
• Restoration of appropriate pattern, dimension, and profile in stream channels and pond bottoms.
• Treatment of exotic invasive species,
• Restoration of riparian forested stream buffers
• Addition of large woody debris such as log vanes, log weirs, and root wads.
The proposed Site will provide numerous ecological and water quality benefits within the Cape Fear River
Basin. These benefits are not limited to the project area, but have more far-reaching effects throughout the
Cape Fear River. The Site will provide improvements to water quality, hydrologic function, and habitat.
1.6 Technical Feasibility
The technical feasibility of the bank is assured due to RES' extensive experience with stream and wetland
restoration and enhancement in North Carolina and throughout the Southeast. Examples of EBX's success
with stream restoration and enhancement include Neu -Con Umbrella Mitigation Bank sites: specifically,
the Marston, Nahunta, and Westbrook sites. The absence of fatal flaws such as hydrologic trespass, and the
absence of threatened and endangered species and their habitats mean the project is unlikely to be impeded
by resource issues, or by objections from landowners.
1.7 Site Ownership
The land required for the construction, management, and stewardship of this mitigation project includes
portions of the parcel listed in Table 1. A landowner map is also provided in Figure 4. Environmental Banc
& Exchange, LLC has control of the property with an option to purchase.
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Table 1. Site Ownership
2 QUALIFICATIONS
2.1 Bank Sponsor
The Site shall be established under the terms and conditions of the RES Cape Fear 02 Stream and Wetland
Umbrella Mitigation Bank made and entered into by Environmental Banc & Exchange, LLC (EBX), acting
as the Bank Sponsor.
Company Name: Environmental Banc & Exchange, LLC
Company Address: 302 Jefferson Street, Suite 110, Raleigh, NC 27605
Contact Name: Daniel Ingram
Telephone: (919) 209-1056
Email: dingram@res.us
2.2 Bank Sponsor Qualifications
Resource Environmental Solutions, LLC (RES) was founded in February 2007 and grew organically from
its roots restoring Louisiana wetlands to deliver mitigation solutions across Louisiana, Texas, Pennsylvania,
West Virginia, Maryland, Virginia, North Carolina and South Carolina. In December 2014, RES acquired
industry pioneer Environmental Banc & Exchange, LLC (EBX), expanding the RES knowledge base and
geographic and technical delivery capabilities.
RES develops and supplies ecological offsets to help public and private sector clients obtain required
permits for unavoidable, project -related impacts to wetlands, streams, and habitats. RES helps clients
proactively manage risk from operations in environmentally sensitive areas by providing proactive impact
analyses, streamlining permitting processes, and limiting liability and regulatory exposure.
• RES is the premier provider of ecological offset solutions in the US
• RES founded in 2007 / EBX founded in 1997
• 110 mitigation sites permitted/in process
• Conservation easements protecting roughly 400 sites
• 32,000 restored wetland acres
• 4,000 acres of custom mitigation solutions
• 155 miles of stream restoration
• Reduced over 240 tons of nutrients
• Rehabilitated and preserved over 3,700 acres of endangered species habitats
In North Carolina, RES and its affiliated companies have won over $70 million in mitigation contracts with
North Carolina state agencies. With a regional office in Raleigh staffed with full-time professionals, RES
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Deed Book
Landowner
Pin
County
and Page
Parcel
Protected
Acreage
Acreage
Number
Walnut Wood Golf
8801829027
Guilford
003459/01002
147
38.4
Course Inc.
2 QUALIFICATIONS
2.1 Bank Sponsor
The Site shall be established under the terms and conditions of the RES Cape Fear 02 Stream and Wetland
Umbrella Mitigation Bank made and entered into by Environmental Banc & Exchange, LLC (EBX), acting
as the Bank Sponsor.
Company Name: Environmental Banc & Exchange, LLC
Company Address: 302 Jefferson Street, Suite 110, Raleigh, NC 27605
Contact Name: Daniel Ingram
Telephone: (919) 209-1056
Email: dingram@res.us
2.2 Bank Sponsor Qualifications
Resource Environmental Solutions, LLC (RES) was founded in February 2007 and grew organically from
its roots restoring Louisiana wetlands to deliver mitigation solutions across Louisiana, Texas, Pennsylvania,
West Virginia, Maryland, Virginia, North Carolina and South Carolina. In December 2014, RES acquired
industry pioneer Environmental Banc & Exchange, LLC (EBX), expanding the RES knowledge base and
geographic and technical delivery capabilities.
RES develops and supplies ecological offsets to help public and private sector clients obtain required
permits for unavoidable, project -related impacts to wetlands, streams, and habitats. RES helps clients
proactively manage risk from operations in environmentally sensitive areas by providing proactive impact
analyses, streamlining permitting processes, and limiting liability and regulatory exposure.
• RES is the premier provider of ecological offset solutions in the US
• RES founded in 2007 / EBX founded in 1997
• 110 mitigation sites permitted/in process
• Conservation easements protecting roughly 400 sites
• 32,000 restored wetland acres
• 4,000 acres of custom mitigation solutions
• 155 miles of stream restoration
• Reduced over 240 tons of nutrients
• Rehabilitated and preserved over 3,700 acres of endangered species habitats
In North Carolina, RES and its affiliated companies have won over $70 million in mitigation contracts with
North Carolina state agencies. With a regional office in Raleigh staffed with full-time professionals, RES
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has the ability to carry out existing projects, as well as secure and carry out new projects and banks in the
State. A few representative projects implemented by RES are presented below.
Neu -Con Umbrella Mitigation Bank (North Carolina): One of the first approved wetland and stream
banks in North Carolina. The service area of the Bank is the entire Neuse River Basin. The Bank was
established in April 2001. Initial contract: 22,964 linear feet of stream mitigation units (SMU) sold to
North Carolina DOT based on credits produced from 3 stream restoration sites (initiated November
2000; sold all credits in November 2000; design initiated December 2001; construction completed on
all sites Spring 2005; monitoring completed on all sites in Fall 2009). Additional sites added starting in
2008.
Chesapeake Wetland Mitigation Bank (City of Chesapeake, Virginia): 545 -acre wetland mitigation
bank in the Lower James Watershed in Virginia. The service territory of the Bank includes HUCs
02080206 and 02080208. The Bank was established in July 2009. The remainder of the 1,156 -acre
property will be sold to the Great Dismal Wildlife Refuge (MBI finalized Spring 2009; construction
completed Spring 2011; in the monitoring phase).
Conoconnara Swamp Site (Halifax County, North Carolina): 87.0 WMU of wetland restoration and
5,050 SMU of stream restoration (initiated July 2005; construction completed Spring 2007; monitoring
completed Fall 2011).
3 EXISTING CONDITIONS
3.1 Existing Reach Conditions
Reach WWI
Reach WWI begins above an existing pond and is entirely contained within a piped system before it drains
directly to Climax Creek. The existing drainage area for the reach is approximately 26 acres. Current land -
use is an inactive golf course fairway. Multiple catch -basins are present along the length of the proposed
reach. There are no existing trees within the riparian zone.
Reach WW2
Reach WW2 originates above a series of four in-line ponds and is contained within a piped system before
it drains directly to Climax Creek. The existing drainage area for the reach is approximately 41 acres.
Current land -use is an inactive golf course fairway, ponds, and fragmented wooded areas. Multiple catch -
basins and pond structures are present throughout the length of the proposed reach.
Reach WW3
Reach WW3 originates above a pond in the southern -most portion of the parcel and contains one in-line
pond before draining to Climax Creek. The inlet and outlet structure on the pond are actively eroding and
no longer functioning as designed. The existing drainage area for the reach is approximately 31 acres.
Reach WW4
Reach WW4 originates as an intermittent stream feature before being piped underground and draining
directly to Climax Creek. Current land -use is an inactive golf course fairway and fragmented wooded areas.
Multiple catch -basins are present along the length of the proposed reach.
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Climax Creek
Climax Creek is a perennial stream channel that is the main drainage feature of the project. Large portions
of the channel have been historically cleared and maintained as part of the golf course operation. Multiple
stream crossings are present on the property.
3.2 Existing Wetlands
Detailed wetland delineation has not been performed. The Site will be delineated by RES and approved by
the USACE during the design phase of the project. The stream channels were classified using North
Carolina Division of Water Quality methodology. Stream determinations will be approved by NCDWR
during the design phase of the project.
3.3 Soil Survey
3.3.1 General Physiographic and Geologic Characteristics
The Site is located in the Southern Outer Piedmont Level IV Ecoregion within the Piedmont Level III
Ecoregion. Pine (mostly loblolly and shortleaf) dominates on old field sites and pine plantations, while
mixed oak forest is found in less heavily altered areas. Gneiss, schist, and granite are typical rock types,
covered with deep saprolite and mostly red, clayey subsoils. Kanhapludults are common soils, such as the
Cecil, Appling, and Madison series. Some areas within this region have more alkaline soils, such as the
Iredell series, formed over diabase, diorite, or gabbro, and may be associated with areas once known as
blackjack oak prairies.
3.3.2 Site Mapped Soil Series
Site soils are mapped by the Natural Resources Conservation Service (MRCS) as Chewacla and Wehadkee,
on the low-lying depressions and floodplains at the proposed project. Chewacla and Wehadkee occur as
loam and are frequently flooded.
Soils that occur on uplands and high stream terraces at the site are mapped as Enon, Mecklenburg, and
Wilkes-Poindexter-Wynott complex. Enon is a fine sandy loam with 2 to 6 percent slopes, Mecklenburg is
a sandy clay loam, and Wilkes-Poindexter-Wynott complex has 15 to 45percent slopes (Figure 5).
3.4 Endangered/Threatened Species
Plants and animals with a federal classification of endangered or threatened are protected under provisions
of Sections 7 and 9 of the Endangered Species Act of 1973, as amended. The US Fish and Wildlife Service
(USFWS) database (accessed 19 June 2017) lists one threatened species for Guildford County, North
Carolina. The species is the Small whorled pogonia (Isotria medeoloides) and it has a current record status.
The Bald eagle (Haliaeetus leucocephalus) is protected under the Bald and Golden Eagle Protection Act
(BGPA) and prohibits take of bald and golden eagles. No protected species or potential habitat for protected
species was observed during preliminary site evaluations.
In addition to the USFWS database, the most recent (January, 2017) NC Natural Heritage Program (NHP)
GIS database was consulted to determine whether previously cataloged occurrences of protected species
are mapped within one mile of the Site. Results from NHP indicated that there are four element
occurrences of animals within a one -mile radius of the project area. Three occurrences maintain historical
status (EO IDs 23383, 31774, 34473), and one occurrence maintains a current status (EO ID 18289).
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Based on initial site investigations, no impacts to federally protected species are anticipated as a result of
the proposed project. The environmental screening phase of the project will include USFWS and NHP
coordination to confirm these findings.
Table 2. Federally Protected Species in Guilford County
Common Name
Scientific name
Federal
Status
Habitat
Present
Record
Status
Vertebrate:
Bald eagle Haliaeetus leucoce halus BGPA Yes Current
Vascular Plant:
Small whorled pogonia
Aeschynomene virginica T
No Historic
E = Endangered; T = Threatened; BGPA = Bald and Golden Eagle Protection Act
3.5 Vegetation and Wildlife
Historically, the majority of the land within the Site was a maintained golf course that included fairways,
greenways, a club house, maintenance building, driving range, water features (i.e., ponds or streams),
maintained field, and golf cart paths. Current land use around the Site is primarily un -maintained fairways
and forest. Common tree species observed include red maple (Acer rubrum), American Sycamore (Platanus
occidentalis), sweetgum (Liquidambar styraciflua), tulip poplar (Liriodendron tulipifera), and red cedar
(Juniperus virginiana). There are low-density residential lots, maintained vegetation, and two-lane roads
also present in the immediate project vicinity.
National Wetland Inventory (NWI) mapping depicts wetlands throughout the project area (Figure 6). The
NWI mapped wetlands are all ponds. During the initial evaluation, few riparian wetlands were identified
along the Climax Creek floodplain. All potential wetland areas in the project corridors will be delineated
during the mitigation plan phase of the project.
3.6 Cultural Resources
A review of North Carolina State Historic Preservation Office (SHPO) GIS Web Service (accessed 19 June
2017) database revealed no eligible historic areas in the proposed project area. The environmental screening
phase of the project will include SHPO coordination to confirm these findings.
3.7 Constraints
Minimal constraints are present or proposed on the Site. The entirety of Climax Creek is within a mapped
FEMA 100 -year floodplain (Figure 7). RES will conduct a FEMA flood study to obtain either a No -Rise
Certification or CLOMR/LOMR from the Guilford County floodplain administrator. Six existing ponds
and a network of drainage tiles and pipes within the property will be removed as part of the restoration.
Construction access is slightly constrained in some areas by existing mature hardwood vegetation. A tree
survey will be conducted to design the mitigation measures and access to minimize impacts to specimen
trees.
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3.8 Site Photographs
Existing pond at top of proposed Reach WWI.
06//20/2017
Drainage patterns above Reach WW2 origin point
before going underground. 06/20/2017
Inlet/drainage connection between two ponds
along Reach WW2. 06/20/2017
Walnut Wood Mitigation Site
RES Cape Fear 02 Umbrella Bank
Failing inlet/pipes along Reach WWI looking
downstream. 06/20/2017
Downstream most pond along proposed Reach
WW2. 06//20/2017
Looking downstream at existing pond inlet -
Reach WW3. 06/20/2017
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7 July 2017
Looking upstream at existing pond inlet- Reach
WW3. 06/20/2017
Existing condition of Reach WW4. 05/12/2017
Proposed channel location/existing floodplain for
Reach WW4. 06//20/2017
Climax Creek during flood conditions.
06/20/2017
Typical inlet along restoration reaches.
05/12/2017
47`�
Typical inlet along restoration reaches.
05/12/2017
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4 PROPOSED BANK CONDITIONS
4.1 Conceptual Mitigation Plan
The Site presents the opportunity to provide up to 6,388 stream mitigation units. These will be derived from
Restoration, and Enhancement Level II. Table 3 details the mitigation types and SMUs generated. The
proposed conceptual design plan is shown in Figure 8.
Table 3. Proposed Mitigation Summary
Reach
Midi ation Type
Length (LF)
Ratio
SMUs
WWI
Restoration
843
1:1
843
WW2
Restoration
1,881
1:1
1,881
WW3
Restoration
1,974
1:1
1,974
WW4
Restoration
433
1:1
433
Climax Creek
Enhancement II
3,084
2.5:1
1,234
Total
8,215
6,365
4.1.1 Project Development
Proposed mitigation for the Site involves Restoration and Enhancement Level Il. The stream system is
situated on four unnamed tributaries to Climax Creek. Current stream conditions along the proposed
restoration reaches are completely contained within a network of pipes and in-line ponds. The current
condition of Climax Creek is a fairly stable channel with a limited riparian buffer along the majority of its
length within the project.
The proposed mitigation approach is based on functional considerations, and generally accepted practices
in North Carolina. Restoration reaches will typically include a meandering single -thread stream pattern and
proposed sinuosity will depend on local reference reach conditions and hydrologic and hydraulic modeling.
The restoration of planform and dimension, periodic flooding and restored riparian buffer will provide the
appropriate hydrology and sediment transport throughout this catchment (mitigation ratio 1:1).
Enhancement Level II treatments include, revegetation of riparian buffers, stream crossing removal, and
invasive species treatment (mitigation ratio 2.5:1).
4.1.2 Stream Restoration and Enhancement
Stream restoration efforts will be accomplished through analyses of geomorphic conditions and watershed
characteristics. The design approach will apply a combination of analytical and reference reach based
design methods that meet objectives commensurate with both ecological and geomorphic improvements.
Proposed treatment activities may range from minor bank grading and planting to re-establishing stable
planform and hydraulic geometry. Natural design concepts will be applied for the restoration reaches and
verified through rigorous engineering analyses and modeling. The objective of this approach is to design a
geomorphically stable channel that provides habitat improvements and ties into the existing landscape.
Because all the restoration reaches are currently contained in a network of pipes and impoundments, Table
4 describes proposed conditions of the restored channels on-site. Climax Creek is approximately 15 feet
wide with an average depth of 3 feet throughout the project area.
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Table 4. Proposed Morphological Parameters of Restoration Reaches
Reach
WWI
WW2
WW3
WW4
Drainage Area (Ac)
25.8
41.4
30.8
21.8
Bankfull Width (ft)
5
7
5
5
Cross -Sectional Area (ft2)
6
8
7
6
Mean Depth (ft)
1
1
1
1
Width/Depth Ratio
5
7
5
5
The Site design approach will begin with a thorough study of existing conditions, including the on-site
streams and ditches, valleys, and watershed. Design parameters, including active channel, habitat and
floodplain features will be developed from analysis of suitable reference streams. Analytical design
techniques will be an important element of the project, and will be used to determine the design discharge
and to verify the design as a whole.
Engineering analysis will be performed using various hydrologic and hydraulic models to verify the
reference reach -based design. A combination of methods, including HEC -HMS, Hydraflow Hydrographs,
and flood frequency analysis, will be used to calculate flows received by the channel for bankfull and other
significant storm events. A HEC -RAS model will then be used to simulate water surface elevations of flows
generated by the hydrologic analysis. The development of the HEC models is an important component to
the design; therefore, model input parameters are field verified when possible. Through this hydrologic
analysis, the design discharge (typically referenced as bankfull or dominant discharge) will be determined.
The subsequent design will be based on this calculated discharge. Design parameters developed through
the analyses of reference reach data and hydrologic and hydraulic modeling will be confirmed using the
Stable Channel Design function and/or the Sediment Transport Analysis components within HEC -RAS.
Engineering analyses are performed concurrently with geomorphic and habitat studies. While stream design
will be verified by simulations of hydrology and fluvial processes, analogs of desirable habitat features will
be derived from reference sites and integrated into the project design. Both in -stream and riparian habitat
features will be designed. In -stream structures such as root wads, rock vanes, and cross weirs will be used
throughout the project to act as grade control and for bank stabilization by dissipating and redirecting the
stream's energy. Bank stability may be further enhanced through the installation of brush mattresses and
cuttings bundles consisting of species such as black willow (Salix nigra), cottonwood (Populus deltoides)
and silky dogwood (Cornus amomum).
In -stream habitat is highly dependent on available cover and organic material. A quantitative habitat
assessment method will be used to measure type, location, and quantity of habitat in the reference streams.
During design, the habitat assessment results will be scaled appropriately to the design parameters such that
the quantity and placement of the habitat features along the restored channel will mimic reference
conditions. This process provides a natural channel design that addresses aquatic function improvements in
addition to stability.
Stream banks will be stabilized using a combination of grading, erosion control matting, plantings, native
material revetment techniques (i.e., bioengineering), and structure placement. The stream and adjacent
riparian areas will be protected by a minimum 50 -foot permanent conservation easement which will be
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fenced to exclude livestock as needed. In most areas the riparian buffer width will exceed 100 feet on each
bank.
4.1.3 Monitoring
Stream stability and vegetation survival will be monitored across both the restoration and enhancement
areas of the site to determine the success of the stream and buffer mitigation. Stream stability will be
monitored with cross section surveys and visual assessment stream walks. Vegetation survival rates will be
monitored using vegetation plots over approximately two percent of the planted area.
4.1.3.1 As -Built Survey
An as -built survey will be conducted following construction to document channel size, condition, and
location on constructed or modified channels. The survey will include a complete profile of thalweg, water
surface, bankfull, and top of bank to compare with future geomorphic data. Longitudinal profiles will not
be required in annual monitoring reports unless requested by the Interagency Review Team (IRT).
4.1.3.2 Visual Monitoring
Visual monitoring of all mitigation areas will be conducted a minimum of twice per monitoring year by
qualified individuals. The visual assessments will include vegetation density, vigor, invasive species, and
easement encroachments. Visual assessments of stream stability will include a complete streamwalk and
structure inspection. Digital images will be taken at fixed representative locations to record each monitoring
event, as well as any noted problem areas or areas of concern. Results of visual monitoring will be presented
in a plan view exhibit with a brief description of problem areas and digital images.
4.1.3.3 Cross Sections
Permanent cross-sections will be installed at a minimum of one per 20 bankfull widths with half in pools
and half in shallows. All cross-section measurements will include bank height ratio and entrenchment ratio.
Cross-sections will be monitored annually. There should be little change in as -built cross-sections. If
changes do take place, they should be evaluated to determine if they represent movement toward a less
stable condition (for example down -cutting or erosion), or are minor changes that represent an increase in
stability (for example settling, vegetative changes, deposition along the banks, or decrease in width/depth
ratio). Bank height ratio shall not exceed 1.2, and the entrenchment ratio shall be no less than 2.2 within
restored reaches. Channel stability should be demonstrated through a minimum of four bankfull events
documented in the seven-year monitoring period.
4.1.3.4 Vegetative Success Criteria
Vegetation monitoring plots will be a minimum of 0.02 acres in size, and cover approximately two percent
of the planted area. The following data will be recorded for all trees in the plots: species, height, planting
date (or volunteer), and grid location. Monitoring will occur each year during the monitoring period. The
interim measures of vegetative success for the site will be the survival of at least 320 planted three-year old
trees per acre at the end of Year 3 and 260 five-year old trees per acre at the end of Year 5. The final
vegetative success criteria will be the survival of 210 trees per acre with an average height of 10 feet at the
end of Year 7 of the monitoring period. Invasive and noxious species will be monitored and controlled so
that none become dominant or alter the desired community structure of the site. If necessary, EBX will
develop a species-specific control plan.
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4.1.3.5 Adaptive Management
The Mitigation Plan will include a detailed adaptive management plan that will address how potential
problems are resolved. In the event that the site, or a specific component of the site, fails to achieve the
defined success criteria, EBX will develop necessary adaptive management plans and/or implement
appropriate remedial actions for the site in coordination with the IRT. Remedial actions will be designed to
achieve the success criteria specified previously, and will include identification of the causes of failure,
remedial design approach, work schedule, and monitoring criteria that will take into account physical and
climatic conditions. If tree mortality affects 40 percent or greater of the canopy in a stream or wetland
restoration area, then a remedial/supplemental planting plan will be developed and implemented for the
affected area(s).
5 BANK ESTABLISHMENT AND OPERATION
5.1 Establishment and Operation of the Bank
This Bank Parcel shall be established under the terms and conditions of the RES Cape Fear 02 Stream and
Wetland Umbrella Mitigation Banking Instrument (LIMBI) made and entered into by and among EBX,
LLC, the U.S. Army Corps of Engineers, the U.S. Environmental Protection Agency, the U.S. Fish and
Wildlife Service, the National Marine Fisheries Services, the North Carolina Department of the
Environment and Natural Resources, the North Carolina Division of Water Resources, and the North
Carolina Wildlife Resources Commission, collectively, the Interagency Review Team.
5.2 Proposed Credit Release Schedule
All credit releases will be based on the total credit generated as reported by the as -built survey of the
Mitigation Site. The pre -construction credit release (15 percent) will be based on the credit total in the Final
Mitigation Plan. The second credit release will be based on the As -Built survey, and will adjust the total
released credits based on the actual constructed channel lengths. Under no circumstances shall any
mitigation project be debited until the necessary DA authorization has been received for its construction or
the District Engineer (DE) has otherwise provided written approval for the project in the case where no DA
authorization is required for construction of the mitigation project. The DE, in consultation with the
Interagency Review Team, will determine if performance standards have been satisfied sufficiently to meet
the requirements of the release schedule below. In cases where some performance standards have not been
met, credits may still be released depending on the specifics of the case. At the direction of the DE, in
consultation with the IRT, monitoring may be required to be extended, depending on the extent to which
the site fails to meet the specified performance standard. The release of project credits will be subject to the
criteria described in Table 5.
Walnut Wood Mitigation Site INSTRUMENT MODIFICATION
RES Cape Fear 02 Umbrella Bank 12 July 2017
Table 5. Stream Credit Release Schedule
Release
Milestone
Credit Release Activity
Interim
Release
Total Released
Site Establishment (includes all required criteria
15%
15%
1
stated above)
Baseline Monitoring Report and As -built Survey
15%
30%
2
First year monitoring report demonstrates
10 °
40 °
/o/0
3
performance standards are being met.
Second year monitoring report demonstrates
10%
4
performance standards are being met.
50%
Third year monitoring report demonstrates
°
10 /o
5
performance standards are being met.
60%
6
Fourth year monitoring report demonstrates
°
5 /°
65%
performance standards are being met.
(75%**)
Fifth year monitoring report demonstrates
10/o °
75%
7
performance standards are being met.
(85%**)
8
Sixth year monitoring report demonstrates
°
5 /°
80%
performance standards are being met.
(95%**)
Seventh year monitoring report demonstrates
90%
9
performance standards are being met, and project
10%
has received close-out approval.
(100%**)
* * 10% reserve of credits to be held back until the bankfull event performance standard has been met.
These reserve credits cannot be released prior to completion of year 4 monitoring.
5.2.1 Initial Allocation of Released Credits
The initial allocation of released credits, as specified in the mitigation plan can be released by the IRT
with written approval of the DE upon satisfactory completion of the following activities:
1. Approval of instrument modification by the DE, in consultation with the IRT;
2. Approval of a Final Mitigation Plan;
3. Confirmation that the Bank site has been secured;
4. Delivery of executed financial assurances as specified in the Mitigation Plan;
5. Delivery of a copy of the recorded long-term protection mechanism as described in the
Mitigation Plan, as well as a title opinion covering the property acceptable to the DE; and
6. Issuance of any DA permits necessary for construction of the Bank site (if necessary).
Walnut Wood Mitigation Site INSTRUMENT MODIFICATION
RES Cape Fear 02 Umbrella Bank 13 July 2017
5.2.2 Subsequent Credit Releases
The second credit release will occur after the completion of implementation of the Mitigation Plan and
submittal of the Baseline Monitoring Report and As -built Survey. All subsequent credit releases must be
approved by the DE, in consultation with the IRT, based on a determination that required performance
standards have been achieved. As projects approach milestones associated with credit release, the Sponsor
will submit a request for credit release to the DE along with documentation substantiating achievement of
criteria required for release to occur. This documentation will be included with the annual monitoring
report.
5.3 Financial Assurances
The Sponsor shall provide financial assurances in the form of a Performance Bond to the IRT sufficient to
assure completion of all mitigation work, required reporting and monitoring, and any remedial work
required. Financial assurances shall be payable at the direction of the USACE to its designee or to a standby
trust. Financial assurances structured to provide funds to the USACE in the event of default by the Bank
Sponsor are not acceptable. A financial assurance must be in the form that ensures that the USACE receives
notification at least 120 days in advance of any termination or revocation.
5.4 Proposed Ownership and Long -Term Management
EBX, LLC, acting as the Bank Sponsor, will establish a Conservation Easement, and will monitor the Site
for a minimum of seven years. The Mitigation Plan will provide detailed information regarding bank
operation, including long term management and annual monitoring activities, for review and approval by
the IRT. Upon approval of the Sites by the IRT, the site will be transferred to a long-term land steward (to
be determined in the Mitigation Plan). The long-term steward shall be responsible for periodic inspection
of the site to ensure that restrictions required in the Conservation Easement or the deed restriction
document(s) are upheld. Endowment funds required to uphold easement and deed restrictions shall be
negotiated prior to site transfer to the responsible party.
The Bank Sponsor will ensure that the Conservation Easement will allow for the implementation of an
initial monitoring phase, which will be developed during the design phase and conducted by the Bank
Sponsor. The Conservation Easement will allow for yearly monitoring and, if necessary, maintenance of
the Site during the initial monitoring phase. These activities will be conducted in accordance with the terms
and conditions of the RES Cape Fear 02 Stream and Wetland Umbrella Mitigation Bank made and entered
into by EBX, LLC and USACE.
5.5 Assurance of Water Rights
Sufficient water rights exist to support the long-term sustainability of the site, as there are no "severed"
rights on the property.
Walnut Wood Mitigation Site INSTRUMENT MODIFICATION
RES Cape Fear 02 Umbrella Bank 14 July 2017
Figures
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FIGURE 1
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FIGURE 2 Date: 7/7/2017
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re
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FIGURE 4
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Walnut Wood Mitigation Site
Guilford County, North Carolina
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Parcels
Date: 7/7/2017
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FIGURE 7 Date: 7/7/2017
8
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of Feet Guilford County, North Carolina
A!!
Reach
Mitigation Type
Length (LF)
Ratio
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Restoration
843
1:1
843
WW2
Restoration
1,881
1:1
1,881
WW3
Restoration
1,974
1:1
1,974
WW4
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433
1:1
433
Climax Creek
Enhancement II
3,084
2.5:1
1,234
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6 365
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FIGURE 8 Date: 7/7/2017
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VVV Conceptual Mapres
o zoo 400 Walnut Wood Mitigation Site
of Feet Guilford County, North Carolina I I /
Appendix A — Landowner Authorization Form
Landowner Authorization Form
Site: Walnut Wood
Property Legal Description
Deed Book: 3459 Page: 1002 County: Guilford
Parcel ID Number: 8801-82-9027
Street Address: 3172 Alamance Church Road, Julian, NC 27283
Record Property Owner: Walnut Wood Golf Course Inc.
Authorized Invitee: Colonel Land LLC
The undersigned, being duly authorized by the record property owner of the above property, in accordance with the
terms of an Offer to Purchase and Contract dated 5/26/2017, do hereby authorize
Resource Environmental Solutions, the NC Division of Water Resources, and the US Army Corps of Engineers,
their employees, agents or assigns to have reasonable access to the above referenced property for the evaluation of
the property as a potential stream, wetland, and or riparian buffer restoration project, including conducting stream
and or wetland determinations and delineations, as well as issuance and acceptance of any required permit(s) or
certification(s).
Authorized Invitee Address: 302 Jefferson Street, Suite 110, Raleigh, NC 27605
I/We hereby certify the above information to be true and accurate to the best of my/our knowledge.
V
(Authorized In ' ee Authorized Signature) Date
IN - J �4 5 O -Al �iM /"I L i 7 /'?/?--o/7
(Authorized Invitee Printed Name) Date
4815-4603-0411, v. 1