20141149 Ver 9_Year 4 Monitoring Report_2021 Draft_20211112

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ID#* 20141149 Version* 9
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Katie Merritt
Initial Review Completed Date 11/19/2021
Mitigation Project Submittal - 11/12/2021
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Type of Mitigation Project:*
Stream Wetlands Buffer Nutrient Offset
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Project Contact Information
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Raymond Holz [e-mail]
Project Information
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ID#:* 20141149 Version:*9
Existing ID# Existing Version
Project Type: DMS • Mitigation Bank
Project Name: Benton Branch
County: Caswell
Document Information
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Mitigation Monitoring Report
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NOC_2021 MY4_.pdf
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YEAR 4(2021)
MONITORING REPORT
Benton Branch Bank Parcel
DWR#20141149 version 9
Pursuant to:
Restoration Systems' Phase One Haw River WS Umbrella Banking Instrument for
Riparian Buffer and Nutrient Offset Mitigation Credits
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PREPARED BY:
RESTORATION SYSTEMS, LLC
1101 HAYNES STREET,SUITE 211
RESTORATION RALEIGH, NORTH CAROLINA 27604
SYSTEMS I LLC
AND
AXIOM ENVIRONMENTAL, INC.
218 SNOW AVENUE
RALEIGH, NORTH CAROLINA 27603
Axiom Environmental,Inc.
November 2021

EXECUTIVE SUMMARY
Restoration Systems, LLC(RS)established the Benton Branch Bank Parcel(Parcel)as part of the RS'Phase
One Haw River WS Umbrella Banking Instrument(Banking Instrument)signed October 25th, 2017 between
RS, and the North Carolina Division of Water Resources(DWR). Per the Jordan Lake Water Supply Nutrient
Strategy, Consolidated Mitigation Rule, and Nutrient Offset Payments (15A NCAC 02B .0267, 15A NCAC
02B.0268, 15A NCAC 02B .0295, &15A NCAC 02B .0240),this Parcel is designed to provide riparian buffer
mitigation and nutrient offset credits for unavoidable impacts due to development within the Haw River
Sub-watershed of Jordan Lake in the Cape Fear River Basin. Supporting figures are included in Appendix
B.
The Parcel was evaluated on January 16th, 2015, by Sue Homewood of DWR. Ms. Homewood's evaluation
was part of an inter-agency review, including the US Army Corps of Engineers, to determine if stream
features located within the Site are applicable to provide compensatory stream mitigation under
Restoration Systems'Cape Fear 02 Phase One Umbrella Banking Instrument(Benton Branch USACE Action
ID SAW-2015-01701). Riparian areas adjacent to Parcel features providing compensatory mitigation for
stream and wetland impacts were restored and provide riparian buffer mitigation and nutrient offset
credit.
The Parcel was planned and designed according to the Banking Instrument with DWR, 15A NCAC 02B
.0240, and the Consolidated Mitigation Rule 15A NCAC 026.0295, which became effective on November
1st,2015.The Parcel was designed in concurrence with the Benton Branch Stream and Wetland Mitigation
Bank (SAW# 2015-01701). The mitigation plan for the Benton Branch Stream and Wetland Mitigation
Bank, along with the Stream and Wetland Umbrella Mitigation Banking Instrument, was approved by the
Interagency Review Team on July 6th, 2017. The Section 404 permit (Clean Water Act, 33 USC 1344) was
granted by the US Army Corps of Engineers on June 30th, 2017. The corresponding Section 401 Water
Quality Certification was granted on June 28th, 2017, and the land quality letter of approval was granted
on June 20th, 2017.
Project construction and planting were completed between February 14th and March 14th, 2018. Baseline
monitoring data was collected between mid-and late March 2018. Activities involved restoring and
enhancing riparian buffers and other riparian areas adjacent to mitigated streams to reduce non-point
source contaminant discharges to downstream waters in the Haw River sub-watershed of Jordan Lake.All
riparian areas were assessed by DWR during an onsite visit to determine viability for buffer mitigation and
nutrient offset. Approximately 33.14 acres are protected with a permanent conservation easement. Of
those 33.14 acres, 10.45 acres were restored, 9.40 acres were enhanced by removing cattle from the
streams and riparian areas, and 5.005 acres were preserved. An additional 0.08 acres were restored and
generate nutrient offset credit.
In general, riparian restoration/enhancement area widths on streams extend out to a maximum of 100
feet from the top of stream banks with a minimum width of 20 from the top of the stream banks. Riparian
buffer enhancement and preservation credits generated on this Bank Parcel are allowed pursuant to 15A
NCAC 02B .0295 (o). Neither the riparian buffer enhancement nor preservation credits can be used to
generate nutrient offset credits.Additionally, no riparian restoration areas that are less than 50 feet wide
from the top of stream banks can be used to generate nutrient offset credit. No riparian restoration areas
that are less than 20 feet wide from the top of any stream bank can be used to generate riparian buffer
credit.Therefore,the maximum acreage of riparian restoration on Site that can be converted into nutrient
offset credits is 10.44 acres. Figure 3 (Appendix B) shows the Credit Determination Map, and Section 2.0
details the Bank Parcel's mitigation determination.
Benton Branch Bank Parcel Year 3(2020)Monitoring Report Executive Summary page i
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

Year 4 (2021) vegetation sampling occurred on September 28th, 2021. Stem density across the Parcel was
above the required average density, with 397 planted tree stems per acre (excluding livestakes) surviving
in year 4 (2021); with natural recruits counted, the Site average is 864 stems per acre, excluding livestakes.
Each individual plot exceeded success criteria except for Plots 3 and 12-14. Plot 13 contained no live
planted woody stems; however, three natural recruits of black walnut (Juglans nigra) are present within
the plot. In 2020 (Yr. 3 Monitoring), random vegetation monitoring transects were performed in February
and September and included a transect (T3) adjacent to Plot 13, which identified 6 stems (243 stems per
acre) in February 2020, and 9 stems (364 stems per acre) in September.
2019 Maintenance Summary:
A Lack of surviving planted stems in and around the upper portions of UT-3 (Plot 13), UT-2, and UT-1
were observed during the as -built walkthrough with DWR in July of 2018. The herbaceous layer
consists of abnormally dense knotweed (Polygonum sp.), Japanese stiltgrass (Microstegium
vimineum), and ragweed (Ambrosia sp.). These areas were treated in July of 2019 as part of the annual
maintenance program (Table 7, Appendix C).
Based on field observations and Yr. 1 (2018) monitoring data, IRS implemented replanting of target
areas (UT-3 around Plot 13, UT-2, and UT-1) at an approximate density of 400 stems per acre. Species
planted and their quantity are detailed in Table 5 of Appendix C. IRS Staff performed the replant in
March 2019.
2020 Maintenance Summary:
Invasive Species Work
Maintenance work
May 18 & 26, 2020 and June 24, 2020
Multiflora Rose, Privet, Sweetgum, Tree -of-
Two easement fence repairs due to falling
Heaven, Cattail, Japanese Stiltgrass, and
trees/limbs
Fescue
2021 Maintenance Summary:
During Year 3 (2020) monitoring review and site visit of the stream and wetland component of the
project, the Interagency Review Team (IRT) determined that areas immediately adjacent to UT-1 and
along UT-6 in the vicinity of plots 14 and 15 were lacking in planted woody vegetation and would
benefit from a supplemental planting effort. In January 2021, 250 3-gallon potted stems were
planted in the vicinity of UT-1, and 50 3-gallon potted stems were planted along UT-6, in and around
plots 14 and 15. A species list is included in Appendix C depicting the area of supplemental planting.
Based on stem counts and visual observations during Year 4 (2021), the newly planted stems appear
vigorous. Supplemental planting areas are depicted in Figure 2 (Appendix A).
General Notes
• No encroachment was identified in Year 4
• No evidence of nuisance animal activity (i.e., beaver, heavy deer browsing, etc.) was observed.
Invasive Species Work
Maintenance work
3/18/2021 & 10/13/2021
None
Fescue Treatment
Benton Branch Bank Parcel Year 3 (2020) Monitoring Report Executive Summary page ii
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC

TABLE OF CONTENTS
EXECUTIVE SUMMARY
1.0 PROJECT GOALS, BACKGROUND, AND ATTRIBUTES 1
1.1 Location and Setting 1
1.2 Project Goals and Objectives 1
2.0 MITIGATION POTENTIAL 2
3.0 MONITORING AND MAINTENANCE PLAN 3
3.1 Monitoring Protocol 3
3.2 Parcel Maintenance 4
4.0 REFERENCES 5
APPENDICES
Appendix A. Background Tables
Table 2. Project Activity and Reporting History
Table 3. Project Contacts Table
Table 4. Project Baseline Information &Attributes
Appendix B. Figures
Figure 1. Site Location & Service Area
Figure 2. Current Conditions Plan View
Figures 3 and 3A-3f. Credit Determination
Figure 4. Potential Conversion of Wetland Credit to Riparian Buffer Credit
Figures 5A and 5B. Credit Determination (Changes from BPDP to As-built)
Figure 6. Potential Conversion of Wetland Credit to Riparian Buffer Credit
Appendix C.Vegetation Data
Table 5. Planted Bare Root Woody Vegetation
Table 6. Total Planted Stems by Plot and Species
Vegetation Plot Photographs
Appendix D. Delivered Credit Yield Table for Jordan Sub Watersheds
Appendix E. Year 4 (2021) Planted Stem Height Data
Benton Branch Bank Parcel Year 3(2020)Monitoring Report Table of Contents page i
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

1.0 PROJECT GOALS, BACKGROUND, AND ATTRIBUTES
1.1 Location and Setting
Restoration Systems, LLC has established the Benton Branch Bank Parcel (Parcel), proposed as part of the
Restoration Systems' Phase One Haw River WS Umbrella Banking Instrument(Banking Instrument)signed
October 25th, 2017, between Restoration Systems and the North Carolina Division of Water Resources
(DWR).
The Site encompasses 33 acres of land located on both sides of Milesville Road at the intersection of
Massey Road. Before construction, the Site was characterized by agricultural land utilized for beef cattle
production and municipal effluent disposal, with scattered disturbed forest. Located in the South
Atlantic/Gulf Region approximately 12 miles north of Burlington, NC, in southwest Caswell County(Figure
1,Appendix B),the Parcel is hydrologically situated within the USGS 14-digit HUC 03030002030030 of the
Cape Fear River Basin and Jordan Lake's Haw Sub-Watershed (North Carolina Division of Water Quality
Subbasin Number 03-06-02). The main hydrologic features include Benton Branch, six unnamed
tributaries (UT)to Benton Branch, and adjacent floodplains.
Directions to the Parcel (from Burlington):
• Take Holt St./NC-62 toward N. Fisher St.—0.1 mile
• Continue on Rauhut St./NC-62—3.2 miles
• Turn left on Union Ridge Rd.—6.0 miles
• Turn left on Stoney Mountain Rd.—2.3 miles
• Stoney Mountain Rd becomes Stoney Creek Mountain Rd.—0.9 mile
• Stoney Creek Mountain Rd. becomes Milesville Rd.—1.4 miles
• Turn left on Massey Rd.
Parcel Coordinates: 36.278744, -79.419371
1.2 Project Goals and Objectives
According to the Final Cape Fear River Basin Restoration Priorities (NCEEP 2009), this watershed should
be targeted for restoration to protect the nutrient-sensitive waters that ultimately drain into the nutrient-
sensitive water supply of Jordan Lake. Overall, the purpose of the Benton Branch Buffer and Nutrient
Offset Bank is to restore, enhance, and preserve riparian buffers and other riparian areas adjacent to
mitigated streams onsite. The riparian restoration and enhancement work will improve water quality
within the Parcel and the downstream watershed.The Parcel is located in a region of the state dominated
by agriculture and livestock; restoration of the riparian buffer is expected to result in immediate water
quality benefits within the vicinity of the Parcel through the removal of livestock access to Parcel streams.
Primary goals focus on 1) improving water quality, 2) enhancing flood attenuation and hydrology, 3)
improving aquatic resources, and 4) restoring riparian habitat. Mitigation activities on Site provide
floodplain connectivity, floodplain resistance, stream stability, sediment transport, surface and
subsurface storage/retention, in-stream habitat, riparian habitat and structure, thermal regulation,
floodplain biogeochemical processing, and pollutant filtration, as well as remove sources of pollutants.
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Page 1
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

2.0 MITIGATION POTENTIAL
The Benton Branch Bank Parcel provides Jordan buffer and nutrient offset mitigation credits for
development impacts within the Haw River Sub-watershed of Jordan Lake (Figures 5-6, Appendix B).The
width of the credit generation areas begins at the most landward limit of the top of stream banks or
rooted herbaceous vegetation and extends landward a maximum distance of 200 feet. No buffer
mitigation credit is generated in areas with less than 20 feet in width, and no nutrient offset credit is
generated in areas that are less than 50 feet from TOB. Buffer Mitigation credits generated from riparian
restoration in non-forested pasture areas, with a minimum width of 50 feet from TOB, can be converted
and transferred from Riparian Buffer Credits to Nutrient Offset Credits and from Nutrient Offset Credit to
Riparian Buffer Credits upon written approval from DWR. A maximum of 10.44 acres of riparian
restoration on this Site can be converted and transferred from Riparian Buffer Credits to Nutrient Offset
Credits and from Nutrient Offset Credit back to Riparian Buffer Credits upon approval.The Sponsor must
submit a written request and receive written approval from DWR before any credit conversions and
transfers to the buffer and nutrient credit ledgers. All delivery factors shall be applied to nutrient offset
credits before requesting a conversion.
According to the nutrient reduction goals for the Haw River arm of Jordan Lake, the generated nitrogen
credits per acre in the Haw Sub-watershed for riparian restoration on agricultural land is 2249.36 pounds,
and the generated phosphorus credit per acre is 143.81 pounds.The delivery factors applied to this Parcel
are 25 percent for nitrogen and 8 percent for phosphorus (Appendix D). Delivered credits are calculated
by applying the delivery factors and the acreage of riparian restoration to the generated credits per acre
stated above. Based on the as-built report, Jordan riparian buffer and nutrient offset (Nitrogen and
Phosphorus) credits for the Benton Bank Parcel are summarized in Table 1 and Figures 5-6 (Appendix B).
Table 1.Jordan Lake: Haw River Sub-Watershed Credit Determination Table
14 Digit Watershed ID:03030002030030
Riparian Buffer Mitigation Units
*Buffer Width Credit Type Total Area Mitigation Percentage of Mitigation
Ratio Full Credit Units
Restoration (located on the right 261.40 ft2 196.05 ft2
TOB-29 ft bank of the upper reach of Benton 1:1 75%
(0.006 ac) (0.004 ac)
Branch [Figure 5A,Appendix B])
TOB-100 ft Restoration 454,860.87 ft2 1:1 100% 454,860.87 ft2
(10.44 ac) (10.44 ac)
Enhancement via Cattle Exclusion 406,754.51 ft2 203,377.25 ft2
TOB-100 ft 2:1 100%
(15A NCAC 02B.0295(o)(6) (9.33 ac) (4.66 ac)
101-200 ft Enhancement via Cattle Exclusion 3,385.53 ft2 2:1 33% 558.61 ft2
(15A NCAC 02B.0295(o)(6) (0.07 ac) (0.01 ac)
Preservation 218,084.72 ft2 21,808.47 ft2
TOB-100 ft 10:1 100%
(Rural Subject Streams) (5.00 ac) (0.50 ac)
TOB-29 ft Preservation 254.87 ft2 10:1 75% 19.11 ft2
(Rural Subject Streams) (0.005 ac) (0.0004 ac)
Total Riparian Buffer Mitigation Units 680,820.36 ft2
(15.62 ac)
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Page 2
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

Table 1.Jordan Lake: Haw River Sub-Watershed Credit Determination Table(continued)
Nutrient Offset Credits
Generated
**Buffer Mitigation Total Generated Delivery Delivered
Width Credit Type Type Acreage Credits per Credits Factor Credits
Acre
101-200 ft Nitrogen Restoration 0.08 2249.36 179.95 25% 44.99
101-200 ft Phosphorus Restoration 0.08 143.81 11.50 8% 0.92
*TOB-20 ft= Buffer is less than 20 ft from the TOB and therefore qualifies for no credit.
TOB-29 ft= Buffer width is contiguous from TOB, is a minimum of 20 ft from the TOB and a maximum of 29 ft from
the TOB,and qualifies for 75%credit.
TOB-100 ft=Buffer width is contiguous from TOB,is a minimum of 29 ft from the TOB and a maximum of 100 ft from
the TOB,and qualifies for 100%credit.
101-200'=Buffer width is contiguous from TOB, is a minimum of 101 ft from the TOB and a maximum of 200 ft from
the TOB,and qualifies for 33%credit.
**Buffer mitigation credits are sought from TOB to 100 feet. Beyond buffer credit generating areas, RS is proposing
nutrient offset credits out to a maximum of 200 feet for a contiguous riparian restoration from TOB to 200 feet
where possible.
The Sponsor will maintain 4 credit ledgers for the Parcel under the Banking Instrument and BPDP: (1) for
buffer restoration mitigation credits in both square feet and acres, (1)for buffer enhancement mitigation
credits in square feet and acres, (1) accounting for nitrogen offset credits in pounds and acres, and (1)
accounting for phosphorus offset credits in pounds and acres.
The Sponsor may elect to use riparian areas for either buffer mitigation credit or wetland mitigation credit,
but not both.The Sponsor must submit a written request and receive written approval from DWR before
any credit conversions and transfers to the buffer credit ledger.As part of that request,the Sponsor must
provide DWR with a written acceptance letter from the USACE, accompanied by supporting documents,
for any wetlands that they want removed from the wetland mitigation bank. Only riparian areas that fail
to generate wetland credit may be viable for generating riparian buffer credit. Figure 3 (Appendix B)
depicts riparian areas that could potentially generate riparian buffer credit if they don't qualify to generate
wetland mitigation credits, and Figure 5 (Appendix B) depicts the potential conversion of failed wetland
mitigation credits to riparian buffer credits. Any areas proposed for buffer mitigation credit must meet
the performance standards detailed in 15A NCAC 02B .0295.
3.0 MONITORING AND MAINTENANCE PLAN
3.1 Monitoring Protocol
Restoration monitoring procedures for riparian vegetation will include periodic visual inspection and
annual plant survival and species diversity survey reports. Quantitative sampling of vegetation will be
performed as outlined in CVS Level 1-2 Protocol for Recording Vegetation, Version 4.2 (Lee et al. 2008).
Photos will be taken from all photo points each monitoring year and provided in the annual reports. All
planted stems in the plots will be marked with flagging tape and recorded. Detailed qualitative and
quantitative monitoring is proposed for vegetated riparian areas. Marsh treatment areas will be visually
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Page 3
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

inspected periodically and reported qualitatively within the annual monitor report as required. Reporting
will include a photographic record of the Parcel's assets.
Monitoring of the restoration efforts will be performed for five years or until success criteria are fulfilled.
Each monitoring year, RS shall submit an annual monitoring report to DWR no later than December 31st.
Quantitative monitoring includes measurements of 20-10x10 meter, permanent vegetation plots(2.0%of
riparian buffer mitigation and nutrient offset credit areas). Plots were randomly placed throughout the
planted riparian areas and are representative of credit generating areas. Sampling of vegetation will be
performed in October of each year; monitoring data can be found in Appendix C.
During the first year, planted vegetation received a cursory visual evaluation to ascertain the degree of
overtopping of planted trees by nuisance species. Success criteria within the riparian buffer and nutrient
offset restoration areas will be based on the survival of planted species at a density of 260 stems per acre
after five years of monitoring. A minimum of four native hardwood tree and shrub species must be
present, with no one species representing greater than 50% of the stems. In addition, appropriate
volunteer stems of native hardwood tree and shrub species may be included to meet the final
performance standard of 260 stems per acre upon DWR approval.
A visual assessment of the cattle exclusion and preservation areas within the conservation easement will
also be performed each year to confirm:
• Fencing is in good condition throughout the Site;
• No cattle access within the conservation easement area;
• No encroachment has occurred;
• Diffuse flow is being maintained in the conservations easement area; and
• There has not been any cutting, clearing, filling, grading, or similar activities that would
negatively affect the function of the restored buffer.
3.2 Parcel Maintenance
2019 Maintenance Summary:
A Lack of surviving planted stems in and around the upper portions of UT-3 (Plot 13), UT-2, and UT-1
were observed during the as-built walkthrough with DWR in July of 2018. The herbaceous layer
consists of abnormally dense knotweed (Polygonum sp.), Japanese stiltgrass (Microstegium
vimineum),and ragweed(Ambrosia sp.).These areas were treated in July of 2019 as part of the annual
maintenance program (Table 7,Appendix C).
Based on field observations and Yr. 1 (2018) monitoring data, RS implemented replanting of target
areas(UT-3 around Plot 13, UT-2, and UT-1)at an approximate density of 400 stems per acre. Species
planted and their quantity are detailed in Table 5 of Appendix C. RS Staff performed the replant in
March 2019.
2020 Maintenance Summary:
Invasive Species Work Maintenance work
May 18&26,2020 and June 24,2020
Multiflora Rose, Privet,Sweetgum,Tree-of- Two easement fence repairs due to falling
Heaven,Cattail,Japanese Stiltgrass, and trees/limbs
Fescue
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Page 4
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

2021 Maintenance Summary:
During Year 3 (2020) monitoring review and site visit of the stream and wetland component of the
project,the Interagency Review Team (IRT)determined that areas immediately adjacent to UT-1 and
along UT-6 in the vicinity of plots 14 and 15 were lacking in planted woody vegetation and would
benefit from a supplemental planting effort. In January 2021, 250 3-gallon potted stems were
planted in the vicinity of UT-1, and 50 3-gallon potted stems were planted along UT-6, in and around
plots 14 and 15. A species list is included in Appendix C depicting the area of supplemental planting.
Based on stem counts and visual observations during Year 4 (2021),the newly planted stems appear
vigorous. Supplemental planting areas are depicted in Figure 2 (Appendix A).
General Notes
• No encroachment was identified in Year 4
• No evidence of nuisance animal activity(i.e., beaver, heavy deer browsing,etc.)was observed.
Invasive Species Work Maintenance work
3/18/2021& 10/13/2021
Fescue Treatment None
4.0 REFERENCES
Griffith, G.E., JM Omernik, J.A. Comstock, M.P. Schafale, W.H. McNab, D.R. Lenat, T.F. MacPherson, J.B.
Glover, and VB Shelbourne. 2002. Ecoregions of North Carolina and South Carolina. US Geological
Survey, Reston,Virginia.
Jordan Lake Water Supply Watershed Buffer Rules 15A NCAC 02B .0267, 15A NCAC 02B .0268, and 15A
NCAC 02B .0295
Lee, M.T., R.K. Peet, SD. Roberts, and T.R. Wentworth. 2008. CVS-EEP Protocol for Recording Vegetation,
Level 1-2 Plot Version 4.2. Ecosystem Enhancement Program, North Carolina Department of
Environment and Natural Resources.
North Carolina Division of Water Quality (NCDWQ). 2005. Cape Fear River Basinwide Water Quality Plan.
Available: http://portal.ncdenr.org/c/document_library/get_file?uuid=2eddbd59-b382-4b58-
97ed-c4049bf4e8e4&groupld=38364. North Carolina Department of Environment and Natural
Resources, Raleigh, North Carolina.
North Carolina Ecosystem Enhancement Program (NCEEP 2009). Cape Fear River Basin Restoration
Priorities 2009 (online). Available: http://portal.ncdenr.org/c/document_library/get_file?uuid=
864e82e8-725c-415e-8ed9-c72dfcb55012&groupld=60329
Schafale, M.P. and A.S. Weakley. 1990. Classification of the Natural Communities of North Carolina: Third
Approximation. North Carolina Natural Heritage Program, Division of Parks and Recreation, NC
Department of Environment, Health, and Natural Resources. Raleigh, North Carolina.
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Page 5
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

Appendix A.
Background Tables
Table 2. Project Activity and Reporting History
Table 3. Project Contacts Table
Table 4. Project Baseline Information &Attributes
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

Table 2: Project Activity and Reporting History
Activity/Milestone BPDP Proposed Date Actual Date
BPDP Approved NA January 22nd,2018
Parcel Protection via conservation easement NA December 8th,2015
Easement Assignment to Land Trust NA August 17th,2017
Cattle exclusion/fence construction NA March 2018
Planting NA March 14th,2018
As-Built Data Collection NA March 5'—23rd,2018
As-Built Report Submittal NA December 2018
Year 1(2018) Monitoring October 2018 December 2018
Year 2(2019) Monitoring October 2019 December 2019
Year 3(2020) Monitoring October 2020 November 2020
Year 4(2021) Monitoring October 2021 November 2021
Table 3: Project Contacts Table
Firm POC&Address
1101 Haynes Street,Suite 211
Bank Sponsor Restoration Systems, LLC Raleigh, North Carolina 27604
George Howard and John Preyer
919.755.9490
Designer: Axiom Environmental, Inc. Grant Lewis; 919.215.1693
218 Snow Ave. Raleigh, NC 27603
Lloyd Glover; 919.422.3392
Construction Contractor: Strader Fencing Inc 780 Landmark Road
Willow Spring, NC 27592-7756
Mary-Margaret McKinney; 252.482.8491
Planting Contractor: Carolina Silvics 908 Indian Trail Road
Edenton, NC 27932
Lloyd Glover; 919.422.3392
Seeding Contractor: Land Mechanics, Inc. 780 Landmark Road
Willow Spring, NC 27592-7756
Nursery Stock Suppliers: ArborGen 1.888.888.7158
Baseline Data Collection& Grant Lewis; 919.215.1693
Annual Monitoring Axiom Environmental, Inc. 218 Snow Ave. Raleigh, NC 27603
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

Table 4: Project Baseline Information &Attributes Table
Project Information
Project Name Benton Branch
County Caswell
Project Area (acres) 33.14
Project Coordinates(latitude and longitude) Latitude: 36°16'33.3" N , Longitude:79°25'26.3"W
Project Watershed Summary Information
Physiographic Province Piedmont
River Basin Cape Fear
USGS Hydrologic Unit 8-digit 03030002 USGS Hydrologic Unit 14-digit 03030002030030
DWQ Sub-basin 03-06-02
Project Drainage Area,Total Outfall (miles) 9.06 mi2
Project Drainage Area Percentage of Impervious Area <5%
CGIA Land Use Classification Pasture and Forest Land
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

Appendix B.
Figures
Figure 1. Site Location & Service Area
Figure 2. Current Conditions Plan View
Figures 3 and 3A-3f. Credit Determination
Figure 4. Potential Conversion of Wetland Credit to Riparian Buffer Credit
Figures 5A and 5B. Credit Determination (Changes from BPDP to As-built)
Figure 6. Potential Conversion of Wetland Credit to Riparian Buffer Credit
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

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Appendix C.
Vegetation Data
Table 5. Planted Woody Vegetation
Table 6.Total Planted Stems by Plot and Species
Table 7A& 7B. 2020 Transect Data
Vegetation Plot Photographs
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

Table 5. Planted Bare Root&Containerized Woody Vegetation
Species Quantity 2019 Replant 2021 Replant
(Bare Root) (Bare Root) (3 Gal.)
River birch (Betula nigra) 2550 500 50
Buttonbush (Cephalanthus occidentalis) 250 -- --
Eastern redbud(Cercis canadensis) 1100 -- --
Silky dogwood (Cornus amomum) 2325 -- --
Green ash (Fraxinus pennsylvanica) 3900 500 --
Tulip poplar(Liriodendron tulipifera) 600 -- --
Sycamore(Platanus occidentalis) 3800 -- 100
Black gum (Nyssa sylvatica var.sylvatica) 2000 -- --
Water oak(Quercus nigra) 2800 -- 50
Willow oak(Quercus phellos) 3000 -- 50
Black willow(Salix nigra) 1225 -- --
Elderberry(Sambucus canadensis) 550 -- --
Persimmon (Diospyros virginiana) -- 250 --
Black cherry(Prunus serotine) -- 400 --
White oak(Quercus alba) -- 500 --
American elm (Ulmus americana) -- 500 --
Swamp Chestnut Oak(Quercus michauxii) -- -- 50
TOTAL 24,100 2,650 300
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

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Benton Branch Bank Parcel Appendices
Monitoring Year 4—November 2021

Benton Branch
MY-04 (2021)Vegetation Monitoring Photographs(taken September 2021)
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Benton Branch Bank Parcel Appendices
Monitoring Year 4—November 2021

Benton Branch
MY-04 (2021)Vegetation Monitoring Photographs (taken September 2021)
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Benton Branch Bank Parcel Appendices
Monitoring Year 4—November 2021

Benton Branch
MY-04 (2021)Vegetation Monitoring Photographs (taken September 2021)
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Benton Branch Bank Parcel Appendices
Monitoring Year 4—November 2021

Appendix D.
Delivered Credit Yield Table for Jordan Sub Watersheds
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

Jordan Water Supply Nutrient Strategy Updated
Delivered Credit Yield Table for Jordan Sub Watersheds 12/20/2012
Attachment B
Delivered credit yields for buffer acres in Jordan small watersheds.
Watershed ID Jordan Delivery Factors TN Credit TP Credit
Subwatershed TN TP (lbs/30yrs) (lbs/30yrs)
03030002010010 Haw 25% 10% 562.34 14.38
03030002010020 Haw 37% 36% 832.26 51.77
03030002010030 Haw 44% 40% 989.72 57.52
03030002010040 Haw 49% 44% 1102.19 63.27
03030002010050 Haw 55% 48% 1237.15 69.03
03030002020010 Haw 15% 4% 337.40 5.75
03030002020020 Haw 22% 12% 494.86 17.26
03030002020030 Haw 48% 43% 1079.69 61.84
03030002020040 Haw 32% 33% 719.80 47.46
03030002020050 Haw 32% 32% 719.80 46.02
03030002020060 Haw 47% 42% 1057.20 60.40
03030002020070 Haw 54% 47% 1214.66 67.59
03030002030010 Haw 60% 56% 1349.62 80.53
03030002030020 Haw 44% 31% 989.72 44.58
03030002030030 Haw 25% 8% 562.34 11.50
03030002030040 Haw 42% 30% 944.73 43.14
03030002030050 Haw 64% 62% 1439.59 89.16
03030002030060 Haw 39% 19% 877.25 27.32
03030002030070 Haw 36% 18% 809.77 25.88
03030002030080 Haw 73% 64% 1642.04 92.04
03030002040010 Haw 30% 14% 674.81 20.13
03030002040020 Haw 28% 14% 629.82 20.13
03030002040030 Haw 71% 63% 1597.05 90.60
03030002040040 Haw 32% 15% 719.80 21.57
03030002040050 Haw 52% 50% 1169.67 71.90
03030002040060 Haw 54% 51% 1214.66 73.34
03030002040070 Haw 67% 60% 1507.07 86.28
03030002040080 Haw 53% 51% 1192.16 73.34
03030002040090 Haw 54% 51% 1214.66 73.34
03030002040100 Haw 75% 65% 1687.02 93.47
03030002040110 Haw 66% 60% 1484.58 86.28
03030002050010 Haw 74% 68% 1664.53 97.79
03030002050020 Haw 81% 74% 1821.98 106.42
03030002050030 Haw 42% 17% 944.73 24.45
03030002050040 Haw 80% 73% 1799.49 104.98
Page 1 of 2

Jordan Water Supply Nutrient Strategy Updated
Delivered Credit Yield Table for Jordan Sub Watersheds 12/20/2012
Watershed ID Jordan Delivery Factors TN Credit TP Credit
Subwatershed TN TP (lbs/30yrs) (lbs/30yrs)
03030002050050 Haw 71% 67% 1597.05 96.35
03030002050060 Haw 79% 73% 1777.00 104.98
03030002050070 Haw 78% 72% 1754.50 103.54
03030002050080 Haw 80% 73% 1799.49 104.98
03030002050090 Haw 79% 73% 1777.00 104.98
03030002050100 Haw 81% 75% 1821.98 107.85
03030002060010 Haw 81% 74% 1821.98 106.42
03030002060020 Haw 95% 97% 2136.90 139.49
03030002060030 Haw 88% 91% 1979.44 130.86
03030002060040 Haw 97% 98% 2181.88 140.93
03030002060050 Haw 92% 95% 2069.41 136.61
03030002060062 Haw 98% 99% 2204.38 142.37
03030002060070 UNH 40% 19% 867.70 27.32
03030002060080 UNH 59% 45% 1279.86 64.71
03030002060100 UNH 69% 63% 1496.79 90.60
03030002060110 UNH 61% 58% 1323.25 83.41
03030002060120 UNH 69% 63% 1496.79 90.60
03030002060140 UNH 85% 89% 1843.87 127.99
03030002060130 UNH 69% 63% 1496.79 90.60
03030002060160 LNH 85% 90% 1932.07 131.76
03030002060090* UNH 92% 94% 1995.71 135.18
03030002060090* LNH 92% 94% 2091.18 137.62
03030002060060* UNH 94% 96% 2039.10 138.05
03030002060060* LNH 94% 96% 2136.64 140.54
03030002060150* UNH 88% 91% 1908.94 130.86
03030002060150* 1 LNH 1 88% 91% 1 2000.26 1 133.22
*Watershed is located in both the Upper New Hope(UNH)and Lower New Hope (LNH)Subwatersheds.
Page 2 of 2

Appendix E.
Year 4(2021) Planted Stem Height Data
Benton Branch Bank Parcel Year 4(2021)Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems,LLC

Plot Scientific Name X Y Height(cm) DBH (cm) Vigor
1 Betula nigra 1.5 1.8 92 4
1 Betula nigra 2.0 5.6 92 3
1 Betula nigra 1.9 6.9 76 3
1 Betula nigra 2.9 8.0 75 3
1 Platanus occidentalis 3.3 1.0 225 1.1 4
1 Platanus occidentalis 3.6 3.8 221 1.1 4
1 Platanus occidentalis 5.5 0.4 289 1.8 4
1 Betula nigra 5.0 2.2 0 Missing
1 Platanus occidentalis 5.3 3.7 322 2.5 4
1 Fraxinus pennsylvanica 5.6 5.2 102 3
1 Betula nigra 5.6 6.7 78 3
1 Platanus occidentalis 5.8 8.2 368 2.5 4
1 Betula nigra 6.0 9.6 95 4
1 Betula nigra 8.7 5.5 91 4
1 Betula nigra 9.3 0.2 0 Missing
1 Platanus occidentalis 3.8 8.0 238 1.1 4
2 Platanus occidentalis 0.6 4.1 368 2.5 4
2 Platanus occidentalis 1.7 7.2 343 2.6 4
2 Platanus occidentalis 4.6 9.7 361 3.5 4
2 Liriodendron tulipifera 4.7 7.4 0 Missing
2 Fraxinus pennsylvanica 6.0 1.7 273 2 4
2 Platanus occidentalis 6.7 5.5 373 3.5 4
2 Fraxinus pennsylvanica 9.0 7.4 337 2.9 4
2 Fraxinus pennsylvanica 7.7 5.7 151 0.5 4
2 Platanus occidentalis 8.9 5.6 264 1.7 4
2 Betula nigra 10.0 2.7 72 1
2 Platanus occidentalis 2.4 4.4 368 3.3 4
3 Quercus nigra 1.2 1.1 55 3
3 Fraxinus pennsylvanica 3.7 7.3 338 2.7 4
3 Betula nigra 6.5 1.6 133 4
3 Betula nigra 9.7 9.1 127 4
3 Platanus occidentalis 9.7 6.6 228 1.3 4
3 Platanus occidentalis 9.7 1.7 348 2 4
6 Platanus occidentalis 1.3 2.1 262 1.5 4
6 Betula nigra 3.9 2.3 68 4
6 Cephalanthus occidentalis 1.7 6.4 80 4
6 Quercus phellos 0.0 8.0 71 4
6 Quercus phellos 1.5 7.8 178 0.6 4
6 Quercus phellos 0.4 9.8 0 Missing
6 Betula nigra 3.3 6.4 110 3
6 Platanus occidentalis 4.6 0.0 235 1.3 4
6 Betula nigra 5.8 7.9 95 3
6 Betula nigra 5.0 5.9 101 4
6 Quercus phellos 4.9 8.9 59 3
6 Betula nigra 6.2 3.2 83 3
6 Platanus occidentalis 8.2 2.3 231 1 4

Plot Scientific Name X Y Height (cm) DBH (cm) Vigor
6 Quercus phellos 9.8 8.5 79 4
6 Betula nigra 8.4 8.5 0 Missing
6 Betula nigra 7.1 8.2 72 3
6 Quercus phellos 6.4 9.3 82 3
6 Platanus occidentalis 6.3 0.9 141 0.4 4
10 Betula nigra 1.2 6.8 91 3
10 Liriodendron tulipifera 1.3 8.2 104 3
10 Betula nigra 1.2 9.7 103 3
10 Betula nigra 2.9 8.7 145 0.2 3
10 Betula nigra 5.3 6.0 62 3
10 Betula nigra 6.4 3.7 160 0.2 3
10 Betula nigra 7.9 1.8 89 3
10 Betula nigra 8.6 4.6 102 3
10 Betula nigra 5.8 9.9 176 0.5 4
10 Quercus michauxii 1.3 4.0 75 3
11 Nyssa sylvatica 2.0 1.5 43 3
11 Cercis canadensis 1.2 4.1 59 3
11 Nyssa sylvatica 0.6 6.0 75 3
11 Fraxinus pennsylvanica 1.4 9.3 104 2
11 Fraxinus pennsylvanica 2.9 10.0 46 2
11 Nyssa sylvatica 4.7 8.3 0 Missing
11 Nyssa sylvatica 4.0 2.5 0 0
11 Nyssa sylvatica 6.3 0.8 0 0
11 Nyssa sylvatica 6.4 6.8 43 2
11 Nyssa sylvatica 6.9 9.1 46 3
11 Nyssa sylvatica 9.2 10.0 45 2
11 Nyssa sylvatica 9.9 7.9 48 2
11 Nyssa sylvatica 7.6 4.6 0 Missing
11 Nyssa sylvatica 8.0 6.8 10 1
11 Nyssa sylvatica 0.8 0.1 64 2
12 Cercis canadensis 1.5 9.0 15 1
12 Nyssa sylvatica 3.3 8.1 37 1
12 Nyssa sylvatica 3.4 3.7 0 Missing
12 Nyssa sylvatica 4.0 1.2 51 3
12 Cercis canadensis 5.7 2.5 0 Missing
12 Nyssa sylvatica 8.0 4.2 30 1
12 Nyssa sylvatica 5.4 6.7 28 1
14 Quercus nigra 1.5 2.5 0 Missing
14 Fraxinus pennsylvanica 6.6 7.4 76 3
14 Fraxinus pennsylvanica 8.8 7.0 0 0
14 Fraxinus pennsylvanica 8.2 4.1 0 0
14 Fraxinus pennsylvanica 6.8 4.1 0 0
14 Quercus phellos 0.2 1.1 241 1 4
14 Fraxinus pennsylvanica 4.5 7.2 112 4
14 Quercus phellos 0.0 0.0 215 1 4
15 Betula nigra 3.6 5.9 225 1.1 4
15 Betula nigra 2.2 8.3 235 1.5 4

Plot Scientific Name X Y Height (cm) DBH (cm) Vigor
15 Betula nigra 6.8 9.4 220 0.5 4
15 Celtis occidentalis 8.0 7.1 141 0.1 4
15 Betula nigra 3.1 0.6 0 Missing
15 Quercus phellos 4.0 1.2 189 0.7 4
15 Quercus nigra 0.8 4.2 168 0.5 4
15 Quercus nigra 8.4 0.6 225 0.9 4
15 Quercus nigra 8.6 5.8 165 0.3 4
16 Betula nigra 0.9 1.2 195 0.5 4
16 Fraxinus pennsylvanica 2.8 6.5 227 0.6 4
16 Betula nigra 1.4 9.6 80 3
16 Fraxinus pennsylvanica 3.1 3.5 273 1.5 4
16 Betula nigra 6.9 1.0 257 0.7 4
16 Betula nigra 9.1 2.0 124 3
16 Fraxinus pennsylvanica 7.1 4.5 195 0.4 4
16 Betula nigra 4.6 9.3 80 3
16 Fraxinus pennsylvanica 5.2 6.8 135 3
17 Betula nigra 1.2 4.2 188 0.2 4
17 Fraxinus pennsylvanica 0.7 8.0 235 0.5 4
17 Fraxinus pennsylvanica 2.9 7.3 151 0.2 4
17 Betula nigra 3.5 3.7 0 Missing
17 Betula nigra 5.8 3.4 155 0.1 4
17 Quercus nigra 5.7 7.0 140 0.1 4
17 Diospyros virginiana 5.8 9.1 115 4
17 Betula nigra 7.2 9.6 135 4
17 Fraxinus pennsylvanica 7.7 8.3 143 0.1 4
17 Betula nigra 8.8 9.8 135 4
17 Betula nigra 10.0 8.2 100 4
17 Quercus 10.0 9.6 72 4
17 Quercus 8.0 4.3 0 Missing
17 Fraxinus pennsylvanica 8.5 0.2 125 4
17 Quercus phellos 9.9 0.4 214 1.5 4
18 Cercis canadensis 0.0 0.6 51 3
18 Cercis canadensis 2.8 1.0 40 2
18 Nyssa sylvatica 2.7 2.6 39 3
18 Quercus rubra 0.5 2.6 36 3
18 Quercus phellos 0.6 4.6 53 3
18 Quercus phellos 2.7 4.6 70 3
18 Cercis canadensis 5.7 0.9 22 3
18 Quercus phellos 6.9 4.8 55 3
18 Quercus nigra 5.9 7.7 0 Missing
18 Quercus alba 4.1 5.8 41 3
18 Quercus phellos 5.1 4.5 53 3
19 Quercus nigra 1.1 0.6 64 3
19 Quercus nigra 2.7 3.0 0 0
19 Quercus nigra 5.6 3.0 40 3
19 Quercus nigra 6.3 0.2 24 3
19 Quercus nigra 8.9 0.6 68 1

Plot Scientific Name X Y Height (cm) DBH (cm) Vigor
19 Quercus nigra 5.9 5.0 32 3
19 Nyssa sylvatica 6.6 8.0 0 Missing
19 Nyssa sylvatica 8.8 8.1 0 0
19 Quercus rubra 1.0 3.8 56 3
19 Quercus alba 3.1 5.0 45 3
19 Quercus phellos 4.2 8.0 62 3
20 Quercus phellos 0.2 0.6 56 3
20 Quercus nigra 2.0 1.3 45 3
20 Quercus nigra 4.1 1.9 40 3
20 Quercus nigra 6.0 2.8 28 3
20 Quercus alba 5.3 0.2 17 2
20 Nyssa sylvatica 7.8 6.0 26 3
20 Quercus pagoda 5.9 5.2 48 3
20 Fraxinus pennsylvanica 6.5 7.2 56 3
20 Fraxinus pennsylvanica 8.5 7.5 54 3
20 Quercus nigra 8.7 9.9 72 3
20 Fraxinus pennsylvanica 4.3 6.3 72 3
20 Fraxinus pennsylvanica 2.2 6.3 35 3
20 Quercus phellos 2.2 8.4 40 3
20 Cercis canadensis 8.6 2.9 20 2
21 Quercus lyrata 0.1 2.6 45 3
21 Nyssa sylvatica 4.2 4.6 0 Missing
21 Quercus phellos 0.4 4.0 42 3
21 Nyssa sylvatica 5.6 7.4 40 2
21 Cercis canadensis 8.5 8.4 44 3
21 Cercis canadensis 6.7 9.5 81 3
21 Quercus phellos 2.2 10.0 65 4
21 Platanus occidentalis 1.6 8.4 52 4
21 Platanus occidentalis 2.8 5.1 118 4
21 Cornus amomum 3.5 7.0 50 2
21 Quercus phellos 2.2 3.3 35 2
21 Nyssa sylvatica 2.7 0.8 0 0
22 Cercis canadensis 1.8 2.9 112 3
22 Cercis canadensis 0.5 0.0 52 3
22 Cercis canadensis 4.5 0.6 65 3
22 Cercis canadensis 4.1 3.3 62 3
22 Quercus phellos 6.5 1.2 110 3
22 Quercus nigra 8.7 1.4 33 3
22 Cephalanthus occidentalis 5.4 9.6 158 0.3 4
22 Quercus phellos 9.2 7.3 148 0.3 4
22 Quercus phellos 2.6 5.3 291 1.3 4
22 Cephalanthus occidentalis 3.4 9.0 135 4
22 Cornus amomum 1.6 8.1 43 4
22 Platanus occidentalis 0.2 9.8 385 2.6 4
22 Fraxinus pennsylvanica 1.5 6.5 66 3
22 Platanus occidentalis 0.5 5.0 415 3.6 4
22 Cercis canadensis 5.7 3.2 53 4

Plot Scientific Name X Y Height(cm) DBH (cm) Vigor
23 Cornus amomum 0.3 1.0 95 3
23 Cornus amomum 1.1 2.7 127 3
23 Cornus amomum 3.6 3.3 90 3
23 Nyssa sylvatica 5.7 2.9 46 3
23 Cercis canadensis 5.7 2.9 0 Missing
23 Quercus nigra 9.8 7.4 41 3
23 Cercis canadensis 6.0 7.6 43 3
23 Cercis canadensis 4.5 9.6 24 2
23 Cornus amomum 3.1 9.0 72 3
23 Cornus amomum 3.7 5.4 75 3
23 Fraxinus pennsylvanica 1.4 6.3 126 3
23 Fraxinus pennsylvanica 1.0 9.4 41 3
24 Quercus phellos 1.1 3.4 103 3
24 Quercus phellos 2.9 4.6 105 3
24 Fraxinus pennsylvanica 9.2 0.3 79 3
24 Quercus nigra 7.5 9.0 60 3
24 Quercus nigra 6.0 8.0 0 0
24 Quercus phellos 4.9 5.4 195 0.8 4
24 Quercus phellos 4.0 7.2 55 3
24 Quercus phellos 2.4 6.3 93 3
24 Fraxinus pennsylvanica 3.9 9.6 85 4
24 Fraxinus pennsylvanica 0.7 8.0 147 0.2 4
24 Quercus nigra 0.6 5.6 51 3
25 Quercus phellos 0.8 0.7 201 0.9 4
25 Quercus phellos 2.8 0.7 63 3
25 Fraxinus pennsylvanica 1.6 2.7 123 3
25 Quercus nigra 9.8 1.2 0 0
25 Fraxinus pennsylvanica 5.2 1.5 243 1.2 4
25 Quercus nigra 6.1 3.9 0 0
25 Betula nigra 8.7 7.0 331 3 4
25 Betula nigra 7.1 7.6 199 0.7 4
25 Quercus phellos 7.6 9.6 0 Missing
25 Platanus occidentalis 4.8 9.8 212 1.2 4
25 Fraxinus pennsylvanica 1.4 7.7 282 2 4
25 Quercus phellos 0.9 9.8 0 0
25 Platanus occidentalis 0.1 5.6 195 1 4
25 Quercus nigra 2.2 5.3 70 3
25 Platanus occidentalis 4.3 5.0 322 1.9 4