20141149 Ver 8_Year 2 Monitoring Report DRAFT_20191217

ID#* 20141149 Version* 8
Select Reviewer:*
Katie Merritt
Initial Review Completed Date 12/18/2019
Mitigation Project Submittal-12/17/2019
Is this a Prospectus, Technical Proposal or a New Site?* O Yes a No
Type of Mitigation Project:*
r Stream r Wetlands W Buffer W Nutrient Offset
(Select all that apply)
Project Contact Information
Contact Name:*
Raymond Holz
Project Information
..................................................................................................................................................................
ID#:* 20141149
Existing ID�
Project Type: r DMS r Mitigation Bank
Project Name: Rocky Top
County: Alamance
Document Information
Email Address:*
[e-mail]
Version: *8
Existing Version
Mitigation Document Type:*
Mitigation Monitoring Report
File Upload: Draft _Rocky Top_MY2-2019_12-17-2019_ pdf 13.27MB
Rease upload only one R7F of the complete file that needs to be subrritted...
Signature
Print Name:* Raymond Holz
Signature:*

YEAR 2 (2019)
MONITORING REPORT

Rocky Top Bank Parcel
DWR# 20141149 version 8

Pursuant to:
Restoration Systems’ Phase One Haw River WS Umbrella Banking Instrument for
Riparian Buffer and Nutrient Offset Mitigation Credits

PREPARED BY:

RESTORATION SYSTEMS, LLC
1101 HAYNES STREET, SUITE 211
RALEIGH, NORTH CAROLINA 27604

AND

AXIOM ENVIRONMENTAL, INC.
218 SNOW AVENUE
RALEIGH, NORTH CAROLINA 27603

December 2019
Rocky Top Bank Parcel Year 2 (2019) Monitoring Report Executive Summary page i
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC
EXECUTIVE SUMMARY
Restoration Systems, LLC has established the Rocky Top 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). 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 and nutrient offset mitigat ion 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 December 19th, 2014 by Virginia Baker of DWR. Ms. Baker’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, (Rocky Top USACE Action ID SAW-
2015-01710). Riparian areas adjacent to features within the parcel providing compensatory mitigation for
stream impacts, were restored and provide riparian buffer mitigation and nutrient off-set 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 02B.0295, which became effective on November
1, 2015. The Parcel was designed in concurrence with the Rocky Top Stream and Wetland Mitigation Bank
(SAW# 2015-01710). The mitigation plan for the Rocky Top 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 (Clean Water Act, 33 USC 1344) was granted by the U.S.
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 June 20th, 2017.

Project construction and planting was completed between October 16 and December 19, 2017. For purposes
of the Rocky Top Nutrient Offset and Riparian Buffer Bank, the Parcel involved restoring riparian buffers
and other riparian areas adjacent to mitigated streams in order to help 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.
During the June 13, 2017 site visit, all riparian areas were confirmed to have been in pasture for cattle
grazing. Approximately 5.16 acres will be protected with a permanent conservation easement. Of those
5.16 acres, 2.35 acres were restored for Jordan riparian buffer credit, 1.09 acres were restored for nutrient
offset credit, and 0.94 acres were enhanced by the removal of cattle from streams and riparian areas for
Jordan riparian buffer credit. In general, riparian restoration/enhancement area widths on streams extend
out to a maximum of 200 feet from the top of bank with a minimum width of 20 from top of banks. Riparian
buffer enhancement credits generated on this Bank Parcel are allowed pursuant to 15A NCAC 02B .0295
(o)(6) but cannot be used to generate nutrient offset credits. Additionally, no riparian restoration areas that
are less than 50 feet wide from Top of Banks can be used to generate nutrient offset credit, and no riparian
restoration areas that are less than 20 feet wide from Top of Banks can be used to generate riparian buffer
credit. Therefore, the maximum acreage of riparian restoration on this site that is able to be converted into
nutrient offset credits if needed by RS, is 2.32 acres) shows the Credit Determination Map and Section 2.0
provides details of the mitigation determination on the Bank Parcel.

Year 2 (2019) vegetation sampling occurred October 3, 2019. Stem density across the Parcel was above the
required average density with 370 planted tree stems per acre (excluding livestakes) surviving in year 2
(2019). In addition, each individual plot exceeded success criteria.

After observing the Site for the Year 2 growing season, routine vegetation management activities will be
implemented in accordance with Section 4.2 (Parcel Maintenance) of the Bank Parcel Development Plan
Rocky Top Bank Parcel Year 2 (2019) Monitoring Report Executive Summary page ii
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC
to facilitate continued success. These activities will include mechanical and chemical control of competing
herbaceous vegetation in targeted areas beginning early in the 3rd year (2020). In areas of intensive
treatment, a short-term nurse-crop seed mix may be planted to suppress weedy herbaceous competition.
These management activities will ensure continued survival of the planted stems as well as establishment
of natural recruits.

Restoration Systems conducted a Site review of the Orphan Creek Stream and Wetland Restoration project
on 11/5/19 with USACE representative Sam Dailey with no outstanding issues.

2019 Maintenance Summary;
Three herbicide applications were performed during the 2019 growing season targeting Japanese
Stiltgrass (Microstegium vimineum). Sweetgum (Liquidambar styraciflua) was a secondary target
species, and were hand treated around Veg Plot 2. Further detail about the herbicide application is
summarized in Table 7 of Appendix C.

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report Table of Contents page i
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC
TABLE OF CONTENTS

EXECUTIVE SUMMARY ........................................................................................................................... i

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
Figure 3. Credit Determination
Figure 4. Close-up of Restoration Buffer Width TOB-29 Feet
Figure 5. 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
Table 7. Herbicide Application Logs
Vegetation Plot Photographs

Appendix D. Delivered Credit Yield Table for Jordan Sub Watersheds

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report page 1
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 (RS) has established the Rocky Top 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).

The Parcel encompasses 5.16 acres of land located 2600 feet northeast of the intersection of Major Hill
Road and Holman Mill Road. Before construction, the Parcel was characterized by disturbed forest,
hayfields, and livestock pasture. Forested areas of the Site were accessible to livestock resulting in a thin
understory with compacted soils. Located in the South Atlantic/Gulf Region approximately 6 miles
southwest of Saxapahaw and 2 miles east of Snow Camp in Alamance County (Figure 1, Appendix B), the
Parcel is hydrologically situated within the USGS 14-digit HUC and Targeted Local Watershed
03030002050050 of the Cape Fear River Basin and Jordan Lake’s Haw Sub-Watershed (DWR Subbasin
Number 03-06-02). The main hydrologic features include two unnamed tributaries (UT) to Reedy Branch
and adjacent floodplains.

Directions to the Site from Snow Camp are as follows.
• Take E. Greensboro Chapel Hill Rd. east – 1.5 miles
• Turn right on Holman Mill Rd. – 1.4 miles
• The site is on the left.
• Access Site at the gate located 0.5 miles down Major Hill Rd.
• Landowner permission required to access Site.
o Site Coordinates: 35.886642, -79.388262

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 Rocky Top Buffer and Nutrient Offset
Bank was to restore, enhance, and preserve riparian buffers and other riparian areas adjacent to mitigated
streams onsite. The riparian restoration and enhancement will result in improved 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 focused on 1) improving water quality, 2) enhancing flood attenuation and hydrology, 3)
improving aquatic resources, and 4) restoring riparian habitat. Mitigation activities will provide floodplain
connectivity, floodplain resistance, stream stability, sediment transport, surface and subsurface storage, and
retention, in-stream habitat, riparian habitat and structure, thermal regulation, floodplain biogeochemical
processing, and pollutant filtration as well as remove sources of pollutants.

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report page 2
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC
2.0 MITIGATION POTENTIAL
The Rocky Top Bank Parcel provides Jordan buffer mitigation and nutrient offset credits for development
impacts within the Haw River Sub-watershed of Jordan Lake. The width of the credit generation area begins
at the most landward limit of the top of bank or the rooted herbaceous vegetation and extends landward a
maximum distance of 200 feet where able. A maximum of 2.32 acres of riparian restoration on this site is
able to be converted and transferred from Riparian Buffer Credits to Nutrient Offset Credits and from
Nutrient Offset Credit back to Riparian Buffer Credits upon approval and does not include any of the
acreage being mitigated to generate wetland mitigation credit. The Sponsor must submit a written request
and receive written approval from DWR prior to any credit conversions and transfers to the buffer and
nutrient credit ledgers. All delivery factors shall be applied to nutrient offset credits prior to 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 agriculture land is 2249.36 pounds
and the generated phosphorus credit per acre is 143.81 pounds. The delivery factors applied to this parcel
are 71 percent for nitrogen and 67 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 asbuilt project, Jordan riparian buffer and nutrient offset (Nitrogen and
Phosphorus) credits for the Rocky Top Bank Parcel are summarized in Table 1 and corresponding Figures
3-4 (Appendix B).

The Sponsor will maintain four 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
qualify 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.

Space Purposefully Left Blank

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report page 3
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC
Table 1. Jordan Lake: Haw River Sub-Watershed Credit Determination Table
14 Digit Watershed ID: 03030002050050
Riparian Buffer Mitigation Credits
*Buffer Width
from TOB Credit Type Total Area Mitigation
Ratio
Percentage of Full
Credit Mitigation Credits
TOB-29 ft
Restoration
152.83 ft2
(0.003 ac) 1:1 75% 114.62 ft2
(0.002 ac)
TOB-100 ft 102,356.48 ft2
(2.35 ac) 1:1 100% 102,356.48 ft2
(2.35 ac)
TOB-29 ft Enhancement
via Cattle
Exclusion (15A
NCAC 02B
.0295 (o)(6)
54.43 ft2
(0.001 ac) 2:1 75% 20.41 ft2
(0.0004 ac)
TOB-100 ft 40,784.55 ft2
(0.94 ac) 2:1 100% 20,392.28 ft2
(0.47 ac)
101-200 ft 113.87 ft2
(0.003 ac) 2:1 33% 18.79 ft2
(0.0005 ac)
Total Riparian Buffer Mitigation Credits 122,902.58 ft2
(2.82 ac)

Nutrient Offset Credits
**Buffer Width
from TOB
Credit
Type
Mitigation
Type
Total
Acreage
Generated
Credits per
Acre
Generated
Credits
Delivery
Factor
Delivered
Credits
101-200 ft Nitrogen Restoration 1.09 2249.36 2451.80 71% 1740.78
101-200 ft Phosphorus Restoration 1.09 143.81 156.75 67% 105.02
* 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 top of bank 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 top of bank
to 200 feet where possible.

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 the 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 inspected

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report page 4
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC
periodically and reported qualitatively within the annual monitor report, which will include photographic
record of the Parcel’s assets.

Monitoring of the restoration efforts will be performed for five years or until success criteria are fulfilled.
Restoration Systems shall submit an annual monitoring report to DWR, no later than December 31st of
each year. Quantitative monitoring includes measurements of 4-10x10 meter, permanent vegetation plots
(2.8% of restoration 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, with the 1st monitoring data to be collected in the fall of 2018 but not within 6
months from initial planting. Monitoring data can be found in Appendix C.

During the first year, vegetation received a cursory, visual evaluation on a periodic basis to ascertain the
degree of overtopping of planted elements 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.

3.2 Parcel Maintenance
After observing the Site for the Year 1 growing season, routine vegetation management activities will be
implemented in accordance with Section 4.2 (Parcel Maintenance) of the Bank Parcel Development Plan
to facilitate continued success. These activities will include mechanical and chemical control of competing
herbaceous vegetation in targeted areas beginning early in the 2nd year (2019). In areas of intensive
treatment, a short-term nurse-crop seed mix may be planted to suppress weedy herbaceous competition.
These management activities will ensure the continued survival of the planted stems as well as the
establishment of natural recruits.

2019 Maintenance Summary;
Three herbicide applications were performed during the 2019 growing season targeting Japanese
Stiltgrass (Microstegium vimineum). Sweetgum (Liquidambar styraciflua) was a secondary target
species, and were hand treated around Veg Plot 2. Further detail about the herbicide application is
summarized in Table 7 of Appendix C.

2020 Planned Maintenance;
Additional herbicide applications are scheduled for the 2020 monitoring season. Treatments will
focus on Tall Fescue (Festuca arundinacea) within the Dry-Mesic Oak Hickory Planting zones of the
Site (i.e., uplands). Treatments for Sweetgum (Liquidambar styraciflua) and other woody invasive
species will continue throughout the 2020 year.

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report page 5
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC
4.0 REFERENCES

Griffith, G.E., J.M. Omernik, 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 Carolina. U.S.
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, S.D. 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&groupId=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&groupId=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,
N.C. Department of Environment, Health, and Natural Resources. Raleigh, North Carolina.

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report Appendices
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

Rocky Top Bank Parcel Year 2 (2019) 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 November 14, 2017
Parcel Protection via conservation easement NA October 17, 2014
Easement Assignment to Land Trust NA August 17, 2017
Cattle exclusion / fence construction NA April 2015
Planting NA March 2018
As-Built Data Collection NA March 5th – 23rd, 2018
As-Built Report Submittal NA July 2018
Year 1 (2018) Monitoring October 2018 December 2018
Year 2 (2019) Monitoring October 2019 October 2019

Table 3: Project Contacts Table
Firm POC & Address
Bank Sponsor Restoration Systems, LLC
1101 Haynes Street, Suite 211
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
Construction Contractor: Strader Fencing Inc
Lloyd Glover; 919.422.3392
780 Landmark Road
Willow Spring, NC 27592-7756
Planting Contractor: Carolina Silvics
Mary-Margaret McKinney 252.482.8491
908 Indian Trail Road
Edenton, NC 27932
Seeding Contractor: Land Mechanics, Inc.
Lloyd Glover; 919.422.3392
780 Landmark Road
Willow Spring, NC 27592-7756
Nursery Stock Suppliers: ArborGen 1.888.888.7158
Baseline Data Collection &
Annual Monitoring Axiom Environmental, Inc. Grant Lewis; 919.215.1693
218 Snow Ave. Raleigh, NC 27603

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC

Table 4: Project Baseline Information & Attributes Table
Project Information
Project Name Rocky Top
County Alamance
Project Area (acres) 5.16
Project Coordinates (latitude and longitude) Latitude: 35°53’12.1”N , Longitude: 79°23’16.1”W
Project Watershed Summary Information
Physiographic Province Piedmont
River Basin Cape Fear
USGS Hydrologic Unit 8-digit 03030002 USGS Hydrologic Unit 14-digit 03030002050050
DWQ Sub-basin 03-06-02
Project Drainage Area, Total Outfall (miles) 0.07 mi²
Project Drainage Area Percentage of Impervious Area < 1%
CGIA Land Use Classification Pasture and Forest Land

Rocky Top Bank Parcel Year 2 (2019) 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
Figure 3. Credit Determination
Figure 4. Close-up of Restoration Buffer Width TOB-29 Feet
Figure 5. Potential Conversion of Wetland Credit to Riparian Buffer Credit

Copyright:© 20 14 DeLo rme
FIGURE
Dra wn by :
Dat e:
Sca le:
Pro jec t N o.:
KRJ
SEPT 2016
1:3500
16-017
Tit le:
Pro jec t:
Pre pa red fo r:
Ala ma nce Co un ty, N C
ROCKY TOPBANK PARCEL
SITE LOCATIO NANDSERVICE AREA
1
Not es :
0 10 20 30 405Miles
Legend
Jor dan La ke 14 -dig it U SG S HU Cs
Par cel Se rvic e A re a - Ha w R ive r S ubw at ers hed
Haw R ive r S ubw at ers hed
New H op e C ree k S ub wa ters he d
³
1. Bac kground Im agery Source:DeLorme Wo rld Basem ap(20 14)^
Bank Parcel LocationUSGS 14-digit HUC03030002050050
1157 Major Hill RoadSnow Camp, NC 27349
35.886591°N, 79.387578°W
2
4
3
1
NCCGIA
FIGURE
Dra wn by :
Dat e:
Sca le:
Pro jec t N o.:
KRJ/CLF
MA R 2018
1:900
16-017
Tit le:
Pro jec t:
Pre pa red for :
Alamance County, NC
ROCKY TO PBANKPARCEL
CURRENTCONDITIONSPLAN VIEW
2
³
Legend
Ro cky Top Easemen t = 5.2 ac
Stream Cha nnel (Design)
CV S Plots
0 150 30075Feet
U T -1
U T -2
2
4
3
1
NCCGIA
FIGURE
Drawn by:
Date:
Scale:
Project No.:
KRJ/CLF
MAR 2018
1:1200
16-017
Title:
Project:
Prepared for:
Alamance County, NC
ROCKY T OPBANK PARCEL
CREDITDET ERMINAT ION
3
Notes:
0 100 200 300 400 50050Feet
Legend
Conservation Easement = 5.16 ac
Restored Stream Channel = 0.18 ac
Riparian Buffer Restoration Area (TOB-29 ft ) = 0.003 ac (152.83 sq ft)
Riparian Buffer Restoration Area (TOB-100 ft) = 2.35 ac (102,356.48 sq ft)
Nutrient Offset Credit Area (101-200 ft) = 1.09 ac (47,626.47 sq ft)
Riparian Buffer Enhancement via Cattle Exclusion (TOB-29 ft) = 0.001 ac (54.43 sq ft)
Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) = 0.94 ac (40,784.55 sq ft)
Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) = 0.003 ac (113.87 sq ft)
Wetland Mitigation Credit Area = 0.54 ac
Constructed BMP Footprint (no credit) = 0.02 ac
50 ft from TOB
100 ft from TOB
200 ft from TOB
CVS Plots
³
1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council)
NOT E: No riparian buffer credit is givenin areas with buffer width of less than20 ft. Additionally, no nutrient offsetcredit is given in areas with buffer widthless than 50 ft.
UT -1
UT -2
NOT E ABOUT BUFFER WIDT HS:T OB-20 ft = Buffer is less than 20 ft from the T OB and therefore qualifies for nocredit.T OB-29 ft = Buffer width is contiguous from T OB, is a m inim um of 20 ft fromthe T OB and a m axim um of 29 ft from the T OB, and qualifies for 75% credit.T OB-100 ft = Buffer width is contiguous from T OB, is a m inim um of 29 ft fromthe T OB and a m axim um of 100 ft from the T OB, and qualifies for 100% credit.101-200’ = Buffer width is contiguous from T OB, is a m inim um of 101 ft fromthe T OB and a m axim um of 200 ft from the T OB, and qualifies for 33% credit.
FIGURE
Drawn by:
Date:
Scale:
Project No.:
KRJ/CLF
OCT 2017
1:2400
16-017
Title:
Project:
Prepared for:
Alamance County, NC
ROCKY TOPBANK PARCEL
CLOSE-UP OFRESTORATIONBUFFER WIDTHTOB-29 FEET
4
Notes:
0 500 1,000250Feet
Legend
Conservation Easement = 5.16 ac
Restored Stream Channel = 0.18 ac
Riparian Buffer Restoration Area (TOB-29 ft ) = 0.003 ac (152.83 sq ft)
Riparian Buffer Restoration Area (TOB-100 ft) = 2.35 ac (102,356.48 sq ft)
Nutrient Offset Credit Area (101-200 ft) = 1.09 ac (47,626.47 sq ft)
Riparian Buffer Enhancement via Cattle Exclusion (TOB-29 ft) = 0.001 ac (54.43 sq ft)
Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) = 0.94 ac (40,784.55 sq ft)
Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) = 0.003 ac (113.87 sq ft)
Wetland Mitigation Credit Area = 0.54 ac
Constructed BMP Footprint (no credit) = 0.02 ac
³
1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council)
Inset Scale 1:600
NOTE: No riparian buffer credit is givenin areas with buffer width of less than20 ft. Additionally, no nutrient offsetcredit is given in areas with buffer widthless than 50 ft.
NOTE ABOUT BUFFER WIDTHS:TOB-20 ft = Buffer is less than 20 ft from the TOB and therefore qualifies forno credit.TOB-29 ft = Buffer width is contiguous from TOB, is a minimum of 20 ft fromthe 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 fromthe 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 fromthe TOB and a maximum of 200 ft from the TOB, and qualifies for 33% credit.
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Rocky Top Bank Parcel Year 2 (2019) Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC

Appendix C.
Vegetation Data

Table 5. Planted Woody Vegetation
Table 6. Total Planted Stems by Plot and Species
Vegetation Plot Photographs

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC
Table 5. Planted Bare Root Woody Vegetation
Species Quantity
River birch (Betula nigra) 200
Buttonbush (Cephalanthus occidentalis) 250
Eastern redbud (Cercis canadensis) 350
Silky dogwood (Cornus amomum) 575
Green ash (Fraxinus pennsylvanica) 350
Tulip poplar (Liriodendron tulipifera) 25
Sycamore (Platanus occidentalis) 550
Black gum (Nyssa sylvatica) 350
Water oak (Quercus nigra) 700
Willow oak (Quercus phellos) 650
Elderberry (Sambucus canadensis) 250
TOTAL 4250

Table 7: Pesticide Application Logs
Date: Herbicide\
Surfactant: Rate/Amount: Total: Target
Species: Method: Applicator:
3/13/19
Oust® XP
(sulfometuron
methyl)

Grounded®
3.52 dry oz

.5%
17.92 fl oz
28 Gallons Michrostegium Mist Blower
Joshua G
Merritt (NC
026-33717)
6/6/19
Roundup®
Custom
(glyphosate)

Agri-Dex®
3% 8 fl oz
8 fl oz

.5%
1.28 fl oz
2 Gallons Sweet Gum Foliage
Backpack
Joshua G
Merritt (NC
026-33717)
6/6/19
Roundup®
Custom
(glyphosate)

Agri-Dex®
.3%
.75 fl oz

.5%
1.28 fl oz
2 Gallons Microstegium Foliage
Backpack
Joshua G
Merritt (NC
026-33717)
Table 6. Planted Stems by Plot and Species
CVS Project Code 1500703. Project Name: Rocky Top
PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T
Betula nigra river birch Tree 1 1 1 1 1 1 2 2 2 6 6 6
Carpinus caroliniana American hornbeam Tree 1 1 1 1 1 1 1 1 1 4 4 4
Celtis occidentalis common hackberry Tree 1 1 1 1 1 1
Cercis canadensis eastern redbud Tree 1 1 1 1 1 1 2 2 2 2 2 2
Cornus amomum silky dogwood Shrub 1 1 1 1 1 1 4 4 4 6 6 6
Diospyros virginiana common persimmon Tree 1 3 4
Fraxinus pennsylvanica green ash Tree 2 2 2 2 2 2 4 4 4 5 5 5 5 5 5
Liquidambar styraciflua sweetgum Tree 2 5 7 7
Liriodendron tulipifera tuliptree Tree 2 2 2 1 1 1 3 3 3 3 3 3 4 4 4
Nyssa tupelo Tree 4 4 4 4 4 4 2 2 2 9 9 9
Platanus occidentalis American sycamore Tree 3 3 3 2 2 3 5 5 6 8 8 9 7 7 7
Quercus oak Tree 1 1 1 1 1 1 2 2 2 4 4 4
Quercus alba white oak Tree 3 3 3 3 3 3 1 1 1 1 1 1
Quercus nigra water oak Tree 1 1 1 2 2 2 3 3 3 8 8 8 13 13 13
Quercus pagoda cherrybark oak Tree 2 2 2 2 2 2 1 1 1 3 3 3
Quercus phellos willow oak Tree 1 1 1 4 4 4 5 5 5 6 6 6 14 14 14
Ulmus rubra slippery elm Tree 1 2 3
11 11 15 11 11 17 6 6 6 9 9 14 37 37 52 43 43 51 76 76 76
5 5 8 8 8 9 3 3 3 5 5 7 14 14 17 12 12 13 12 12 12
445.2 445.2 607 445.2 445.2 688 242.8 242.8 242.8 364.2 364.2 566.6 370 370 520 435 435 516 768.9 768.9 768.9
Color for Density
Exceeds requirements by 10%PnoLS = Planted excluding livestakes
Exceeds requirements, but by less than 10%P-all = Planted including livestakes
Fails to meet requirements, by less than 10%T = All planted and natural recruits including livestakes
Fails to meet requirements by more than 10%T includes natural recruits
Annual Means
MY2 (2019)
4
0.10 0.10
4
0.10
Species count
Stems per ACRE
1
0.02
1
0.02size (ACRES)0.02 0.02
MY1 (2018)MY0 (2017)
Stem count
size (ares)1 41
Current Plot Data (MY2 2019)
Scientific Name Common Name Species Type
1500703-01-0001 1500703-01-0002 1500703-01-0003 1500703-01-0004

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC
Rocky Top
Baseline Vegetation Monitoring Photographs
Taken October 2019

Plot 1
Plot 4 Plot 3
Plot 2

Rocky Top Bank Parcel Year 2 (2019) Monitoring Report Appendices
Phase One Haw River WS Umbrella Bank Restoration Systems, LLC

Appendix D.
Delivered Credit Yield Table for Jordan Sub Watersheds

Jordan Water Supply Nutrient Strategy
Delivered Credit Yield Table for Jordan Sub Watersheds
Updated
12/20/2012

Page 1 of 2

Attachment B

Delivered credit yields for buffer acres in Jordan small watersheds.
Watershed ID Jordan
Subwatershed
Delivery Factors TN Credit TP Credit
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

Jordan Water Supply Nutrient Strategy
Delivered Credit Yield Table for Jordan Sub Watersheds
Updated
12/20/2012

Page 2 of 2

Watershed ID Jordan
Subwatershed
Delivery Factors TN Credit TP Credit
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* LNH 88% 91% 2000.26 133.22
*Watershed is located in both the Upper New Hope (UNH) and Lower New Hope (LNH) Subwatersheds.