HomeMy WebLinkAbout20190675 Ver 1_SwampGrape_100115_MY2_2023_20240129FINAL
MY2 (2023) MONITORING REPORT
SWAMP GRAPE STREAM AND WETLAND MITIGATION SITE
Robeson County, North Carolina
Lumber River Basin
Cataloging Unit 03040204
DMS Project No. 100115
Full Delivery Contract No. 7869
DMS RFP No. 16-007705
USACE Action ID No. SAW-2019-00904
DWR Project No. 2019-0675
Data Collection: January - November 2023
Submission: January 2024
Prepared for:
NORTH CAROLINA DEPARTMENT OF ENVIRONMENTAL QUALITY
DIVISION OF MITIGATION SERVICES
1652 MAIL SERVICE CENTER
RALEIGH, NORTH CAROLINA 27699-1652
Restoration Systems, LLC
1101 Haynes St. Suite 211
Raleigh, North Carolina
Ph: (919) 755-9490
Fx: (919) 755-9492
1101 Haynes St., Suite 211 • Raleigh, NC 27604 • www.restorationsystems.com • Ph 919.755.9490 • Fx 919.755.9492
Response to Monitoring Year 2 (2023) DMS Comments
Swamp Grape Mitigation Site
Lumber River Basin – CU# 03040204 – Robeson County
DMS Project ID No. 100115, Contract # 7869
DMS Comments Received (Black Text) & RS Responses (Blue Text)
Report & Field Visit:
1. During site visit a newly created beaver dam was observed on UT-1, on the downstream stream
enhancement II reach, upstream of the conservation easement boundary. Overall, the site looked great.
The location of the beaver dam was added to the report, CCPV, and digital submittal.
Digital Deliverables:
1. Please note for all future submissions, all vegetation data presented in the report are required to be
submitted in digital format, for fixed and temporary/mobile plots.
Understood, Table 8 in the document and digital submittal has been updated to include temporary plots.
Swamp Grape Year 2, 2023 Monitoring Summary
General Notes
• A small area of encroachment was observed during year 2 (2023) along UT-2. Restoration Systems
replanted this area with 3-gallon upland containerized species from an approved Site Mitigation
plan during the 2023/2024 dormant season. RS also installed additional fence posts along this
boundary line with signage (Site Photo Log, Appendix A).
• Minimal evidence of nuisance animal activity (beaver) was observed. One beaver dam was
observed on UT-1 at the northern easement boundary. Beavers and the dam will be removed.
Streams
• All streams are functioning as designed. Upstream on UT2 has experienced some sediment
deposition in pools during year 2. Cross sections of this area were measured several times
throughout the year, and sediment appears to be moving its way through the reach.
• All engineered structures were stable and functioning within design parameters; no stream areas
of concern were documented.
• Four bankfull events were documented during MY2 (2023), making 7 total bankfull events during
the 2 monitoring years (Table 11, Appendix D).
Vegetation
• Measurements of the 23 vegetation plots resulted in an average of 458 planted stems/acre. All
individual plots met success criteria except plots 2, 19, and 23 (Tables 7-8, Appendix B). Plots 2, 19,
and 23 averaged 243, 243, and 283 stems per acre, respectively.
• Three random vegetation transects (50m x 5m) were conducted in year 2 (2023). None of the
transects met the success criteria of 320 stems per acre (Table 7B, Appendix B).
• Three random herbaceous vegetation plots (5-meter by 2-meter) were sampled in year 2 (2023).
All three plots met the success criteria of at least 3 different herbaceous species per plot (Table 7C,
Appendix B).
• Invasive vegetation treatments have been effective in reducing populations and currently areas of
invasive vegetation are below the mapping threshold. These areas will continue to be monitored
and treated as needed.
Wetlands
• Twelve of sixteen groundwater gauges met success criteria for the year 2 (2023) monitoring period.
Insufficient and inconsistent rainfall between mid-February and late-March likely caused
groundwater levels in the vicinity of gauges 1, 2, 3, and 6 to drop below 12 inches for a few short
periods during this time (Appendix D).
Site Maintenance Report (2023)
Invasive Species Work Maintenance work
05/22-23/2023: Cattail, Chinese Privet
06/26-27/2023: Chinaberry, Chinese Privet
10/11/2023: Cattail, Chinaberry, Chinese Privet
07/04/2023: Repaired Fence
09/19/2023: Beaver Dam Removal
12/12/2023: Easement Encroachment area (3-
gallon container planting, additional easement
marking)
FINAL
MY2 (2023) MONITORING REPORT
SWAMP GRAPE STREAM AND WETLAND MITIGATION SITE
Robeson County, North Carolina
Lumber River Basin
Cataloging Unit 03040204
DMS Project No. 100115
Full Delivery Contract No. 7869
DMS RFP No. 16-007705
USACE Action ID No. SAW-2019-00904
DWR Project No. 2019-0675
Data Collection: January - October 2023
Submission: January 2024
Prepared for:
NORTH CAROLINA DEPARTMENT OF ENVIRONMENTAL QUALITY
DIVISION OF MITIGATION SERVICES
1652 MAIL SERVICE CENTER
RALEIGH, NORTH CAROLINA 27699-1652
Prepared by:
And
Restoration Systems, LLC Axiom Environmental, Inc.
1101 Haynes Street, Suite 211 218 Snow Avenue
Raleigh, North Carolina 27604 Raleigh, North Carolina 27603
Contact: Worth Creech Contact: Grant Lewis
919-755-9490 (phone) 919-215-1693 (phone)
919-755-9492 (fax)
MY2 Monitoring Report (Project No. 100115) Table of Contents
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
TABLE OF CONTENTS
1.0 PROJECT SUMMARY .............................................................................................................................. 1
1.1 Project Background, Components, and Structure ........................................................................ 1
1.2 Success Criteria ............................................................................................................................. 4
2.0 METHODS .............................................................................................................................................. 4
2.1 Monitoring .................................................................................................................................... 4
3.0 REFERENCES ............................................................................................................................................ 9
APPENDICES
Appendix A. Visual Assessment Data
Figure 1. Current Conditions Plan View
Table 4A-D. Visual Stream Morphology Stability Assessment Table
Table 5. Vegetation Condition Assessment Table
Vegetation Plot Photographs
Site Photo Log
Appendix B. Vegetation Plot Data
Table 6. Planted Bare-Root Woody Vegetation
Table 7A. Vegetation Plot Counts and Densities
Table 7B. Temporary Vegetation Plots Data
Table 7C. Herbaceous Vegetation Plots
Table 8. Vegetation Plot Data Table from Vegetation Data Entry Tool
Appendix C. Stream Geomorphology Data
Cross-Sections with Annual Overlays
Table 9A-D. Baseline Stream Data Summary Tables
Table 10A-C. Cross-Section Morphology Monitoring Summary
Appendix D. Hydrologic Data
Table 11. Verification of Bankfull Events
Stream Crest Gauge Graphs
Table 12. Groundwater Hydrology Data
Groundwater Gauge Graphs
Figure D1. 30/70 Percentile Graph for Rainfall
Soil Temperature Graph
Appendix E. Project Timeline and Contact Info
Table 13. Project Timeline
Table 14. Project Contacts
Appendix F. Project Notes
Aggradation Memo to DMS June 7, 2023
IRT Site Visit Notes July 14, 2023
MY2 Monitoring Report (Project No. 100115) Page 1
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
1.0 PROJECT SUMMARY
Restoration Systems, LLC (RS) has established the North Carolina Division of Mitigation Services (NCDMS)
Swamp Grape Stream and Wetland Mitigation Site (Site). The Site is on two contiguous parcels used
primarily for row crop production with small pockets of livestock pasture in the Atlantic Southern Loam
Plains portion of the Southeastern Plains ecoregion of North Carolina. Located in the Lumber River Basin,
Cataloging Unit 03040204, the Site is in the Targeted Local Watershed (TLW) 03040204048010 and North
Carolina Division of Water Resources [NCDWR] subbasin number 03-07-55. The Site is not located in a
Local Watershed Plan (LWP), Regional Watershed Plan (RWP), or Targeted Resource Area (TRA). Site
watersheds range from approximately 0.41 of a square mile (263 acres) on UT2 to 1.53 square miles (977
acres) at the Site’s outfall.
1.1 Project Background, Components, and Structure
Located approximately 4 miles northwest of Rowland and 2.5 miles southwest of Alfordsville along the
southwest edge of Robeson County, the Site encompasses 24.68 acres. Mitigation work within the Site
included 1) stream restoration, 2) stream enhancement (Level I), 3) stream enhancement (Level II), 4)
wetland reestablishment, 5) wetland rehabilitation, 6) wetland enhancement, 7) wetland creation, and 7)
vegetation planting. The Site is expected to provide 3,228.333 warm water stream credits and 12.705
riparian wetland credits by closeout (Table 1, Page 2). A conservation easement was granted to the State
of North Carolina and recorded at the Robeson County Register of Deeds on February 23, 2021.
Before construction, land use at the Site was characterized by breached agriculture ponds, failed/eroded
agricultural crossings, row crops, livestock pasture, and disturbed forest. Site design was completed in
June 2021; construction started on July 12, 2021, and ended with a final walkthrough on September 23,
2021. The Site was planted on January 18, 2022. Completed project activities, reporting history,
completion dates, and project contacts are summarized in Tables 13-14 (Appendix E).
Space Purposefully Left Blank
Original
Mitigation Original Original Original
Plan As-Built Mitigation Restoration Mitigation
Project Segment Ft/Ac Ft/Ac Category Level Ratio (X:1)Credits Comments
Stream
UT 1 Reach 1 297 296 Warm EI 2.00000 148.500
UT 1 Reach 2 1215 1211 Warm R 1.00000 1,215.000
UT 1 Reach 3 546 544 Warm EI 2.00000 273.000
UT 1 Reach 4 235 235 Warm EII 3.00000 78.333
UT 1 Reach 5 230 230 Warm R 1.00000 230.000
UT 1 Reach 6 165 166 Warm EI 2.00000 82.500
UT 1 Reach 7 206 207 Warm R 1.00000 206.000
UT 1 Reach 8 87 88 Warm EI 2.00000 43.500
UT 2 Reach 1 684 681 Warm R 1.00000 684.000
UT 2 Reach 2 266 265 Warm EI 2.00000 133.000
UT 3 Reach 1 133 132 Warm EI 2.00000 66.500
UT 3 Reach 2 68 66 Warm R 1.00000 68.000
Total:3,228.333
Wetland
Wetland Reestablish 4.470 4.47 R REE 1.00000 4.470
Wetland Rehabilitation 2.671 2.671 R RH 1.50000 1.781
Wetland Enhancement 12.244 12.244 R E 2.00000 6.122
Wetland Creation 0.997 0.997 R C 3:100 0.332
Total:12.705
Project Credits
Riparian Non-Rip Coastal
Warm Cool Cold Wetland Wetland Marsh
Restoration 2,403.000
Re-establishment 4.470
Rehabilitation 1.781
Enhancement 6.122
Enhancement I 747.000
Enhancement II 78.333
Creation 0.332
Preservation 0.000
Totals 3,228.333 12.705
Total Stream Credit 3,228.333
Total Wetland Credit 12.705
Wetland Mitigation Category Restoration Level
CM Coastal Marsh HQP High Quality Preservation
R Riparian P Preservation
NR Non-Riparian E Wetland Enhancement - Veg and Hydro
EII Stream Enhancement II
EI Stream Enhancement I
C Wetland Creation
RH Wetland Rehabilitation - Veg and Hydro
REE Wetland Re-establishment Veg and Hydro
R Restoration
Table 1. Swamp Grape Mitigation Site (ID-100115) Project Mitigation Quantities and Credits
Restoration Level
Stream
MY2 Monitoring Report (Project No. 100115) Page 3
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
Table 2. Summary: Goals, Performance, and Results
Goals Objectives Success Criteria
(1) HYDROLOGY
• Minimize
downstream
flooding to the
maximum extent
possible.
• Connect streams to
functioning wetland
systems.
• Construct new channel at historic floodplain
elevation to restore overbank flows and restore
jurisdictional wetlands
• Plant woody riparian buffer
• Remove livestock
• Remove a ditch/drain tile network that
contributes surface waters directly to the channel
• Protect riparian buffers with a perpetual
conservation easement
• BHR not to exceed 1.2
• Document four overbank events in
separate monitoring years
• Livestock excluded from the easement
• Attain Wetland Hydrology Success Criteria
• Attain Vegetation Success Criteria
• Conservation Easement recorded
• Increase stream
stability within the
Site so that channels
are neither
aggrading nor
degrading.
• Construct channels with the proper pattern,
dimension, and longitudinal profile
• Remove livestock from the Site
• Construct stable channels that do not contribute
sediment to downstream receiving waters.
• Plant woody riparian buffer
• Cross-section measurements indicate a
stable channel with appropriate substrate
• Visual documentation of stable channels
and structures
• BHR not to exceed 1.2
• < 10% change in BHR in any given year
• Livestock excluded from the easement
• Attain Vegetation Success Criteria
(1) WATER QUALITY
• Remove direct
nutrient and
pollutant inputs
from the Site and
reduce
contributions to
downstream waters.
• Remove livestock and reduce agricultural
land/inputs
• Plant woody riparian buffer
• Restore/enhance jurisdictional wetlands adjacent
to Site streams
• Remove a ditch/drain tile network that
contributes surface waters directly to the channel
• Restore overbank flooding by constructing
channels at historic floodplain elevation.
• Livestock excluded from the easement
• Attain Wetland Hydrology Success Criteria
• Attain Vegetation Success Criteria
(1) HABITAT
• Improve instream
and stream-side
habitat.
• Construct stable channels with woody debris
available as instream habitat
• Plant woody riparian buffer to provide organic
matter and shade
• Construct new channel at historic floodplain
elevation to restore overbank flows
• Protect riparian buffers with a perpetual
conservation easement
• Restore/enhance jurisdictional wetlands adjacent
to Site streams
• Stabilize stream banks
• Install in-stream structures
• Cross-section measurement indicates a
stable channel with appropriate substrate
• Visual documentation of stable channels
and in-stream structures.
• Attain Wetland Hydrology Success Criteria
• Attain Vegetation Success Criteria
• Conservation Easement recorded
MY2 Monitoring Report (Project No. 100115) Page 4
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
1.2 Success Criteria
Monitoring and success criteria for stream restoration should relate to project goals and objectives
identified from onsite NC SAM and NC WAM data collection. From a mitigation perspective, several
goals and objectives are assumed to be functionally elevated by restoration activities without direct
measurement. Other goals and objectives will be considered successful upon achieving success criteria.
The following summarizes Site success criteria.
Project Success Criteria
Streams
• All streams must maintain an Ordinary High-Water Mark (OHWM), per RGL 05-05.
• Bank height ratio (BHR) cannot exceed 1.2 at any measured cross-section.
• BHR at any measured riffle cross-section should not change by more than 10% from baseline condition during
any given monitoring period.
• The stream project shall remain stable, and all other performance standards shall be met through four
separate bankfull events, occurring in separate years, during the monitoring years 1-7.
Wetland Hydrology
• Saturation or inundation within the upper 12 inches of the soil surface for, at a minimum, 12 percent of the
growing season, during average climatic conditions.
Vegetation
• Within planted portions of the Site, a minimum of 320 stems per acre must be present at year 3; a minimum
of 260 stems per acre must be present at year 5, and a minimum of 210 stems per acre must be present at
year 7.
• Trees must average 7 feet in height at year 5 and 10 feet at year 7 in each plot.
• Planted and volunteer stems are counted, provided they are included in the approved planting list for the
Site; natural recruits not on the planting list may be considered by the IRT on a case-by-case basis.
• Herbaceous vegetation plots must have a minimum of three species present.
2.0 METHODS
Monitoring will be conducted by Axiom Environmental, Inc. Annual monitoring reports of the data
collected will be submitted to the NCDMS by Restoration Systems no later than December 31 of each
monitoring year data is collected. The monitoring schedule is summarized in the following table.
Monitoring Schedule
Resource Year 1 Year 2 Year 3 Year 4 Year 5 Year 6 Year 7
Streams X X X X X
Wetlands X X X X X X X
Vegetation X X X X X
Visual Assessment X X X X X X X
Report Submittal X X X X X X X
2.1 Monitoring
The monitoring parameters are summarized in the following table.
MY2 Monitoring Report (Project No. 100115) Page 5
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
Monitoring Summary
Stream Parameters
Parameter Method Schedule/Frequency Number/Extent Data Collected/Reported
Stream Profile Full longitudinal survey As-built (unless
otherwise required)
All restored stream
channels Graphic and tabular data.
Stream
Dimension Cross-sections Years 1, 2, 3, 5, and 7
Total of 16 cross-
sections on restored
channels
Graphic and tabular data.
Channel
Stability
Visual Assessments Yearly All restored stream
channels
Areas of concern will be depicted on
a plan view figure with a written
assessment and photograph of the
area included in the report.
Additional Cross-sections Yearly
Only if instability is
documented during
monitoring
Graphic and tabular data.
Stream
Hydrology NA NA NA NA
Bankfull Events
Continuous monitoring
surface water gauges
(pressure transducers)
and/or trail camera
Continuous recording
through monitoring
period
3 surface water gauges
on UT 1 and UT 2
Surface water data for each
monitoring period
Visual/Physical Evidence Continuous through
monitoring period N.A. Visual evidence, photo
documentation, and/or rain data.
Wetland Parameters
Parameter Method Schedule/Frequency Number/Extent Data Collected/Reported
Wetland
Restoration Groundwater gauges
As-built, Years 1, 2, 3, 4,
5, 6, and 7 throughout
the year with the
growing season defined
as March 1-November 6
16 gauges spread
throughout restored
wetlands
Soil temperature at the beginning of
each monitoring period to verify the
start of the growing season,
groundwater and rain data for each
monitoring period. Graphic and
tabular data.
Vegetation Parameters
Parameter Method Schedule/Frequency Number/Extent Data Collected/Reported
Vegetation
establishment
and vigor
Permanent vegetation plots
0.0247 acre (100 square
meters) in size; CVS-EEP
Protocol for Recording
Vegetation, Version 4.2 (Lee
et al. 2008)
As-built, Years 1, 2, 3, 5,
and 7
23 plots spread across
the Site (2 plots in
cypress gum swamp
and 21 plots in C.P.
small stream swamp)
Species, height, planted vs.
volunteer, stems/acre, areas of
concern
Annual random vegetation
plots, 0.0247 acre (100
square meters) in size
As-built, Years 1, 2, 3, 5,
and 7
As needed to
determine vegetation
density in a
questionable area
Species and height
Annual random herbaceous
vegetation plots, 0.00247
acre (5 meters by 2 meters)
in size
Years 1, 2, 3, 5, and 7
3 plots located in
herbaceous dominated
vegetation areas
Number of species in plot
Note: All vegetation plots and stream cross sections have fixed photo point locations. In addition, fixed photo
points will be installed at two culverts entering the Site.
Note: Vegetation data should be collected between July 1 and leaf drop. In addition, vegetation data will not be
collected until 180 days after Site planting.
MY2 Monitoring Report (Project No. 100115) Page 6
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
Stream Summary
All streams are functioning as designed. Upstream on UT2 has experienced some sediment deposition in
pools during year 2. Cross sections of this area were measured several times throughout the year, and
sediment appears to be moving its way through the reach. However, the reach will be closely monitored
during subsequent years.
Wetland Summary
Summary of Monitoring Period/Hydrology Success Criteria by Year
Year Soil Temperatures/Date Bud
Burst Documented
Monitoring Period Used for
Determining Success
12 Percent of the
Monitoring Period
2022 (Year 1) March 1, 2022 March 1-November 6
(251 days) 30 days
2023 (Year 2) March 1, 2023* March 1-November 6
(251 days) 30 days
*Based on bud burst and a soil temperature of 58.1°F documented on March 1. Soil temperature did not fall below
49.44°F after March 1.
Twelve of sixteen groundwater gauges met success criteria for the year 2 (2023) monitoring period.
Insufficient and inconsistent rainfall between mid-February and late-March likely caused groundwater
levels in the vicinity of gauges 1, 2, 3, and 6 to drop below 12 inches for a few short periods during this
time (Figure D1 and Groundwater Gauge Graphs, Appendix D). It is expected that with normal to above-
average rainfall during this time, all gauges would have met the 12% hydroperiod.
Vegetation Summary
During quantitative vegetation sampling, 23 sample plots (10-meter by 10-meter) were installed within
the Site as per guidelines established in CVS-EEP Protocol for Recording Vegetation, Version 4.2 (Lee et al.
2008). Year 2 (2023) vegetation measurements occurred on September 14, 2023. Measurements of all 23
plots resulted in an average of 458 stems/acre, excluding livestakes. Additionally, 20 of the 23 individual
plots met the year 3 stem density requirement (Tables 7-8, Appendix B).
Table 8 (Appendix B) indicates that plots 2, 3, 6, 7, 9, 10, 11, 15, 20, and 21 each exceeded 50% dominant
species composition during year 2, and plots 2, 6, 10, 15, 16, 20, 21, and 22 each had less than 4 different
species counted during year 2. Although these criteria are not explicitly tied to vegetation success, they
will be monitored closely during subsequent monitoring years. It is expected that vegetation within these
areas will continue to diversify as natural recruitment increases throughout the monitoring period.
Three temporary plots were counted, resulting in an average of 243 average stems per acre across the 3
plots. Additionally, none of the temporary plots met year 3 stem density requirement. These areas will be
further assessed to determine if a replanting effort is needed (Table 7B, Appendix B).
Three random herbaceous vegetation plots (5-meter by 2-meter) were also sampled in year 2 (2023). All
3 plots met the success criteria of at least 3 different herbaceous species per plot (Table 7C, Appendix B).
One small area of easement encroachment was observed during year 2 (2023) along UT-2. RS replanted
this area with 3-gallon upland containerized species from the approved Site Mitigation plan during the
2023/2024 dormant season. Additional fence post corners were installed along this boundary line with
signage (Site Photo Log, Appendix A).
MY2 Monitoring Report (Project No. 100115) Page 7
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
Table 3. Project Attribute Table
Swamp Grape Mitigation Site
Project Information
Project Name Swamp Grape Mitigation Site
Project County Robeson County, North Carolina
Project Area (acres) 24.7
Project Coordinates (latitude & latitude) 34.5639, -79.3490
Planted Area (acres) 22.5
Project Watershed Summary Information
Physiographic Province Atlantic Southern Loam Plains
Project River Basin Lumber
USGS HUC for Project (14-digit) 03040204048010
NCDWR Sub-basin for Project 03-07-55
Project Drainage Area (acres) 977.0
Percentage of Project Drainage Area that is
Impervious <2%
CGIA Land Use Classification Managed Herbaceous Cover & Hardwood Swamps
Reach Summary Information
Parameters UT 1 Upstream UT 1 Downstream UT 2 UT 3
Length of reach (linear feet) 1293 1673 826 149
Valley Classification &
Confinement Wide and flat alluvial valley
Drainage Area (acres) 192 977 263 392
NCDWR Stream ID Score -- -- -- --
Perennial, Intermittent,
Ephemeral Perennial Perennial Perennial Perennial
NCDWR Water Quality
Classification C, Sw
Existing Morphological
Description (Rosgen 1996) F 5 Eg 5 Cg 5 Eg 5
Proposed Stream
Classification (Rosgen 1996) Ce 5 Ce 5 Ce 5 Ce 5
Existing Evolutionary Stage
(Simon and Hupp 1986) III/IV V V III/IV
Underlying Mapped Soils Bibb Soils
Drainage Class Poorly drained
Hydric Soil Status Hydric
Valley Slope 0.0062 0.0036 0.0042 0.0125
FEMA Classification NA Zone AE NA NA
Native Vegetation Community Cypress-Gum Swamp (Brownwater Subtype) and Coastal Plain Small Stream
Swamp (Brownwater Subtype)
Watershed Land Use/Land
Cover (Site)
15% agriculture land, 84% disturbed swamp forest, <1% low density
residential/impervious surface
Watershed Land Use/Land
Cover (McRae and Jordan Cr
Reference Channel)
McRae - 40% agriculture, 35% forest, 5% low density residential/impervious
surface
Jordan Cr - 70% agriculture, 28% forest, 2% low density residential/impervious
surface
Percent Composition of Exotic
Invasive Vegetation <5%
MY2 Monitoring Report (Project No. 100115) Page 8
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
Table 3. Project Attribute Table (continued)
Swamp Grape Mitigation Site
Wetland Summary Information
Parameters Wetlands
Wetland acreage 5.32 acre drained/impacted & 15.07 acre degraded
Wetland Type Riparian riverine
Mapped Soil Series Bibb
Drainage Class Poorly drained
Hydric Soil Status Hydric
Source of Hydrology Groundwater, stream overbank
Hydrologic Impairment Impoundment, incised streams, compacted soils, livestock,
ditches
Native Vegetation Community Cypress-Gum Swamp (Brownwater Subtype) and Coastal Plain
Small Stream Swamp (Brownwater Subtype)
% Composition of Exotic Invasive Vegetation <5%
Restoration Method Hydrologic, vegetative, livestock
Enhancement Method Vegetative, livestock
Regulatory Considerations
Regulation Applicable? Resolved? Supporting Documentation
Waters of the United States-Section 401 Yes Yes Section 401 Certification
Waters of the United States-Section 404 Yes Yes Section 404 Permit
Endangered Species Act Yes Yes CE Document (Mitigation Plan, App E)
Historic Preservation Act Yes Yes CE Document (Mitigation Plan, App E)
Coastal Zone Management Act No -- NA
FEMA Floodplain Compliance Yes Yes DMS FEMA Checklist (Mitigation Plan,
App F)
Essential Fisheries Habitat No -- NA
Space Purposefully Left Blank
MY2 Monitoring Report (Project No. 100115) Page 9
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
3.0 REFERENCES
Lee, M.T., R.K. Peet, S.D. Roberts, and T.R. Wentworth. 2008. CVS-EEP Protocol for Recording
Vegetation. Version 4.2. North Carolina Department of Environment and Natural Resources,
Ecosystem Enhancement Program. Raleigh, North Carolina.
North Carolina Ecosystem Enhancement Program (NCEEP). 2008. Lumber River Basin Restoration
Priorities (online). Available:
https://files.nc.gov/ncdeq/Mitigation%20Services/Watershed_Planning/Lumber_River_Basin/Lu
mber_RBRP_2008_FINAL.pdf (January 9, 2018)
North Carolina Stream Functional Assessment Team. (NC SFAT 2015). N.C. Stream Assessment Method
(NC SAM) User Manual. Version 2.1.
North Carolina Wetland Functional Assessment Team. (NC WFAT 2010). N.C. Wetland Assessment
Method (NC WAM) User Manual. Version 4.1.
Rosgen, D. 1996. Applied River Morphology. Wildland Hydrology (Publisher). Pagosa Springs, Colorado
Simon A, Hupp CR. 1986. Geomorphic and Vegetative Recovery Processes Along Modified Tennessee
Streams: An Interdisciplinary Approach to Disturbed Fluvial Systems. Forest Hydrology and
Watershed Management. IAHS-AISH Publ.167.
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
Appendix A
Visual Assessment Data
Figure 1. Current Conditions Plan View
Tables 4A-D. Stream Visual Stability Assessment
Table 5. Visual Vegetation Assessment
Vegetation Plot Photographs
Site Photo Log
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NCCGIA, NC 911 Board
FIGURE
Drawn by:
Date:
Scale:
Project No.:
KRJ
JAN 2024
1:2700
20-003
Title:
Project:
Prepared for:
Robeson County, NC
SWAMP GRAPEMITIGATION SITE
CURRENTCONDITIONSPLAN VIEW
1
³
0 500 1,000250Feet
Legend
Conservation Easement = 24.7 acres
Parcel Boundaries
Stream Restoration
Stream Enhancement (Level I)
Stream Enhancement (Level II)
Stream Generating No Credit
Wetland Restablishment
Wetland Rehabilitation
Wetland Enhancement
Wetland Creation
Vegetation Plots Meeting MY3 Stem Density Requirement
Vegetation Plots Not Meeting MY3 Stem Density Requirement
^_Vegetation Plot Origins
MY2 (2023) Temporary Vegetation Plots Not Meeting MY3 Stem Density Requirement
")MY2 (2023) Herbaceous Plot Locations (5m x 2m)
Cross Sections
Groundwater Gauges Meeting Success Criteria
Groundwater Gauges Not Meeting Success Criteria
")Rain Gauge/Soil Probe
#*Stream Crest Gauges
2023 Encroachment Area (~0.20 acres)
Beaver Dam (Observed January 2024)
UT-2
UT-3
UT-1
UT-1
XS 1
XS 2
XS4XS3
X S 5
X
S
6
X S 7
X S 8
X
S
9
XS10
X S 1 1
XS12
XS13
XS14
KitchenSt
Note: Basemap is drone imagery from October 2021
on top of 2021 aerial orthoimagery from NC OneMap
X S 1 5
X S 1 6
Table 4A. Visual Stream Stability Assessment
Reach UT 1 Upstream
Assessed Stream Length 1849
Assessed Bank Length 3698
Bank Surface Scour/Bare
Bank
Bank lacking vegetative cover resulting simply from poor growth
and/or surface scour 0 100%
Toe Erosion
Bank toe eroding to the extent that bank failure appears likely.
Does NOT include undercuts that are modest, appear sustainable
and are providing habitat.
0 100%
Bank Failure Fluvial and geotechnical - rotational, slumping, calving, or collapse 0 100%
0 100%
Structure Grade Control Grade control structures exhibiting maintenance of grade across
the sill. 28 28 100%
Bank Protection
Bank erosion within the structures extent of influence does not
exceed 15%. (See guidance for this table in DMS monitoring
guidance document)
28 28 100%
Major Channel Category Metric
Number
Stable,
Performing as
Intended
Total Number
in As-built
Amount of
Unstable
Footage
Survey Date: November 20, 2023
% Stable,
Performing as
Intended
Totals
Table 4B. Visual Stream Stability Assessment
Reach UT 1 Downstream
Assessed Stream Length 1157
Assessed Bank Length 2314
Bank Surface Scour/Bare
Bank
Bank lacking vegetative cover resulting simply from poor growth
and/or surface scour 0 100%
Toe Erosion
Bank toe eroding to the extent that bank failure appears likely.
Does NOT include undercuts that are modest, appear sustainable
and are providing habitat.
0 100%
Bank Failure Fluvial and geotechnical - rotational, slumping, calving, or collapse 0 100%
0 100%
Structure Grade Control Grade control structures exhibiting maintenance of grade across
the sill. 5 5 100%
Bank Protection
Bank erosion within the structures extent of influence does not
exceed 15%. (See guidance for this table in DMS monitoring
guidance document)
5 5 100%
Totals
Survey Date: November 20, 2023
Major Channel Category Metric
Number
Stable,
Performing as
Intended
Total Number
in As-built
Amount of
Unstable
Footage
% Stable,
Performing as
Intended
Table 4C. Visual Stream Stability Assessment
Reach UT 2
Assessed Stream Length 1070
Assessed Bank Length 2140
Bank Surface Scour/Bare
Bank
Bank lacking vegetative cover resulting simply from poor growth
and/or surface scour 0 100%
Toe Erosion
Bank toe eroding to the extent that bank failure appears likely.
Does NOT include undercuts that are modest, appear sustainable
and are providing habitat.
0 100%
Bank Failure Fluvial and geotechnical - rotational, slumping, calving, or collapse 0 100%
0 100%
Structure Grade Control Grade control structures exhibiting maintenance of grade across
the sill. 6 6 100%
Bank Protection
Bank erosion within the structures extent of influence does not
exceed 15%. (See guidance for this table in DMS monitoring
guidance document)
6 6 100%
% Stable,
Performing as
Intended
Totals
Major Channel Category Metric
Number
Stable,
Performing as
Intended
Total Number
in As-built
Amount of
Unstable
Footage
Survey Date: November 20, 2023
Table 4D. Visual Stream Stability Assessment
Reach UT 3
Assessed Stream Length 199
Assessed Bank Length 398
Bank Surface Scour/Bare
Bank
Bank lacking vegetative cover resulting simply from poor growth
and/or surface scour 0 100%
Toe Erosion
Bank toe eroding to the extent that bank failure appears likely.
Does NOT include undercuts that are modest, appear sustainable
and are providing habitat.
0 100%
Bank Failure Fluvial and geotechnical - rotational, slumping, calving, or collapse 0 100%
0 100%
Structure Grade Control Grade control structures exhibiting maintenance of grade across
the sill. 3 3 100%
Bank Protection
Bank erosion within the structures extent of influence does not
exceed 15%. (See guidance for this table in DMS monitoring
guidance document)
3 3 100%
% Stable,
Performing as
Intended
Totals
Major Channel Category Metric
Number
Stable,
Performing as
Intended
Total Number
in As-built
Amount of
Unstable
Footage
Survey Date: November 20, 2023
Table 5. Visual Vegetation Assessment
Planted acreage 22.5
Bare Areas Very limited cover of both woody and herbaceous material.0.10 acres 0.00 0.0%
Low Stem Density Areas Woody stem densities clearly below target levels based on current MY stem count criteria.0.10acres 0.00 0.0%
0.00 0.0%
Areas of Poor Growth Rates Planted areas where average height is not meeting current MY Performance Standard.0.10 acres 0.00 0.0%
0.00 0.0%
Easement Acreage 24.7
Invasive Areas of Concern
Invasives may occur outside of planted areas and within the easement and will therefore be calculated
against the total easement acreage. Include species with the potential to directly outcompete native,
young, woody stems in the short-term or community structure for existing communities. Species
included in summation above should be identified in report summary.
0.10 acres 0.00 0.0%
Easement Encroachment Areas
Encroachment may be point,line,or polygon.Encroachment to be mapped consists of any violation of
restrictions specified in the conservation easement.Common encroachments are mowing,cattle access,
vehicular access.Encroachment has no threshold value as will need to be addressed regardless of impact
area.
none
Survey Date: November 20, 2023
% of Planted
Acreage
0.20 acres of
enchroachment near the
right bank of UT2 and left
bank of UT1
Cumulative Total
Vegetation Category Definitions
Mapping
Threshold
Combined
Acreage
% of Easement
Acreage
Total
Vegetation Category Definitions
Mapping
Threshold
Combined
Acreage
Swamp Grape Site
MY2 (2023) Vegetation Monitoring Photographs
Swamp Grape Site Appendix A: Visual Assessment Data
MY2 Monitoring Report – December 2023
Plot 7
Plot 1 Plot 2
Plot 3 Plot 4
Plot 5 Plot 6
Plot 8
Swamp Grape Site
MY2 (2023) Vegetation Monitoring Photographs
Swamp Grape Site Appendix A: Visual Assessment Data
MY2 Monitoring Report – December 2023
Plot 15
Plot 9 Plot 10
Plot 11 Plot 12
Plot 13 Plot 14
Plot 16
Swamp Grape Site
MY2 (2023) Vegetation Monitoring Photographs
Swamp Grape Site Appendix A: Visual Assessment Data
MY2 Monitoring Report – December 2023
Plot 23
Plot 17 Plot 18
Plot 19 Plot 20
Plot 21 Plot 22
Temporary Plot 1
Swamp Grape Site
MY2 (2023) Vegetation Monitoring Photographs
Swamp Grape Site Appendix A: Visual Assessment Data
MY2 Monitoring Report – December 2023
Temporary Plot 2 Temporary Plot 3
Herb Plot 1 Herb Plot 2
Herb Plot 3
Swamp Grape
MY-02 (2023) Photo Log
Photo 1: UT1
Photo 2: Wetland development at groundwater
gauge 15
MY2 (2023) Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream & Wetland Mitigation Site Restoration Systems, LLC
Photo 3: Culvert on UT 1 upstream of easement boundary
Photo 4: UT 2 Upstream
Swamp Grape
MY-02 (2023) Photo Log
MY2 (2023) Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream & Wetland Mitigation Site Restoration Systems, LLC
Photo 5: Crossing on UT 2 (upstream from easement boundary)
downstream end, facing upstream
Photo 6: Crossing on UT 2 (upstream from easement boundary)
Upstream end, facing downstream
Swamp Grape
MY-02 (2023) Photo Log
MY2 (2023) Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream & Wetland Mitigation Site Restoration Systems, LLC
Photo 7: UT 1 Channel
Photo 8: Stream flow on UT 1
Swamp Grape
MY-02 (2023) Photo Log
MY2 (2023) Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream & Wetland Mitigation Site Restoration Systems, LLC
Photo 9: Herbaceous wetland vegetation
Photo 10: Wetland Vegetation
Swamp Grape
MY-02 (2023) Photo Log
MY2 (2023) Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream & Wetland Mitigation Site Restoration Systems, LLC
Photo 11: Bud burst of Celtis occidentalis
Photo taken 2/28/23
MY2 (2023) Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream & Wetland Mitigation Site Restoration Systems, LLC
Photo 12: Bud burst of Quercus sp.
Photo taken 2/28/2023
Swamp Grape
MY-02 (2023) Photo Log
Photo 13: Emergent wetland vegetation and bud burst of Salix nigra
Photo taken 2/28/23
Swamp Grape
MY-02 (2023) Photo Log
MY2 (2023) Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream & Wetland Mitigation Site Restoration Systems, LLC
Photo 14: Easement marking and supplemental planting
Photo taken 12/12/23
Photo 15: Easement marking and supplemental planting
Photo taken 12/12/23
Swamp Grape
MY-02 (2023) Photo Log
MY2 (2023) Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream & Wetland Mitigation Site Restoration Systems, LLC
Photo 16: Easement marking and supplemental planting
Photo taken 12/12/23
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
Appendix B
Vegetation Data
Table 6. Planted Bare-Root Woody Vegetation
Table 7A. Vegetation Plot Counts and Densities
Table 7B. Temporary Vegetation Plots Data
Table 7C. Herbaceous Vegetation Plots
Table 8. Vegetation Plot Data Table from Vegetation Data Entry Tool
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
Table 6. Planted Bare Root Woody Vegetation
Swamp Grape Stream and Wetland Mitigation Site
Species Total
Acres 22.5
Alnus serrulata 750
Betula nigra 1,000
Carya aquatica 800
Carya ovata 800
Cephalanthus occidentalis 800
Nyssa aquatica 500
Nyssa sylvatica 700
Quercus nigra 2,200
Quercus phellos 2,200
Quercus shumardii 2,000
Taxodium ascendens 1,000
Taxodium distichum 3,000
Ulmus americana 2,000
TOTALS 17,750
Average Stems/Acre 789
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
Table 7A. Planted Vegetation Totals
Swamp Grape Stream and Wetland Mitigation Site
Plot # Planted Stems/Acre Success Criteria Met?
1 648 Yes
2 243 No
3 486 Yes
4 526 Yes
5 567 Yes
6 445 Yes
7 445 Yes
8 486 Yes
9 364 Yes
10 405 Yes
11 526 Yes
12 648 Yes
13 648 Yes
14 526 Yes
15 607 Yes
16 324 Yes
17 445 Yes
18 486 Yes
19 243 No
20 364 Yes
21 445 Yes
22 364 Yes
23 283 No
Average Planted Stems/Acre 458 Yes
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina January 2024
Table 7B. Temporary Vegetation Plots
Swamp Grape Stream and Wetland Mitigation Site
Species
50m x 2m Temporary Plots
T-1 T-2 T-3
Cephalanthus occidentalis 1 0 1
Liriodendron tulipifera 6 4 3
Quercus nigra 0 0 1
Salix nigra 0 2 0
Total Stems 7 6 5
Total Stems/Acre 283 243 202
Average Stems/Acre: 243
Table 7C. Herbaceous Vegetation Plots
Swamp Grape Stream and Wetland Mitigation Site
Plot # Species Count Success Criteria
Met? Taxa Identified
H1 6 Yes
Carex sp.
Cladium mariscus
Eclipta prostrata
Galium tinctorium
Penthorum sedoides
Juncus effusus
H2 5 Yes
Carex sp.
Eupatorium capillifolium
Juncus effusus
Rubus sp.
Scirpus cyperinus
H3 4 Yes
Juncus effusus
Ludwigia alternifolia
Scirpus cyperinus
Carex sp.
Average 5 Yes
Table 8. Vegetation Plot Data Table from Vegetation Data Entry Tool
22.5
2022‐01‐18
NA
NA
2023‐09‐14
0.0247
Planted Total Planted Total Planted Total Planted Total Planted Total Planted Total Planted Total Planted Total
Alnus serrulata hazel alder Tree OBL 4 4 11 1122
Betula nigra river birch Tree FACW 11
Carya sp.
Cephalanthus occidentalis common buttonbush Shrub OBL 4 4 1122
Liriodendron tulipifera tuliptree Tree FACU
Nyssa sp.22
Nyssa sylvatica blackgum Tree FAC 1 1
Quercus nigra water oak Tree FAC 3 3 3322 44
Quercus phellos willow oak Tree FAC 2 2 6611 2222
Quercus shumardii Shumard's oak Tree FAC 11111122
Quercus sp.114422 22662244
Salix nigra black willow Tree OBL
Salix sp.
Taxodium sp.1177 33 66
Ulmus americana American elm Tree FACW 1 1 331133
Sum Performance Standard 16 16 6 6 12 12 13 13 14 14 11 11 11 11 12 12
16 6 121314111112
648 243 486 526 567 445 445 486
73548344
25 67 58 46 21 55 55 33
22223233
00000000
16 6 121314111112
648 243 486 526 567 445 445 486
73548344
25 67 58 46 21 55 55 33
22223233
00000000
1). Bolded species are proposed for the current monitoring year, italicized species are not approved, and a regular font indicates that the species has been approved.
2). The "Species Included in Approved Mitigation Plan" section contains only those species that were included in the original approved mitigation plan. The "Post Mitigation Plan Species" section includes species that are being proposed through a mitigation plan addendum for the current monitoring year (bolded) , species that have been approved in prior monitoring years
through a mitigation plan addendum (regular font), and species that are not approved (italicized).
3). The "Mitigation Plan Performance Standard" section is derived only from stems included in the original mitigation plan, whereas the "Post Mitigation Plan Performance Standard" includes data from mitigation plan approved, post mitigation plan approved, and proposed stems.
Species
Included in
Approved
Mitigation Plan
Mitigation Plan
Performance
Standard
Post Mitigation
Plan
Performance
Standard
Current Year Stem Count
Current Year Stem Count
Stems/Acre
Stems/Acre
Species Count
Species Count
Dominant Species Composition (%)
Dominant Species Composition (%)
Average Plot Height (ft.)
Average Plot Height (ft.)
% Invasives
% Invasives
Veg Plot 5 F Veg Plot 6 F Veg Plot 7 F Veg Plot 8 FIndicator
Status
Veg Plot 1 F Veg Plot 2 F Veg Plot 3 F Veg Plot 4 F
Date of Current Survey
Plot size (ACRES)
Scientific Name Common Name Tree/S
hrub
Planted Acreage
Date of Initial Plant
Date(s) of Supplemental Plant(s)
Date(s) Mowing
Table 8. Vegetation Plot Data Table from Vegetation Data Entry Tool (continued)
22.5
2022‐01‐18
NA
NA
2023‐09‐14
0.0247
Planted Total Planted Total Planted Total Planted Total Planted Total Planted Total Planted Total Planted Total
Alnus serrulata hazel alder Tree OBL 1 1 4 4
Betula nigra river birch Tree FACW 44
Carya sp.
Cephalanthus occidentalis common buttonbush Shrub OBL 1 1 1111
Liriodendron tulipifera tuliptree Tree FACU
Nyssa sp.1177
Nyssa sylvatica blackgum Tree FAC 223311 3333
Quercus nigra water oak Tree FAC 3 3 1 1 5 5
Quercus phellos willow oak Tree FAC 2255 44
Quercus shumardii Shumard's oak Tree FAC 2211
Quercus sp.1111 11
Salix nigra black willow Tree OBL
Salix sp.11
Taxodium sp.557777666611 33
Ulmus americana American elm Tree FACW 3333
Sum Performance Standard 9 9 10 10 13 13 16 16 16 16 13 13 15 15 8 8
9 101316161315 8
364 405 526 648 648 526 607 324
42565633
56 70 54 38 38 31 47 50
33322222
00000000
9 101316161315 8
364 405 526 648 648 526 607 324
42565633
56 70 54 38 38 31 47 50
33322222
00000000
1). Bolded species are proposed for the current monitoring year, italicized species are not approved, and a regular font indicates that the species has been approved.
2). The "Species Included in Approved Mitigation Plan" section contains only those species that were included in the original approved mitigation plan. The "Post Mitigation Plan Species" section includes species that are being proposed through a mitigation plan addendum for the current monitoring year (bolded) , species that have been approved in prior monitoring years
through a mitigation plan addendum (regular font), and species that are not approved (italicized).
3). The "Mitigation Plan Performance Standard" section is derived only from stems included in the original mitigation plan, whereas the "Post Mitigation Plan Performance Standard" includes data from mitigation plan approved, post mitigation plan approved, and proposed stems.
Species Count
Dominant Species Composition (%)
Average Plot Height (ft.)
Tree/S
hrub
Indicator
Status
% Invasives
Post Mitigation
Plan
Performance
Standard
Current Year Stem Count
Stems/Acre
Species Count
Dominant Species Composition (%)
Average Plot Height (ft.)
% Invasives
Planted Acreage
Date of Initial Plant
Date(s) of Supplemental Plant(s)
Date(s) Mowing
Date of Current Survey
Plot size (ACRES)
Scientific Name Common Name
Species
Included in
Approved
Mitigation Plan
Mitigation Plan
Performance
Standard
Current Year Stem Count
Stems/Acre
Veg Plot 15 F Veg Plot 16 FVeg Plot 10 F Veg Plot 11 F Veg Plot 12 F Veg Plot 13 F Veg Plot 14 FVeg Plot 9 F
Table 8. Vegetation Plot Data Table from Vegetation Data Entry Tool (continued)
22.5
2022‐01‐18
NA
NA
2023‐09‐14
0.0247
Veg Plot 1 R Veg Plot 2 R Veg Plot 3 R
Planted Total Planted Total Planted Total Planted Total Planted Total Planted Total Planted Total Total Total Total
Alnus serrulata hazel alder Tree OBL
Betula nigra river birch Tree FACW 1 1 3 3
Carya sp.11 22
Cephalanthus occidentalis common buttonbush Shrub OBL 11
Liriodendron tulipifera tuliptree Tree FACU 643
Nyssa sp.
Nyssa sylvatica blackgum Tree FAC 2 2 2 2
Quercus nigra water oak Tree FAC 1 1 1
Quercus phellos willow oak Tree FAC 114411 3322
Quercus shumardii Shumard's oak Tree FAC 1 1 5 5
Quercus sp.1111 1133 11
Salix nigra black willow Tree OBL 2
Salix sp.
Taxodium sp.22552233773322
Ulmus americana American elm Tree FACW 3322
Sum Performance Standard 11 11 12 12 669911119977765
11 12 6 9 11 9 7765
445 486 243 364 445 364 283 283 243 202
7443334223
27 42 33 56 64 33 29 86 67 60
2222222222
0000000000
11 12 6 9 11 9 7765
445 486 243 364 445 364 283 283 243 202
7443334223
27 42 33 56 64 33 29 86 67 60
2222222222
0000000000
1). Bolded species are proposed for the current monitoring year, italicized species are not approved, and a regular font indicates that the species has been approved.
2). The "Species Included in Approved Mitigation Plan" section contains only those species that were included in the original approved mitigation plan. The "Post Mitigation Plan Species" section includes species that are being proposed through a mitigation plan addendum for the current monitoring year (bolded) , species that have been approved in prior monitoring years
through a mitigation plan addendum (regular font), and species that are not approved (italicized).
3). The "Mitigation Plan Performance Standard" section is derived only from stems included in the original mitigation plan, whereas the "Post Mitigation Plan Performance Standard" includes data from mitigation plan approved, post mitigation plan approved, and proposed stems.
Post Mitigation
Plan
Performance
Standard
Current Year Stem Count
Stems/Acre
Species Count
Dominant Species Composition (%)
Average Plot Height (ft.)
% Invasives
Tree/S
hrub
Planted Acreage
Date of Initial Plant
Date(s) of Supplemental Plant(s)
Date(s) Mowing
Date of Current Survey
Species
Included in
Approved
Mitigation Plan
Mitigation Plan
Performance
Standard
Current Year Stem Count
Stems/Acre
Species Count
Dominant Species Composition (%)
Average Plot Height (ft.)
% Invasives
Plot size (ACRES)
Scientific Name Common Name Veg Plot 20 F Veg Plot 21 F Veg Plot 22 F Veg Plot 23 FIndicator
Status
Veg Plot 17 F Veg Plot 18 F Veg Plot 19 F
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina December 2023
Appendix C
Stream Geomorphology Data
Cross-Sections with Annual Overlays
Table 9A-D. Baseline Stream Data Summary Tables
Table 10A-C. Cross-Section Morphology Monitoring Summary
Station Elevation
0.4 110.0 109.25
2.7 109.7 0.97
4.2 109.4 107.67
4.8 109.4 109.20
5.8 109.0 1.53
6.9 108.6 13.2
8.1 108.2
8.9 107.9
10.1 108.1
11.7 107.9
12.4 108.0
14.1 108.0
14.8 108.1 E/C 5
15.9 109.0
17.5 109.4
18.4 109.8
21.4 109.8
22.3 110.0
Stream Type
LTOB Max Depth:
LTOB Cross Sectional Area:
SUMMARY DATA
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
Feature Pool
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT1, XS -1, Pool
107
109
110
111
0 10 20
El
e
v
a
t
i
o
n
(
f
e
e
t
)
Station (feet)
Swamp Grape, UT 1, XS - 1, Pool
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
-0.2 110.1 110.07
2.4 110.0 0.95
4.6 110.0 108.13
5.7 109.6 109.97
6.9 109.3 1.84
8.0 109.1 11.3
9.3 109.1
10.5 109.1
11.5 109.0
12.1 108.5
12.6 108.8
13.6 108.1
14.0 108.5 E/C 5
14.4 109.3
15.0 108.9
16.2 109.4
16.2 109.4
17.4 109.5
19.5 110.0
21.8 110.2
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT1, XS -2, Riffle
Feature Riffle
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
107
109
110
111
0 10 20
El
e
v
a
t
i
o
n
(
f
e
e
t
)
Station (feet)
Swamp Grape, UT 1, XS - 2, Riffle
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
0.1 110.4 110.69
2.8 110.3 0.79
5.3 110.2 108.55
6.6 109.9 110.24
7.6 109.7 1.69
8.9 109.3 11.8
10.1 108.9
11.1 108.7
11.8 108.6
12.5 108.6
13.2 108.7
14.1 108.9
15.4 109.5 E/C 5
17.0 109.8
18.7 110.3
20.7 110.5
20.7 110.5
23.2 110.7
24.9 110.7
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT1, XS -3, Pool
Feature Pool
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
107
109
110
111
112
0 10 20
El
e
v
a
t
i
o
n
(
f
e
e
t
)
Station (feet)
Swamp Grape, UT 1, XS - 3, Pool
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
0.0 111.0 110.54
4.1 110.8 0.89
8.3 110.7 109.12
10.7 110.3 110.38
12.6 110.0 1.27
13.7 109.9 9.5
14.6 109.5
15.8 109.5
16.8 109.3
17.6 109.4
18.8 109.6
19.8 109.7
21.6 109.8 E/C 5
23.3 110.1
24.9 110.6
26.7 110.6
28.3 110.6
31.6 110.7
33.0 110.5
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT1, XS -4, Pool
Feature Riffle
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
109
110
111
112
0 10 20 30
El
e
v
a
t
i
o
n
(
f
e
e
t
)
Station (feet)
Swamp Grape, UT 1, XS - 4, Riffle
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
-0.2 113.8 113.63
2.9 113.7 1.01
5.2 113.6 112.89
7.1 113.3 113.64
8.0 113.3 0.74
8.9 113.0 3.5
9.4 113.2
10.0 112.9
10.6 112.9
11.3 113.1
12.0 113.3
12.7 113.4
14.0 113.4 E/C 5
15.3 113.7
17.1 113.8
19.3 113.7
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT1, XS - 5, Riffle
Feature Riffle
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
112
113
114
0 10 20
El
e
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(
f
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t
)
Station (feet)
Swamp Grape, UT 1, XS - 5, Riffle
Bankfull
MY-00 9/29/21
MY-01 07/18/22
MY-02 3/28/20
Station Elevation
-0.2 113.8 113.74
2.9 113.7 0.94
5.2 113.6 111.76
7.1 113.3 113.61
8.0 113.3 1.85
8.9 113.0 11.5
9.4 113.2
10.0 112.9
10.6 112.9
11.3 113.1
12.0 113.3
12.7 113.4
14.0 113.4 E/C 5
15.3 113.7
17.1 113.8
19.3 113.7
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT1, XS - 6, Pool
Feature Pool
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
111
112
113
114
0 2 4 6 8 10 12 14 16 18 20
El
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v
a
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i
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(
f
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)
Station (feet)
Swamp Grape, UT 1, XS - 6, Pool
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
-0.9 120.2 120.25
1.4 120.2 1.09
3.8 120.3 119.47
5.6 120.1 120.32
6.3 119.8 0.85
7.0 119.7 2.8
7.9 119.7
8.8 119.5
10.3 120.3
11.5 120.5
13.6 120.8
15.7 120.8
E/C 5
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT1, XS - 7, Riffle
Feature Riffle
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
119
120
122
0 10 20
El
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(
f
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)
Station (feet)
Swamp Grape, UT 1, XS - 7, Riffle
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
-0.1 120.4 120.69
2.4 120.6 1.01
4.6 120.7 119.38
6.6 120.5 120.71
7.3 120.0 1.33
8.3 119.7 6.6
9.1 119.4
9.9 119.4
10.7 119.8
11.8 119.6
13.0 120.2
14.2 120.7
15.8 120.8 E/C 5
17.5 120.9
19.0 120.7
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT1, XS - 8, Pool
Feature Pool
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
119
120
121
122
0 10 20
El
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(
f
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)
Station (feet)
Swamp Grape, UT 1, XS - 8, Pool
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
-0.1 112.5 112.75
2.8 112.4 0.93
4.7 112.3 111.82
6.2 112.1 112.68
7.4 112.0 1.00
8.2 112.0 4.6
9.0 112.0
9.6 111.9
10.3 111.8
10.8 111.9
11.5 112.0
12.2 112.2
13.3 112.4 E/C 5
14.1 112.7
15.0 112.7
15.6 112.5
17.7 112.6
20.5 112.7
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT3, XS - 9, Riffle
Feature Riffle
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
111
112
113
114
0 10 20
El
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(
f
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)
Station (feet)
Swamp Grape, UT 3, XS - 9, Riffle
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
-0.3 112.9 113.35
2.5 112.8 0.69
4.8 113.1 111.82
5.8 112.7 112.87
6.7 112.9 1.06
8.4 112.9 6.4
9.3 112.6
9.8 112.3
10.3 112.2
10.9 112.3
12.3 112.3
13.9 112.1
15.1 112.1 E/C 5
16.1 111.8
16.9 111.9
17.7 112.2
18.4 112.8
19.1 112.9
20.4 112.8
22.9 113.0
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT3, XS - 10, Pool
Feature Pool
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
111
112
113
114
0 10 20
El
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(
f
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)
Station (feet)
Swamp Grape, UT 3, XS - 10, Pool
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02
Station Elevation
-0.4 114.5 113.80
2.8 114.3 0.88
5.7 114.1 112.01
8.3 113.9 113.58
9.2 113.8 1.57
9.6 113.6 8.9
10.0 113.0
10.9 112.4
11.8 112.2
12.6 112.2
13.4 112.0
14.6 112.2
16.0 112.6 E/C 5
17.1 113.1
18.1 113.6
20.4 113.7
23.7 113.7
26.9 113.8
30.0 113.7
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT2, XS - 11, Pool
Feature Pool
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
111
112
113
114
115
0 10 20 30
El
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a
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(
f
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)
Station (feet)
Swamp Grape, UT 2, XS - 11, Pool
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
1.0 114.3 114.24
3.7 114.1 1.03
5.4 114.2 113.40
7.9 114.1 114.26
10.3 113.9 0.86
12.2 113.8 6.5
13.8 113.6
14.5 113.4
15.0 113.3
15.3 113.4
15.8 113.5
16.8 113.7
17.6 113.8 E/C 5
18.3 114.1
20.2 114.1
22.2 114.3
24.6 114.2
27.3 114.0
29.8 113.8
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT2, XS - 12, Riffle
Feature Riffle
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
113
114
115
0 10 20 30
El
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(
f
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)
Station (feet)
Swamp Grape, UT 2, XS - 12, Riffle
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02
Station Elevation
0 114.803 115.10
2.7210693 114.946 1.105.1895542 114.776 114.34
7.0357666 115.099 115.18
8.423572 115.139 0.839.9086478 115.267 4.2
10.83857 115.332
11.850907 115.178
12.438166 114.921
12.84272 114.534
14.012188 114.429
14.761161 114.408
15.711867 114.343 E/C 5
16.212275 114.391
16.867666 114.921
17.550487 115.004
18.167741 114.879
19.665272 115.068
21.966662 115.126
24.233551 115.164
26.524733 115.121
30.039262 115.185
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
Feature Riffle
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT2, XS - 13, Riffle
114
115
116
0 10 20 30
El
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(
f
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t
)
Station (feet)
Swamp Grape, UT 2, XS - 13, Riffle
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
0.0 115.3 115.52
2.0 115.3 1.04
4.1 115.3 114.73
5.6 115.0 115.59
7.3 115.1 1.78
8.8 115.2 10.8
11.0 115.2
11.8 115.1
12.5 115.0
13.0 114.7
13.5 114.7
14.0 114.8
14.7 114.9 E/C 5
15.5 115.0
16.4 115.0
17.2 115.3
18.0 115.6
18.8 115.5
19.9 115.6
22.7 115.4
24.4 114.94
26.3 115.2
28.7 115.2
30.3 115.1
31.5 115.2
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
Feature Pool
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT2, XS - 14, Pool
113
114
115
116
0 10 20 30
El
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(
f
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)
Station (feet)
Swamp Grape, UT 2, XS - 14, Pool
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02
Station Elevation
0.0 116.7 116.85
2.3 116.9 0.96
5.3 116.7 116.03
7.3 116.6 116.82
8.0 116.2 0.79
8.6 116.1 3.5
9.5 116.3
10.4 116.0
11.7 116.5
14.0 116.8
16.2 116.8
18.9 116.8
E/C 5
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT1, XS - 15, Riffle
Feature Riffle
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
SUMMARY DATA
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
Note: As-Built cross section data changed to match actual field conditions
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
115
116
117
0 10 20
El
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(
f
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)
Station (feet)
Swamp Grape, UT 1, XS - 15, Riffle
Bankfull
MY-00 3/11/2022
MY-01 7/18/22
MY-02 3/28/23
Station Elevation
0.0 116.8 116.82
2.3 116.8 0.90
4.8 116.7 115.42
5.0 116.7 116.68
5.9 116.4 1.26
5.9 116.4 8.0
7.2 115.7
8.6 115.5
9.6 115.4
10.5 115.4
12.0 115.8
13.5 116.2
14.7 116.4 E/C 5
16.5 116.7
18.8 116.7
21.1 116.8
Site Swamp Grape Site
Watershed:Lumber River Basin, 03040204
XS ID UT1, XS - 16, Pool
Feature Pool
Date:3/28/2023
Field Crew:Adams, Flemming, Lance
Bankfull Elevation:
Bank Hieght Ratio:
Thalweg Elevation:
LTOB Elevation:
LTOB Max Depth:
LTOB Cross Sectional Area:
Stream Type
SUMMARY DATA
115
116
118
0 10 20
El
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(
f
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)
Station (feet)
Swamp Grape, UT 1, XS - 16, Pool
Bankfull
MY-00 3/11/2022
MY-01 7/18/22
MY-02 3/28/23
Parameter
Riffle Only Min Mean Med Max n Min Max Min Max n
Bankfull Width (ft)5.2 13.2 17.6 8 6.8 7.9 8.8 11.8 3
Floodprone Width (ft)8 20 50 8 50 150 100 100 3
Bankfull Mean Depth (ft)0.2 0.3 0.8 8 0.5 0.6 0.2 0.4 3
Bankfull Max Depth (ft)0.4 0.7 1.5 8 0.6 0.9 0.6 0.9 3
Bankfull Cross Sectional Area (ft2)3.9 3.9 3.9 8 3.9 3.9 2.9 3.9 3
Width/Depth Ratio 6.5 44 88 8 12 16 19.8 48.0 3
Entrenchment Ratio 1 1.5 9.3 8 7.3 19 8.4 11.3 3
Bank Height Ratio 1.5 2.8 6.6 8 1 1.3 1 1 3
Max part size (mm) mobilized at bankfull
Rosgen Classification
Bankfull Discharge (cfs)
Sinuosity (ft)
Water Surface Slope (Channel) (ft/ft)
Other
Parameter
Riffle Only Min Mean Med Max n Min Max Min Max n
Bankfull Width (ft)10.2 12.2 20.3 7 12.4 14.4 17.9 19.4 2
Floodprone Width (ft)50 150 150 7 100 200 100 100 2
Bankfull Mean Depth (ft)0.6 1.1 2.4 7 0.9 1 0.6 0.7 2
Bankfull Max Depth (ft)1.1 1.8 2.4 7 1.2 1.6 1.2 1.3 2
Bankfull Cross Sectional Area (ft2)12.9 12.9 12.9 7 12.9 12.9 11.9 12.8 2
Width/Depth Ratio 7.8 11.1 33.8 7 12 16 25.1 31.5 2
Entrenchment Ratio 2.8 12.3 14.7 7 8 13.9 5.2 5.6 2
Bank Height Ratio 1 1.3 1.8 7 1 1.3 1 1 2
Max part size (mm) mobilized at bankfull
Rosgen Classification
Bankfull Discharge (cfs)
Sinuosity (ft)
Water Surface Slope (Channel) (ft/ft)
Other
0.0036 0.0054 0.00474
12.1 12.1
1.3 1.15 1.15
Table 9B. Baseline Stream Data Summary
Swamp Grape - UT 1 (Downstream)
Pre-Existing Condition (applicaple)Design
Monitoring Baseline
(MY0)
Eg 5 Ce 5 Ce 5
12.1
Pre-Existing Condition (applicaple)
Monitoring Baseline
(MY0)Design
Table 9A. Baseline Stream Data Summary
Swamp Grape - UT 1 (Upstream)
1.15
0.0062 0.0031 0.0024
1.01 1.15
3.53.5 3.5
Ce 5F 5 Ce 5
Parameter
Riffle Only Min Mean Med Max n Min Max Min Max n
Bankfull Width (ft)6.9 7.5 7.9 7.7 8.9 8.8 16.7 2
Floodprone Width (ft)50 75 75 100 200 100.0 100.0 2
Bankfull Mean Depth (ft)0.6 0.6 0.7 0.6 0.6 0.4 0.4 2
Bankfull Max Depth (ft)1.2 1.4 1.7 0.7 1 0.7 0.9 2
Bankfull Cross Sectional Area (ft2)4.9 4.9 4.9 4.9 4.9 3.5 6.0 2
Width/Depth Ratio 9.9 12.5 13.2 12 16 22.2 46.5 2
Entrenchment Ratio 6.7 9.5 10.9 13 22.6 6.0 11.4 2
Bank Height Ratio 1.1 1.3 1.4 1 1.3 1.0 1.0 2
Max part size (mm) mobilized at bankfull
Rosgen Classification
Bankfull Discharge (cfs)
Sinuosity (ft)
Water Surface Slope (Channel) (ft/ft)
Other
Parameter
Riffle Only Min Mean Med Max n Min Max Min Max n
Bankfull Width (ft)6.8 7.8 8.8 8.9 10.3 15.8 15.8 1
Floodprone Width (ft)27 31 35 100 200 100.0 100.0 1
Bankfull Mean Depth (ft)0.7 0.9 1 0.6 0.7 0.4 0.4 1
Bankfull Max Depth (ft)1.2 1.3 1.4 0.8 1.1 1.1 1.1 1
Bankfull Cross Sectional Area (ft2)6.6 6.6 6.6 6.6 6.6 5.9 5.9 1
Width/Depth Ratio 6.8 9.7 12.6 12 16 42.0 42.0 1
Entrenchment Ratio 3.1 4.1 5.1 11.2 19.5 6.3 6.3 1
Bank Height Ratio 1.4 1.6 1.8 1 1.3 1.0 1.0 1
Max part size (mm) mobilized at bankfull
Rosgen Classification
Bankfull Discharge (cfs)
Sinuosity (ft)
Water Surface Slope (Channel) (ft/ft)
Other
Monitoring Baseline
(MY0)DesignPre-Existing Condition (applicaple)
Swamp Grape - UT 3
0.0125 0.0039 0.0032
6.1 6.1 6.1
1.17 1.15 1.15
Eg 5 Ce 5 Ce 5
Table 9D. Baseline Stream Data Summary
0.0042 0.0035 0.0029
4.5 4.5 4.5
1.02 1.15 1.15
Cg 5 Ce 5 Ce 5
Table 9C. Baseline Stream Data Summary
Swamp Grape - UT 2
Pre-Existing Condition (applicaple)Design
Monitoring Baseline
(MY0)
MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+
Bankfull Elevation (ft) - Based on AB-Bankfull1 Area 109.50 109.49 109.25 110.09 110.14 110.07 110.37 110.36 110.69 110.50 110.54 110.63 113.72 113.78 113.63
Bank Height Ratio_Based on AB Bankfull1 Area 1.00 1.03 0.97 1.00 0.98 0.95 1.00 0.92 0.79 1.00 1.01 0.98 1.00 1.06 1.01
Thalweg Elevation 107.77 107.92 107.67 108.75 108.60 108.13 108.60 108.41 108.55 109.30 109.12 109.30 113.01 112.99 112.89
LTOB2 Elevation 109.50 109.54 109.20 110.09 110.10 109.97 `110.37 110.21 110.24 110.50 110.55 110.60 113.72 113.83 113.64
LTOB2 Max Depth (ft)1.73 1.62 1.53 1.34 1.50 1.84 1.77 1.80 1.69 1.20 1.43 1.30 0.70 0.84 0.74
LTOB2 Cross Sectional Area (ft2)13.9 14.65 13.24 12.8 12.15 11.28 17.8 15.09 11.78 11.9 12.09 11.38 3.4 3.92 3.52
MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+
Bankfull Elevation (ft) - Based on AB-Bankfull1 Area 114.21 113.94 113.74 120.40 120.35 120.25 120.44 120.46 120.69 116.68 116.64 116.85 116.80 116.83 116.82
Bank Height Ratio_Based on AB Bankfull1 Area 1.00 0.77 0.94 1.00 1.17 1.09 1.00 0.96 1.01 1.00 1.07 0.96 1.00 0.97 0.90
Thalweg Elevation 113.00 111.90 111.76 119.79 119.67 119.47 119.11 119.22 119.38 115.79 115.92 116.03 115.47 115.41 115.42
LTOB2 Elevation 114.21 113.47 113.61 120.40 120.46 120.32 120.44 120.42 120.71 116.68 116.69 116.82 116.80 116.79 116.68
LTOB2 Max Depth (ft)1.22 1.57 1.85 0.60 0.79 0.85 1.33 1.20 1.33 0.89 0.76 0.79 1.34 1.38 1.26
LTOB2 Cross Sectional Area (ft2)6.2 9.15 11.53 2.9 3.07 2.77 6.5 6.03 6.56 3.9 4.43 3.54 9.6 8.99 8.01
0.00
1.80
Bankfull Elevation (ft) - Based on AB-Bankfull1 Area
Bank Height Ratio_Based on AB Bankfull1 Area
Thalweg Elevation
LTOB2 Elevation
LTOB2 Max Depth (ft)
LTOB2 Cross Sectional Area (ft2)
Table 10A. Monitoring Data - Cross Section Morphology Monitoring Summary
(Swamp Grape/ DMS:100115) UT 1
UT 1 - Cross Section 1 (Pool)UT 1 - Cross Section 2 (Riffle)UT 1 - Cross Section 3 (Pool)UT 1 - Cross Section 4 (Riffle)UT 1 - Cross Section 5 (Riffle)
UT 1 - Cross Section 16 (Pool)
Note: The smaller the channel the closer the survey measurements are to their limit of reliable detection, therefore inter-annual variation in morphological measurement (as a percentage) is by default magnified as channel size decereases. Some of the variability above is the result of this factor and some is due to the large amount of depositional sediments observed.
UT 1 - Cross Section 6 (Pool)UT 1 - Cross Section 7 (Riffle)UT 1 - Cross Section 8 (Pool)UT 1 - Cross Section 15 (Riffle)
The above morphology parameters reflect the 2018 guidance that arose from the mitigation technical workgroup consisting of DMS, the IRT and industry mitigation providers/practitioners. The outcome
resulted in the focus on three primary morphological parameters of interest for the purposes of tracking channel change moving forward. They are the bank height ratio using a constant As-built bankfull area
and the cross sectional area and max depth based on each years low top of bank. These are calculated as follows:
1 - Bank Height Ratio (BHR) takes the As-built bankful area as the basis for adjusting each subsequent years bankfull elevation. For example if the As-built bankfull area was 10 ft2, then the MY1 bankfull
elevation would be adjusted until the calculated bankfull area within the MY1 cross section survey = 10 ft2. The BHR would then be calculated with the difference between the low top of bank (LTOB) elevation
for MY1 and the thalweg elevation for MY1 in the numerator with the difference between the MY1 bankfull elevation and the MY1 thalweg elevation in the denominator. This same process is then carried out
in each successive year.
2 - LTOB Area and Max depth - These are based on the LTOB elevation for each years survey (The same elevation used for the LTOB in the BHR calculation). Area below the LTOB elevation will be used and
tracked for each year as above. The difference between the LTOB elevation and the thalweg elevation (same as in the BHR calculation) will be recroded and tracked above as LTOB max depth.
MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+
Bankfull Elevation (ft) - Based on AB-Bankfull1 Area 113.81 113.83 113.80 114.20 114.27 114.24 114.95 114.98 115.10 115.20 115.27 115.52
Bank Height Ratio_Based on AB Bankfull1 Area 1.00 1.02 0.88 1.00 0.87 1.03 1.00 1.09 1.10 1.00 0.92 1.04
Thalweg Elevation 112.08 112.06 112.01 113.28 113.22 113.40 114.27 114.33 114.34 113.78 113.79 114.73
LTOB2 Elevation 113.81 113.87 113.58 114.2 114.14 114.26 `114.95 115.04 115.18 115.20 115.15 115.59
LTOB2 Max Depth (ft)1.73 1.80 1.57 0.92 0.92 0.86 0.68 0.71 0.83 1.42 1.36 1.78
LTOB2 Cross Sectional Area (ft2)10.8 11.12 8.89 6.0 4.62 6.49 3.5 3.91 4.18 9.19 7.83 10.76
Bankfull Elevation (ft) - Based on AB-Bankfull1 Area
Bank Height Ratio_Based on AB Bankfull1 Area
Thalweg Elevation
LTOB2 Elevation
LTOB2 Max Depth (ft)
LTOB2 Cross Sectional Area (ft2)
0.00
1.80
Bankfull Elevation (ft) - Based on AB-Bankfull1 Area
Bank Height Ratio_Based on AB Bankfull1 Area
Thalweg Elevation
LTOB2 Elevation
LTOB2 Max Depth (ft)
LTOB2 Cross Sectional Area (ft2)
Table 10B. Monitoring Data - Cross Section Morphology Monitoring Summary
(Swamp Grape/ DMS:100115) UT 2
UT 2 - Cross Section 11 (Pool)UT 2 - Cross Section 12 (Riffle)UT 2 - Cross Section 13 (Riffle)UT 2 - Cross Section 14 (Pool)
Note: The smaller the channel the closer the survey measurements are to their limit of reliable detection, therefore inter-annual variation in morphological measurement (as a percentage) is by default magnified as channel size decereases. Some of the variability above is the result of this factor and some is due to the large amount of depositional sediments observed.
The above morphology parameters reflect the 2018 guidance that arose from the mitigation technical workgroup consisting of DMS, the IRT and industry mitigation providers/practitioners. The outcome
resulted in the focus on three primary morphological parameters of interest for the purposes of tracking channel change moving forward. They are the bank height ratio using a constant As-built bankfull area
and the cross sectional area and max depth based on each years low top of bank. These are calculated as follows:
1 - Bank Height Ratio (BHR) takes the As-built bankful area as the basis for adjusting each subsequent years bankfull elevation. For example if the As-built bankfull area was 10 ft2, then the MY1 bankfull
elevation would be adjusted until the calculated bankfull area within the MY1 cross section survey = 10 ft2. The BHR would then be calculated with the difference between the low top of bank (LTOB) elevation
for MY1 and the thalweg elevation for MY1 in the numerator with the difference between the MY1 bankfull elevation and the MY1 thalweg elevation in the denominator. This same process is then carried out in
each successive year.
2 - LTOB Area and Max depth - These are based on the LTOB elevation for each years survey (The same elevation used for the LTOB in the BHR calculation). Area below the LTOB elevation will be used and
tracked for each year as above. The difference between the LTOB elevation and the thalweg elevation (same as in the BHR calculation) will be recroded and tracked above as LTOB max depth.
MY0 MY1 MY2 MY3 MY5 MY7 MY+MY0 MY1 MY2 MY3 MY5 MY7 MY+
Bankfull Elevation (ft) - Based on AB-Bankfull1 Area 112.69 112.65 112.75 112.84 112.78 113.35
Bank Height Ratio_Based on AB Bankfull1 Area 1.00 0.97 0.93 1.00 1.01 0.69
Thalweg Elevation 111.54 111.60 111.82 111.30 111.30 111.82
LTOB2 Elevation 112.69 112.62 112.68 112.84 112.80 112.87 `
LTOB2 Max Depth (ft)1.15 1.02 1.00 1.54 1.49 1.06
LTOB2 Cross Sectional Area (ft2)5.9 5.25 4.63 11.4 11.69 6.44
Bankfull Elevation (ft) - Based on AB-Bankfull1 Area
Bank Height Ratio_Based on AB Bankfull1 Area
Thalweg Elevation
LTOB2 Elevation
LTOB2 Max Depth (ft)
LTOB2 Cross Sectional Area (ft2)
0.00
1.80
Bankfull Elevation (ft) - Based on AB-Bankfull1 Area
Bank Height Ratio_Based on AB Bankfull1 Area
Thalweg Elevation
LTOB2 Elevation
LTOB2 Max Depth (ft)
LTOB2 Cross Sectional Area (ft2)
Table 10C. Monitoring Data - Cross Section Morphology Monitoring Summary
(Swamp Grape/ DMS:100115) UT 3
UT 3 - Cross Section 9 (Riffle)UT 3 - Cross Section 10 (Pool)
Note: The smaller the channel the closer the survey measurements are to their limit of reliable detection, therefore inter-annual variation in morphological measurement (as a percentage) is by default magnified as channel size decereases. Some of the variability above is the result of this factor and some is due to the large amount of depositional sediments observed.
The above morphology parameters reflect the 2018 guidance that arose from the mitigation technical workgroup consisting of DMS, the IRT and industry mitigation providers/practitioners. The outcome
resulted in the focus on three primary morphological parameters of interest for the purposes of tracking channel change moving forward. They are the bank height ratio using a constant As-built bankfull area
and the cross sectional area and max depth based on each years low top of bank. These are calculated as follows:
1 - Bank Height Ratio (BHR) takes the As-built bankful area as the basis for adjusting each subsequent years bankfull elevation. For example if the As-built bankfull area was 10 ft2, then the MY1 bankfull
elevation would be adjusted until the calculated bankfull area within the MY1 cross section survey = 10 ft2. The BHR would then be calculated with the difference between the low top of bank (LTOB) elevation
for MY1 and the thalweg elevation for MY1 in the numerator with the difference between the MY1 bankfull elevation and the MY1 thalweg elevation in the denominator. This same process is then carried out
in each successive year.
2 - LTOB Area and Max depth - These are based on the LTOB elevation for each years survey (The same elevation used for the LTOB in the BHR calculation). Area below the LTOB elevation will be used and
tracked for each year as above. The difference between the LTOB elevation and the thalweg elevation (same as in the BHR calculation) will be recroded and tracked above as LTOB max depth.
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina December 2023
Appendix D
Hydrologic Data
Table 11. Verification of Bankfull Events
Stream Crest Gauge Graphs
Table 12. Groundwater Hydrology Data
Groundwater Gauge Graphs
Figure D1. 30/70 Percentile Graph for Rainfall
Soil Temperature Graph
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina December 2023
Table 11. Verification of Bankfull Events
Date of Data
Collection Date of Occurrence Method Photo
(if available)
July 18, 2022 July 10, 2022
Crest gauges documented a bankfull event on UT2 after
4.95” of rain was recorded between July 8-10, 2022 at an
onsite rain gauge. UT2 crested at 2.44 ft, and wrack lines
were observed along UT1 and UT2.
1
August 19-20, 2022 August 19, 2022
Crest gauges documented a bankfull event on UT1 and UT2
after 2.73” of rain was recorded at an onsite rain gauge. UT1
and UT2 crested at 2.92 ft and 2.63 ft, respectively.
--
November 17, 2022 September 30, 2022
Crest gauges documented a bankfull event on UT1 and UT2
after 1.04” of rain was recorded between July 8-10, 2022 at
an onsite rain gauge. UT1 and UT2 crested at 2.42 ft and 2.48
ft, respectively. Additionally, wrack lines were observed
along UT1 and UT2.
2-3
February 28, 2023 January 25, 2023
Crest gauges documented a bankfull event on UT1 and UT2
after 1.75” of rain was recorded the day before at an onsite
rain gauge. UT1 and UT2 crested at 1.60’ and 1.77’,
respectively.
4
May 19, 2023 April 9, 2023
Crest gauges and trail cameras documented a bankfull event
on UT1 and UT2 after 2.30” of rain was recorded over two
days at an onsite rain gauge. UT1 and UT2 crested at 2.00’
and 1.52’, respectively.
5
August 3, 2023 June 21, 2023
Crest gauges documented a bankfull event on UT1 and UT2
after 5.90” of rain was recorded the day before at an onsite
rain gauge. UT1 and UT2 crested at 3.99’ and 2.81’,
respectively.
--
November 20, 2023 August 31, 2023
Crest gauges trail cameras documented a bankfull event on
UT1 and UT2 after 3.29” of rain was recorded over two days
at an onsite rain gauge. UT1 and UT2 crested at 3.17’ and
1.96’, respectively. Wrack lines were observed along UT1.
6-7
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina December 2023
Photo 1: Wrack line along UT1 resulting from a bankfull event.
Photo 2: Wrack lines along UT1 resulting from a bankfull event.
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina December 2023
Photo 3: Wrack line along UT2 resulting from a bankfull event.
Photo 4: Overbank event occurring on UT1
(NOTE: Date malfunction on photo footer, but it was confirmed based on the metadata of the file)
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina December 2023
Photo 5: Overbank event occurring on UT2
Photo 6: Overbank event occurring on UT2
(NOTE: Date malfunction on photo footer, but it was confirmed based on the metadata of the file)
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina December 2023
Photo 7: Wrack lines along UT1 resulting from a bankfull event.
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Swamp Grape Crest Gauge UT1 Upstream
Year 2 (2023 Data)
6/21/23
2.36 ft
Gauge malfunctioned with
corrupt data between
1/19/23 and 3/29/23. It was
replaced on 3/30/23.
4/8/23
2.00 ft
8/31/2023
1.98 ft
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Swamp Grape Crest Gauge UT2
Year 2 (2023 Data)
4/8/23
1.52 ft
6/21/2023
2.81 ft
1/25/23
1.77 ft 8/31/2023
1.96 ft
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Swamp Grape Crest Gauge UT1 Downstream
Year 2 (2023 Data)
6/21/2023
3.99 ft
1/25/2023
1.60 ft
Gauge malfunctioned
on 2/28/23 resulting in
data loss. It was
replaced on 5/18/23.
8/31/2023
3.17 ft
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina December 2023
Table 12. Groundwater Hydrology Data
Gauge
Success Criteria Achieved/Max Consecutive Days During Growing Season (Percentage)
Year 1
(2022)
Year 2
(2023)
Year 3
(2024)
Year 4
(2025)
Year 5
(2026)
Year 6
(2027)
Year 7
(2028)
1 No
8 days (3.2%)
No
6 Days (2.4%)
2 No
14 days (5.6%)
No
12 Days (4.8%)
3 No
12 days (4.8%)
No
11 Days (4.4%)
4 No
17 days (6.8%)
Yes
73 Days (30.4%)
5 No
12 days (4.8%)
Yes
51 Days (20%)
6 No
3 days (1.2%)
No
4 Days (1.6%)
7 Yes
82 days (32.7%)
Yes
95 Days (32.7%)
8 Yes
80 days (31.9%)
Yes
85 Days (33.9%)
9 Yes
61 days (24.3%)
Yes
73 Days (29%)
10 Yes
83 days (33.1%)
Yes
86 Days (34.2%)
11 Yes
52 Days (20.7%)
Yes
65 Days (25.9%)
12 Yes
70 Days (27.9%)
Yes
101 Days (40.2%)
13 Yes
83 Days (33.1%)
Yes
108 Days (43.0%)
14 Yes
128 Days (51.0%)
Yes
251 Days (100%)
15 Yes
58 Days (23.1%)
Yes
74 Days (29.5%)
16 Yes
34 Days (13.5%)
Yes
69 Days (27.5%)
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Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
6 Days
2.4%
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r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 2
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
12 Days
4.8%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
n
t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 3
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1 11 Days
4.4%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
n
t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 4
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
73 Days
29.1%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
n
t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 5
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
51 Days
20.3%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
n
t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 6
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
4 Days
1.6%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
n
t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 7
Year 2 (2023 Data)
Start Growing Season
March 1
End Growing Season
November 695 Days
37.8%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
n
t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 8
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1 85 Days
33.9%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
n
t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 9
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
73 Days
29.1%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
n
t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 10
Year 2 (2023 Data)
End Growing Season
November 6Start Growing Season
March 1
86 Days
34.3%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
n
t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 11
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
65 Days
25.9%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
n
t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 12
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
101 Days
40.2%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
0
/
2
3
6/
2
0
/
2
3
6/
3
0
/
2
3
7/
1
0
/
2
3
7/
2
0
/
2
3
7/
3
0
/
2
3
8/
9
/
2
3
8/
1
9
/
2
3
8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
n
f
a
l
l
Am
o
u
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t
s
(i
n
)
Gr
o
u
n
d
w
a
t
e
r
Le
v
e
l
(i
n
)
Swamp Grape Groundwater Gauge 13
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
108 Days
43.0%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
14
16
18
20
22
24
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
2
3
5/
3
1
/
2
3
6/
1
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/
2
3
6/
2
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/
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3
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3
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/
2
3
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1
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/
2
3
7/
2
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/
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3
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/
2
3
8/
9
/
2
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8/
1
9
/
2
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8/
2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
3
9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
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f
a
l
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Am
o
u
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t
s
(i
n
)
Gr
o
u
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d
w
a
t
e
r
Le
v
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l
(i
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)
Swamp Grape Groundwater Gauge 14
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
251 Days
100%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
5/
1
1
/
2
3
5/
2
1
/
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3
5/
3
1
/
2
3
6/
1
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/
2
3
6/
2
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3
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/
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3
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1
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/
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3
7/
2
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3
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8/
9
/
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3
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/
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2
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/
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9/
8
/
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9/
1
8
/
2
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9/
2
8
/
2
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10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Ra
i
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f
a
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Am
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s
(i
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)
Gr
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w
a
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e
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Le
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(i
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)
Swamp Grape Groundwater Gauge 15
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1 74 Days
29.5%
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
‐40
‐38
‐36
‐34
‐32
‐30
‐28
‐26
‐24
‐22
‐20
‐18
‐16
‐14
‐12
‐10
‐8
‐6
‐4
‐2
0
2
4
6
8
10
12
1/
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/
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1/
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1
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1/
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1
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/
2
3
2/
2
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/
2
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3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
3
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1
1
/
2
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5/
2
1
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2
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3
1
/
2
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1
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/
2
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2
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3
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2
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8
/
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/
2
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9/
2
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/
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10
/
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/
2
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/
1
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/
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3
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/
2
8
/
2
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11
/
7
/
2
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/
1
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/
2
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/
2
7
/
2
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12
/
7
/
2
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/
1
7
/
2
3
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/
2
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/
2
3
Ra
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(i
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)
Gr
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a
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Le
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(i
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)
Swamp Grape Groundwater Gauge 16
Year 2 (2023 Data)
End Growing Season
November 6
Start Growing Season
March 1
69 Days
27.5%
0
1
2
3
4
5
6
7
8
9
Ra
i
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f
a
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Am
o
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t
in
In
c
h
e
s
Figure D1: Swamp Grape
30‐70 Percentile Graph for Rainfall
30‐70th percentile data from WETS Station: Lumberton, NC
2022
2023
2024
2026
2028
30th Percentile
70th Percentile
36
38
40
42
44
46
48
50
52
54
56
58
60
62
64
66
68
70
72
74
76
78
80
82
84
86
88
1/
1
/
2
3
1/
1
1
/
2
3
1/
2
1
/
2
3
1/
3
1
/
2
3
2/
1
0
/
2
3
2/
2
0
/
2
3
3/
2
/
2
3
3/
1
2
/
2
3
3/
2
2
/
2
3
4/
1
/
2
3
4/
1
1
/
2
3
4/
2
1
/
2
3
5/
1
/
2
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5/
1
1
/
2
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5/
2
1
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5/
3
1
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1
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/
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6/
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3
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1
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/
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2
9
/
2
3
9/
8
/
2
3
9/
1
8
/
2
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9/
2
8
/
2
3
10
/
8
/
2
3
10
/
1
8
/
2
3
10
/
2
8
/
2
3
11
/
7
/
2
3
11
/
1
7
/
2
3
11
/
2
7
/
2
3
12
/
7
/
2
3
12
/
1
7
/
2
3
12
/
2
7
/
2
3
Te
m
p
e
r
a
t
u
r
e
(D
e
g
r
e
e
s
Fa
h
r
e
n
h
e
i
t
)
Swamp Grape
Year 2 (2023) Soil Temperature Data
March 1:
58.1oF
March 16:
49.44oF
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina December 2023
Appendix E
Project Timeline and Contact Info
Table 13. Project Timeline
Table 14. Project Contacts
Table 13. Project Timeline
Data Collection Task Completion or
Activity or Deliverable Complete Deliverable Submission
Project Instituted NA Apr‐19
Mitigation Plan Approved NA Feb‐21
Construction (Grading) Completed NA 23‐Sep‐21
Planting Completed NA 18‐Jan‐22
As‐built Survey Completed NA Sep‐21
MY0 Baseline Report Jan‐22 Feb‐22
MY1 Monitoring Report Nov‐22 Dec‐22
MY2 Monitoring Report Nov‐23 Dec‐23
MY3‐MY7 Monitoring Reports On Schedule On Schedule
Table 14. Project Contacts
Provider Restoration Systems, LLC
1101 Haynes Street, Suite 211
Raleigh, NC 27604
Mitigation Provider POC Worth Creech
919‐755‐9490
Designer Axiom Environmental, Inc.
218 Snow Ave
Raleigh, NC 27603
Primary project design POC Grant Lewis
919‐215‐1693
Construction Contractor Land Mechanics Designs, Inc.
126 Circle G Lane
Willow Spring, NC 27592
Charles Hill
919‐639‐6132
Swamp Grape Stream and Wetland Mitigation Site/100115
MY2 Monitoring Report (Project No. 100115) Appendices
Swamp Grape Stream and Wetland Mitigation Site Restoration Systems, LLC
Robeson County, North Carolina December 2023
Appendix F
Project Notes
Aggradation Memo to DMS June 7, 2023
IRT Site Visit Notes July 14, 2023
Restoration Systems, LLC
1101 Haynes St. Suite 211
Raleigh, North Carolina
Ph: (919) 755-9490
Fx: (919) 755-9492
1101 Haynes St., Suite 211 • Raleigh, NC 27604 • www.restorationsystems.com • Ph 919.755.9490 • Fx 919.755.9492
Wednesday, June 7, 2023
Jeremiah Dow
Eastern Regional Supervisor, Division of Mitigation Services
North Carolina Department of Environmental Quality
Sent Electronically: jeremiah.dow@ncdenr.gov
Subject: Observations of Aggregation During MY2 (2023) / Upper Half of UT2
Swamp Grape Stream and Wetland Mitigation Site, DMS Project No. 100115
Lumber River Basin 03040204, Robeson County
Full Delivery Contract No. 7869, DMS RFP No. 16-007705
USACE Action ID No. SAW-2019-00904, DWR Project No. 2019-0675
Dear Mr. Dow,
While conducting a quarterly site assessment walkthrough in May of Swamp Grape, Axiom Environmental Inc.
(Axiom) noted that the upper reach of UT 2 has received excess sediment deposition. The aggregation begins above
the UT2 vented-ford crossing, located outside the Site’s conservation easement, and continues downstream
through cross sections 14 (pool) and 13 (riffle). Minimal observance of aggregation was documented in cross-
section 12 (riffle), and none was observed in cross-section 11 (pool).
Once the deposition was noted, Axiom conducted surveys of cross-sections 11-14 to ascertain the degree of
aggradation. Cross sections are plotted in Figure 1, attached with photo documentation.
Possible causes of aggradation include:
1.) Excessive upstream erosion/agriculture. The online USGS StreamStats portal delineated the UT 2 drainage
area entering at 243 acres. Of the drainage area, 80.2% is in agricultural production, with much of the land
drained by non-buffered ditches and streams.
2.) A lack of flushing stormwater discharges. Between September 2022 and December 2022, rainfall data
indicates rainfall was at or below the 30th percentile. While enough rain fell to move sediment within UT2’s
watershed, the rain events lacked the energy to move sediment through the Site’s restored UT2 reach.
Rainfall has normalized in the first quarter of 2023.
3.) As indicated in the MY1 (2022) CCPV and included in Figure 1, herbicide treatment for Cattail within and
around the subject UT2 area was conducted. While the Cattail treatment successfully curtailed the
problematic areas, some Cattail remains (which will be treated in 2023). It is possible that the root
structure of the treated Cattail remains and is providing stability to the sediment within UT2.
We believe that a combination of these causes resulted in the observed aggregation, with the lack of flushing flows
being the main contributor. No aggregation/excess sediment deposition was observed on UT1 or UT3. Restoration
Systems is aware of the aggradation and wanted to ensure DMS and the IRT know about this development prior to
the July 12th IRT Site walkthrough. Please feel free to contact me to discuss this at your convenience.
Sincerely,
Raymond Holz
Attachments:
- Figure 1, Overview and Cross Sections
- Photo Documentation
- USGS StreamStats – UT 2 Drainage Area Report
- 30-70 Percentile Graph for Rainfall
#*
")
17
14
13
12
15
10
16
11
Rain Gauge
4
3
UT-2
NC Center for Geographic Information & Anaylsis
FIGURE
Drawn by:
Date:
Scale:
Project No.:
CML
NOV 2022
1:2700
20-003
Title:
Project:
Prepared for:
Robeson County, NC
SWAMP GRAPE
MITIGATION SITE
Agradation
Areas
1
³
0 420210Feet
Legend
Conservation Easement = 24.7 acres
Parcel Boundaries
Stream Restoration
Stream Enhancement (Level I)
Stream Enhancement (Level II)
Stream Generating No Credit
Wetland Restablishment
Wetland Rehabilitation
Wetland Enhancement
Wetland Creation
Vegetation Plots Meeting Stem Density Requirement
Vegetation Plots Not Meeting Stem Density Requirement
Cross Sections
")Rain Gauge/Soil Probe
#*Stream Crest Gauges
MY1 Invasive Species Treatment Areas
Cattails
Chinese Privet
Chinese Privet, Chinaberry, Tree-of-Heaven
UT-2
U
T-1
X S 5
XS
6
X S 1 1
X S 12
XS13
XS14
Note: Basemap is drone imagery from October 2021
on top of 2017 aerial orthoimagery from NC OneMap
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Station (feet)
Swamp Grape, UT 2, XS - 13, Riffle
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
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Swamp Grape, UT 2, XS - 14, Pool
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02
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Swamp Grape, UT 2, XS - 11, Pool
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02 3/28/23
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Station (feet)
Swamp Grape, UT 2, XS - 12, Riffle
Bankfull
MY-00 9/29/21
MY-01 7/18/22
MY-02
Swamp Grape Mitigation Site: MY2(2023) Observations of Aggregation, UT2
DMS Contract #: 7869; DMS Project ID: 100115; RFP # 16-007705
UT2 Cross Section 14 (pool) -03/30/2023
UT2 Cross Section 13 (riffle) -03/30/2023
Page 1
Swamp Grape Mitigation Site: MY2(2023) Observations of Aggregation, UT2
DMS Contract #: 7869; DMS Project ID: 100115; RFP # 16-007705
UT2 Cross Section 12 (riffle) -03/30/2023
UT2 Cross Section 11 (pool) -03/30/2023
Page 2
Swamp Grape Mitigation Site: MY2(2023) Observations of Aggregation, UT2
DMS Contract #: 7869; DMS Project ID: 100115; RFP # 16-007705
UT2 Vented Ford Crossing -05/17/2023
UT2 below the Vented Ford Crossing -05/17/2023
Page 3
Swamp Grape Mitigation Site: MY2(2023) Observations of Aggregation, UT2
DMS Contract #: 7869; DMS Project ID: 100115; RFP # 16-007705
UT2 upstream of cross section 14 -05/17/2023
UT2 upstream between cross sections 13 and 12 -05/17/2023
Page 4
6/7/23, 9:50 AM StreamStats
https://streamstats.usgs.gov/ss/1/3
StreamStats Report
Collapse All
Basin Characteristics
Parameter
Code Parameter Description Value Unit
BASINPERIM Perimeter of the drainage basin as defined in SIR 2004-5262 3.98 miles
BSLDEM30FT Mean basin slope, based on slope percent grid 1.15 percent
CSL10_85fm Change in elevation between points 10 and 85 percent of length along main channel
to basin divide divided by length between points ft per mi
16.71 feet per
mi
DRNAREA Area that drains to a point on a stream 0.38 square
miles
ELEV Mean Basin Elevation 147 feet
ELEVMAX Maximum basin elevation 152 feet
I24H50Y Maximum 24-hour precipitation that occurs on average once in 50 years 7.71 inches
LC01BARE Percentage of area barren land, NLCD 2001 category 31 0 percent
LC01CRPHAY Percentage of cultivated crops and hay, classes 81 and 82, from NLCD 2001 80.2 percent
LC01DEV Percentage of land-use from NLCD 2001 classes 21-24 1.4 percent
LC01FOREST Percentage of forest from NLCD 2001 classes 41-43 1.5 percent
LC01HERB Percentage of herbaceous upland from NLCD 2001 class 71 0 percent
LC01IMP Percent imperviousness of basin area 2001 NLCD 0.09 percent
LC01SHRUB Percent of area covered by shrubland using 2001 NLCD 1.8 percent
LC01WATER Percentage of open water, class 11, from NLCD 2001 0 percent
Region ID:NC
Workspace ID:NC20230607134256487000
Clicked Point (Latitude, Longitude):34.56208, -79.34942
Time:2023-06-07 09:43:11 -0400
6/7/23, 9:50 AM StreamStats
https://streamstats.usgs.gov/ss/2/3
Parameter
Code Parameter Description Value Unit
LC01WETLND Percentage of wetlands, classes 90 and 95, from NLCD 2001 15 percent
LC06BARE Percent of area covered by barren rock using 2006 NLCD 0 percent
LC06DEV Percentage of land-use from NLCD 2006 classes 21-24 1.4 percent
LC06FOREST Percentage of forest from NLCD 2006 classes 41-43 1.5 percent
LC06GRASS Percent of area covered by grassland/herbaceous using 2006 NLCD 0 percent
LC06IMP Percentage of impervious area determined from NLCD 2006 impervious dataset 0.09 percent
LC06PLANT Percent of area in cultivation using 2006 NLCD 80.2 percent
LC06SHRUB Percent of area covered by shrubland using 2006 NLCD 1.8 percent
LC06WATER Percent of open water, class 11, from NLCD 2006 0 percent
LC06WETLND Percent of area covered by wetland using 2006 NLCD 15 percent
LC11BARE Percentage of barren from NLCD 2011 class 31 0 percent
LC11CRPHAY Percentage of cultivated crops and hay, classes 81 and 82, from NLCD 2011 80.2 percent
LC11DEV Percentage of developed (urban) land from NLCD 2011 classes 21-24 1.4 percent
LC11FOREST Percentage of forest from NLCD 2011 classes 41-43 1.5 percent
LC11GRASS Percent of area covered by grassland/herbaceous using 2011 NLCD 0 percent
LC11IMP Average percentage of impervious area determined from NLCD 2011 impervious
dataset
0.1 percent
LC11SHRUB Percent of area covered by shrubland using 2011 NLCD 1.8 percent
LC11WATER Percent of open water, class 11, from NLCD 2011 0 percent
LC11WETLND Percentage of wetlands, classes 90 and 95, from NLCD 2011 15.1 percent
LC92FOREST Percentage of forest from NLCD 1992 classes 41-43 27.3 percent
LFPLENGTH Length of longest flow path 1.209 miles
LU92BARE Percent of area covered by barren rock using 1992 NLCD 0 percent
LU92DEV Percent of area covered by all densities of developed land using 1992 NLCD 0 percent
LU92PLANT Percent of area in cultivation using 1992 NLCD 67.3 percent
LU92WATER Percent of area covered by water using 1992 NLCD 0 percent
LU92WETLN Percent of area covered by wetland using 1992 NLCD 5.3 percent
MINBELEV Minimum basin elevation 130 feet
OUTLETELEV Elevation of the stream outlet in feet above NAVD88 134 feet
PCTREG1 Percentage of drainage area located in Region 1 - Piedmont / Ridge and Valley 0 percent
PCTREG2 Percentage of drainage area located in Region 2 - Blue Ridge 0 percent
PCTREG3 Percentage of drainage area located in Region 3 - Sandhills 0 percent
PCTREG4 Percentage of drainage area located in Region 4 - Coastal Plains 100 percent
PCTREG5 Percentage of drainage area located in Region 5 - Lower Tifton Uplands 0 percent
PRECIP Mean Annual Precipitation 48.1 inches
PROTECTED Percent of area of protected Federal and State owned land 0 percent
SSURGOA Percentage of area of Hydrologic Soil Type A from SSURGO 3 percent
SSURGOB Percentage of area of Hydrologic Soil Type B from SSURGO 47.1 percent
SSURGOC Percentage of area of Hydrologic Soil Type C from SSURGO 25.4 percent
SSURGOD Percentage of area of Hydrologic Soil Type D from SSURGO 24.4 percent
6/7/23, 9:50 AM StreamStats
https://streamstats.usgs.gov/ss/3/3
General Disclaimers
This watershed has been edited, computed flows and basin characteristics may not apply. For more information, submit a support request
from the 'Help' button in the upper-right of the screen, attach a pdf of this report and request assistance from your local StreamStats regional
representative.
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which the data were collected. Although these data and associated metadata have been reviewed for accuracy and completeness and approved for release by the U.S.
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Application Version: 4.15.0
StreamStats Services Version: 1.2.22
NSS Services Version: 2.2.1
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Figure D1: Swamp Grape
30-70 Percentile Graph for Rainfall
30-70th percentile data from WETS Station: Lumberton, NC
2022
2023
2024
2026
2028
30th Percentile
70th Percentile
Restoration Systems, LLC
1101 Haynes St. Suite 211
Raleigh, North Carolina
Ph: (919) 755-9490
July 14, 2023 Fx: (919) 755-9492
1101 Haynes St., Suite 211 • Raleigh, NC 27604 • www.restorationsystems.com • Ph 919.755.9490 • Fx 919.755.9492
Emily Dunnigan
Project Manager – Eastern Region
Division of Mitigation Services
Sent via email to: Emily.Dunnigan@deq.nc.gov
Copied, Jeremiah Dow, Eastern Regional Supervisor, Division of Mitigation Services: jeremiah.dow@ncdenr.gov
Subject: Swamp Grape, MY2 (2023) IRT Site Visit Notes
DMS Project No. 100115
USACE Action ID No. SAW-2019-00904 & DWR Project No. 2019-0675
On July 12, 2023, Restoration Systems (RS) held an on-site meeting with regulatory agencies to review and discuss
the Swamp Grape Mitigation Site (Site). Below is a list of attendees and site visit notes, accompanied by a proposed
planting effort.
Attendees:
USACE:
- Todd Tugwell
- Erin Davis
NC DWR:
- Maria Polizzi
- Mac Haupt
NC DMS:
- Emily Dunnigan
Restoration Systems:
- Raymond Holz
Axiom Environmental:
- Grant Lewis
Site Visit Notes:
General
• The perennial nature of the Site’s streams has prevented the channels from becoming choked out by
herbaceous vegetation. RS has not completed and does not anticipate having to perform any stream
maintenance work regarding in-channel herbaceous vegetation. RS will continue to monitor the channels
for excessive herbaceous vegetation and report to the IRT if the condition changes.
• The sedimentation of UT2’s upper reach, as reported in RS’s June 7th letter, appeared to have mostly
worked its way through the Site. RS will continue to monitor this reach for sedimentation issues.
• The UT1 and UT2 crossings are performing as expected.
- The IRT noted that the height of the vented ford crossing on UT2 may be a contributing factor to
sediment deposition above and below the crossing.
• Treatment of cattails has significantly reduced the on-site monoculture clusters. Treatment will continue,
and RS will continue to plot cattail clusters on the yearly CCPV.
• Herbaceous monitoring will continue, and RS/Axiom will move the plots yearly, focusing on observed
emergent wetland areas.
• Beginning in the Year 3 (2024) monitoring report, RS will plot observed emergent wetland areas
throughout the Site.
UT1-Upper Reach, Right-bank Wetland Seeps
• Based on Year 1 (2022) permanent vegetation monitoring plots, and on-site observations, RS will conduct
three (3) random vegetation transects between permanent vegetation monitoring plots 19-23, as shown
on the attached meeting notes, CCPV.
Swamp Grape, MY2 (2023) IRT Site Visit Notes Page 2
DMS Project No. 100115
USACE Action ID No. SAW-2019-00904 & DWR Project No. 2019-0675
Easement Encroachment – Residential lot between UT1 and UT2
• RS and the IRT reviewed the observed area of encroachment along UT2’s right easement boundary (shown
in the attached figure). RS will replant this area with 3-gallon upland containerized species from the
approved Site Mitigation Plan during the dormant season of 2023/2024. The approved mitigation plan
planting list is provided below for reference.
• RS will install additional treated fence post corners along this boundary line and add additional signage.
Table 1. Planting Plan (Swamp Grape Final/Approved Mitigation Plan
Vegetation Association Cypress Gum Swamp* Coastal Plain Small
Stream Swamp*
Stream-side
Assemblage** TOTAL
Area (acres) 2.3 17.4 2.8 22.5
Species # planted* % of total # planted* % of total # planted** % of total # planted
Swamp black gum (Nyssa
biflora) 391 25 2366 20 776 10 3533
Bald cypress (Taxodium
distichum) 391 25 2366 20 776 10 3533
Tupelo gum (Nyssa aquatica) 391 25 -- -- -- -- 391
Pond cypress (Taxodium
ascendens) 391 25 -- -- -- -- 391
Water oak (Quercus nigra) -- -- 1775 15 776 10 2550
Willow oak (Quercus
phellos) -- -- 1775 15 776 10 2550
Schumard oak (Quercus
schumardii) -- -- 1183 10 776 10 1959
American elm (Ulmus
americana) -- -- 1183 10 776 10 1959
Shagbark hickory (Carya
ovata) -- -- 1183 10 776 10 1959
Black willow (Salix nigra) -- -- -- -- 776 10 776
Tag alder (Alnus serrulata) -- -- -- -- 776 10 776
Buttonbush (Cephalanthus
occidentalis) -- -- -- -- 776 10 776
TOTAL 1564 100 11832 100 7756 100 21,152
Highlighted Species are those RS will use for 3-gallon replanting in the observed MY2 (2023) encroachment areas.
Attachment:
- MY 1 (2022) CCPV with Site Visit Notes
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Rain Gauge
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UT-2
UT-1 Up
UT-1 Down
NC Center for Geographic Information & Anaylsis
FIGURE
Drawn by:
Date:
Scale:
Project No.:
CML
NOV 2022
1:2700
20-003
Title:
Project:
Prepared for:
Robeson County, NC
SWAMP GRAPEMITIGATION SITE
CCPV
1
³
0 500 1,000250Feet
Legend
Conservation Easement = 24.7 acres
Parcel Boundaries
Stream Restoration
Stream Enhancement (Level I)
Stream Enhancement (Level II)
Stream Generating No Credit
Wetland Restablishment
Wetland Rehabilitation
Wetland Enhancement
Wetland Creation
Vegetation Plots Meeting Stem Density Requirement
Vegetation Plots Not Meeting Stem Density Requirement
^_Vegetation Plot Origins
MY1 Herbaceous Plot Locations (5m x 2m)
Cross Sections
Groundwater Gauges Meeting Success Criteria
Groundwater Gauges Not Meeting Success Criteria
")Rain Gauge/Soil Probe
#*Stream Crest Gauges
MY1 Invasive Species Treatment Areas
Cattails
Chinese Privet
Chinese Privet, Chinaberry, Tree-of-Heaven
UT-2
UT-3
UT-1
UT-1
XS 1
XS 2
XS4XS3
X S 5
X
S
6
X S 7
X S 8
X
S
9
XS10
X S 1 1
XS12
XS13
XS14
KitchenSt
Note: Basemap is drone imagery from October 2021
on top of 2017 aerial orthoimagery from NC OneMap
X S 1 5
X S 1 6