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ID#* 20180198 Version* 1
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Erin Davis
Initial Review Completed Date 12/16/2021
Mitigation Project Submittal - 12/15/2021
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Stream Wetlands Buffer Nutrient Offset
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Project Contact Information
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Jeremiah Dow jeremiah.dow@ncdenr.gov
Project Information
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ID#:* 20180198 Version:* 1
Existing ID# Existing Version
Project Type: DMS Mitigation Bank
Project Name: Sassarixa Swamp Mitigation Site
County: Johnston
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Mitigation Monitoring Report
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MONITORING YEAR 1 SASSARIXA SWAMP MITIGATION SITE
Johnston County, NC
ANNUAL REPORT Neuse River Basin
Final HUC 03020201
DMS Project No. 100040
December 2021 DMS Contract No. 7425
DMS RFP No. 16-007279
USAGE Action ID No. 2018-00432
DWR Project No. 2018-0198
Data Collection Dates: April-November 2021
PREPARED FOR:
hri il
NC Department of Environmental Quality
Division of Mitigation Services
1652 Mail Service Center
Raleigh, NC 27699-1652
PREPARED BY:
&P
WILDLANDS
ENGINEERING
312 West Mil!brook Road, Suite 225
Raleigh, NC 27609
Jason Lorch
jlorch@wildlandseng.com
Phone: 919.851.9986
SASSARIXA SWAMP MITIGATION SITE
Monitoring Year 1 Annual Report
TABLE OF CONTENTS
Section 1: PROJECT OVERVIEW 1-1
1.1 Project Quantities and Credits 1-1
1.2 Project Goals and Objectives 1-2
1.3 Project Attributes 1-3
Section 2: Monitoring Year 1 Data Assessment 2-1
2.1 Vegetative Assessment 2-1
2.2 Vegetation Areas of Concern 2-1
2.3 Stream Assessment 2-1
2.4 Stream Areas of Concern 2-1
2.5 Hydrology Assessment 2-2
2.6 Wetland Assessment 2-2
2.7 Adaptive Management Plan 2-2
2.8 Monitoring Year 1 Summary 2-2
Section 3: METHODOLOGY 3-1
Section 4: REFERENCES 4-1
TABLES
Table 1: Project Quantities and Credits 1-1
Table 2: Goals, Performance Criteria, and Functional Improvements 1-2
Table 3: Project Attributes 1-4
FIGURES
Figure la-c Current Condition Plan View
APPENDICES
Appendix A Visual Assessment Data
Table 4 Visual Stream Morphology Stability Assessment Table
Table 5 Vegetation Condition Assessment Table
Stream Photographs
Stream Crossing Photographs
Vegetation Plot Photographs
Appendix B Vegetation Plot Data
Table 6 Vegetation Plot Data
Table 7 Vegetation Performance Standards Summary Table
Appendix C Stream Geomorphology Data
Cross-Section Plots
Table 8 Baseline Stream Data Summary
Table 9 Cross-Section Morphology Monitoring Summary
Appendix D Hydrology Data
Table 10 Bankfull Events
Sassarixa Swamp Mitigation Site
Monitoring Year 1 Annual Report-Final i
Table 11 Rainfall Summary
Table 12 Wetland Gauge Summary
Wetland Gauge Plot
Table 13 Recorded In-Stream Flow Events Summary
Recorded In-Stream Flow Events Plot
Appendix E Project Timeline and Contact Info
Table 14 Project Activity and Reporting History
Table 15 Project Contact Table
Appendix F Additional Documentation
As-Built IRT Comments
Sassarixa Swamp Mitigation Site
Monitoring Year 1 Annual Report-Final ii
Section 1: PROJECT OVERVIEW
The Sassarixa Swamp Mitigation Site (Site) is located in Johnston County, approximately six miles
southwest of Smithfield and five miles north of Four Oaks.The Site drains to Holts Lake, which drains to
the Neuse River. Holts Lake is a recreational lake classified as a Nutrient Sensitive Water(NSW) and the
Neuse River is a water supply for the City of Goldsboro.Table 3 presents information related to the
project attributes.
1.1 Project Quantities and Credits
The Site is located on 10 parcels under 7 different landowners and a conservation easement was
recorded on 65.06 acres. Mitigation work within the Site included restoration, enhancement II, and
preservation of perennial and intermittent stream channels.Table 1 below shows stream credits by
reach and the total amount of stream credits expected at closeout.
Table 1: Project Quantities and Credits
PROJECT MITIGATION QUANTITIES
Mitigation Mitigation
Project Plan As Built Mitigation Restoration Ratio Credits Comments
Segment Footage Footage Category Level (X:1)
Stream
Sassarixa 2 631 2,631 Warm Ell 2.5 1,052.400 Ford Crossing, Fencing Out
Creek R1 R3 Livestock
T1 R1 570 570 Warm Ell 2.5 228.000 Bank Stabilization, Fencing
Out Livestock
T1 R2 824 810 Warm R 1.0 824.000 Full Channel Restoration,
Fencing Out Livestock
T1 R3 509 507 Warm R 1.0 509.000 Full Channel Restoration,
Fencing Out Livestock
T1 R4 252 252 Warm Ell 2.5 100.800 Fencing Out Livestock
T1A 358 356 Warm Ell 2.5 143.200 Fencing Out Livestock
T1B 275 276 Warm Ell 2.5 110.000 Fencing Out Livestock
T1C 307 307 Warm Ell 2.5 122.800 Fencing Out Livestock
T2 1,010 1,006 Warm R 1.0 1,010.000 Pond Removal, Fencing Out
Livestock
T3 R1 1,053 1,041 Warm R 1.0 1,053.000 Full Channel Restoration,
Fencing Out Livestock
T3 R2 61 61 Warm P 10.0 6.100 Conservation Easement
T4 R1 206 206 Warm Ell 2.5 82.400 Ford Crossing, Fencing Out
Livestock
T4 R2 398 399 Warm Ell 2.5 159.200 Bank Stabilization, Fencing
Out Livestock
T4 R3 1,509 1,510 Warm P 10.0 150.900 Culvert Crossing,
Conservation Easement
T5 R1 670 642 Warm Ell 2.5 268.000 Bank Stabilization
Sassarixa Swamp Mitigation Site
Monitoring Year 1 Annual Report-Final 1-1
T5 R2 885 874 Warm R 1.0 885.000 Full Channel Restoration,
Fencing Out Livestock
T5 R3 965 961 Warm Ell 4.0 241.250 Culvert Crossing, Bank
Stabilization
T5A 1,026 1,018 Warm Ell 2.5 410.400 Bank Stabilization, Fencing
Out Livestock
T5B 580 580 Warm Ell 2.5 232.000 Fencing Out Livestock
T5C1 588 588 Warm Ell 2.5 235.200 Fencing Out Livestock
T6 R1 381 383 Warm R 1.0 381.000 Full Channel Restoration,
Fencing Out Livestock
Culvert Crossing, Bank
T6 R2 1,035 1,037 Warm II 2.5 414.000 Stabilization. Fencing Out
Livestock
Total: 8,618.650
1. T5C Credited using the Headwater Stream guidance method of the valley length.
Stream
Restoration Level
Warm Cool Cold
Restoration 4,662.000
Enhancement I --
Enhancement II 3,799.650
Preservation 157.000
Totals 8,618.650
Total Stream Credit 8,618.650
1.2 Project Goals and Objectives
The project is intended to provide numerous ecological benefits.Table 2 below describes expected
outcomes to water quality and ecological processes and provides project goals and objectives.
Table 2:Goals, Performance Criteria,and Functional Improvements
Likely Functional Performance Cumulative
Goal Objective/Treatment Uplift Criteria Measurement Monitoring
Resu Its
Cross-section
ER stays over 2.2 monitoring will be
Construct stream No deviations
Reduce sediment and BHR below assessed during
Improve the channels that will from design. In-
inputs from bank 1.2 with visual MY1, MY2, MY3,
stability of maintain stable cross- stream vegetation
stream sections, patterns, erosion. Reduce assessments MYS, and MY7 was treated Site
channels. and profiles over shear stress on showing and visual wide in
channel boundary. progression inspections will
time. September 2021.
towards stability. be assessed
annually.
Sassarixa Swamp Mitigation Site
Monitoring Year 1 Annual Report-Final 1-2
Cumulative
Goal Objective/Treatment Likely Functional Performance Measurement Monitoring
Uplift Criteria
Resu Its
Install habitat Increase and
features such as diversify available
constructed riffles, habitats for
lunker logs, and brush macroinvertebrates, There is no
Improve required
toes into fish, and
instream performance N/A N/A
restored/enhanced amphibians leading
habitat. standard for this
streams.Add woody to colonization and
materials to channel increase in
metric.
beds. Construct pools biodiversity over
of varying depth. time.
Four bankfull Bankfull events
Reconnect events in documented on
Reconstruct stream
channels separate years all reaches during
channels with Crest gauges
with Allow more within MY1. Greater than
designed bankfull and/or pressure
floodplains frequent flood monitoring 30 consecutive
to allow a dimensions and depth transducers
flows to disperse on period. days of flow
based on reference recording flow
natural the floodplain. 30 consecutive recorded on all
reach data. Remove elevations.
flooding days of flow for intermittent
regime. pond above T2. intermittent streams during
channels. MY1.
Reduce sediment Survival rate of One hundred 10 out of 11
inputs from bank 320 stems per square meter vegetation plots
Restore and Plant native tree and erosion and runoff. acre at MY3, 260 vegetation plots have a planted
enhance Increase nutrient planted stems
understory species in are placed on 2% stem density
native cycling and storage per acre at MY5,
riparian zones and of the planted greater than 320
floodplain in floodplain. and 210 stems
plant native shrub and area of the Site stems per acre.
and Provide riparian per acre at MY7.
herbaceous species and monitored Veg plot 2 has a
streambank habitat.Add a Height
on streambanks. during MY1, MY2, stem density of
vegetation. source of LWD and requirement is 7
MY3, MY5, and 243 planted stems
organic material to feet at MY5 and
stream. 10 feet at MY7. MY7. per acre.
Permanently Protect the Site Visually inspect Cattle
protect the from encroachment the perimeter of encroachment
Establish conservation Prevent
project Site easements on the on the riparian easement the Site to ensure occurred in July
from corridor and direct no easement 2021. No cattle
Site. encroachment.
harmful impact to streams encroachment is have been seen
uses. and wetlands. occurring. on Site since.
1.3 Project Attributes
The project includes several adjacent properties that have been owned and operated as a livestock farm
by a single family since 1850, where livestock were continually rotated through all fields with access to
the project streams. Based on aerial photos from 1950 to 2012 onsite streams have existed in their
approximate locations with very little change to riparian buffer extents since 1950.Two alterations to
the Site visible from historical aerial photography were the addition of the pond on T2 between 1964
and 1973, and the addition of the large pond below T5A,T5B, and T5C between 1950 and 1961.
According to the landowners, in the 1960's and early 1970's a hog yard was located at the upstream end
of T4 and T5,where the streams were diverted to make a hog wallow area.The hogs were moved to a
hog house in the early 1970's, however goats, horses, and cattle had continuous access to this portion of
the site until Hurricane Matthew struck in September 2016.The floods from the storm destroyed much
Sassarixa Swamp Mitigation Site
Monitoring Year 1 Annual Report-Final 1-3
of the fencing around T4 and T5 and livestock have been rotated in other fields since that time while
fencing was being repaired. Other portions of the site had not seen significant changes in land use with
livestock or crop rotations from existing activities.Table 3 below and Table 9 in Appendix C present
additional information on pre-restoration conditions.
Table 3: Project Attributes
la
Sassarixa Swamp
Project Name County Johnston County
Mitigation Site
Project Area (acres) 65.06 Project Coordinates 35.472153,-78.436000
PROJECT WATERSHED •
Physiographic Province Rolling Coastal Plain River Basin Neuse River
USGS HUC 8-digit 03020201 USGS HUC 14-digit 03020201130030
66%agriculture, 27%
DWR Sub-basin 03-04-04 Land Use Classification forested, 7%developed
Project Drainage Area (acres) 5,024 Percentage of Impervious Area 0.9%
Parameters T1 T2 T3 T5 T6
Pre-project length (feet) 2,202 348 1,098 2,544 1,342
Post-project(feet) 2,155 1,010 1,114 2,553 1,451
Valley confinement (Confined, moderately confined, Unconfined Moderately Confined to Unconfined
unconfined)
Drainage area (acres) 45 25 26 41.25 38.25
Perennial, Intermittent, Ephemeral Intermittent Perennial
DWR Water Quality Classification C, NSW B, NSW
Dominant Stream Classification (existing) G5 G5 B5/G5 E5 G5/E5
Dominant Stream Classification (proposed) C5b/E5b C5b/E5b C5b/E5b C5/E5 C5/E5
Dominant Evolutionary class (Simon) if applicable Stage Ill Stage IV Stage Ill Stage IV
Parameters Applicable? Resolved? Supporting Documentation
Water of the United States-Section 404 Yes Yes USACE Nationwide Permit No. 27
and DWQ 401 Water Quality
Water of the United States-Section 401 Yes Yes Certification No.4134.
Endangered Species Act Yes Yes Categorical Exclusion in Mitigation
Historic Preservation Act Yes Yes Plan (Wildlands, 2019)
Coastal Zone Management Act (CZMA or CAMA) N/A N/A N/A
Essential Fisheries Habitat N/A N/A N/A
Sassarixa Swamp Mitigation Site
Monitoring Year 1 Annual Report-Final 1-4
Section 2: Monitoring Year 1 Data Assessment
Annual monitoring and site visits were conducted during MY1 to assess the condition of the project.The
vegetation and stream success criteria for the Site follow the approved success criteria presented in the
Mitigation Plan (Wildlands, 2019). Performance criteria for vegetation, stream, and hydrologic
assessment are located in Section 1.2 Table 3: Goals, Performance Criteria, and Functional
Improvements.
2.1 Vegetative Assessment
The MY1 vegetative survey was completed in September 2021. Vegetation monitoring resulted in a stem
density range of 243 to 607 planted stems per acre and average stem density was 504 planted stems per
acre. Out of the eleven vegetation plots, ten met the interim success criteria of 320 stems per acres,
while Vegetation Plot 2 has 243 stems per acres and is on track to meet the final success criteria of 210
stems per acre. A more thorough visual assessment will take place in the area near Vegetation Plot 2 in
Spring 2022 to assess the survivability of the planted trees and resprouts. Refer to Appendix A for
Vegetation Plot Photographs and the Vegetation Condition Assessment Table and Appendix B for
Vegetation Plot Data.
There were a significant number of mature hardwood trees that were left untouched from construction.
A visual site assessment in November 2021 indicated that mature hardwood trees in construction areas
have survived. Planted trees and volunteer species are growing throughout the Site and starting to fill in
an understory that will eventually become a mature hardwood forest.
.2 Vegetation Areas of Concern
Before construction, Chinese privet (Ligustrum sinense) was treated along Sasssarixa Creek during the
winter of 2020/2021 using a combination of methods including foliar and cut stump applications. Out of
the 27.00 acres that was originally treated, resprouts did emerge along the lower half of Sassarixa Creek
totaling 11.99 acres (Figure la). A follow up treatment will occur during MY2 to treat the resprouts.
Several cattle were observed within the Site throughout July 2021. Cattle had access to 11.39 acres of
the Site between the Sassarixa Creek ford crossing to the top of T1 (Figure la). The cattle were entering
the Site through the high tensile fence along the Sassarixa Creek ford crossing.The landowner has
agreed to keep the outside gates closed unless supervising the cattle crossing Sassarixa Creek. No cattle
have been seen in the easement since July 2021, indicating the easement encroachment has been
resolved. No major damage occurred to the Site due to cattle encroachment, except for several dented
easement signs.
2.3 Stream Assessment
Morphological surveys for MY1 were conducted in July 2021. All streams within the Site are stable and
functioning as designed. All 10 cross-sections at the Site show little to no change in the bankfull area and
width-to-depth ratio, and bank height ratios are less than 1.2. Refer to Appendix A for the Visual Stream
Morphology Stability Assessment Table and Stream Photographs. Refer to Appendix C for Stream
Geomorphology Data.
2.4 Stream Areas of Concern
The spring and summer of 2021 had below average rainfall. Due to dry conditions and lack of shade
before woody vegetation has become established, Murdanina (Figure la-b)was observed in most
tributaries. Wildlands was proactive with in-stream vegetation management and treated T1 Reach 1-3,
Sassarixa Swamp Mitigation Site
Monitoring Year 1 Annual Report-Final 2-1
T2,T3 Reach 1,T5 Reach 2, and T6 Reach 1 and 2 in September 2021.The treatment was effective and
follow up treatments will occur in MY2 to ensure the in-stream vegetation is eradicated.
2.5 Hydrology Assessment
By the end of MY7, four bankfull events must have occurred in separate years within the restoration
reaches. At least one bankfull event was recorded on all stream restoration reaches.Therefore, the
hydrologic success criterion for bankfull events has been partially met in MY1.
In addition, the presence of baseflow must be documented on restored intermittent reaches (T1 Reach
2,T2 and T3 Reach 1) for a minimum of 30 consecutive days during a normal precipitation year. In-
stream flow gauges equipped with pressure transducers were installed to monitor continuity of
baseflow. All intermittent reaches in MY1 exceeded baseflow success criteria.The maximum
consecutive days ranged from 44 days to 108 days. Refer to Appendix 5 for hydrologic data.
2.6 Wetland Assessment
One groundwater gauge was installed and monitored within an existing wetland zone along T3 at a
location requested by North Carolina Division of Water Resources.The purpose of the gauge is to assess
potential effects to wetland hydrology from the construction of the restored stream channel through
this area. The results of this monitoring are not tied to a success criteria. Results from the groundwater
gauge, during MY1, show that the existing wetland maintained free groundwater within 12 inches of the
ground surface for 47.5%of the defined growing season (March 1 to November 16).
..7 Adaptive Management Plan
As indicated in Section 2.2, 11.99 acres of Chinese privet resprouts will be treated throughout MY2.The
management plan will integrate multiple treatment options of cut stump and foliar spray depending on
plant height.
A follow up in-stream vegetation treatment will occur in the spring of 2022 to treat the remaining
vegetation that survived the September 2021 treatment.
�.8 Monitoring Year 1 Summary
Overall,the Site has met the success criteria for MY1.Ten out of eleven veg plots are on track to meet
the MY3 interim success criteria.The area surrounding veg plot 2 will be assessed during MY2 to check
for planted tree resprouts and survivability. Mature trees that were avoided during construction are
healthy with a new understory layer coming in. Follow up treatments of 11.99 acres of Chinese privet
resprouts and in-stream vegetation will occur during MY2.The landowner will keep the outside gates
closed along the Sassarixa Creek ford crossing, resolving the July 2021 cattle encroachment. Bankfull
events were documented on all stream restoration reaches partially fulfilling the final bankfull
hydrologic success requirement. Greater than 30 days of consecutive flow were recorded on monitored
intermittent stream reaches T1 Reach 2,T2, and T3 Reach 1 fulfilling MY1 success requirement. Overall,
the Site is meeting its goals of preventing excess nutrients and sediment from entering the Neuse River
tributaries and is on track to meet final success criteria.
Summary information and data related to the performance of various project and monitoring elements
can be found in the tables and figures in the report appendices. All raw data supporting the tables and
figures in the appendices are available from DMS upon request.
Sassarixa Swamp Mitigation Site
Monitoring Year 1 Annual Report-Final 2-2
Section 3: METHODOLOGY
Geomorphic data was collected following the standards outlined in The Stream Channel Reference Site:
An Illustrated Guide to Field Techniques (Harrelson et al., 1994) and in Stream Restoration:A Natural
Channel Design Handbook(Doll et al., 2003). All Integrated Current Condition Mapping was recorded
using a Trimble handheld GPS with sub-meter accuracy and processed using Pathfinder and ArcGIS.
Crest gauges and pressure transducers were installed in riffle cross-sections and monitored throughout
the year. Hydrologic monitoring instrument installation and monitoring methods are in accordance with
the United States Army Corps of Engineers standards (USACE, 2003). Vegetation monitoring protocols
followed the Wilmington District Stream and Wetland Compensatory Mitigation Update (NCIRT, 2016).
Sassarixa Swamp Mitigation Site
Monitoring Year 1 Annual Report-Final 3-1
Section 4: REFERENCES
Breeding, R. 2010. Neuse River Basin Restoration Priorities 2010. NCEEP, NC
Doll, B.A., Grabow, G.L., Hall, K.A., Halley,J., Harman,W.A.,Jennings, G.D., and Wise, D.E. 2003. Stream
Restoration A Natural Channel Design Handbook.
Harrelson, C.C., Rawlins, C.L., Potyondy,J.P. 1994.Stream Channel Reference Sites:An Illustrated Guide
to Field Technique. Gen.Tech. Rep. RM-245. Fort Collins, CO: U.S. Department of Agriculture, Forest
Service, Rocky Mountain Forest and Range Experiment Station. 61 p.
Rosgen, D. L. 1994. A classification of natural rivers. Catena 22:169-199.
Rosgen, D.L. 1996. Applied River Morphology. Pagosa Springs, CO: Wildland Hydrology Books.
Rosgen, D.L. 1997. A Geomorphological Approach to Restoration of Incised Rivers. Proceedings of the
Conference on Management of Landscapes Disturbed by Channel Incision. Center For
Computational Hydroscience and Bioengineering, Oxford Campus, University of Mississippi, Pages
12-22.
North Carolina Division of Water Resources (DWR). 2015. Neuse 01 CU Update. River Basin Restoration
Priorities Transition Approach.
North Carolina Interagency Review Team (NCIRT). 2016. Wilmington District Stream and Wetland
Compensatory Mitigation Update. Accessed at: https://saw-
reg.usace.army.mil/PN/2016/Wilmington-District-M itigation-Update.pdf
United States Army Corps of Engineers. 2003. Stream Mitigation Guidelines. USACE, NCDENR-DWQ,
USEPA, NCWRC.
United States Geological Survey. 1998. North Carolina Geology.
Wildlands Engineering, Inc. (2019). Sassarixa Swamp Mitigation Project Mitigation Plan. DMS, Raleigh,
NC.
Sassarixa Swamp Mitigation Site
Monitoring Year 1 Annual Report-Final 4-1
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Figure ib.Current Condition Plan View
bikili/41y W I L D L A N D S 300 600 Feet , Sassarixa Swamp Mitigation Site
ENGINEERING DMS Project No.loo040
N Monitoring Year 1-2021
Johnston County, NC
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Figure lc. Current Condition Plan View
0 W I L D L A N D S 0 100 200 Feet Sassarixa Swamp Mitigation Site
ENGINEERING I I I I N DMSProjectNo. 100040
Monitoring Year 1-2021
Johnston County, NC
APPENDIX A. VISUAL ASSESSMENT DATA
Table 4. Visual Stream Morphology Stability Assessment Table
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
T1 R2
Number
Stable, Amount of %Stable,
Major Channel Category Metric Nu Unstable Performing as
Performing
as Intended A Footage ntended
Assessed Stream Length 810
Assessed Bank Length 1,620
Surface Scour/ Bank lacking vegetative cover resulting simply from 0 100%
Bare Bank poor growth and/or surface scour.
Bank toe eroding to the extent that bank failure
appears likely. Does NOT include undercuts that are
Bank Toe Erosion 0 100%
modest,appear sustainable and are providing
habitat.
Fluvial and geotechnical-rotational,slumping,
Bank Failure 0 100%
calving,or collapse.
Totals: 0 100%
Grade control structures exhibiting maintenance of
Grade Control 0 0 N/A
grade across the sill.
Structure
Bank Protection Bank erosion within the structures extent of 27 27 100%
influence does not exceed 15%.
T1 R3
Number
Stable, Total Amount of �o Stable,
Major Channel Category Metric Number' I Unstable Performing as
Performing
Footage Intended
as Intended
Assessed Stream Length 507
Assessed Bank Length 1,014
Surface Scour/ Bank lacking vegetative cover resulting simply from 0 100%
Bare Bank poor growth and/or surface scour.
Bank toe eroding to the extent that bank failure
appears likely. Does NOT include undercuts that are
Bank Toe Erosion 0 100%
modest,appear sustainable and are providing
habitat.
Fluvial and geotechnical-rotational,slumping,
Bank Failure 0 100%
calving,or collapse.
Totals: 0 100%
Grade control structures exhibiting maintenance of
Grade Control 0 0 N/A
grade across the sill.
Structure
Bank Protection Bank erosion within the structures extent of 14 14 100%
influence does not exceed 15%.
Table 4. Visual Stream Morphology Stability Assessment Table
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
T2
Number
Stable, Amount of %Stable,
Major Channel Category Metric Nu Unstable Performing as
Performing
as Intended A Footage untended
Assessed Stream Length 1,006
Assessed Bank Length 2,012
Surface Scour/ Bank lacking vegetative cover resulting simply from 0 100%
Bare Bank poor growth and/or surface scour.
Bank toe eroding to the extent that bank failure
appears likely. Does NOT include undercuts that are
Bank Toe Erosion 0 100%
modest,appear sustainable and are providing
habitat.
Fluvial and geotechnical-rotational,slumping,
Bank Failure 0 100%
calving,or collapse.
Totals: 0 100%
Grade Control Grade control structures exhibiting maintenance of 34 34 100%
grade across the sill.
Structure
Bank Protection Bank erosion within the structures extent of 18 18 100%
influence does not exceed 15%.
T3 R1
Number I
Stable, Total Amount of �o Stable,
Major Channel Category Metric Number' I Unstable Performing as
Performing
Footage Intended
as Intended
Assessed Stream Length 1,041
Assessed Bank Length 2,082
Surface Scour/ Bank lacking vegetative cover resulting simply from 0 100%
Bare Bank poor growth and/or surface scour.
Bank toe eroding to the extent that bank failure
appears likely. Does NOT include undercuts that are
Bank Toe Erosion 0 100%
modest,appear sustainable and are providing
habitat.
Fluvial and geotechnical-rotational,slumping,
Bank Failure 0 100%
calving,or collapse.
Totals: 0 100%
Grade control structures exhibiting maintenance of
Grade Control 0 0 N/A
grade across the sill.
Structure
Bank Protection Bank erosion within the structures extent of 30 30 100%
influence does not exceed 15%.
Table 4. Visual Stream Morphology Stability Assessment Table
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
T5 R2
Number
Stable, Amount of %Stable,
Major Channel Category Metric Nu Unstable Performing as
Performing
as Intended A Footage ntended
Assessed Stream Length 874
Assessed Bank Length 1,748
Surface Scour/ Bank lacking vegetative cover resulting simply from 0 100%
Bare Bank poor growth and/or surface scour.
Bank toe eroding to the extent that bank failure
appears likely. Does NOT include undercuts that are
Bank Toe Erosion 0 100%
modest,appear sustainable and are providing
habitat.
Fluvial and geotechnical-rotational,slumping,
Bank Failure 0 100%
calving,or collapse.
Totals: 0 100%
Grade control structures exhibiting maintenance of
Grade Control 0 0 N/A
grade across the sill.
Structure
Bank Protection Bank erosion within the structures extent of 20 20 100%
influence does not exceed 15%.
T6 R1
Number
Stable, Total Amount of %Stable,
Major Channel Category Metric Number' I Unstable Performing as
Performing
Footage Intended
as Intended
Assessed Stream Length 383
Assessed Bank Length 766
Surface Scour/ Bank lacking vegetative cover resulting simply from 0 100%
Bare Bank poor growth and/or surface scour.
Bank toe eroding to the extent that bank failure
appears likely. Does NOT include undercuts that are
Bank Toe Erosion 0 100%
modest,appear sustainable and are providing
habitat.
Fluvial and geotechnical-rotational,slumping,
Bank Failure 0 100%
calving,or collapse.
Totals: 0 100%
Grade control structures exhibiting maintenance of
Grade Control 0 0 N/A
grade across the sill.
Structure
Bank Protection Bank erosion within the structures extent of 5 5 100%
influence does not exceed 15%.
Table 5. Vegetation Condition Assessment Table
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
Planted Acrea:e 13.03
Mapping
Definitions Threshold(ac) Combined %of Planted
Acreage Acreage
Bare Areas Very limited cover of both woody and herbaceous material. 0.10 0 0%
Low Stem Density Woody stem densities clearly below target levels based on current MY stem count 0.10 0 0%
Areas criteria.
Total 0 0%
Areas of Poor Growth Planted areas where average height is not meeting current MY Performance 0.10 0 0%
Rates Standard.
Cumulative Total 0.0 0%
Easement Acreage 65.06
Ma..in: %of
ombined
tion Catego Definitions Easement
Acrea:e
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
Invasive Areas of
potential to directly outcompete native,young,woody stems in the short-term or 0.10 11.99* 18%
Concern
community structure for existing communities. Invasive species included in
summation above should be identified in report summary.
Encroachment may be point, line, or polygon. Encroachment to be mapped consists
Easement of any violation of restrictions specified in the conservation easement. Common 1 Encroachments Noted
none
Encroachment Areas encroachments are mowing, cattle access, vehicular access. Encroachment has no /11.39ac**
threshold value as will need to be addressed regardless of impact area.
*Chinese privet(Ligustrum sinense)resprouted throughout an existing mautre canopy forest along Sassarixa Creek.
**Cattle accessed the Site in July but minimal impacts were made and the encroachment has been resolved.
STREAM PHOTOGRAPHS
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PHOTO POINT 3 Ti R2—upstream (11/9/2021J PHOTO POINT 3 T1 R2—downstream (11/9/2021)
Sassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Stream Photographs
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Sassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Stream Photographs
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PHOTO POINT 9 T1A—upstream(11/9/2021) PHOTO POINT 9 T1A—downstream (11/9/2021)
Sassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Stream Photographs
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Sassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Stream Photographs
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PHOTO POINT 13 Sassarixa Creek R2—upstream (11/9/2021) PHOTO POINT 13 Sassarixa Creek R2—iv,downstream(11/9/2021)
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Sassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Stream Photographs
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PHOTO POINT 18 Sassarixa Creek R3—upstream (11/9/2021) PHOTO POINT 18 Sassarixa Creek R3—downstream(11/9/2021)
Sassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Stream Photographs
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Appendix A:Visual Assessment Data—Stream Photographs
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Appendix A:Visual AssessmentSite Data—Stream Photographs
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Sassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Stream Photographs
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Sassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Stream Photographs
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Appendix A:Visual Assessment Data—Stream Photographs
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Appendix A:Visual Assessment Data—Stream Photographs
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Sassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Stream Photographs
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Appendix A:Visual Assessment Data—Stream Photographs
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Appendix A:Visual Assessment Data—Stream Photographs
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Appendix A:Visual Assessment Data—Stream Photographs
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Sassarixa Swamp Mitigation Site
tiiii Appendix A:Visual Assessment Data—Stream Photographs
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Sassarixa Swamp Mitigation
Appendix A:Visual AssessmentSite Data—Stream Photographs
STREAM CROSSING PHOTOGRAPHS
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Nal Appendix A:Visual Assessment Data—Stream Crossing Photographs
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we Appendix A:Visual Assessment Data—Stream Crossing Photographs
VEGETATION PLOT PHOTOGRAPHS
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FIXED VEG PLOT 3(9/2/2021) FIXED VEG PLOT 4(9/2/2021)
-,....,,,4„,,ry.-,7,-, --_,..ii-4- '''.=Of i..g,-, 1!
yy u+
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FIXED VEG PLOT 5(9/2/2021) FIXED VEG PLOT 6(9/2/2021)
Ilk Sassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Vegetation Plot Photographs
r,
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RANDOM VEG PLOT 11(9/2/2021)
tillSassarixa Swamp Mitigation Site
Appendix A:Visual Assessment Data—Vegetation Plot Photographs
APPENDIX B. VEGETATION PLOT DATA
Table 6. Vegetation Plot Data
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
Planted Acreage 13.03
Date of Initial Plant 2021-03-05
Date of Current Survey 2021-09-06
Plot size(ACRES) 0.0247
Tree/ Indicator Veg Plot 1 F Veg Plot 2 F Veg Plot 3 F Veg Plot 4 F Veg Plot 5 F
Scientific Name Common Name Shrub Status
Planted Total Planted Total Planted Total Planted Total Planted Total
Acer negundo boxelder Tree FAC 1 1 1 1 1 1 1 1
Betula nigra river birch Tree FACW 2 2 4 4 1 1 2 2
Species Liquidambar styraciflua sweetgum Tree FAC
Included in Magnolia virginiana sweetbay Tree FACW 1 1 2 2 1 1 1 1 1 1
Approved Platanus occidentalis American sycamore Tree FACW 1 1 4 4 2 2 4 4
Mitigation Populus deltoides eastern cottonwood Tree FAC 3 3 1 1 1 1
Plan Quercus michauxii swamp chestnut oak Tree FACW 2 2 2 2 4 4 1 1
Quercus nigra water oak Tree FAC 2 2 1 1
Quercus phellos willow oak Tree FACW 1 1 3 3 3 3 2 2
• Performance Standard 9 9 6 6 15 15 14 14 12 12
Current Year Stem Count 9 6 15 14 12
Mitigation Stems/Acre 364 243 607 567 486
Plan Species Count 6 3 6 8 7
Performance Dominant Species Composition(%) 22 50 27 29 33
Standard Average Plot Height 2 2 3 2 3
Invasives 0 0 0 0 0
Current Year Stem Count 9 6 15 14 12
Post Stems/Acre 364 243 607 567 486
Mitigation Species Count 6 3 6 8 7
Plan
Performance Dominant Species Composition(%) 22 50 27 29 33
Standard Average Plot Height 2 2 3 2 3
Invasives IMMI 0 IIEL 0 0 0
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.
Table 6. Vegetation Plot Data
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
Planted Acreage 13.03
Date of Initial Plant 2021-03-05
Date of Current Survey 2021-09-06
Plot size(ACRES) 0.0247
Tree/ Indicator Veg Plot 6 F Veg Plot 7 F Veg Plot 8 F Veg Plot 9 F Veg Plot 10 F Veg Plot 11
Scientific Name Common Name R
Shrub Status Planted Total Planted Total Planted Total Planted Total Planted Total Total
Acer negundo boxelder Tree FAC 2 2 1 1 2 2 2 2 1
Betula nigra river birch Tree FACW 2 2 2 2 1 1 3 3 1 1 4
Species Liquidambar styraciflua sweetgum Tree FAC 1
Included in Magnolia virginiana sweetbay Tree FACW 1 1 1 1 1 1 1 1 2 2 1
Approved Platanus occidentalis American sycamore Tree FACW 2 2 3 3 3 3 5 5 3 3 1
Mitigation Populus deltoides eastern cottonwood Tree FAC 1 1 1 1 2 2 2 2 1
Plan Quercus michauxii swamp chestnut oak Tree FACW 3 3 3 3 4 4 1 1 2 2 1
Quercus nigra water oak Tree FAC 1 1 1 1
Quercus phellos willow oak Tree FACW 3 3 2 2 2 2 1 1 2 2 2
• Performance Standard 13 13 14 14 14 14 15 15 13 13 12
Current Year Stem Count 13 14 14 15 13 12
Mitigation Stems/Acre 526 567 567 607 526 486
Plan Species Count 6 8 7 7 7 8
Performance Dominant Species Composition(%) 23 21 29 33 23 33
Standard Average Plot Height 2 3 3 3 2 3
Invasives 0 0 0 0 0 0
Current Year Stem Count 13 14 14 15 13 12
Post Stems/Acre 526 567 567 607 526 486
Mitigation Species Count 6 8 7 7 7 8
Plan
Performance Dominant Species Composition(%) 23 21 29 33 23 33
Standard Average Plot Height 2 3 3 3 2 3
Invasives IMMI 0 IIEL 0 0 0 0
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.
Table 7. Vegetation Performance Standards Summary Table
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
Veg Plot 1 F Veg Plot 2 F Veg Plot 3 F
Stems/Ac. Av.Ht.(ft) #Species %Invasives Stems/Ac. Av.Ht.(ft) #Species %Invasives Stems/Ac. Av.Ht.(ft) #Species %Invasives
Monitoring Year 7
Monitoring Year 5
Monitoring Year 3
Monitoring Year 2
Monitoring Year 1 pil 364 2 6 0 243 2 3 0 607 3 6 0
Monitoring Year 0 567 3 8 0 445 2 5 0 607 2 6 0
Veg Plot 4 F Veg Plot 5 F Veg Plot 6 F
Stems/Ac. Av.Ht.(ft) #Species %Invasives Stems/Ac. Av.Ht.(ft) #Species %Invasives Stems/Ac. Av.Ht.(ft) #Species %Invasives
Monitoring Year 7
Monitoring Year 5
Monitoring Year 3
Monitoring Year 2
Monitoring Year 1 567 2 8 0 486 3 7 0 526 2 6 0
Monitoring Year 0 607 2 - 8 0 486 3 7 0 567 3 6
Veg Plot 7 F Veg Plot 8 F Veg Plot 9 F
Stems/Ac. Av.Ht.(ft) #Species %Invasives Stems/Ac. Av.Ht.(ft) #Species %Invasives Stems/Ac. Av.Ht.(ft) #Species %Invasives
Monitoring Year 7
Monitoring Year 5
Monitoring Year 3
Monitoring Year 2
Monitoring Year 1 567 3 8 0 567 3 7 0 607 3 7 0
Monitoring Year 0 567 2 8 0 567 3 7 0 648 2 7 0
Veg Plot 10 F Veg Plot Group 1 R
Stems/Ac. Av.Ht.(ft) #Species %Invasives Stems/Ac. Av.Ht.(ft) #Species %Invasives
Monitoring Year 7
Monitoring Year 5
Monitoring Year 3
Monitoring Year 2
Monitoring Year 1 526 2 7 0 3 8 0
Monitoring Year 0 Ilk 8 lai 0 2 8 0
*Each monitoring year represents a different plot for the random vegetation plot"groups".Random plots are denoted with an R,and fixed plots with an F.
APPENDIX C. STREAM GEOMORPHOLOGY DATA
Cross-Section Plots
Cross-Section 1 (Riffle) T1 Reach 2
151-
150-
i
C
Q t49 ipt--- Nr. . -4
-
tir
ru
L11
14l
1-1i
14 <L1 36
Distance(ft.)
-- MY 0 + kw I -- Bankfull Elevation-Based on As-Built Banklull Area
— Current Low Top of Bank
MVO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation - Based
on AB-Bankfull Area 149.35 149.41
Bank Height Ratio - Based
on AB-Bankfull Area 1.00 0.93
Thalweg Elevation 148.45 148.62
LTOB Elevation 149.35 149.36
LTOB Max Depth 0.90 0.74
LTOB Cross-Sectional Area 2.47 2.16 • /!�p�1 rT
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Sassarixa Swamp Mitigation Site
Appendix C:Stream Geomorphology Data—Cross-Section Plots
Cross-Section 2 (Pool) T1 Reach 2
150-
149- J �
c
g 148-
ri
a
us
LLI
14i-
LAG-
1 t1 <L1 3L1
Distance(ft.)
MY 0 + k iY 1 -- Bankfull Elevation-Based on As-Built Banklull Area
— Current Low Top of Bank
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation - Based N/A N/A
on AB-Bankfull Area
Bank Height Ratio - Based N/A N/A
on AB-Bankfull Area
Thalweg Elevation 147.78 147.58
LTOB Elevation 148.82 148.77
LTOB Max Depth 1.04 1.19
LTOB Cross-Sectional Area 3.20 2.84
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14, Appendix C:Stream Geomorphology Data—Cross-Section Plots
Cross-Section 3 (Riffle) T1 Reach 3
1-a-
11: ::
li
03
Ca
1r_9-
1 2J-
Distance(ft.)
MY 0 -*- MY 1 -- Bankfull Elevation-Based on As-Built Bankfull Area
— Current Low Top of Bank
MVO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation - Based
on AB-Bankfull Area 130.69 130.77
Bank Height Ratio - Based
on AB-Bankfull Area 1.00 0.91
Thalweg Elevation 130.04 130.24
LTOB Elevation 130.69 130.72
LTOB Max Depth 0.64 0.48
LTOB Cross-Sectional Area 1.67 1.45
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Appendix C:Stream Geomorphology Data—Cross-Section Plots
Cross-Section 4 (Riffle) T2
1.13-
142 10
•
o .---4—ilFt--"Im't\k's*fiP-a-- ri---i"- —
141
G7
L11
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1 l 211 30,
Distance(ft.)
,- MY 0 -•- my 1 -- Bankfull Elevation-Based on As-Built Bankfull Area
— Current Low Top of Bank
MVO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation - Based
on AB-Bankfull Area 141.46 141.52
Bank Height Ratio - Based
on AB-Bankfull Area 1.00 0.94
Thalweg Elevation 140.66 140.78
LTOB Elevation 141.46 141.47
LTOB Max Depth 0.80 0.69
LTOB Cross-Sectional Area 1.99 1.76
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Appendix C:Stream Geomorphology Data-Cross-Section Plots
Cross-Section 5 (Pool) T2
142-
• — —_
141-
ti
2 vao to
7
411
-F
U
1;i':1-
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Distance(ft.)
My n -.- MV I -- Bankfull Elevation-Based on As-Built Banklull Area
— Current Low Top of Bank
MVO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation - Based N/A N/A
on AB-Bankfull Area
Bank Height Ratio - Based N/A N/A
on AB-Bankfull Area
Thalweg Elevation 139.53 139.50
LTOB Elevation 141.12 141.10
LTOB Max Depth 1.58 1.60
LTOB Cross-Sectional Area 4.88 4.82
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Appendix C:Stream Geomorphology Data—Cross-Section Plots
Cross-Section 6 (Pool) T3
130-
129-
i
1128
I
12i-
12G-
,i Fp 211 io
Distance(ft.)
•- MY 0 . kw I -- Bankfull Elevation-Based on As-Built Banklull Area
— Current Low Top of Bank
MVO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation - Based N/A N/A
on AB-Bankfull Area
Bank Height Ratio - Based N/A N/A
on AB-Bankfull Area
Thalweg Elevation 126.70 127.32
LTOB Elevation 128.16 128.35
LTOB Max Depth 1.46 1.03
LTOB Cross-Sectional Area 3.25 2.57
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Appendix C:Stream Geomorphology Data-Cross-Section Plots
Cross-Section 7 (Riffle)T3
13a-
129-
•
•
128-
Tst
L1l
.1/- k°
127-
126-
II sn L 3U
Distance(ft,)
MY 0 • MV a -- Bankfull Elevation-Bed on As-Built Bankfull Area
Current Low Top of Bank
MYO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation - Based
on AB Bankfull Area 127.58 127.56
Bank Height Ratio - Based
on AB-Bankfull Area 1.00 1.10
Thalweg Elevation 127.06 126.89
LTOB Elevation 127.58 127.63
LTOB Max Depth 0.52 0.74
1.82 LTOB Cross Sectional Area 1.50
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1.41
Sassarixa Swamp Mitigation Site
Appendix C:Stream Geomorphology Data—Cross-Section Plots
Cross-Section 8 (Riffle) T5 Reach 2
135-
134-
c
12 133- --- —_:
o
a
cis
LLI
1ii
2C1 Ai
Distance(ft.)
No n -•- MY -- Bankfull Elevation-Based on As-Built Banklull Area
Current Low Top of Bank
MVO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation - Based
on AB-Bankfull Area 133.06 133.12
Bank Height Ratio - Based
on AB-Bankfull Area 1.00 0.85
Thalweg Elevation 132.36 132.42
LTOB Elevation 133.06 133.02
LTOB Max Depth 0.70 0.60
LTOB Cross-Sectional Area 2.49 1.95
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Appendix C:Stream Geomorphology Data—Cross-Section Plots
Cross-Section 9 (Pool) T5 Reach 2
1-31
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r
t
— 1*4,4
o ,'
tO
LL1
1il
A. 3C 6U
Distance(ft.)
MY 6 • MY I -- Bankfull Elevation Based on As-Suil%Banklull Area
— Current Low lop of Bank
my() MY1 MY2 MY3 MY5 MY7
Bankfull Elevation - Based N/A N/A
on AB-Bankfull Area
Bank Height Ratio Based N/A N/A
on AB
131.03
Bankfull Area
Thalweg Elevation
132.53
131.50
LTOB Elevation
132.46
LTOB Max Depth 1.50 0.96
LTOB Cross Sectional Area 6.97 3.86
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Appendix C:Stream Geomorphology Data—Cross-Section Plots
Cross-Section 10 (Riffle) T6
1° -
ti
vim---•
Q 156-
m
LU
11 1 t< 211 30,
Distance(ft.)
My 0 -•- TAy I -- Bankfull Elevation-Based on As-Built Banklull Area
— Current Low Top of Bank
MVO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation - Based
on AB-Bankfull Area 156.43 156.50
Bank Height Ratio - Based
on AB-Bankfull Area 1.00 0.88
Thalweg Elevation 155.62 155.69
LTOB Elevation 156.43 156.40
LTOB Max Depth 0.81 0.71
LTOB Cross-Sectional Area 2.69 2.20
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Sassarixa Swamp Mitigation Site
Appendix C:Stream Geomorphology Data-Cross-Section Plots
Table 8. Baseline Stream Data Summary
Sassarixa Swamp Mitigation Site
DMS Project No. 100040
Monitoring Year 1-2021
PRE-EXISTING MONITORING BASELINE
CONDITIONS DESIGN (MYO)
Parameter T1 R2
Riffle Only Min Max n Min Max Min Max n
Bankfull Width(ft) 3.4 1 3.6 5.2 1
Floodprone Width(ft) 8 1 >7.9 200 1
Bankfull Mean Depth 1 1 0.3 0.4 1
Bankfull Max Depth 0.7 1 0.4 0.5 0.9 1
Bankfull Cross Sectional Area(ft2) 2.5 1 1.2 2.5 1
Width/Depth Ratio 4.9 1 11.0 11.0 1
Entrenchment Ratio 2.2 1 >2.2 34.6 1
Bank Height Ratio 3.0 1 1.0 1.2 1.0 1
Max part size(mm)mobilized at bankfull --- --- ---
Rosgen Classification G5 C5b/E5b C5b/E5b
Bankfull Discharge(cfs) 8.8 3.0 9.0
Sinuosity 1.20 1.20 1.20
Water Surface Slope(ft/ft)2 0.0190 0.0300 2 0.0250 0.0410 0.0322
Other --- --
Parameter T1 R3
Riffle Only Min Max n Min Max Min Max n
Bankfull Width(ft) 3.4 1 4.2 4.3 1
Floodprone Width(ft) 8 1 >9.2 90 1
Bankfull Mean Depth 1 1 0.4 0.4 1
Bankfull Max Depth 0.7 1 0.4 0.6 0.6 1
Bankfull Cross Sectional Area(ft2) 2.5 1 1.5 1.7 1
Width/Depth Ratio 4.9 1 12.0 11.1 1
Entrenchment Ratio 2.2 1 >2.2 21.9 1
Bank Height Ratio 3.0 1 1.0 1.2 1.0 1
Max part size(mm)mobilized at bankfull --- --- ---
Rosgen Classification G5 C5/E5 C5/E5
Bankfull Discharge(cfs) 8.8 3.5 4.3
Sinuosity 1.20 1.20 1.20
Water Surface Slope(ft/ft)2 0.0190 0.0300 2 0.0092 0.0250 0.0181
Other --- --
Table 8. Baseline Stream Data Summary
Sassarixa Swamp Mitigation Site
DMS Project No. 100040
Monitoring Year 1-2021
PRE-EXISTING MONITORING BASELINE
CONDITIONS DESIGN (MYO)
Parameter T2
Riffle Only Min Max n Min Max Min Max n
Bankfull Width(ft) 3 1 4.2 5.6 1
Floodprone Width(ft) 4 1 >9.2 75 1
Bankfull Mean Depth 0.5 1 0.4 0.4 1
Bankfull Max Depth 0.6 1 0.5 0.8 1
Bankfull Cross Sectional Area(ft2) 1.5 1 1.5 2.0 1
Width/Depth Ratio 6 1 12.0 15.7 1
Entrenchment Ratio 1.2 1 >2.2 13.4 1
Bank Height Ratio 6.5 1 1.0 1.2 1.0 1
Max part size(mm)mobilized at bankfull --- --- ---
Rosgen Classification G5 C5b/E5b C5b/E5b
Bankfull Discharge(cfs) 5.4 2.0 4.3
Sinuosity 1.14 1.40 1.40
Water Surface Slope(ft/ft)2 0.0290 1 0.0051 0.0064 0.0147
Other --- --
Parameter T3 R1
Riffle Only Min Max n Min Max Min Max n
Bankfull Width(ft) 3.2 4.2 2 3.6 4.7 1
Floodprone Width (ft) 5 24 2 >7.9 35 1
Bankfull Mean Depth 0.42 0.5 2 0.3 0.3 1
Bankfull Max Depth 0.7 0.56 2 0.4 0.5 0.5 1
Bankfull Cross Sectional Area(ft2) 1.7 2 1.0 1.5 1
Width/Depth Ratio 6.4 10 2 12.0 14.8 1
Entrenchment Ratio 1.1 7.1 2 >2.2 7.4 1
Bank Height Ratio 2.7 7.0 2 1.0 1.2 1.0 1
Max part size(mm)mobilized at bankfull --- --- ---
Rosgen Classification B5/G5 C5/E5b C5/E5b
Bankfull Discharge(cfs) 6.2 6.9 2 2.5 4.5
Sinuosity 1.16 1.20 1.20
Water Surface Slope(ft/ft)2 0.0340 1 0.0280 0.0330 0.0312
Other --- --
Table 8. Baseline Stream Data Summary
Sassarixa Swamp Mitigation Site
DMS Project No. 100040
Monitoring Year 1-2021
PRE-EXISTING MONITORING BASELINE
CONDITIONS DESIGN (MYO)
Parameter T5 R2
Riffle Only Min Max n Min Max Min Max n
Bankfull Width(ft) 3.1 1 5.6 5.9 1
Floodprone Width(ft) 27 1 >11 170 1
Bankfull Mean Depth 1.1 1 0.5 0.4 1
Bankfull Max Depth 1.4 1 0.6 0.8 0.7 1
Bankfull Cross Sectional Area(ft2) 3.5 1 2.7 2.5 1
Width/Depth Ratio 2.8 1 12.0 14.0 1
Entrenchment Ratio 8.7 1 >2.2 16.9 1
Bank Height Ratio 1.6 1 1.0 1.2 1.0 1
Max part size(mm)mobilized at bankfull --- --- ---
Rosgen Classification E5 C5/E5 C5/E5
Bankfull Discharge(cfs) 10.9 6.0 5.4
Sinuosity 1.20 1.40 1.40
Water Surface Slope(ft/ft)2 0.0120 1 0.0086 0.0170 0.0111
Other --- --
Parameter T6 R1
Riffle Only Min Max n Min Max Min Max n
Bankfull Width(ft) 4.1 1 6.4 6.0 1
Floodprone Width (ft) 7 1 >14 90 1
Bankfull Mean Depth 1.1 1 0.41 0.4 1
Bankfull Max Depth 1.5 1 0.5 0.7 0.8 1
Bankfull Cross Sectional Area(ft2) 4.4 1 3.3 2.7 1
Width/Depth Ratio 3.7 1 12.0 13.3 1
Entrenchment Ratio 1.7 1 >2.2 15.1 1
Bank Height Ratio 2.0 1 1.0 1.2 1.0 1
Max part size(mm)mobilized at bankfull --- --- ---
Rosgen Classification G5 C5/E5 C5/E5
Bankfull Discharge(cfs) 12.8 5.5 5.9
Sinuosity 1.10 1.20 1.20
Water Surface Slope(ft/ft)2 0.0086 1 0.0049 0.0150 0.0107
Other --- --
Table 9. Cross-Section Morphology Monitoring Summary
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
Cross-Section 1(Riffle) Cross-Section 2(Pool) Cross-Section 3(Riffle) Cross-Section 4(Riffle)
MYO MY1 MY2 MY3 MY5 MY7 MYO MY1 MY2 MY3 MY5 MY7 MYO MY1 MY2 MY3 MY5 MY7 MYO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation(ft)-Based on AB-Bankfull'Area 149.35 149.41 N/A N/A 130.69 130.77 141.46 141.52
Bank Height Ratio-Based on AB Bankfulll Area 1.00 0.93 N/A N/A 1.00 0.91 1.00 0.94
Thalweg Elevation 148.45 148.62 147.78 147.58 130.04 130.24 140.66 140.79
LTOB2 Elevation 149.35 149.36 148.82 148.77 130.69 130.72 141.46 141.48
LTOB2 Max Depth(ft) 0.90 0.74 1.04 1.19 0.64 0.48 0.80 0.69
LTOB2 Cross Sectional Area(ft2) 2.47 2.16 3.20 2.84 1.67 1.45 1.99 1.76
Cross-Section 5(Pool) Cross-Section 6(Pool) Cross-Section 7(Riffle) Cross-Section 8(Riffle)
MYO MY1 MY2 MY3 MY5 MY7 MYO MY1 MY2 MY3 MY5 MY7 MYO MY1 MY2 MY3 MY5 MY7 MYO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation(ft)-Based on AB-Bankfulll Area N/A N/A N/A N/A 127.58 127.56 133.06 133.12
Bank Height Ratio-Based on AB Bankfulll Area N/A N/A N/A N/A 1.00 1.10 1.00 0.85
Thalweg Elevation 139.53 139.51 126.70 127.32 127.06 126.89 132.36 132.42
LTOB2 Elevation 141.12 141.11 128.16 128.35 127.58 127.63 133.06 133.02
LTOB2 Max Depth(ft) 1.58 1.60 1.46 1.03 0.52 0.74 0.70 0.60
LTOB2 Cross Sectional Area(ft2) 4.88 4.82 3.25 2.57 1.50 1.82 2.49 1.95
Cross-Section 9(Pool) Cross-Section 10(Riffle)
MYO MY1 MY2 MY3 MY5 MY7 MYO MY1 MY2 MY3 MY5 MY7
Bankfull Elevation(ft)-Based on AB-Bankfulll Area N/A N/A 156.43 156.50
Bank Height Ratio-Based on AB Bankfulll Area N/A N/A 1.00 0.88
Thalweg Elevation 131.03 131.50 155.62 155.69
LTOB2 Elevation 132.53 132.46 156.43 156.40
LTOB2 Max Depth(ft) 1.50 0.96 0.81 0.71
LTOB2 Cross Sectional Area(ft2) 6.97 3.86 2.69 2.20
'Bank Height Ratio(BHR)takes the As-built bankful area as the basis for adjusting each subsequent years bankfull elevation.
2LTOB 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.
APPENDIX D. HYDROLOGY DATA
Table 10. Bankfull Events
Sassarixa Swamp Mitigation Site
DMS Project No. 100040
Monitoring Year 1-2021
Reach MY1(2021) MY2(2022) MY3(2023) MY4(2024) MY5(2025) MY6(2026) MY7(2027)
T1 Reach 3 2/16/2021
7/28/2021
T2 7/27/2021
10/9/2021
T3 Reach 1 7/28/2021
T5 Reach 2 1/24/2021
7/28/2021
Table 11. Rainfall Summary
Sassarixa Swamp Mitigation Site
DMS Project No. 100040
Monitoring Year 1-2021
MY1(2021) MY2(2022) MY3(2023) MY4(2024) MY5(2025) MY6(2026) MY7(2027)
Annual Precip *
Total 31.38
WETS 30th
44.35
Percentile
WETS 70th
52.31
Percentile
Normal
*Annual precipitation total was collected up until 11/9/2021.Data will be updated in MY2.
Table 12. Wetland Gauge Summary
Sassarixa Swamp Mitigation Site
DMS Project No. 100040
Monitoring Year 1-2021
Max.Consecutive Hydroperiod(Percentage)
Gauge
MY1(2021)* MY2(2022) MY3(2023) MY4(2024) MY5(2025) MY6(2026) MY7(2027)
1 124 Days
(47.5%)
Performance Standard: None
WETS Station:Smithfield 2 North
Growing Season:3/1/2021 to 11/16/2021(260 Days)
*Data was collected from 3/1/2021 to 11/9/2021 (253 Days).
Wetland Gauge Plot
Sassarixa Swamp Mitigation Site
DMS Project No. 100040
Monitoring Year 1-2021
Sassarixa Swamp Groundwater Gauge
a, a,
In Monitoring Year 1-2021 a N-1
-o C o
15 - o �- 3 10
o 124 max consecutive days 2
m o -1_
10 5 - o %--1- - 9
L w
5 8
0 - 7
M — o 0 0 0 �� o —� -- 6
L \\___
I 5 -"\476\7117k r ( o
> 10 4 i, ` o
J
5 as
T — 17 — 15cti G
15 / I 4 ;v
- L I 3,_kri-
20
I I
25 I / 2
30 \-\ rl II 1
3 5 I li �I ■ I .1 , J . I . I L I. I Y I , I II_ II L I I I i. 1 0
0 _0 i T 0 — to 0_ > V
V
L.L Q 5 Q N [) z 0
Daily Precipitation Gauge Depth — -Criteria Level o Soil Surface 30-Day Rolling Precip Total 30th&70th Percentile
Table 13. Recorded In-Stream Flow Events Summary
Sassarixa Swamp Mitigation Site
DMS Project No. 100040
Monitoring Year 1-2021
Max Consecutive Days/Total Days Meeting Success Criteria*
Reach MY1(2021)** MY2(2022) MY3(2023) MY4(2024) MY5(2025) MY6(2026) MY7(2027)
T1 Reach 2 44 Days/
108 Days
T2 103 Days/
177 Days
T3 Reach 1 108 Days/
190 Days
*Success criteria is 30 consecutive days of flow.
**Data was colleted through 11/9/2021.Data will be updated in MY2.
Recorded In-Stream Flow Events Plot
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
Sassarixa Swamp:T1 Reach 2
Monitoring Year 1-2021
163 - - 7
` \44 days of consecutive strea low - 6
162 i
16.k,•�,.+IY ._ ,____L
c
1 -- 1 1. .. . . ... . . . . . . ..—
- 5 a
W �I 3
12
_ I Wuul + a 161 . 1 �
1
--
/ 2
_ - 1
L
160 1 - 1 L■ I ■I J ■ I ■ . l I l . I■ I. I ilid ' I I II . L II1. I 0
Ul ` fl- J al Y O u
5 a 5 ¢ in o Z 0
Daily Precipitation —Water Level — — Thalweg — • •Bankfull 30-Day Rolling Precip Total 30th&70th Percentile
Recorded In-Stream Flow Events Plot
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
Sassarixa Swamp:T2
Monitoring Year 1-2021
141 7
I ` \
:03 days of consecutive stream f • _ 6
. �. —. - 5
140 I
I r _,_, , ...
c
0 !y_�.r�yT�� o
L
0.
a
W 139 F ., L I
rl \-- L
` L IZJ IIIL _ 1
138 - 1ILIII ■i J ■ i . l i l . �i■ i I ■ d + ' I L I it . L i i 1. i 0
C Ul ` 'a J a, Y O al
5 a 5 ¢ in O Z 0
Daily Precipitation —Water Level — — Thalweg — • •Bankfull 30-Day Rolling Precip Total 30th&70th Percentile
Recorded In-Stream Flow Events Plot
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
Sassarixa Swamp:T3 Reach 1
Monitoring Year 1-2021
153 7
I ` \
:08 days of consecutive stream f • - 6
x I AA LA - 4 .�
G
G •Y
a - 3 .a
a`
151r\ilii°14.14
I eM6wWNr WALWAaa
I - 2
\:— I
LJ III - 11 1L11111 J ■ 1 J . l 1 l . 1■ i I L J 1 ' I L I L II . 1 11s I 0
C Ul ` 'a J W Y O al
5 ¢ 5 ¢ in O Z 0
Daily Precipitation —Water Level — — Thalweg _ • •Bankfull 30-Day Rolling Precip Total 30th&70th Percentile
APPENDIX E. PROJECT TIMELINE AND CONTACT INFO
Table 14. Project Activity and Reporting History
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
11111. Activity or Deliverable Data Collection Complete Task Completion or Deliverable
Submission
Project Instituted NA January 2018
Mitigation Plan Approved November 2019 November 2019
Construction(Grading)Completed NA January 2021
Planting Completed NA March 2021
As-Built Survey Completed Febuary 2021 Febuary 2021
Stream Survey January 2021
Baseline Monitoring Document(Year 0) April 2021
Vegetation Survey March 2021
Easement Encroachment July 2021
In-Stream Vegetation Treatment September 2021
Stream Survey July 2021
Year 1 Monitoring December 2021
Vegetation Survey September 2021
Stream Survey 2022
Year 2 Monitoring December 2022
Vegetation Survey 2022
Stream Survey 2023
Year 3 Monitoring December 2023
Vegetation Survey 2023
Year 4 Monitoring December 2024
Stream Survey 2025
Year 5 Monitoring December 2025
Vegetation Survey 2025
Year 6 Monitoring December 2026
Stream Survey 2027
Year 7 Monitoring December 2027
Vegetation Survey 2027
Table 15. Project Contact Table
Sassarixa Swamp Mitigation Site
DMS Project No.100040
Monitoring Year 1-2021
Wildlands Engineering,Inc.
Designer 312 West Millbrook Road,Suite 225
Angela Allen,PE Raleigh,NC 27609
919.851.9986
Land Mechanic Designs,Inc.
Construction Contractor 126 Circle G Lane
Willow Spring,NC 27592
Monitoring Performers Wildlands Engineering,Inc.
Jason Lorch
Monitoring,POC
919.851.9986
APPENDIX F. Additional Documentation
WILDLANDS
ENGINEERING
November 30, 2021
Kim Browning
Wilmington District, Regulatory Division
U.S. Army Corps of Engineers
11405 Falls of Neuse Road
Wake Forest, NC 27587
Subject: IRT Comments on Sassarixa Swamp Mitigation Site Baseline Report and Record Drawings
Sassarixa Swamp, SAQ 2018-00432, DMS Project Number 100040
Dear Ms. Browning,
We have reviewed the comments on the MYO Report for the above referenced project dated August 27,
2021. Below are responses to each of your comments. For your convenience, the comments are
reprinted with our response in italics.
USACE Comments, Kim Browning:
1. Table 1:T1 R4,T1A,T1B and T1C are listed as Ell at 2.5:1 and part of the rationale for this ratio
was livestock exclusion and understory planting. Were these areas planted? If so, with what
species?The IRT agreed to a 4:1 ratio during the draft mitigation plan review but ultimately
accepted 2.5:1 based on increasing understory diversity and livestock exclusion.
The mitigation plan stated that T1A, T1B, and T1C would require, anting and the
exclusion of livestock to improve stream function (pg 24). However, it does not mention
understory planting. We could not find mention of understory planting in any comment
responses or meeting minutes.
2. The final mitigation plan planting list included 10%cherry bark oak in the floodplain and wetland
planting zone.This is not listed in the MYO report;which species were increased as a
substitution?
Cherrybark oak was only planted in the wetland areas. Of the 660 trees planted in the
wetland areas, 66 were cherrybark oak so the likelihood that we would see a species in
the veg plots is low.
3. In future monitoring reports it would be helpful to include planted stem percentages in Table 6.
Table 6 is an exported excel document from a DMS template. Wildlands can discuss the
possibility of including planted stem percentages in future reports.
4. Please include photo points of all crossings in future monitoring reports.
Photo of stream crossings are now in Appendix A.
WWildlands Engineering,Inc. (P)919.851.9986 • 312 West Millbrook Road,Suite 225 • Raleigh,NC 27609
WILDLANDS
ENGINEERING
5. Sediment is observed in the channel in several sections of T2 in the photos and on the video. Do
you anticipate that this will be flushed out of the system and form more defined channel
features?The area where the pond was removed appears to be trending towards developing
wetland features.
Yes, sediment has already started to make its way through the system.A more defined
channel can be seen on the site.
6. Please verify that a flow gauge was installed on T3. I was able to spot the gauge on T2 in the
photos but photo point 24 didn't capture the gauge.
Yes, a flow gauge was installed on T3. It is shown in Figure la and data is in Appendix D.
7. Is the large amount of rock observed in the video at the upper end of T2 the BMP shown on
Sheet 1.25? I noted that the PCN included impacts for grading wetland GG, but the design
sheets show the BMP in the wetland, which would be considered a permanent impact.
Treatment features should not be placed in jurisdictional features.
The PCN called out wetland GG as a permanent impact for grading. Wetland GG was
originally a manmade wetland similar to a small retention basin that had a pipe
connecting it to the pond. The original plan was to grade this into the proposed valley.
However, high runoff volumes from the cattle pastures during construction began to
cause erosion on the valley walls. Adding the BMP as a field adjustment was necessary
to prevent future erosion by slowing the runoff from the adjacent fields.
8. In future monitoring reports please provide an estimate of how many of the mature trees that
were still present after construction have died. I'm curious about the effects of construction
equipment and tree survival.
A visual assessment of mature tree mortality will be documented during every
monitoring report.
9. A lot of mature pine was noted in the video that will serve as a seed source in the buffer. Please
explain how this will be addressed if pine volunteers dominate the site.
Selective pine removal will be considered if pine volunteers dominate the site.
10. Was there only one random veg plot? I'd like to request one be located along T5 near cross
section 8.
Yes, one random veg plot was approved in the Mitigation Plan. T5 is mostly mature
forest with only a narrow corridor impacted during construction; therefore, only a small
area was planted.A random veg plot would be very difficult to place in this small area.
The random veg plot will be moved throughout the Site and can assess T5 if requested by
the IRT. Attached is as-built plan sheet 3.3 showing the narrow planting zone along T5.
WWildlands Engineering,Inc. (P)919.851.9986 • 312 West Millbrook Road,Suite 225 • Raleigh,NC 27609
WILDLANDS
ENGINEERING
DWR Comments, Erin Davis:
1. DWR appreciated the discussion of the storm damage and Old Olive Road sediment source
during construction. It was important to have that context given what was shown in the
photos, video, and restoration profile sheets.The excess sediment is concerning.Just a
reminder that any channel maintenance activities should be proposed within the next two
years, since the IRT wants to see the trajectory (stream/wetland) the credit features are
trending through the second half of the monitoring period.
Excess sediment has started to make its way through the channels. Wildlands does not
plan to remove excess sediment at this point.
2. It was noted that sections of T2 and Sassarixa Creek Reach 2 were stable and didn't require
construction of approved design structures. Since these areas were in backwater during
construction, how was stream stability assessed? Do these areas still appear stable under
summer baseflow conditions?
Stability was assessed by looking at the bed and bank features and bed slope.Summer
low flow conditions show a stable system in this area. The brush toe connects the
constructed channel to the confluence of Sassarixa Swamp and the bed shows no signs
of scour or erosion.
3. Sheet 1.25 shows two pipes, please confirm these structures were removed.
The field drains were not removed;however, they remain above the point of jurisdiction
on the channel. Removing the drains at the easement boundary was not viable due to
high elevation of the pipe outlets on steep side slopes of the floodplain and the amount
of concentrated flow they produced. If the drains were removed at the easement
boundary, there was a very high likelihood of significant erosion on the side slopes.
4. Sheet 5.9 has a note that an area was not fenced because of the swamp. Please confirm
whether the terminal boundaries of T4 and T5 were fenced as shown.
A site walk was completed on November 8, 2021 to verify the terminal boundaries of T4
and T5 are fenced as reported.
5. Looking at the video, it appears there are mature pines present within and/or adjacent to the
site. Has a pine management strategy been developed for the monitoring period?
A pine management strategy has not been developed at this point. Wildlands will assess
the situation and treat pines as needed.
WWildlands Engineering,Inc. (P)919.851.9986 • 312 West Millbrook Road,Suite 225 • Raleigh,NC 27609
WILDLANDS
ENGINEERING
6. Just to confirm, the video segment (9:30) of T2 is showing coir logs installed at the top of slope
along the terrace?
Yes, coir logs were installed at the top of slope along T2 to prevent erosion.
If you have any questions, please contact me by phone (919) 851-9986, or by email
(jlorch@wildlandseng.com).
Sincerely,
Jason Lorch, Monitoring Coordinator
Wildlands Engineering,Inc. (P)919.851.9986 • 312 West Millbrook Road,Suite 225 • Raleigh,NC 27609
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1. DEVIATIONS FROM THE DESIGN WILL BE 0' 100' 200' 300' z T r a
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