HomeMy WebLinkAbout20160406 Ver 1_Buckwater_97084_MY5_2023_20240205
MONITORING YEAR 5
ANNUAL REPORT
Final
January 2023
BUCKWATER MITIGATION SITE
Orange County, NC
Neuse River Basin
HUC 03020201
DMS Project No. 97084
NCDEQ Contract No. 006829
USACE Action ID No. 2016‐00873
DWR Project No. 2016‐0406v2
Data Collection Dates: January‐November 2023
PREPARED FOR:
NC Department of Environmental Quality
Division of Mitigation Services
1652 Mail Service Center
Raleigh, NC 27699‐1652
Wildlands Engineering, Inc. (P) 919.851.9986 • 312 West Millbrook Road, Suite 225 • Raleigh, NC 27609
January 29, 2024
Jeremiah Dow
Eastern Regional Supervisor
North Carolina DEQ Division of Mitigation Services
217 West Jones Street, Raleigh, NC 27603
RE: DMS Comments on the MY5 Report
Buckwater, Project ID #97084, DMS Contract 6829
Dear Mr. Dow:
We have reviewed the comments on the Monitoring Year 5 Report for the above referenced project
dated December 11, 2023 and have revised the report based on these comments. The revised
documents are submitted with this letter. Below are responses to each of your comments. For your
convenience, the comments are reprinted with our response in italics.
Stream Report:
1. Table 2 – since veg plot data was collected in MY5, we recommend changing the “Cumulative
Monitoring Results” column associated with vegetation success to something more quantitative, i.e.,
15 of 19 plots met success.
Response: Table 2 “Cumulative Monitoring Results” column associated with vegetation success
has been updated to reflect a quantitative result.
2. Section 2.3 – contains possible conflicting statements that majority of streams are “functioning as
designed” and then calls out XS 34 on T7A as a potential problem (pool filling), but then goes on to
say T7A is functioning as designed. What streams or reaches are not functioning as designed? Also,
pool XS 26 has lost about 60% of its cross‐sectional area while XS 34 has lost about 38%. Why was XS
34 singled out and not XS 26 (is XS 26 a result of point bar formation vs. XS 34 simply losing pool
depth)? Are the repair areas considered not functioning as intended for MY5?
Response: Section 2.3 has been updated to remove any conflicting statements. XS 26 is now
included in Section 2.3. It was not originally included because it developed a point bar and was
not considered aggrading as seen in XS 34. The repairs are stable and are functioning as
intended.
3. Figure 1b – a couple of the veg plots are not labeled, or the label is offset so it is difficult to see.
Response: Figure 1b has been updated to clearly show the veg plot labels.
4. Table 4 – the visual stream assessment tables indicate that that 100% of all structures were
functioning as intended. The structures that required repair in August should be included here,
especially as they weren’t identified for the MY4 report. In MY6, assuming the repairs were
successful, they would no longer need to be reported.
Response: Table 4 has been updated to reflect the structures that were repaired in August.
Wildlands Engineering, Inc. (P) 919.851.9986 • 312 West Millbrook Road, Suite 225 • Raleigh, NC 27609
5. Table 5 – shows no invasive areas of concern, but a 1.72‐acre polygon of privet treatment is shown
on the CCPV. The privet treatment polygon was included in this Table in the riparian buffer report.
Response: Table 5 has been updated to reflect the 1.72‐acre polygon of privet treatment.
6. Due to the number of sweetgum volunteers recorded in VPs 13 and 15, is there any plan, or need, to
expand sweetgum thinning efforts?
Response: Currently there is no plan to expand the sweetgum thinning efforts. The planted trees
height and density are on track to meet MY7 success criteria and do not seem to be outcompeted
by the sweetgum volunteers. However, Wildlands will continue to monitor this area throughout
the year and will thin if deemed necessary.
If you have any questions, please contact me by phone (919) 851‐9986, or by email
(jlorch@wildlandseng.com).
Sincerely,
Jason Lorch, Monitoring Coordinator
PREPARED BY:
312 West Millbrook Road, Suite 225
Raleigh, NC 27609
Jason Lorch
jlorch@wildlandseng.com
Phone: 919.851.9986
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final i
BUCKWATER MITIGATION SITE
Monitoring Year 5 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 ..................................................................................................... 1‐3
1.3 Project Attributes ....................................................................................................................... 1‐5
Section 2: MONITORING YEAR 5 DATA ASSESSMENT ........................................................................ 2‐1
2.1 Vegetative Assessment .............................................................................................................. 2‐1
2.2 Vegetation Areas of Concern and Management ....................................................................... 2‐1
2.3 Stream Assessment .................................................................................................................... 2‐2
2.4 Stream Areas of Concern and Management .............................................................................. 2‐2
2.5 Hydrology Assessment ............................................................................................................... 2‐2
2.6 Wetland Assessment .................................................................................................................. 2‐3
2.7 Monitoring Year 5 Summary ...................................................................................................... 2‐3
Section 3: REFERENCES .................................................................................................................... 3‐1
TABLES
Table 1: Project Quantities and Credits ..................................................................................................... 1‐1
Table 2: Goals, Performance Criteria, and Functional Improvements ...................................................... 1‐3
Table 3: Project Attributes ......................................................................................................................... 1‐5
FIGURES
Figure 1a‐e Integrated 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
Vegetation Plot Photographs
Appendix B Vegetation Plot Data
Table 6 Vegetation Plot Criteria Attainment Table
Table 7 Planted and Total Stem Counts
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
Table 11 Rainfall Summary
Bankfull Events Visual Observations
Table 12 Recorded In‐Stream Flow Events Summary
Recorded In‐Stream Flow Events Plot
Table 13 Groundwater Gauge Summary
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final ii
Groundwater Gauge Plot
Appendix E Project Timeline and Contact Info
Table 14 Project Activity and Reporting History
Table 15 Project Contact Table
Appendix F Additional Documentation
Stream Repair Plan
Stream Repair Area Photographs
IRT Site Walk Meeting Summary
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final 1‐1
Section 1: PROJECT OVERVIEW
The Buckwater Mitigation Site (Site) is located in central Orange County, approximately 4.5 miles
northeast of Hillsborough, NC. The Site lies in the Carolina Slate Belt of the Piedmont Physiographic
Province (USGS, 1998). Table 3 presents information related to the project attributes.
1.1 Project Quantities and Credits
The Site is located on eleven parcels under nine different landowners and a conservation easement was
recorded on 51.84 acres. Mitigation work within the Site included restoration, enhancement I, and
enhancement II 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
Reach ID
Mitigation
Plan
Footage
As‐Built
Footage
Mitigation
Category
Restoration
Level
Mitigation
Ratio
(X:1)
Comments
STREAMS
Buckwater
Reach 1 445 433 Warm EII 2.5 Grade Control Structures, Bank Repair,
Conservation Easement
Buckwater
Reach 2 160 162 Warm EI 1.5 Grade Control Structures, Bank Repair,
Planted Buffer
Buckwater
Reach 3 232 232 Warm EI 1.5 Grade Control Structures, Bank Repair,
Planted Buffer
Buckwater
Reach 4
2,067 2,071 Warm R 1.0 Full Channel Restoration, Planted Buffer,
Invasive Control
30 29 N/A N/A 0.0 Utility Crossing
206 209 Warm R 1.0 Full Channel Restoration, Planted Buffer
72 70 N/A N/A 0.0 Road Crossing
194 198 Warm R 1.0 Full Channel Restoration, Planted Buffer
Buckwater
Reach 5 486 485 Warm R 1.0 Full Channel Restoration, Planted Buffer,
Invasive Control
Buckwater
Reach 6
379 363 Warm R 1.0 Full Channel Restoration, Planted Buffer,
Invasive Control
118 30 N/A N/A 0.0 Utility Crossing
Buckwater
Reach 7
43 132 N/A N/A 0.0 Utility Crossing
891 885 Warm EII 2.5
Grade Control Structures, Bank Repair,
Enhancement Work Completed Beyond
Limits of Conservation Easement
Buckwater
Reach 8 188 185 Warm EII 2.5 Bank Repair, Conservation Easement
T1 Reach 1 366 375 Warm EI 1.5 Grade Control Structures, Planted Buffer
119 0 N/A N/A 0.0 Road Crossing
T1 Reach 2
123 244 N/A N/A 0.0 Utility Crossing
485 477 Warm R 1.0 Full Channel Restoration, Planted Buffer
25 43 N/A N/A 0.0 Utility Crossing
T2 587 592 Warm R 1.0 Full Channel Restoration, Planted Buffer
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final 1‐2
PROJECT MITIGATION QUANTITIES
Reach ID
Mitigation
Plan
Footage
As‐Built
Footage
Mitigation
Category
Restoration
Level
Mitigation
Ratio
(X:1)
Comments
STREAMS
T3 Reach 1
1,101 1,107 Warm EII 2.5 Livestock Exclusion, Grade Control
Structures, Planted Buffer
30 29 N/A N/A 0.0 Road Crossing
166 167 Warm EII 2.5 Livestock Exclusion, Grade Control
Structures, Planted Buffer
T3 Reach 2
658 665 Warm R 1.0 Full Channel Restoration, Planted Buffer,
Livestock Exclusion
63 93 N/A N/A 0.0 Road Crossing
193 197 Warm R 1.0 Full Channel Restoration, Planted Buffer,
Livestock Exclusion
T4 961 956 Warm R 1.0 Full Channel Restoration, Planted Buffer
T4A Reach
1 311 327 Warm R 1.0 Farm Pond Drained, Full Channel
Restoration, Planted Buffer
T4A Reach
2
175 155 Warm EII 2.5 Livestock Exclusion, Grade Control
Structures, Conservation Easement
72 75 N/A N/A 0.0 Road Crossing
T4A Reach
3
201 208 Warm R 1.0 Full Channel Restoration, Planted Buffer
64 66 N/A N/A 0.0 Road Crossing
T4B Reach
1 345 346 Warm R 1.0 Full Channel Restoration, Livestock
Exclusion
T5
548 554 Warm R 1.0 Full Channel Restoration, Planted Buffer,
Invasive Control
167 0 N/A N/A 0.0 Road Crossing
711 722 Warm R 1.0 Full Channel Restoration, Planted Buffer,
Farm Pond Drained
T6 Reach 1 695 697 Warm EII 2.5 Invasive Control, Bank Repair,
Conservation Easement
T6 Reach 2
458 458 Warm EII 2.5 Invasive Control, Bank Repair,
Conservation Easement
30 30 N/A N/A 0.0 Road Crossing
T6 Reach 3 620 623 Warm EI 1.5 Grade Control Structures, Planted Buffer,
Invasive Control
T6A 311 313 Warm EII 2.5 Grade Control Structures, Bank Repair,
Conservation Easement
T6B 136 136 Warm EII 2.5 Grade Control Structures, Bank Repair,
Conservation Easement
T7 Reach 1 322 320 Warm EI 1.5 Grade Control Structures, Planted Buffer
T7 Reach 2 363 367 Warm R 1.0 Full Channel Restoration, Planted Buffer
T7 Reach 3 356 357 Warm R 1.0 Full Channel Restoration, Planted Buffer
T7A 242 240 Warm EI 1.5 Grade Control Structures, Planted Buffer
T8 631 621 Warm EI 1.5 Grade Control Structures, Planted Buffer
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final 1‐3
PROJECT MITIGATION QUANTITIES
Reach ID
Mitigation
Plan
Footage
As‐Built
Footage
Mitigation
Category
Restoration
Level
Mitigation
Ratio
(X:1)
Comments
STREAMS
T9 73 73 Warm EII 2.5 Grade Control Structures, Conservation
Easement
Blue = Restoration Yellow = Enhancement I Orange = Enhancement II
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
Goal Objective/
Treatment Likely Functional Uplift Performance Criteria Measurement Cumulative
Monitoring Results
Improve the
stability of
stream
channels.
Construct stream
channels that will
maintain stable
cross‐sections,
patterns, and
profiles over time.
Significantly reduce
sediment inputs from
bank erosion. Reduce
shear stress on channel
boundary.
ER stays over 2.2 and
BHR below 1.2 with
visual assessments
showing progression
towards stability.
Cross‐section
monitoring and
visual
inspections.
Beaver dams were
removed along
Buckwater Creek
Reach 6. Cross‐
section surveys
show the channels
are stable.
Improve
in‐stream
habitat.
Install habitat
features such as
constructed riffles,
cover/lunker logs,
and brush toes into
restored/enhanced
streams. Add woody
materials to channel
beds. Construct
pools of varying
depth.
Increase and diversify
available habitats for
macroinvertebrates,
fish, and amphibians
leading to colonization
and increase in
biodiversity over time.
Add complexity
including LWD to
streams.
There is no required
performance
standard for this
metric.
N/A
Repairs to failing
structures along T3
Reach 2, T4, T4B
Reach 1, and T6
Reach 3 were
made to improve
quality of stream
habitat and overall
function.
Restoration Level Stream
Warm Cool Cold
Restoration 9,051.000
Enhancement I 1,715.334
Enhancement II 1,855.600
Preservation
Totals 12,621.934
Total Stream Credit 12,621.934
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final 1‐4
Goal Objective/
Treatment Likely Functional Uplift Performance Criteria Measurement Cumulative
Monitoring Results
Reconnect
channels
with
floodplains
and riparian
wetlands to
allow a
natural
flooding
regime.
Reconstruct stream
channels for
bankfull dimensions
and depth relative
to the existing
floodplain.
Raise water table and
hydrate riparian
wetlands. Allow more
frequent flood flows to
disperse on the
floodplain.
Two or more bankfull
events in separate
years and two
geomorphically
significant events
throughout the
monitoring period.
30 consecutive days
of flow for
intermittent
channels.
Crest gauges
and/or pressure
transducers
recording flow
elevations.
Bankfull or
gemorphically
significant events
were recorded on
all streams with
crest gauges. T4B,
T6, T7 Reach 2, and
T7A exceeded 30
days of
consecutive flow
during MY5.
Exclude
cattle from
project
streams.
Install fencing
around
conservation
easements adjacent
to cattle pastures.
Reduce and control
sediment inputs;
reduce and manage
nutrient inputs; reduce
and manage fecal
coliform inputs.
Contribute to
protection of or
improvement to a
Water Supply
Waterbody. Support
Falls Lake recovery
plan.
Prevent cattle from
accessing the stream.
Visually inspect
the Site to
ensure no
cattle
encroachment
is occurring.
No cattle
encroachments.
Restore and
enhance
native
floodplain
and
streambank
vegetation.
Plant native tree
and understory
species in riparian
zone and plant
appropriate species
on streambank.
Reduce sediment
inputs from bank
erosion and runoff.
Increase nutrient
cycling and storage in
floodplain. Provide
riparian habitat. Add a
source of LWD and
organic material to
stream.
Survival rate of 320
stems per acre at
MY3, 260 stems per
acre at MY5, and 210
stems per acre at
MY7. Height
requirement is 7 feet
at MY5 and 10 feet at
MY7.
One hundred
square meter
vegetation
plots are placed
on 2% of the
planted area of
the Site and
monitored
annually.
15 of 19 VPs met
the MY5 success
criteria. 3 of the 4
failing VPs are on
track to meet the
MY7 success
criteria. Invasive
vegetation was
removed in March
2023. Repair LODs
have been
replanted.
Permanently
protect the
project Site
from
harmful
uses.
Establish
conservation
easements on the
Site.
Protect Site from
encroachment on the
riparian corridor and
direct impact to
streams and wetlands.
Prevent easement
encroachment.
Visually inspect
the perimeter
of the Site to
ensure no
easement
encroachment
is occurring.
Mowing within the
easement occurred
along T6 where the
conservation
easement shares a
boundary with a
utility easement.
Boundary signage
will be checked,
refreshed, and
reposted in winter
2023.
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final 1‐5
1.3 Project Attributes
Prior to construction activities, the primary causes of Site degradation were stream channelization and
livestock grazing, both of which originated prior to 1938. Agricultural activity remained intensive
through the 1990s with several thousand beef cattle and three hog houses. Currently, approximately
100 cows graze on two properties and non‐forested land is used for cultivating hay. Several ponds along
Buckwater Creek, T3, and T5 were built between 1938 and 1955. According to 1955 aerial photography,
the top 1,000 feet of Buckwater Creek on the Site were channelized. Landowners maintained lower
Buckwater Creek below Walnut Hill Drive as a straightened channel until the 1990s. Table 3 below and
Table 8 in Appendix C present additional information on pre‐restoration conditions.
Table 3: Project Attributes
PROJECT INFORMATION
Project Name Buckwater
Mitigation Site County Orange County
Project Area (acres) 51.84 Project Coordinates 36.62349 N, 79.12911 W
PROJECT WATERSHED SUMMARY INFORMATION
Physiographic Province Piedmont River Basin Neuse
USGS HUC 8‐digit 03020201 USGS HUC 14‐digit 03020201030030
DWR Sub‐basin 03‐04‐01 Land Use Classification 63.9% Forested, 32.1%
Cultivated, 3.9% Impervious
Project Drainage Area (acres) 2,259 Percentage of Impervious Area 3.9%
RESTORATION TRIBUTARY SUMMARY INFORMATION
Parameters Buckwater
Creek T1 T2 & T3 T4, T4A, & T4B
Pre‐project length (feet) 5,557 1,073 2,728 2,216
Post‐project (feet) 5,223 852 2,728 1,992
Valley confinement
Moderately
Confined to
Unconfined
Unconfined Unconfined to
Confined
Moderately Confined
to Unconfined
Drainage area (acres) 2,259 1,216 218 77
Perennial, Intermittent, Ephemeral Perennial Perennial Perennial Intermittent
DWR Water Quality Classification WS‐IV
Dominant Stream Classification (existing) E4/G4c E4/B4c E4/G4c G4
Dominant Stream Classification (proposed) C4/E4 E4 B4/C4 B4
Dominant Evolutionary class (Simon) if applicable Stage V Stage IV
Parameters T5 & T6 T7 & T7A T8
Pre‐project length (feet) 3,184 1,235 620
Post‐project (feet) 3,054 1,284 621
Valley confinement Moderately
Confined
Moderately Confined to
Confined Moderately Confined
Drainage area (acres) 109 28 21
Perennial, Intermittent, Ephemeral Intermittent Intermittent Intermittent
DWR Water Quality Classification WS‐IV
Dominant Stream Classification (existing) E4/C4 E4/G4 E4
Dominant Stream Classification (proposed) B4/C4 B4/C4
Dominant Evolutionary class (Simon) if applicable Stage IV
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final 1‐6
REGULATORY CONSIDERATIONS
Parameters Applicable? Resolved? Supporting Documentation
Water of the United States ‐ Section 404 Yes Yes USACE Nationwide Permit No. 27 and
DWQ 401 Water Quality Certification
No. 4134. Water of the United States ‐ Section 401 Yes Yes
Endangered Species Act Yes Yes Categorical Exclusion in Mitigation Plan
(Wildlands, 2017) Historic Preservation Act Yes Yes
Coastal Zone Management Act (CZMA or CAMA) N/A N/A N/A
Essential Fisheries Habitat N/A N/A N/A
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final 2‐1
Section 2: MONITORING YEAR 5 DATA ASSESSMENT
Annual monitoring and site visits were conducted during MY5 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, 2017). Performance criteria for vegetation, stream, and hydrologic
assessment are located in Section 1.2 Table 2: Goals, Performance Criteria, and Functional
Improvements. Methodology for annual monitoring is presented in the MY0 Annual Report (Wildlands,
2019).
2.1 Vegetative Assessment
The MY5 vegetative survey was completed in October 2023. Vegetation monitoring resulted in a planted
stem density range of 162 to 647 stems per acre. Out of the 19 vegetation plots, 15 are meeting the
interim requirement of 260 stems per acre required at MY5. Vegetation plots 6, 7, 8, and 18 do not meet
the interim success criteria. However, vegetation plots 6 and 7 are only failing to meet requirements by
less than 10% with 243 stems per acre each and are on track to meet the final success criteria of 210
stems per acre. Despite the mortality of planted stems in plot 18, when accounting for volunteer
American elm this plot surpasses the final success criteria with the number of stems per acre totaling
243. Tulip poplar (Liriodendron tulipifera) and eastern red cedar (Juniperus virginiana) were approved by
the NCIRT as desirable species and were counted toward the MY5 vegetation success criteria.
Herbaceous vegetation is abundant across the Site and includes native pollinator species, which is
indicative of a healthy riparian habitat. The riparian habitat is helping to reduce nutrient runoff from the
cattle fields outside the easement and stabilizing the stream banks. Refer to Appendix A for Vegetation
Plot Photographs and the Vegetation Condition Assessment Table and Appendix B for Vegetation Plot
Data.
2.2 Vegetation Areas of Concern and Management
A small area of dense sweetgum (Liquidambar styraciflua) saplings was noted along T6 Reach 1
(Appendix 2). The sweetgum population was thinned to approximately 50% density in February 2023.
Wildlands will continue to monitor and manage this area for overgrowth of sweetgums.
Several small areas totaling 1.72 acres of Chinese privet (Ligustrum sinense) growth were noted along
Buckwater Creek Reaches 6 and 7, T2, and T4. The invasive removal was completed along Buckwater
Creek Reach 6, T2, and T4 in March 2023 (Appendix 2). Wildlands will continue to manage and remove
the remaining populations of Chinese privet along Buckwater Creek Reach 7 through winter 2023‐2024.
In April 2023, several constructed instream structures along T3 Reach 2, T4, T4B Reach 1, and T6 Reach 3
were observed to be performing poorly or failing (Appendix 2). In August 2023, mechanical repairs to
these structures were made which required equipment access into the easement. The resulting limits of
disturbance (LOD) for all four repair areas totaled approximately 0.20 acres. Replanting of the LODs was
completed in November 2023. A total of 140 stems were planted across the four repair area LODs and
livestakes will be added to the adjacent streambanks in winter 2023‐2024.
Soil amendments and ring sprays were conducted in April 2023. Soil amendments were applied locally to
trees with low heights across the site. Ring sprays were conducted in areas across the site with dense
fescue to reduce competition with planted trees.
In September 2023, it was noted that the utility company that maintains the electrical distribution
easement adjoining the easement boundary south of T6 mowed within the conservation easement. The
entire mowed area is approximately 0.04 acres. The encroachment has been addressed with the utility
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final 2‐2
company and approximately one dozen containerized trees of species included in the approved planting
list were planted in the mowed area in November 2023. Wildlands will check, refresh, and repost
boundary signage throughout the site in winter 2023‐2024.
2.3 Stream Assessment
Morphological surveys for MY5 were conducted in March 2023. All streams within the Site are stable. All
but two of the 36 cross‐sections show little to no change in the bankfull area and width‐to‐depth ratio,
and bank height ratios are less than 1.2. Cross‐section 26 on T5 developed a point bar after construction,
before the floodplain soils became stabilized. The cross‐section has remained stable since MY1, and the
riffle (cross‐section 27) shows no signs of filling in. T5 has been monitored closely since construction and
is not a concern. Cross‐section 34 on T7A shows some aggradation in the pool, but the riffle (cross‐
section 33) shows no aggradation. By multiple visual assessments, T7A is stable, and the sediment
source is believed to be coming from outside the conservation easement. Pebble count data is no longer
required per the September 29, 2021 Technical Work Group Meeting and is not included in this report.
The IRT reserves the right to request pebble count data/particle distributions if deemed necessary
during the monitoring period. Refer to Appendix A for the Visual Stream Morphology Stability
Assessment Table and Stream Photographs and Appendix C for Stream Geomorphology Data. See
Appendix A for stream photographs and visual assessment data.
2.4 Stream Areas of Concern and Management
Several small beaver dams were removed along Buckwater Creek Reaches 5 and 6 in February 2023 and
two beavers were trapped by APHIS. Beaver returned to the stream later in 2023 and an additional
beaver dam was removed along Buckwater Creek Reach 6 (Figure 1b) in November 2023 along with
several smaller dams on Buckwater Creek Reaches 4 and 5. A total of nine beavers were trapped by
APHIS. It is believed the beaver were displaced from further downstream outside of the conservation
easement and moved upstream to the Site. The area where the beaver dam occurred experienced some
herbaceous vegetation loss and sediment deposition. Some black willows (Salix nigra) along the top of
bank were gnawed, but the majority of planted stems and mature trees further from the stream
experienced little to no gnawing damage. The vegetation is expected to grow back over the next year.
The sediment deposition occurred on the point bars and is not a concern.
Several piping rock and log sills and a failed log riffle were observed along T3 Reach 2, T4, T4B Reach 1,
and T6 Reach 3, as well as a perched culvert below a crossing on T4. Mechanical repairs of these
structures were completed in August 2023. The locations of all stream repair areas and associated LODs
are shown on Figures 1c and 1d. Details of the failed structures and repairs completed are included in
Appendix F. All stream repairs are stable and functioning as intended.
2.5 Hydrology Assessment
Bankfull or geomorphically significant events were recorded on Buckwater Creek Reach 6, T1 Reach 2,
T2, T4, T5 (upstream and downstream of St. Mary’s Road), and T7 Reach 3. All channels have met the
hydrologic success criteria of two bankfull events in separate years and two geomorphically significant
events throughout the monitoring period.
In addition, the presence of baseflow must be documented on intermittent reaches (T4A, T4B, T6, T7
Reach 2, T7A, and T8) for a minimum of 30 consecutive days during a normal precipitation year. All of
the intermittent reaches met the criteria and maintained baseflow from 133 to 243 consecutive days.
The T6 flow gauge malfunctioned at the beginning of November 2023 and data from the beginning of
June 2023 to November was not available. Despite this, T6 still met baseflow requirements with the
limited data available. The gauge was replaced in mid‐November 2023.
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final 2‐3
The barotroll onsite malfunctioned in June 2023, but the faulty readings were not noticeable until the
beginning of November. Data from a barotroll at a site approximately 1.5 miles away (Martin Dairy
Mitigation Site) was used to replace the faulty readings from June to September 2023. The barotroll at
the Martin Dairy Mitigation Site malfunctioned and started producing faulty data at the beginning of
September 2023. Comparable barotroll data was not available for use between September 2023 and
mid‐November 2023 when the onsite barotroll could be replaced. Refer to Appendix D for hydrologic
data.
2.6 Wetland Assessment
Three groundwater gauges were installed and monitored within the existing wetlands zones. All gauges
were installed at locations requested by NCDWR and were downloaded and maintained quarterly. The
purpose of these gauges is to assess potential effects to wetland hydrology from the construction of
restored stream channels through these areas. The results of this monitoring are not tied to any success
criteria. The measured hydroperiod ranged from 3.0% to 38.1% of the growing season, consecutively.
Refer to Appendix D for wetland data.
Per the Mitigation Plan (Wildlands, 2017) wetlands were delineated in MY4 and results were compared
to the delineation completed pre‐construction in 2016. The results of the field investigation indicated
that overall, wetland area increased by 4.93 acres within the easement. Most of the wetland area
gained resulted from expansion of floodplain wetland boundaries, indicating that stream restoration has
had an overall positive effect on wetlands within the Site. Despite groundwater data recorded at
groundwater gauge one showing a shortened hydroperiod between MY1 and MY5, and groundwater
gauge two having an average hydroperiod of 8 days (3.0%), all wetland areas where groundwater gauges
were installed were determined to still be functioning as jurisdictional wetlands in MY4 according to the
1987 U.S. Army Corps of Engineers (USACE) Wetlands Delineation Manual and subsequent Eastern
Mountains and Piedmont Regional Supplement (2012). All wetland areas had evidence of hydric soils
and a hydroperiod within 12 inches for part or most of the year and vegetative communities dominated
by hydrophytic species.
2.7 Monitoring Year 5 Summary
Visual assessment indicated that the vast majority of stream reaches within the Site are geomorphically
stable and functioning as designed. This is especially true once mechanical repairs were completed.
Beaver dams were removed in February 2023 and again in November 2023, and the impacted
herbaceous and woody vegetation is expected to fill in over time. Vegetation has become well
established along the streambanks providing shade, stability, and a source of organic material. Repairs
were made to failing stream structures in August 2023 and replanting of the LODs was completed in
November 2023. An invasive vegetation treatment will be scheduled for 2024 to address remaining
scattered Chinese privet. All channels have met the hydrologic success criteria. Greater than 30 days of
consecutive flow were recorded on all stream reaches with flow gauges. Stream crossings are stable and
all fences are in good condition. Additional signage will be added where the utility company
encroachment occurred; no other encroachments have occurred.
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.
Buckwater Mitigation Site
Monitoring Year 5 Annual Report ‐ Final 3‐1
Section 3: 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.
Lee, M.T., Peet, R.K., S.D., Wentworth, T.R. 2008. CVS‐EEP Protocol for Recording Vegetation Version
4.2.
Rosgen, D. L. 1994. A classification of natural rivers. Catena 22:169‐199.
United States Army Corps of Engineers. 2003. Stream Mitigation Guidelines. USACE, NCDENR‐DWQ,
USEPA, NCWRC.
Wildlands Engineering, Inc. 2019. Buckwater Mitigation Project As‐Built Baseline Report. DMS, Raleigh,
NC.
Wildlands Engineering, Inc. 2017. Buckwater Mitigation Project Mitigation Plan. DMS, Raleigh, NC.
T
T5
T
T2
T3
Reach 1
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Reach
T6AT6
Reach 1
TA
T6
Reach 3
T3
Reach 2
T6
Reach 2 T1 Reach 2
T6B
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Reach
T1
Reach 1
T
Reach 3
T
Reach 2
T
Reach 1
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Reach 1
T
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Reach 1
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Reach 1 TA
Reach 3
TA
Reach 2
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Reach 2
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Reach
BXcNZaWeU &UeeN
Reach 3
BXcNZaWeU &UeeN
Reach 6
BXcNZaWeU &UeeN
Reach 5
Figure 1. Integrated Current Condition Plan View
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Orange County, NC
0 800400 Feet
2021 Aerial Photography
Conservation Easement
Internal Crossing
Encroachment (0.041 acres)
Existing Wetlands (2016)
Vegetaton Plots - MY5
Criteria Met
Criteria Not Met
Vegetation Area of Concern - MY5
Repair Replanting
Chinese Privet Removal
Sweetgum Thinning
^treaŵ ApproaĐh
Restoration
Enhancement I
Enhancement II
No Credit
Utility Easement
Cross-Sections
Stream Area of Concern - MY5
Beaver Dam
Stream Repair Area
Groundwater Gauges (Not for Credit)
Flow Gauges
Crest Gauges
Photo Points
Reach Breaks
&igƵre 1a
&igƵre 1ď
&igƵre 1Đ
&igƵre 1Ě
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T
T
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Reach 1
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Reach 3
BXcNZaWeU &UeeN
Reach
BXcNZaWeU &UeeN
Reach 2
PP 8
PP 7
PP 6
PP 5
PP 4
PP 3
PP 2
PP 1
PP 49
PP 48
PP 47
XS
7
X
S
5
X
S
2
X
S
3
XS
6
XS
4
X
S
8
XS 35
X
S
1
XS 36
1
0
0
+
0
0
1
0
5
+
0
0
800+0
0
12
0
+
0
0
125+0
0
805+00
11
0
+
0
0
115
+
0
0
PP 9
GWG 2
GWG 1
1
3
0
+
0
0
2
1
3
1
Figure 1a. Integrated Current Condition Plan View
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Orange County, NC
0 300150 Feet
2021 Aerial Photography
Conservation Easement
Structures
Existing Wetlands (2016)
Vegetaton Plots - MY5
Criteria Met
Stream Approach
Restoration
Enhancement I
Enhancement II
As-Built Bankfull
Utility Easement
Cross-Sections
Groundwater Gauges (Not for Credit)
Flow Gauges
Photo Points
Reach Breaks
!(
!(
!(
!(
!(
!(
!(
!A
!A
!A
!A
!A!A
^_
^_
^_
^_
^_^_
^_
^_
^_
^_
^_
^_
^_
^_
^_
^_
^_
^_
^_
!A
T2
T7A
T1
Reach 2 Buckwater Creek
Reach 7
T1
Reach 1
T7
Reach 3
T7
Reach 2
Buckwater Creek
Reach 8
Buckwater Creek
Reach 5
Buckwater Creek
Reach 6
PP 9
PP 41
PP 40
PP 26
PP 25
PP 46
PP 45
PP 44
PP 43
PP 19
PP 18
PP 15
PP 14
PP 12
PP 11
X
S
1
4
XS 15
X
S
1
1
XS
1
2
XS
9
XS 29
XS
3
1
X
S
1
0
XS 27
XS 19
XS 33
XS 32
XS 13
GWG 3
1
3
0
+
0
0
1
3
5
+
0
0
140
+
0
0
14
5
+
0
0
15
0
+
0
0
15
5
+
0
0
200+0
0
21
0
+
0
0
705+00
710+0
0
750+
0
0
T2
PP 41
PP 40
PP 26
PP 44
PP 18 PP 16
PP 15
PP 12
PP 11
PP 10 XS 30
XS 29
XS 27
325+00 XS 30
XS 29
XS 27
XS
2
8
XS 34
PP 13
PP 17
!A
5
4
1
6
18
3 17
Figure 1b. Integrated Current Condition Plan View
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Orange County, NC
¹0 300150 Feet
2021 Aerial Photography
W
a
l
n
u
t
H
i
l
l
D
r
Conservation Easement
Structures
Existing Wetlands (2016)
Vegetaton Plots - MY5
Criteria Met
Criteria Not Met
Stream Approach
Restoration
Enhancement I
Enhancement II
As-Built Bankfull
Utility Easement
Cross-Sections
!A Groundwater Gauges
(Not for Credit)
!A Crest Gauges
!A Flow Gauges
^_Photo Points
!(Reach Breaks
!A Barotroll
125+0
0
PP 9 PP 25 XS 29
XS
2
1
1
3
0
+
0
0
PP 28
PP 23
PP 22
T2
T3
Reach 2
T
Reach 1
TA
Reach 3
TA
Reach 2
PP 30
PP 29
PP 42
PP 10 XS 30
XS 29
X
S
2
2
XS 18
XS
1
7
XS 16
PP 31
PP 24
315+00
325+00
405+00
410
+
0
0
415+00
450+
0
0
3
1
0
+
0
0
T3
Reach 1
TB
Reach 1
TA
Reach 3
XS 30
XS 29
XS
2
1
XS
2
3
PP 31
8
11
1
10
3
Figure 1c. Integrated Current Condition Plan View
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Orange County, NC
0 300150 Feet
2021 Aerial Photography
Conservation Easement
Internal Crossing
Structures
Existing Wetlands (2016)
Vegetaton Plots - MY5
Criteria Met
Criteria Not Met
Vegetation Area of Concern - MY5
Repair Replanting
Chinese Privet Removal
Stream Approach
Restoration
Enhancement I
Enhancement II
As-Built Bankfull
Utility Easement
Cross-Sections
Stream Area of Concern - MY5
Stream Repair Area
Crest Gauges
Flow Gauges
Photo Points
Reach Breaks
TA
Reach 3
TA
Reach 2
PP 31
PP 27PP 21
PP 20
405+00
450+
0
0
3
1
0
+
0
0
T3
Reach 1
TB
Reach 1
TA
Reach 3
TA
Reach 1
XS
2
3
XS 20
PP 31
PP 27
305+0
0
3
0
0
+
0
0
Figure 1d. Integrated Current Condition Plan View
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Orange County, NC
0 300150 Feet
2021 Aerial Photography
Conservation Easement
Internal Crossing
Structures
Existing Wetlands (2016)
Vegetaton Plots - MY5
Criteria Met
Criteria Not Met
Vegetation Area of Concern - MY5
Repair Replanting
Stream Approach
Restoration
Enhancement II
As-Built Bankfull
Utility Easement
Cross-Sections
Stream Area of Concern - MY5
Stream Repair Area
Flow Gauges
Photo Points
Reach Breaks
PP 9
XS
2
6
XS
2
4
X
S
2
5
PP 39PP 38
PP 36
PP 35PP 34
PP 37
PP 33
PP 32
T5
T6AT6
Reach 1
T6
Reach 3
T6
Reach 2
T6B
510
+
0
0
51
5
+
0
0
52
0
+
0
0
60
0
+
0
0
650+00
5
0
5
+
0
0
14
13
12
15
Figure 1e. Integrated Current Condition Plan View
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Orange County, NC
0 300150 Feet
2021 Aerial Photography
Wa
l
n
u
t
H
i
l
l
D
r
Conservation Easement
Internal Crossing
Structures
Encroachment (0.041 acres)
Existing Wetlands (2016)
Vegetaton Plots - MY5
Criteria Met
Vegetation Area of Concern - MY5
Repair Replanting
Sweetgum Thinning
Stream Approach
Restoration
Enhancement I
Enhancement II
As-Built Bankfull
Utility Easement
Cross-Sections
Stream Area of Concern - MY5
Stream Repair Area
Crest Gauges
Flow Gauges
Photo Points
Reach Breaks
APPENDIX A. Visual Assessment Data
Table 4. Visual Stream Morphology Stability Assessment Table
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 ‐ 2023
Buckwater Creek Reach 2/3
394
788
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%
Grade Control Grade control structures exhibiting maintenance of
grade across the sill. 25 25 100%
Bank Protection Bank erosion within the structures extent of
influence does not exceed 15%. 58 58 100%
Buckwater Reach 4
2,478
4,956
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%
Grade Control Grade control structures exhibiting maintenance of
grade across the sill. 15 15 100%
Bank Protection Bank erosion within the structures extent of
influence does not exceed 15%. 4 4 100%
Visual assessment was completed on 11/1/2023.
Structure
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total
Number in
As‐Built
Amount of
Unstable
Footage
Assessed Stream Length
Assessed Bank Length
Bank
Totals:
% Stable,
Performing as
Intended
Structure
Visual assessment was completed on 11/1/2023.
% Stable,
Performing as
Intended
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total
Number in
As‐Built
Amount of
Unstable
Footage
Assessed Stream Length
Assessed Bank Length
Bank
Totals:
Table 4. Visual Stream Morphology Stability Assessment Table
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 ‐ 2023
Buckwater Creek Reach 5/6
848
1,696
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%
Grade Control Grade control structures exhibiting maintenance of
grade across the sill. 22 22 100%
Bank Protection Bank erosion within the structures extent of
influence does not exceed 15%. 30 30 100%
T1
1,444
2,888
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%
Grade Control Grade control structures exhibiting maintenance of
grade across the sill. 14 14 100%
Bank Protection Bank erosion within the structures extent of
influence does not exceed 15%. 7 7 100%
Visual assessment was completed on 11/1/2023.
Visual assessment was completed on 11/1/2023.
Totals:
Structure
% Stable,
Performing as
Intended
Assessed Stream Length
Assessed Bank Length
Bank
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total
Number in
As‐Built
Amount of
Unstable
Footage
Assessed Stream Length
Assessed Bank Length
Totals:
Bank
Structure
% Stable,
Performing as
Intended
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total
Number in
As‐Built
Amount of
Unstable
Footage
Table 4. Visual Stream Morphology Stability Assessment Table
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 ‐ 2023
T2/T3
2,136
4,272
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.40* 99%
40 99%
Grade Control Grade control structures exhibiting maintenance of
grade across the sill. 4 4 100%
Bank Protection Bank erosion within the structures extent of
influence does not exceed 15%. 17 17 100%
*Mechanical repairs were conducted August 2023.
T4/T4A
1,646
3,292
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.78 98%
78 98%
Grade Control Grade control structures exhibiting maintenance of
grade across the sill. 13* 14 93%
Bank Protection Bank erosion within the structures extent of
influence does not exceed 15%. 23 23 100%
*Nine piping rock sills were counted as one step pool structure at As‐Built. Mechanical repairs were conducted August 2023.
Visual assessment was completed on 11/1/2023.
Structure
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total
Number in
As‐Built
Amount of
Unstable
Footage
Assessed Stream Length
Assessed Bank Length
Bank
Totals:
% Stable,
Performing as
Intended
Structure
Visual assessment was completed on 11/1/2023.
% Stable,
Performing as
Intended
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total
Number in
As‐Built
Amount of
Unstable
Footage
Assessed Stream Length
Assessed Bank Length
Bank
Totals:
Table 4. Visual Stream Morphology Stability Assessment Table
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 ‐ 2023
T4B
346
692
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.50* 93%
50 93%
Grade Control Grade control structures exhibiting maintenance of
grade across the sill. 1* 2 50%
Bank Protection Bank erosion within the structures extent of
influence does not exceed 15%. 5 5 100%
*Six piping rock sills were counted as one step pool structure at As‐Built. Mechanical repairs were conducted August 2023.
T5/T6
3,503
7,006
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.40* 99%
40 99%
Grade Control Grade control structures exhibiting maintenance of
grade across the sill. 00 N/A
Bank Protection Bank erosion within the structures extent of
influence does not exceed 15%. 13 13 100%
*Mechanical repairs were conducted August 2023.
Visual assessment was completed on 11/1/2023.
Visual assessment was completed on 11/1/2023.
% Stable,
Performing as
Intended
Structure
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total
Number in
As‐Built
Amount of
Unstable
Footage
Assessed Stream Length
Assessed Bank Length
Bank
Totals:
% Stable,
Performing as
Intended
Structure
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total
Number in
As‐Built
Amount of
Unstable
Footage
Assessed Stream Length
Assessed Bank Length
Bank
Totals:
Table 4. Visual Stream Morphology Stability Assessment Table
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 ‐ 2023
T7
1,044
2,088
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%
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%. 20 20 100%
T7A
240
480
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%
Grade Control Grade control structures exhibiting maintenance of
grade across the sill. 0 0 N/A
Bank Protection Bank erosion within the structures extent of
influence does not exceed 15%. 2 2 100%
Visual assessment was completed on 11/1/2023.
Visual assessment was completed on 11/1/2023.
Structure
% Stable,
Performing as
Intended
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total
Number in
As‐Built
Amount of
Unstable
Footage
Assessed Stream Length
Assessed Bank Length
Bank
Totals:
% Stable,
Performing as
Intended
Structure
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total
Number in
As‐Built
Amount of
Unstable
Footage
Assessed Stream Length
Assessed Bank Length
Bank
Totals:
Table 4. Visual Stream Morphology Stability Assessment Table
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 ‐ 2023
T8
621
1,242
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%
Grade Control Grade control structures exhibiting maintenance of
grade across the sill. 0 0 N/A
Bank Protection Bank erosion within the structures extent of
influence does not exceed 15%. 6 6 100%
Visual assessment was completed on 11/1/2023.
% Stable,
Performing as
Intended
Structure
Major Channel Category Metric
Number
Stable,
Performing
as Intended
Total Number in
As‐Built
Amount of
Unstable
Footage
Assessed Stream Length
Assessed Bank Length
Bank
Totals:
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 ‐ 2023
Planted Acreage 23.60
Vegetation Category Definitions
Mapping
Threshold
(ac)
Combined
Acreage
% of Planted
Acreage
Bare Areas Very limited cover of both woody and herbaceous material. 0.10 0 0%
Low Stem Density
Areas
Woody stem densities clearly below target levels based on current MY stem count
criteria.0.10 0 0%
0.00 0%
Areas of Poor Growth
Rates
Planted areas where average height is not meeting current MY Performance
Standard.0.25 0 0%
0.00 0%
Easement Acreage 51.84
Vegetation Category Definitions
Mapping
Threshold
(ac)
Combined
Acreage
% of
Easement
Acreage
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
*Chinese privet (Ligustrum sinense) was chemically treated along a 1.72‐acre polygon in March 2023.
** Mowing occurred within the easement near T6 during maintenance of the adjacent utility easement.
Table 5. Vegetation Condition Assessment Table
Total
Cumulative Total
1 Encroachments Noted
/ 0.04 ac**
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. Invasive species included in
summation above should be identified in report summary.
0.10 1.72* 3%
STREAM PHOTOGRAPHS
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 1 Buckwater R1 – upstream (3/28/2023) PHOTO POINT 1 Buckwater R1 – downstream (3/28/2023)
PHOTO POINT 2 Buckwater R1 – upstream (3/28/2023) PHOTO POINT 2 Buckwater R1 – downstream (3/28/2023)
PHOTO POINT 3 Buckwater R3 – upstream (3/28/2023) PHOTO POINT 3 Buckwater R3 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 4 Buckwater R4 – upstream (3/28/2023) PHOTO POINT 4 Buckwater R4 – downstream (3/28/2023)
PHOTO POINT 5 Buckwater R4 – upstream (3/28/2023) PHOTO POINT 5 Buckwater R4 – downstream (3/28/2023)
PHOTO POINT 6 Buckwater R4 – upstream (3/28/2023) PHOTO POINT 6 Buckwater R4 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 7 Buckwater R4 – upstream (3/28/2023) PHOTO POINT 7 Buckwater R4 – downstream (3/28/2023)
PHOTO POINT 8 Buckwater R4 – upstream (3/28/2023) PHOTO POINT 8 Buckwater R4 – downstream (3/28/2023)
PHOTO POINT 9 Buckwater R4 – upstream (3/28/2023) PHOTO POINT 9 Buckwater R4 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 10 Buckwater R4 – upstream (3/28/2023) PHOTO POINT 10 Buckwater R4 – downstream (3/28/2023)
PHOTO POINT 11 Buckwater R4 – upstream (3/28/2023) PHOTO POINT 11 Buckwater R4 – downstream (3/28/2023)
PHOTO POINT 12 Buckwater R5 – upstream (3/28/2023) PHOTO POINT 12 Buckwater R5 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 13 Buckwater R6 – upstream (3/28/2023) PHOTO POINT 13 Buckwater R6 – downstream (3/28/2023)
PHOTO POINT 14 Buckwater R7 – upstream (3/28/2023) PHOTO POINT 14 Buckwater R7 – downstream (3/28/2023)
PHOTO POINT 15 Buckwater R7 – upstream (3/28/2023) PHOTO POINT 15 Buckwater R7 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 16 Buckwater R8 – upstream (3/28/2023) PHOTO POINT 16 Buckwater R8 – downstream (3/28/2023)
PHOTO POINT 17 T1 Reach 1 – upstream (3/28/2023) PHOTO POINT 17 T1 Reach 1 – downstream (3/28/2023)
PHOTO POINT 18 T1 Reach 2 – upstream (3/28/2023) PHOTO POINT 18 T1 Reach 2 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 19 T1 Reach 2 – upstream (3/28/2023) PHOTO POINT 19 T1 Reach 2 – downstream (3/28/2023)
PHOTO POINT 20 T3 Reach 1 – upstream (3/28/2023) PHOTO POINT 20 T3 Reach 1 – downstream (3/28/2023)
PHOTO POINT 21 T3 Reach 1 – upstream (3/28/2023) PHOTO POINT 21 T3 Reach 1 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 22 T3 Reach 2 – upstream (3/28/2023) PHOTO POINT 22 T3 Reach 2 – downstream (3/28/2023)
PHOTO POINT 23 T3 Reach 2 – upstream (3/28/2023) PHOTO POINT 23 T3 Reach 2 – downstream (3/28/2023)
PHOTO POINT 24 T3 Reach 2 – upstream (3/28/2023) PHOTO POINT 24 T3 Reach 2 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 25 T2 – upstream (3/28/2023) PHOTO POINT 25 T2 – downstream (3/28/2023)
PHOTO POINT 26 T2 – upstream (3/28/2023) PHOTO POINT 26 T2 – downstream (3/28/2023)
PHOTO POINT 27 T4A Reach 1 – upstream (3/28/2023) PHOTO POINT 27 T4A Reach 1 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 28 T4 – upstream (4/6/2023) PHOTO POINT 28 T4 – downstream (4/6/2023)
PHOTO POINT 29 T4 – upstream (3/28/2023) PHOTO POINT 29 T4 – downstream (3/28/2023)
PHOTO POINT 30 T4 – upstream (3/28/2023) PHOTO POINT 30 T4 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 31 T4B Reach 1 – upstream (3/28/2023) PHOTO POINT 31 T4B Reach 1 – downstream (3/28/2023)
PHOTO POINT 32 T6 Reach 1 – upstream (3/28/2023) PHOTO POINT 32 T6 Reach 1 – downstream (3/28/2023)
PHOTO POINT 33 T6 Reach 1 – upstream (3/28/2023) PHOTO POINT 33 T6 Reach 1 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 34 T6 Reach 2 – upstream (3/28/2023) PHOTO POINT 34 T6 Reach 2 – downstream (3/28/2023)
PHOTO POINT 35 T6 Reach 3 – upstream (3/28/2023) PHOTO POINT 35 T6 Reach 3 – downstream (3/28/2023)
PHOTO POINT 36 T6 Reach 3 – upstream (3/28/2023) PHOTO POINT 36 T6 Reach 3 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 37 T6B – upstream (3/28/2023) PHOTO POINT 37 T6B – downstream (3/28/2023)
PHOTO POINT 38 T6A – upstream (3/28/2023) PHOTO POINT 38 T6A – downstream (3/28/2023)
PHOTO POINT 39 T5 – upstream (3/28/2023) PHOTO POINT 39 T5 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 40 T5 – upstream (3/28/2023) PHOTO POINT 40 T5 – downstream (3/28/2023)
PHOTO POINT 41 T5 – upstream (3/28/2023) PHOTO POINT 41 T5 – downstream (3/28/2023)
PHOTO POINT 42 T7 Reach 1 – upstream (3/28/2023) PHOTO POINT 42 T7 Reach 1 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 43 T7 Reach 2 – upstream (3/28/2023) PHOTO POINT 43 T7 Reach 2 – downstream (3/28/2023)
PHOTO POINT 44 T7 Reach 2 – upstream (3/28/2023) PHOTO POINT 44 T7 Reach 2 – downstream (3/28/2023)
PHOTO POINT 45 T7 Reach 3 – upstream (3/28/2023) PHOTO POINT 45 T7 Reach 3 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 46 T7A – upstream (3/28/2023) PHOTO POINT 46 T7A – downstream (3/28/2023)
PHOTO POINT 47 T8 – upstream (3/28/2023) PHOTO POINT 47 T8 – downstream (3/28/2023)
PHOTO POINT 48 T8 – upstream (3/28/2023) PHOTO POINT 48 T8 – downstream (3/28/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Stream Photographs
PHOTO POINT 49 T9 – upstream (3/28/2023) PHOTO POINT 49 T9 – downstream (3/28/2023)
VEGETATION PLOT PHOTOGRAPHS
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Vegetation Plot Photographs
VEG PLOT 1 (10/03/2023) VEG PLOT 2 (10/03/2023)
VEG PLOT 3 (10/03/2023) VEG PLOT 4 (10/03/2023)
VEG PLOT 5 (10/03/2023) VEG PLOT 6 (10/03/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Vegetation Plot Photographs
VEG PLOT 7 (10/03/2023) VEG PLOT 8 (10/03/2023)
VEG PLOT 9 (10/03/2023) VEG PLOT 10 (10/03/2023)
VEG PLOT 11 (10/03/2023) VEG PLOT 12 (10/03/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Vegetation Plot Photographs
VEG PLOT 13 (10/03/2023) VEG PLOT 14 (10/03/2023)
VEG PLOT 15 (10/24/2023) VEG PLOT 16 (10/03/2023)
VEG PLOT 17 (10/03/2023) VEG PLOT 18 (10/03/2023)
Buckwater Mitigation Site
Appendix A: Visual Assessment Data – Vegetation Plot Photographs
VEG PLOT 19 (10/24/2023)
APPENDIX B. Vegetation Plot Data
Table 6. Vegetation Plot Criteria Attainment Table
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Plot
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
No*
No
Success Criteria Met *Tract Mean
Yes
Yes
Yes
*Vegetation Plots 6 and 7 only failed to meet criteria by less than 10%.
Yes
79%
Yes
Yes
Yes
Yes
No
Yes
Yes
Yes
Yes
Yes
Yes
Yes
No*
Table 7. Planted and Total Stem Counts
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T
Acer negundo Box Elder Tree 222
Acer rubrum Red Maple Tree
Aesculus pavia Red Buckeye Shrub Tree 111
Betula nigra River Birch Tree 111222333222111
Carya Hickory spp. Tree
Celtis occidentalis Hackberry Shrub Tree
Diospyros virginiana American Persimmon Tree 1
Fraxinus pennsylvanica Green Ash Tree 333111222444112
Juglans nigra Black Walnut Tree 2 2 1
Juniperus virginiana Eastern Red Cedar Tree
Liquidambar styraciflua Sweet Gum Tree 2 1 1
Liriodendron tulipifera Tulip-poplar Tree 1 1 1 1
Nyssa biflora Swamp Tupelo Tree
Pinus taeda Loblolly Pine Tree 1
Platanus occidentalis Sycamore Tree 111555444222444444111
Pyrus calleryana Callery Pear Exotic
Quercus alba White Oak Tree 222 222
Quercus lyrata Overcup Oak Tree 333111
Quercus michauxii Swamp Chestnut OakTree 111 111
Quercus pagoda Cherrybark Oak Tree 111
Quercus phellos Willow Oak Tree 1 1 1 333111 111
Quercus shumardii Shumard Oak Shrub Tree 222111 222 111
Salix nigra Black Willow Tree
Ulmus Elm spp.Tree
Ulmus alata Winged Elm Tree
Ulmus americana American Elm Tree
Viburnum dentatum Arrow-wood Shrub Tree
778101010121213141414131314666666
558445668556889222556
283 283 324 405 405 405 486 486 526 567 567 567 526 526 567 243 243 243 243 243 243
Color for Density
Exceeds requirements by 10%
Exceeds requirements, but by less than 10%
Fails to meet requirements, by less than 10%
Fails to meet requirements by more than 10%
Volunteer species included in total
PnoLS: Number of planted stems excluding live stakes
P-all: All planted stems
T: Total stems
Scientific Name Common Name Species Type
VP 1VP 2VP 3VP 4VP 5VP 6VP 7
1
0.02
Stem count
size (ares)
size (ACRES)
Species count
Stems per ACRE
1
0.02
1
0.02
1
0.02
1
0.02
1
0.02
1
0.02
Current Plot Data (MY5 2023)
Table 7. Planted and Total Stem Counts
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Acer negundo Box Elder Tree
Acer rubrum Red Maple Tree
Aesculus pavia Red Buckeye Shrub Tree
Betula nigra River Birch Tree
Carya Hickory spp. Tree
Celtis occidentalis Hackberry Shrub Tree
Diospyros virginiana American Persimmon Tree
Fraxinus pennsylvanica Green Ash Tree
Juglans nigra Black Walnut Tree
Juniperus virginiana Eastern Red Cedar Tree
Liquidambar styraciflua Sweet Gum Tree
Liriodendron tulipifera Tulip-poplar Tree
Nyssa biflora Swamp Tupelo Tree
Pinus taeda Loblolly Pine Tree
Platanus occidentalis Sycamore Tree
Pyrus calleryana Callery Pear Exotic
Quercus alba White Oak Tree
Quercus lyrata Overcup Oak Tree
Quercus michauxii Swamp Chestnut Oak Tree
Quercus pagoda Cherrybark Oak Tree
Quercus phellos Willow Oak Tree
Quercus shumardii Shumard Oak Shrub Tree
Salix nigra Black Willow Tree
Ulmus Elm spp.Tree
Ulmus alata Winged Elm Tree
Ulmus americana American Elm Tree
Viburnum dentatum Arrow-wood Shrub Tree
Color for Density
Exceeds requirements by 10%
Exceeds requirements, but by less than 10%
Fails to meet requirements, by less than 10%
Fails to meet requirements by more than 10%
Volunteer species included in total
PnoLS: Number of planted stems excluding live stakes
P-all: All planted stems
T: Total stems
Scientific Name Common Name Species Type
Stem count
size (ares)
size (ACRES)
Species count
Stems per ACRE
PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T
111
12
222444555
222
21
444111 1333333
1
8 1167
111
444333111 555444334
111 444111
111222
111 333 222
111
222 111
111 111111
16
7
111
4448898814777151520111121161617
1125564454447712337778
162 162 162 324 324 364 324 324 567 283 283 283 607 607 809 445 445 850 647 647 688
VP 12VP 8 VP 9 VP 10 VP 11 VP 13 VP 14
1
0.02
1
0.02
1
0.02
1
0.02
1
0.02
1
0.02
Current Plot Data (MY5 2023)
1
0.02
Table 7. Planted and Total Stem Counts
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Acer negundo Box Elder Tree
Acer rubrum Red Maple Tree
Aesculus pavia Red Buckeye Shrub Tree
Betula nigra River Birch Tree
Carya Hickory spp. Tree
Celtis occidentalis Hackberry Shrub Tree
Diospyros virginiana American Persimmon Tree
Fraxinus pennsylvanica Green Ash Tree
Juglans nigra Black Walnut Tree
Juniperus virginiana Eastern Red Cedar Tree
Liquidambar styraciflua Sweet Gum Tree
Liriodendron tulipifera Tulip-poplar Tree
Nyssa biflora Swamp Tupelo Tree
Pinus taeda Loblolly Pine Tree
Platanus occidentalis Sycamore Tree
Pyrus calleryana Callery Pear Exotic
Quercus alba White Oak Tree
Quercus lyrata Overcup Oak Tree
Quercus michauxii Swamp Chestnut Oak Tree
Quercus pagoda Cherrybark Oak Tree
Quercus phellos Willow Oak Tree
Quercus shumardii Shumard Oak Shrub Tree
Salix nigra Black Willow Tree
Ulmus Elm spp.Tree
Ulmus alata Winged Elm Tree
Ulmus americana American Elm Tree
Viburnum dentatum Arrow-wood Shrub Tree
Color for Density
Exceeds requirements by 10%
Exceeds requirements, but by less than 10%
Fails to meet requirements, by less than 10%
Fails to meet requirements by more than 10%
Volunteer species included in total
PnoLS: Number of planted stems excluding live stakes
P-all: All planted stems
T: Total stems
Scientific Name Common Name Species Type
Stem count
size (ares)
size (ACRES)
Species count
Stems per ACRE
PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T
333
335444 111333
222
222111111222222
41
25 4 5
1
444444111111222
111
111
111
222 111
7
1
222111111
1111131313138885569916
445666557448556
445 445 526 526 526 526 324 324 324 202 202 243 364 364 647
VP 19VP 15 VP 16 VP 17 VP 18
0.02
Current Plot Data (MY5 2023)
1
0.02
1
0.02
1
0.02
1
0.02
1
Table 7. Planted and Total Stem Counts
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Acer negundo Box Elder Tree
Acer rubrum Red Maple Tree
Aesculus pavia Red Buckeye Shrub Tree
Betula nigra River Birch Tree
Carya Hickory spp. Tree
Celtis occidentalis Hackberry Shrub Tree
Diospyros virginiana American Persimmon Tree
Fraxinus pennsylvanica Green Ash Tree
Juglans nigra Black Walnut Tree
Juniperus virginiana Eastern Red Cedar Tree
Liquidambar styraciflua Sweet Gum Tree
Liriodendron tulipifera Tulip-poplar Tree
Nyssa biflora Swamp Tupelo Tree
Pinus taeda Loblolly Pine Tree
Platanus occidentalis Sycamore Tree
Pyrus calleryana Callery Pear Exotic
Quercus alba White Oak Tree
Quercus lyrata Overcup Oak Tree
Quercus michauxii Swamp Chestnut Oak Tree
Quercus pagoda Cherrybark Oak Tree
Quercus phellos Willow Oak Tree
Quercus shumardii Shumard Oak Shrub Tree
Salix nigra Black Willow Tree
Ulmus Elm spp.Tree
Ulmus alata Winged Elm Tree
Ulmus americana American Elm Tree
Viburnum dentatum Arrow-wood Shrub Tree
Color for Density
Exceeds requirements by 10%
Exceeds requirements, but by less than 10%
Fails to meet requirements, by less than 10%
Fails to meet requirements by more than 10%
Volunteer species included in total
PnoLS: Number of planted stems excluding live stakes
P-all: All planted stems
T: Total stems
Scientific Name Common Name Species Type
Stem count
size (ares)
size (ACRES)
Species count
Stems per ACRE
PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T PnoLS P-all T
444666666
356
111111222111999101010
30 30 32 30 30 32 33 33 33 22 22 24 34 34 35 41 41 41
1
222222444
226224224 1
30 30 32 29 29 30 32 32 38 33 33 33 34 34 34 34 34 34
103211
141
70 49 27 5 3
223111222222222222323232
1
231
51 51 52 51 51 57 53 53 58 47 47 49 56 56 56 62 62 62
1
10 10 10 12 12 12 19 19 19 5 5 5 10 10 10 11 11 11
8 8 8 10 10 11 12 12 12 13 13 13 25 25 25 22 22 22
7 7 7 11 11 11 16 16 16 10 10 10 13 13 13 13 13 13
333555888
11 11 11 13 13 14 17 17 18 10 10 10 33 33 33 33 33 33
999121212121212555888999
149103
74
112
15
555777777999131313151515
175 175 211 192 192 231 226 226 264 157 157 168 257 257 259 282 282 282
15 15 23 15 15 23 16 16 23 11 11 17 11 11 13 11 11 11
373 373 449 409 409 492 481 481 562 334 334 358 547 547 552 601 601 601
Annual Means
MY0 (2019)MY5 (2023) MY4 (2022) MY3 (2021) MY2 (2020) MY1 (2019)
19
0.47
19
0.47
19
0.47
19
0.47
19
0.47
19
0.47
APPENDIX C. Stream Geomorphology Data
Cross‐Section Plots
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 509.51 509.54 509.56 509.52 509.52
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.98 1.02 1.03 1.02
Thalweg Elevation 507.26 507.43 507.49 507.42 507.33
LTOB Elevation 509.51 509.51 509.61 509.59 509.59
LTOB Max Depth 2.25 2.08 2.12 2.17 2.26
LTOB Cross‐Sectional Area 31.89 31.23 32.94 33.42 32.60
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 504.68 504.61 504.59 504.61 504.66
LTOB Elevation 508.12 508.03 508.22 508.14 508.17
LTOB Max Depth 3.44 3.42 3.63 3.53 3.51
LTOB Cross‐Sectional Area 49.15 45.28 48.58 47.46 47.63
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 509.71 509.67 509.59 509.66 509.74
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 1.00 1.03 1.01 0.99
Thalweg Elevation 506.17 505.95 505.98 505.97 506.08
LTOB Elevation 509.71 509.65 509.85 509.70 509.70
LTOB Max Depth 3.54 3.70 3.87 3.73 3.62
LTOB Cross‐Sectional Area 55.32 54.90 61.52 56.15 54.37
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 505.91 505.94 505.98 505.99 506.04
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.99 0.95 0.95 0.97
Thalweg Elevation 503.75 503.83 503.80 503.83 503.90
LTOB Elevation 505.91 505.93 505.88 505.89 505.97
LTOB Max Depth 2.16 2.10 2.08 2.06 2.60
LTOB Cross‐Sectional Area 21.88 21.70 20.12 20.22 20.63
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 502.72 502.72 502.58 502.68 502.71
LTOB Elevation 506.10 506.05 506.10 506.09 506.08
LTOB Max Depth 3.38 3.33 3.52 3.41 3.37
LTOB Cross‐Sectional Area 50.42 47.80 49.84 48.40 47.11
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 500.92 500.73 500.71 500.73 501.03
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 1.16 1.17 1.19 1.02
Thalweg Elevation 499.75 498.96 498.97 498.92 498.89
LTOB Elevation 500.92 501.01 501.00 501.07 501.07
LTOB Max Depth 1.17 2.05 2.03 2.15 2.18
LTOB Cross‐Sectional Area 13.61 17.62 18.12 18.31 18.50
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 496.97 497.03 496.98 497.23 497.09
LTOB Elevation 500.69 500.88 500.92 500.85 500.90
LTOB Max Depth 3.72 3.85 3.94 3.62 3.81
LTOB Cross‐Sectional Area 38.82 39.83 41.79 39.42 39.68
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 496.69 496.75 496.74 496.73 496.74
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.88 0.93 0.94 0.95
Thalweg Elevation 494.96 495.03 495.06 495.01 494.99
LTOB Elevation 496.69 496.55 496.63 496.62 496.65
LTOB Max Depth 1.73 1.52 1.57 1.61 1.66
LTOB Cross‐Sectional Area 12.51 9.82 10.96 11.14 11.35
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/23/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 486.70 486.77 486.81 486.71 486.74
LTOB Elevation 488.72 488.74 488.72 488.74 488.78
LTOB Max Depth 2.02 1.97 1.91 2.03 2.04
LTOB Cross‐Sectional Area 21.71 21.23 20.04 21.57 21.46
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/23/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 488.49 488.59 488.57 488.59 488.62
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.94 0.99 0.97 0.95
Thalweg Elevation 485.98 486.11 486.12 486.08 486.15
LTOB Elevation 488.49 488.43 488.55 488.52 488.49
LTOB Max Depth 2.51 2.32 2.43 2.44 2.34
LTOB Cross‐Sectional Area 33.27 30.04 32.87 31.76 30.21
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/23/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 482.75 482.57 482.70 482.77 482.59
LTOB Elevation 486.68 486.46 486.67 486.69 486.78
LTOB Max Depth 3.93 3.89 3.97 3.92 4.19
LTOB Cross‐Sectional Area 52.40 45.99 50.03 49.81 49.93
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/23/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 487.04 487.13 487.11 487.15 487.19
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.97 0.99 0.97 0.98
Thalweg Elevation 484.46 484.68 484.67 484.63 484.60
LTOB Elevation 487.04 487.06 487.08 487.06 487.15
LTOB Max Depth 2.58 2.38 2.41 2.43 2.55
LTOB Cross‐Sectional Area 30.55 29.06 30.00 28.82 29.71
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/23/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 488.81 488.96 488.98 489.08 489.09
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.94 0.91 0.93 0.92
Thalweg Elevation 486.36 486.61 486.60 486.43 486.14
LTOB Elevation 488.81 488.82 488.78 488.88 488.68
LTOB Max Depth 2.45 2.21 2.18 2.45 2.70
LTOB Cross‐Sectional Area 31.45 28.29 27.01 27.28 25.91
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/23/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 487.70 487.79 487.77 487.76 487.88
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.96 0.98 1.00 0.99
Thalweg Elevation 485.22 485.58 485.43 485.41 485.46
LTOB Elevation 487.70 487.70 487.73 487.76 487.85
LTOB Max Depth 2.48 2.12 2.30 2.35 2.39
LTOB Cross‐Sectional Area 32.68 30.85 31.75 32.64 32.04
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/23/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 483.99 484.03 483.97 484.04 484.12
LTOB Elevation 487.21 487.66 487.65 487.49 487.71
LTOB Max Depth 3.22 3.63 3.68 3.45 3.59
LTOB Cross‐Sectional Area 42.23 55.47 52.77 44.48 50.72
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 503.36 503.16 503.14 503.23 503.28
LTOB Elevation 505.82 505.97 506.03 505.98 506.28
LTOB Max Depth 2.46 2.81 2.89 2.75 3.00
LTOB Cross‐Sectional Area 17.64 19.53 19.92 20.15 22.25
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 505.31 505.29 505.33 505.33 505.41
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 1.01 0.98 0.99 0.97
Thalweg Elevation 503.29 503.28 503.39 503.36 503.46
LTOB Elevation 505.31 505.32 505.28 505.31 505.34
LTOB Max Depth 2.02 2.04 1.89 1.95 1.88
LTOB Cross‐Sectional Area 15.32 15.70 14.66 15.09 14.30
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 494.17 494.21 494.22 494.20 494.23
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.98 0.99 1.00 0.93
Thalweg Elevation 493.00 492.92 492.99 492.91 492.93
LTOB Elevation 494.17 494.19 494.21 494.21 494.14
LTOB Max Depth 1.17 1.27 1.22 1.30 1.21
LTOB Cross‐Sectional Area 6.35 6.22 6.27 6.46 5.61
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 489.22 489.24 489.22 489.19 489.64
LTOB Elevation 491.10 491.21 491.16 491.14 491.16
LTOB Max Depth 1.88 1.97 1.94 1.95 1.52
LTOB Cross‐Sectional Area 13.58 13.41 13.08 12.29 11.69
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 539.53 539.62 539.61 539.74 539.65
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.92 0.88 0.82 0.80
Thalweg Elevation 538.83 538.89 538.83 538.82 539.03
LTOB Elevation 539.53 539.56 539.52 539.57 539.53
LTOB Max Depth 0.70 0.67 0.69 0.75 0.50
LTOB Cross‐Sectional Area 1.33 0.99 0.96 0.85 0.79
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 500.89 501.27 501.14 501.05 501.37
LTOB Elevation 502.51 502.53 502.59 502.64 502.70
LTOB Max Depth 1.62 1.26 1.45 1.59 1.33
LTOB Cross‐Sectional Area 6.66 5.33 5.75 5.63 5.20
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 502.09 502.23 502.18 502.16 502.19
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.86 0.94 1.04 1.09
Thalweg Elevation 501.12 501.44 501.20 501.22 501.23
LTOB Elevation 502.09 502.12 502.12 502.19 502.27
LTOB Max Depth 0.97 0.68 0.92 0.97 1.04
LTOB Cross‐Sectional Area 3.62 2.83 3.20 3.83 4.17
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 540.79 540.78 540.80 540.82 540.85
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.95 0.94 0.98 1.01
Thalweg Elevation 540.00 540.12 540.13 540.16 540.20
LTOB Elevation 540.79 540.75 540.76 540.81 540.86
LTOB Max Depth 0.79 0.63 0.63 0.65 0.69
LTOB Cross‐Sectional Area 2.14 1.96 1.96 2.03 2.14
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/23/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 517.07 516.99 517.06 517.11 517.15
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 1.02 1.01 0.96 0.97
Thalweg Elevation 515.82 515.39 515.40 515.54 515.49
LTOB Elevation 517.07 517.02 517.07 517.05 517.10
LTOB Max Depth 1.25 1.63 1.67 1.51 1.61
LTOB Cross‐Sectional Area 7.15 7.37 7.26 6.55 6.49
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/23/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 504.92 504.91 505.02 505.07 505.11
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 1.01 0.96 0.93 0.94
Thalweg Elevation 503.40 503.47 503.56 503.48 503.39
LTOB Elevation 504.92 504.93 504.97 504.96 505.01
LTOB Max Depth 1.52 1.46 1.41 1.48 1.62
LTOB Cross‐Sectional Area 8.45 7.85 7.98 7.67 7.55
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/23/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 502.32 503.13 502.96 502.87 503.06
LTOB Elevation 504.17 504.15 504.19 504.19 504.30
LTOB Max Depth 1.85 1.02 1.23 1.32 1.24
LTOB Cross‐Sectional Area 8.48 3.84 3.81 3.21 3.39
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 491.22 491.37 491.37 491.32 491.35
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.92 1.11 1.12 1.16
Thalweg Elevation 490.13 490.33 490.25 490.27 490.39
LTOB Elevation 491.22 491.29 491.49 491.45 491.51
LTOB Max Depth 1.09 0.96 1.24 1.18 1.15
LTOB Cross‐Sectional Area 4.55 3.92 5.36 5.28 5.73
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 488.27 488.39 488.28 488.25 488.3
LTOB Elevation 490.75 490.81 490.77 490.77 490.75
LTOB Max Depth 2.48 2.39 2.49 2.52 2.45
LTOB Cross‐Sectional Area 15.16 12.25 11.84 12.46 10.39
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 506.31 506.33 506.36 506.35 506.33
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.97 1.03 1.05 1.08
Thalweg Elevation 505.13 504.78 504.77 504.97 504.99
LTOB Elevation 506.31 506.29 506.41 506.41 506.44
LTOB Max Depth 1.18 1.51 1.64 1.44 1.45
LTOB Cross‐Sectional Area 7.40 6.98 7.89 8.08 8.56
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 504.22 504.17 504.15 504.25 504.43
LTOB Elevation 505.68 505.88 505.96 505.95 506.17
LTOB Max Depth 1.46 1.71 1.81 1.70 1.74
LTOB Cross‐Sectional Area 7.53 8.87 9.55 9.19 11.04
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 493.84 493.91 493.90 493.97 493.99
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.94 0.97 0.96 0.87
Thalweg Elevation 492.95 492.87 492.84 492.98 493.04
LTOB Elevation 493.84 493.84 493.87 493.93 493.86
LTOB Max Depth 0.89 0.97 1.03 0.95 0.82
LTOB Cross‐Sectional Area 4.56 4.03 4.31 4.29 3.44
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 485.52 485.59 485.58 485.63 485.57
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 1.01 0.98 0.92 0.99
Thalweg Elevation 484.65 484.69 484.68 484.67 484.71
LTOB Elevation 485.52 485.60 485.56 485.56 485.56
LTOB Max Depth 0.87 0.91 0.88 0.89 0.88
LTOB Cross‐Sectional Area 5.15 5.26 4.92 4.57 5.14
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 490.11 490.11 490.11 490.24 490.14
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.96 0.97 0.95 1.09
Thalweg Elevation 489.10 489.07 488.90 489.14 489.06
LTOB Elevation 490.11 490.07 490.07 490.18 490.23
LTOB Max Depth 1.01 1.00 1.17 1.04 1.17
LTOB Cross‐Sectional Area 3.31 3.06 3.08 2.96 3.95
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/15/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 487.87 488.42 488.43 488.85 488.93
LTOB Elevation 489.85 489.92 489.73 489.87 489.83
LTOB Max Depth 1.98 1.50 1.30 1.02 0.90
LTOB Cross‐Sectional Area 9.43 8.51 6.60 6.42 5.76
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area 529.20 529.29 529.27 529.30 529.25
Bank Height Ratio ‐ Based
on AB‐Bankfull Area 1.00 0.92 0.96 0.99 1.03
Thalweg Elevation 528.48 528.47 528.54 528.44 528.55
LTOB Elevation 529.20 529.22 529.24 529.29 529.27
LTOB Max Depth 0.72 0.75 0.70 0.85 0.72
LTOB Cross‐Sectional Area 2.61 2.24 2.46 2.54 2.84
Buckwater Mitigation Site
Appendix C: Stream Geomorphology Data – Cross‐Section Plots
Downstream (3/21/2023)
MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based
on AB‐Bankfull Area N/A N/A N/A N/A N/A
Thalweg Elevation 526.93 527.42 527.40 527.54 527.72
LTOB Elevation 528.62 528.78 528.84 528.96 529.03
LTOB Max Depth 1.69 1.36 1.44 1.42 1.31
LTOB Cross‐Sectional Area 6.71 5.98 6.75 6.69 7.31
Table 8. Baseline Stream Data Summary
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 ‐ 2023
Parameter
Riffle Only Min Max n Min Max Min Max n
Bankfull Width (ft)1 13.8 17.2 3
Floodprone Width (ft) 17 44 1 38 87 150 200 3
Bankfull Mean Depth (ft) 1.5 1.8 1 0.9 1.3 3
Bankfull Max Depth (ft) 2.1 2.2 1 1.2 1.5 1.7 2.2 3
Bankfull Cross Sectional Area (ft2)20.0 24.0 1 12.5 21.9 3
Width/Depth Ratio 7.3 8.6 1 13.5 15.3 3
Entrenchment Ratio 1.3 3.3 1 2.5 5.0 8.7 14.5 3
Bank Height Ratio 1.6 1.7 1 3
Max particle size (mm) mobilized at bankfull
Rosgen Classification
Bankfull Discharge (cfs)1
Sinuosity
Water Surface Slope (ft/ft)1
Other
Parameter
Riffle Only Min Max n Min Max Min Max n
Bankfull Width (ft)1 20.5 21.5 2
Floodprone Width (ft)1 40 91 2
Bankfull Mean Depth (ft)1 2
Bankfull Max Depth (ft)1 1.2 1.5 2.5 2.6 2
Bankfull Cross Sectional Area (ft2)1 30.6 33.6 2
Width/Depth Ratio 1 13.8 13.9 2
Entrenchment Ratio 1 2.2 5.0 9.3 9.8 2
Bank Height Ratio 12
Max particle size (mm) mobilized at bankfull
Rosgen Classification
Bankfull Discharge (cfs)1 91.0 100.0
Sinuosity
Water Surface Slope (ft/ft)1 0.0040 0.0070
Other
Parameter
Riffle Only Min Max n Min Max Min Max n
Bankfull Width (ft) 8.8 11.0 1 1
Floodprone Width (ft) 14 49 1 23 53 1
Bankfull Mean Depth (ft) 0.9 1.4 1 1
Bankfull Max Depth (ft) 1.2 1.8 1 1.2 1.3 1
Bankfull Cross Sectional Area (ft2)8.3 15.0 1 1
Width/Depth Ratio 7.9 9.4 1 1
Entrenchment Ratio 1.3 >5.6 1 2.2 5.0 1
Bank Height Ratio 1.4 2.0 1 1
Max particle size (mm) mobilized at bankfull
Rosgen Classification
Bankfull Discharge (cfs)1
Sinuosity
Water Surface Slope (ft/ft)1 0.0120 0.0200
Other
10.9
MONITORING BASELINE
(MY0)
9.1
100
PRE‐EXISTING
CONDITIONS
29.7
2.3
28.0
‐‐‐
Buckwater Creek Reach 4
13 17.6
14.0
22.5
1.3
DESIGN
1.14 1.30
1.0
8.3
1.3
2.0
0.0070
E4/G4c
80
0.0070
0.0060
G4c E4 E4
109.0
‐‐‐
200
1.5
1.0
0.0071
C4
53.0
1.30
Buckwater Creek Reach 5/6
1.40
1.8
‐‐‐‐‐‐
1.41
15
20
110
‐‐‐‐‐‐
1.40
10.6
0.0070
0.0170
1.0
E4/G4c
1.0
1.0
1.0
C4
12.0
1.6
19.0
78.0
T2
‐‐‐‐‐‐‐‐‐
0.0150
36.036
B4/C4 B4/C4
20
1.20 1.20 1.20
8.9
13.0
0.8 0.7
1.2
6.4
13.2
Table 8. Baseline Stream Data Summary
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 ‐ 2023
Parameter
Riffle Only Min Max n Min Max Min Max n
Bankfull Width (ft) 7.5 13 1 1
Floodprone Width (ft) 22 26 1 21 48 1
Bankfull Mean Depth (ft) 0.6 0.8 1 1
Bankfull Max Depth (ft) 1.1 1.3 1 0.9 1.1 1
Bankfull Cross Sectional Area (ft2)6.2 7.5 1 1
Width/Depth Ratio 9.2 23 1 1
Entrenchment Ratio 1.7 >3.4 1 2.2 5.0 1
Bank Height Ratio 1.2 1.7 1 1
Max particle size (mm) mobilized at bankfull
Rosgen Classification
Bankfull Discharge (cfs)1
Sinuosity 1
Water Surface Slope (ft/ft)1 0.0100 0.0230
Other
Parameter
Riffle Only Min Max n Min Max Min Max n
Bankfull Width (ft)1 3
Floodprone Width (ft)1 11 17 3
Bankfull Mean Depth (ft)1 3
Bankfull Max Depth (ft)1 0.7 0.9 3
Bankfull Cross Sectional Area (ft2)4.8 5.1 1 3
Width/Depth Ratio 1 3
Entrenchment Ratio 1 1.4 2.2 3
Bank Height Ratio 13
Max particle size (mm) mobilized at bankfull
Rosgen Classification
Bankfull Discharge (cfs)1
Sinuosity 1
Water Surface Slope (ft/ft)1
Other
Parameter
Riffle Only Min Max n Min Max Min Max n
Bankfull Width (ft) 6.1 8.9 1 6.1 8.6 2
Floodprone Width (ft) 10 22 1 20 46 100 200 2
Bankfull Mean Depth (ft)1 0.8 1.0 2
Bankfull Max Depth (ft) 0.9 1.4 1 0.8 1.0 1.1 1.5 2
Bankfull Cross Sectional Area (ft2)6.2 6.3 1 8.1 8.5 2
Width/Depth Ratio 9.7 13.0 1 4.5 8.7 2
Entrenchment Ratio 1.6 2.3 1 2.2 5.0 11.7 33.0 2
Bank Height Ratio 2.1 4.1 1 2
Max particle size (mm) mobilized at bankfull
Rosgen Classification
Bankfull Discharge (cfs)1
Sinuosity
Water Surface Slope (ft/ft)1
Other
14.4
13.0
1.01.0
0.8
7.3
2.0
13.0
13.6
20.8
PRE‐EXISTING
CONDITIONS DESIGN MONITORING BASELINE
(MY0)
T3
9.6
300
1.1
E4/Incised B4c C4 C4
26.0 66.0
1.30 1.201.20
26
0.8
0.0159
‐‐‐‐‐‐‐‐‐
T4
7.6 6.77.2
0.0180
0.6
4.3
11
1.3
1.6
150
0.5
1.0
9
0.6
70.0
1.20
1.0
1.10
G4 B4/C4 B4
C4
6.7
14.0
0.7
3.6
12.3
22.3
1.0
0.0239
13.0
1.30
0.0150 0.0138
1.01.0
Incised E4/C4 B4/C4
‐‐‐‐‐‐‐‐‐
1.10
21
0.0130
22.0 12.0
1.10 1.30
0.6
17
T5
9.7
0.0240
‐‐‐‐‐‐‐‐‐
0.0270
18.0
Buckwater Mitigation Site
DMS Project No. 97084
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area 509.51 509.54 509.56 509.52 509.56 N/A N/A N/A N/A N/A 509.71 509.67 509.59 509.66 509.74
Bank Height Ratio ‐ Based on AB Bankfull1 Area 1.00 0.98 1.02 1.03 1.02 N/A N/A N/A N/A N/A 1.00 1.00 1.03 1.01 0.99
Thalweg Elevation 507.26 507.43 507.49 507.42 507.33 504.68 504.61 504.59 504.61 504.66 506.17 505.95 505.98 505.97 506.08
LTOB2 Elevation 509.51 509.51 509.61 509.59 509.59 508.12 508.03 508.22 508.14 508.17 509.71 509.65 509.85 509.70 509.70
LTOB2 Max Depth (ft)2.25 2.08 2.12 2.17 2.26 3.44 3.42 3.63 3.53 3.51 3.54 3.70 3.87 3.73 3.62
LTOB2 Cross Sectional Area (ft2)31.89 31.23 32.94 33.42 32.60 49.15 45.28 48.58 47.46 47.63 55.32 54.90 61.52 56.15 54.37
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area 505.91 505.94 505.98 505.99 506.04 N/A N/A N/A N/A N/A 500.92 500.73 500.71 500.73 501.03
Bank Height Ratio ‐ Based on AB Bankfull1 Area 1.00 0.99 0.95 0.95 0.97 N/A N/A N/A N/A N/A 1.00 1.16 1.17 1.19 1.02
Thalweg Elevation 503.75 503.83 503.80 503.83 503.90 502.72 502.72 502.58 502.68 502.71 499.75 498.96 498.97 498.92 498.89
LTOB2 Elevation 505.91 505.93 505.88 505.89 505.97 506.10 506.05 506.10 506.09 506.08 500.92 501.01 501.00 501.07 501.07
LTOB2 Max Depth (ft)2.16 2.10 2.08 2.06 2.60 3.38 3.33 3.52 3.41 3.37 1.17 2.05 2.03 2.15 2.18
LTOB2 Cross Sectional Area (ft2)21.88 21.70 20.12 20.22 20.63 50.42 47.80 49.84 48.40 47.11 13.61 17.62 18.12 18.31 18.50
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area N/A N/A N/A N/A N/A 496.69 496.75 496.74 496.73 496.74 N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based on AB Bankfull1 Area N/A N/A N/A N/A N/A 1.00 0.88 0.93 0.94 0.95 N/A N/A N/A N/A N/A
Thalweg Elevation 496.97 497.03 496.98 497.23 497.09 494.96 495.03 495.06 495.01 494.99 486.70 486.77 486.81 486.71 486.74
LTOB2 Elevation 500.69 500.88 500.92 500.85 500.90 496.69 496.55 496.63 496.62 496.65 488.72 488.74 488.72 488.74 488.78
LTOB2 Max Depth (ft)3.72 3.85 3.94 3.62 3.81 1.73 1.52 1.57 1.61 1.66 2.02 1.97 1.91 2.03 2.04
LTOB2 Cross Sectional Area (ft2)38.82 39.83 41.79 39.42 39.68 12.51 9.82 10.96 11.14 11.35 21.71 21.23 20.04 21.57 21.46
1Bank Height Ratio (BHR) takes the As‐built bankful area as the basis for adjusting each subsequent years bankfull elevation.
Table 9. Cross‐Section Morphology Monitoring Summary
Monitoring Year 5 ‐ 2023
Cross‐Section 1 (Riffle)Cross‐Section 2 (Pool)Cross‐Section 3 (Riffle)
Buckwater Creek Reach 2 Buckwater Creek Reach 3
Buckwater Creek Reach 4
Buckwater Creek Reach 4
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.
Buckwater Creek Reach 5
Cross‐Section 7 (Pool)Cross‐Section 8 (Riffle)Cross‐Section 9 (Pool)
Cross‐Section 4 (Riffle)Cross‐Section 5 (Pool)Cross‐Section 6 (Riffle)
Buckwater Mitigation Site
DMS Project No. 97084
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area 488.49 488.59 488.57 488.59 488.62 N/A N/A N/A N/A N/A 487.04 487.13 487.11 487.15 487.19
Bank Height Ratio ‐ Based on AB Bankfull1 Area 1.00 0.94 0.99 0.97 0.95 N/A N/A N/A N/A N/A 1.00 0.97 0.99 0.97 0.98
Thalweg Elevation 485.98 486.11 486.12 486.08 486.15 482.75 482.57 482.70 482.77 482.59 484.46 484.68 484.67 484.63 484.60
LTOB2 Elevation 488.49 488.43 488.55 488.52 488.49 486.68 486.46 486.67 486.69 486.78 487.04 487.06 487.08 487.06 487.15
LTOB2 Max Depth (ft)2.51 2.32 2.43 2.44 2.34 3.93 3.89 3.97 3.92 4.19 2.58 2.38 2.41 2.43 2.55
LTOB2 Cross Sectional Area (ft2)33.27 30.04 32.87 31.76 30.21 52.40 45.99 50.03 49.81 49.93 30.55 29.06 30.00 28.82 29.71
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area 488.81 488.96 488.98 489.08 489.09 487.70 487.79 487.77 487.76 487.88 N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based on AB Bankfull1 Area 1.00 0.94 0.91 0.93 0.92 1.00 0.96 0.98 1.00 0.99 N/A N/A N/A N/A N/A
Thalweg Elevation 486.36 486.61 486.60 486.43 486.14 485.22 485.58 485.43 485.41 485.46 483.99 484.03 483.97 484.04 484.12
LTOB2 Elevation 488.81 488.82 488.78 488.88 488.68 487.70 487.70 487.73 487.76 487.85 487.21 487.66 487.65 487.49 487.71
LTOB2 Max Depth (ft)2.45 2.21 2.18 2.45 2.70 2.48 2.12 2.30 2.35 2.39 3.22 3.63 3.68 3.45 3.59
LTOB2 Cross Sectional Area (ft2)31.45 28.29 27.01 27.28 25.91 32.68 30.85 31.75 32.64 32.04 42.23 55.47 52.77 44.48 50.72
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area N/A N/A N/A N/A N/A 505.31 505.29 505.33 505.33 505.41 494.17 494.21 494.22 494.20 494.23
Bank Height Ratio ‐ Based on AB Bankfull1 Area N/A N/A N/A N/A N/A 1.00 1.01 0.98 0.99 0.97 1.00 0.98 0.99 1.00 0.93
Thalweg Elevation 503.36 503.16 503.14 503.23 503.28 503.29 503.28 503.39 503.36 503.46 493.00 492.92 492.99 492.91 492.93
LTOB2 Elevation 505.82 505.97 506.03 505.98 506.28 505.31 505.32 505.28 505.31 505.34 494.17 494.19 494.21 494.21 494.14
LTOB2 Max Depth (ft)2.46 2.81 2.89 2.75 3.00 2.02 2.04 1.89 1.95 1.88 1.17 1.27 1.22 1.30 1.21
LTOB2 Cross Sectional Area (ft2)17.64 19.53 19.92 20.15 22.25 15.32 15.70 14.66 15.09 14.30 6.35 6.22 6.27 6.46 5.61
1Bank Height Ratio (BHR) takes the As‐built bankful area as the basis for adjusting each subsequent years bankfull elevation.
T1 Reach 1 T1 Reach 2
Table 9. Cross‐Section Morphology Monitoring Summary
Monitoring Year 5 ‐ 2023
Cross‐Section 10 (Riffle)Cross‐Section 11 (Pool)Cross‐Section 12 (Riffle)
Buckwater Creek Reach 6
T3 Reach 2 T2
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.
Buckwater Creek Reach 5
Cross‐Section 16 (Pool)Cross‐Section 17 (Riffle)Cross‐Section 18 (Riffle)
Cross‐Section 13 (Riffle)Cross‐Section 14 (Riffle)Cross‐Section 15 (Pool)
Buckwater Mitigation Site
DMS Project No. 97084
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area N/A N/A N/A N/A N/A 539.53 539.62 539.61 539.74 539.65 N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based on AB Bankfull1 Area N/A N/A N/A N/A N/A 1.00 0.92 0.88 0.82 0.80 N/A N/A N/A N/A N/A
Thalweg Elevation 489.22 489.24 489.22 489.19 489.64 538.83 538.89 538.83 538.82 539.03 500.89 501.27 501.14 501.05 501.37
LTOB2 Elevation 491.10 491.21 491.16 491.14 491.16 539.53 539.56 539.52 539.57 539.53 502.51 502.53 502.59 502.64 502.70
LTOB2 Max Depth (ft)1.88 1.97 1.94 1.95 1.52 0.70 0.67 0.69 0.75 0.50 1.62 1.26 1.45 1.59 1.33
LTOB2 Cross Sectional Area (ft2)13.58 13.41 13.08 12.29 11.69 1.33 0.99 0.96 0.85 0.79 6.66 5.33 5.75 5.63 5.20
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area 502.09 502.23 502.18 502.16 502.19 540.79 540.78 540.80 540.82 540.85 517.07 516.99 517.06 517.11 517.15
Bank Height Ratio ‐ Based on AB Bankfull1 Area 1.00 0.86 0.94 1.04 1.09 1.00 0.95 0.94 0.98 1.01 1.00 1.02 1.01 0.96 0.97
Thalweg Elevation 501.12 501.44 501.20 501.22 501.23 540.00 540.12 540.13 540.16 540.20 515.82 515.39 515.40 515.54 515.49
LTOB2 Elevation 502.09 502.12 502.12 502.19 502.27 540.79 540.75 540.76 540.81 540.86 517.07 517.02 517.07 517.05 517.10
LTOB2 Max Depth (ft)0.97 0.68 0.92 0.97 1.04 0.79 0.63 0.63 0.65 0.69 1.25 1.63 1.67 1.51 1.61
LTOB2 Cross Sectional Area (ft2)3.62 2.83 3.20 3.83 4.17 2.14 1.96 1.96 2.03 2.14 7.15 7.37 7.26 6.55 6.49
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area 504.92 504.91 505.02 505.07 505.11 N/A N/A N/A N/A N/A 491.22 491.37 491.37 491.32 491.35
Bank Height Ratio ‐ Based on AB Bankfull1 Area 1.00 1.01 0.96 0.93 0.94 N/A N/A N/A N/A N/A 1.00 0.92 1.11 1.12 1.16
Thalweg Elevation 503.40 503.47 503.56 503.48 503.39 502.32 503.13 502.96 502.87 503.06 490.13 490.33 490.25 490.27 490.39
LTOB2 Elevation 504.92 504.93 504.97 504.96 505.01 504.17 504.15 504.19 504.19 504.30 491.22 491.29 491.49 491.45 491.51
LTOB2 Max Depth (ft)1.52 1.46 1.41 1.48 1.62 1.85 1.02 1.23 1.32 1.24 1.09 0.96 1.24 1.18 1.15
LTOB2 Cross Sectional Area (ft2)8.45 7.85 7.98 7.67 7.55 8.48 3.84 3.81 3.21 3.39 4.55 3.92 5.36 5.28 5.73
1Bank Height Ratio (BHR) takes the As‐built bankful area as the basis for adjusting each subsequent years bankfull elevation.
Cross‐Section 22 (Riffle)Cross‐Section 23 (Riffle)Cross‐Section 24 (Riffle)
Table 9. Cross‐Section Morphology Monitoring Summary
Monitoring Year 5 ‐ 2023
T2
Cross‐Section 19 (Pool)Cross‐Section 20 (Riffle)Cross‐Section 21 (Pool)
Cross‐Section 25 (Riffle)Cross‐Section 26 (Pool)Cross‐Section 27 (Riffle)
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.
T4A Reach 1T4
T4B Reach 1T6 Reach 3
T5
T4
Buckwater Mitigation Site
DMS Project No. 97084
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area N/A N/A N/A N/A N/A 506.31 506.33 506.36 506.35 506.33 N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based on AB Bankfull1 Area N/A N/A N/A N/A N/A 1.00 0.97 1.03 1.05 1.08 N/A N/A N/A N/A N/A
Thalweg Elevation 488.27 488.39 488.28 488.25 488.3 505.13 504.78 504.77 504.97 504.99 504.22 504.17 504.15 504.25 504.43
LTOB2 Elevation 490.75 490.81 490.77 490.77 490.75 506.31 506.29 506.41 506.41 506.44 505.68 505.88 505.96 505.95 506.17
LTOB2 Max Depth (ft)2.48 2.39 2.49 2.52 2.45 1.18 1.51 1.64 1.44 1.45 1.46 1.71 1.81 1.70 1.74
LTOB2 Cross Sectional Area (ft2)15.16 12.25 11.84 12.46 10.39 7.40 6.98 7.89 8.08 8.56 7.53 8.87 9.55 9.19 11.04
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area 493.84 493.91 493.90 493.97 493.99 485.52 485.59 485.58 485.63 485.57 490.11 490.11 490.11 490.24 490.14
Bank Height Ratio ‐ Based on AB Bankfull1 Area 1.00 0.94 0.97 0.96 0.87 1.00 1.01 0.98 0.92 0.99 1.00 0.96 0.97 0.95 1.09
Thalweg Elevation 492.95 492.87 492.84 492.98 493.04 484.65 484.69 484.68 484.67 484.71 489.10 489.07 488.90 489.14 489.06
LTOB2 Elevation 493.84 493.84 493.87 493.93 493.86 485.52 485.60 485.56 485.56 485.56 490.11 490.07 490.07 490.18 490.23
LTOB2 Max Depth (ft)0.89 0.97 1.03 0.95 0.82 0.87 0.91 0.88 0.89 0.88 1.01 1.00 1.17 1.04 1.17
LTOB2 Cross Sectional Area (ft2)4.56 4.03 4.31 4.29 3.44 5.15 5.26 4.92 4.57 5.14 3.31 3.06 3.08 2.96 3.95
MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7
Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area N/A N/A N/A N/A N/A 529.20 529.29 529.27 529.30 529.25 N/A N/A N/A N/A N/A
Bank Height Ratio ‐ Based on AB Bankfull1 Area N/A N/A N/A N/A N/A 1.00 0.92 0.96 0.99 1.03 N/A N/A N/A N/A N/A
Thalweg Elevation 487.87 488.42 488.43 488.85 488.93 528.48 528.47 528.54 528.44 528.55 526.93 527.42 527.40 527.54 527.72
LTOB2 Elevation 489.85 489.92 489.73 489.87 489.83 529.20 529.22 529.24 529.29 529.27 528.62 528.78 528.84 528.96 529.03
LTOB2 Max Depth (ft)1.98 1.50 1.30 1.02 0.90 0.72 0.75 0.70 0.85 0.72 1.69 1.36 1.44 1.42 1.31
LTOB2 Cross Sectional Area (ft2)9.43 8.51 6.60 6.42 5.76 2.61 2.24 2.46 2.54 2.84 6.71 5.98 6.75 6.69 7.31
1Bank Height Ratio (BHR) takes the As‐built bankful area as the basis for adjusting each subsequent years bankfull elevation.
Cross‐Section 31 (Riffle)Cross‐Section 32 (Riffle)Cross‐Section 33 (Riffle)
Table 9. Cross‐Section Morphology Monitoring Summary
Monitoring Year 5 ‐ 2023
T5
Cross‐Section 28 (Pool)Cross‐Section 29 (Riffle)Cross‐Section 30 (Pool)
Cross‐Section 34 (Pool)Cross‐Section 35 (Riffle)Cross‐Section 36 (Pool)
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.
T7 Reach 1
T7A T8
T7 Reach 2T7 Reach 3 T7A
APPENDIX D. Hydrology Data
Reach MY1 (2019) MY2 (2020) MY3 (2021) MY4 (2022) MY5 (2023) MY6 (2024) MY7 (2025)
Buckwater Creek
Reach 6 6/18/2019 2/6/2020*
5/21/2020
1/3/2021*
4/9/2021*4/6/20222 3/28/20232
T1 Reach 2 4/13/2019 2/6/2020*
5/21/2020***
3/17/2022
5/23/2022*
12/15/2022*
4/7/2023
T2 6/18/2019*2/6/2020*
5/21/2020***
3/12/2022
3/17/2022*
12/15/2022
4/7/2023
T4 4/14/2019*
6/18/2019
2/6/2020
5/21/2020
1/3/2021
3/31/2021*3/12/2022*
9/1/2023
9/27/2023
10/23/2023
T5: US of St.
Mary's Rd N/A 2/6/2020
5/21/2020
1/3/2021*
4/9/2021*1/3/2022* 10/24/2023
T5: DS of St.
Mary's Rd
4/13/2019
6/18/2019
2/6/2020
5/21/2020
1/3/2021*
4/9/2021*1/3/2022 9/3/2023*
10/24/2023
T7 Reach 3 6/18/2019* 2/6/2020
1/3/20211
4/9/2021*
1/3/2022
3/12/20221
12/15/2022
9/1/2023
9/26/2023
10/23/2023
MY1 (2019) MY2 (2020) MY3 (2021) MY4 (2022) MY5 (2023) MY6 (2024) MY7 (2025)
Annual Precip
Total 43.35 61.38 47.80 50.16 48.05*
WETS 30th
Percentile 43.75 43.73 43.79 43.52 43.92
WETS 70th
Percentile 51.13 50.88 51.30 51.01 51.42
Normal YYYY*
Annual Precipitation Source: Durham 11 W Station, Orange County, NC, State Climate Office (Approximately 10 miles south of the Site).
30 Year Avereage Precipitation Source: Chapel Hill 2 W Station, Orange County, NC, AgCIS (Approximately 12 miles south of the Site).
*Annual precipitation total was collected up until 11/14/2022. Data will be updated in MY6.
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Table 10. Bankfull Events
DMS Project No. 97084
Monitoring Year 5 - 2023
Table 11. Rainfall Summary
Buckwater Mitigation Site
*Only a geomorphically significant event. Not a bankfull event.
**No bankfull or geomorphically significant events discernible due to gauge freezing.
1. T7 Reach 3 recorded bankfull events on the flow gauge on T7 Reach 2.
2. Bankfull event recorded based on visual observations.
BANKFULL EVENTS
VISUAL OBSERVATIONS
Buckwater Mitigation Site
Appendix D: Hydrology Data – Bankfull Events Visual Observations
Buckwater Creek Reach 4 (3/28/2023) Buckwater Creek Reach 5 (3/28/2023)
Buckwater Mitigation Site
DMS Project No. 97084
MY1 (2019) MY2 (2020) MY3 (2021) MY4 (2022) MY5 (2023) MY6 (2024) MY7 (2025)
T4A 96 Days/
120 Days
70 Days/
216 Days
52 Days/
155 Days
63 Days/
179 Days
133 Days/
182 Days
T4B 63 Days/
91 Days
208 Days/
290 Days
188 Days/
263 Days
166 Days/
252 Days
160 Days/
193 Days
T6 73 Days/
103 Days
294 Days/
294 Days
238 Days/
280 Days
161 Days/
317 Days
150 Days/
150 Days**
T7 Reach 2 Not Installed 194 Days/
234 Days
146 Days/
171 Days
137 Days/
235 Days
156 Days/
174 Days
T7A 169 Days/
233 Days
133 Days/
281 Days
250 Days/
338 Days
221 Days/
317 Days
233 Days/
226 Days
T8 19 Days/
21 Days**
207 Days/
272 Days
101 Days/
196 Days
57 Days/
122 Days
243 Days/
243 Days
**Gauge malfunctioned.
*Success criteria is 30 consecutive days of flow.
Table 12. Recorded In-Stream Flow Events Summary
Monitoring Year 5 - 2023
Reach Max Consecutive Days/ Total Days Meeting Success Criteria*
Recorded In‐Stream Flow Events Plots
Monitoring Year 5 ‐ 2023
Buckwater Mitigation Site
DMS Project No. 97084
133 days of consecutive stream flow
Ja
n
Fe
b
Ma
r
Ap
r
Ma
y
Ju
n
Ju
l
Au
g
Se
p
Oc
t
No
v
De
c
0
1
2
3
4
5
6
7
8
9
539
540
541
542
Pr
e
c
i
p
i
t
a
t
i
o
n
(i
n
)
El
e
v
a
t
i
o
n
(f
t
)
Monitoring Year 5 ‐2023
Daily Precipitation Water Level Thalweg Bankfull 30‐Day Rolling Precip Total 30th & 70th Percentile
Buckwater Mitigation Site: T4A
Barotroll malfunctioned
9/1/2023. Replaced
on 11/13/2023.
Recorded In‐Stream Flow Events Plots
Monitoring Year 5 ‐ 2023
Buckwater Mitigation Site
DMS Project No. 97084
160 days of consecutive stream flow
Ja
n
Fe
b
Ma
r
Ap
r
Ma
y
Ju
n
Ju
l
Au
g
Se
p
Oc
t
No
v
De
c
0
1
2
3
4
5
6
7
8
9
539
540
541
542
Pr
e
c
i
p
i
t
a
t
i
o
n
(i
n
)
El
e
v
a
t
i
o
n
(f
t
)
Monitoring Year 5 ‐2023
Daily Precipitation Water Level Thalweg Bankfull 30‐Day Rolling Precip Total 30th & 70th Percentile
Buckwater Mitigation Site: T4B
Barotroll malfunctioned
9/1/2023. Replaced
on 11/13/2023.
Recorded In‐Stream Flow Events Plots
Monitoring Year 5 ‐ 2023
Buckwater Mitigation Site
DMS Project No. 97084
150 days of consecutive stream flow
Ja
n
Fe
b
Ma
r
Ap
r
Ma
y
Ju
n
Ju
l
Au
g
Se
p
Oc
t
No
v
De
c
0
1
2
3
4
5
6
7
8
9
95
96
97
98
Pr
e
c
i
p
i
t
a
t
i
o
n
(i
n
)
El
e
v
a
t
i
o
n
(f
t
)
Monitoring Year 5 ‐2023
Daily Precipitation Water Level Thalweg Bankfull 30‐Day Rolling Precip Total 30th & 70th Percentile
Buckwater Mitigation Site: T6
Transducer malfunctioned
5/31/2023. Replaced
on 11/13/2023.
Recorded In‐Stream Flow Events Plots
Monitoring Year 5 ‐ 2023
Buckwater Mitigation Site
DMS Project No. 97084
156 days of consecutive stream flow
Ja
n
Fe
b
Ma
r
Ap
r
Ma
y
Ju
n
Ju
l
Au
g
Se
p
Oc
t
No
v
De
c
0
1
2
3
4
5
6
7
8
9
496
497
498
499
Pr
e
c
i
p
i
t
a
t
i
o
n
(i
n
)
El
e
v
a
t
i
o
n
(f
t
)
Monitoring Year 5 ‐2023
Daily Precipitation Water Level Thalweg Bankfull 30‐Day Rolling Precip Total 30th & 70th Percentile
Buckwater Mitigation Site: T7 Reach 2
Barotroll malfunctioned
9/1/2023. Replaced
on 11/13/2023.
Recorded In‐Stream Flow Events Plots
Monitoring Year 5 ‐ 2023
Buckwater Mitigation Site
DMS Project No. 97084
233 days of consecutive stream flow
Ja
n
Fe
b
Ma
r
Ap
r
Ma
y
Ju
n
Ju
l
Au
g
Se
p
Oc
t
No
v
De
c
0
1
2
3
4
5
6
7
8
9
504
505
506
507
Pr
e
c
i
p
i
t
a
t
i
o
n
(i
n
)
El
e
v
a
t
i
o
n
(f
t
)
Monitoring Year 5 ‐2023
Daily Precipitation Water Level Thalweg Bankfull 30‐Day Rolling Precip Total 30th & 70th Percentile
Buckwater Mitigation Site: T7A
Barotroll malfunctioned
9/1/2023. Replaced
on 11/13/2023.
Recorded In‐Stream Flow Events Plots
Monitoring Year 5 ‐ 2023
Buckwater Mitigation Site
DMS Project No. 97084
243 days of consecutive stream flow
Ja
n
Fe
b
Ma
r
Ap
r
Ma
y
Ju
n
Ju
l
Au
g
Se
p
Oc
t
No
v
De
c
0
1
2
3
4
5
6
7
8
9
527.0
528.0
529.0
530.0
Pr
e
c
i
p
i
t
a
t
i
o
n
(i
n
)
El
e
v
a
t
i
o
n
(f
t
)
Monitoring Year 5 ‐2023
Daily Precipitation Water Level Thalweg Bankfull 30‐Day Rolling Precip Total 30th & 70th Percentile
Buckwater Mitigation Site: T8
Barotroll malfunctioned
9/1/2023. Replaced
on 11/13/2023.
Table 13. Groundwater Gauge Summary
Buckwater Mitigation Site
Monitoring Year 5 ‐ 2023
MY1 (2019) MY2 (2020) MY3 (2021) MY4 (2022) MY5 (2023)* MY6 (2024) MY7 (2025)
1 55 Days
(20.7%)
34 Days
(12.8%)
24 Days
(9.4%)
28 Days
(10.6%)
8 Days
(3.0%)
2 13 Days
(4.9%)
6 Days
(2.3%)
8 Days
(3.1%)
6 Days
(2.3%)
8 Days
(3.0%)
3 58 Days
(21.8%)
135 Days
(50.4%)
110 Days
(43.0%)
105 Days
(39.6%)
101 Days
(38.1%)
Daily Rainfall: Durham 11 W Station, Orange County, NC, State Climate Office
WETS Station (30th & 70th Percentile): Chapel Hill 2 W Station, Orange County, NC, AgCIS
Growing Season: 3/1/2021 to 11/11/2021 (255 Days)
DMS Project No. 97084
Summary of Groundwater Gauge Results for Monitoring Years 1 through 7
Gauge Max Consecutive Days During Growing Season (Percentage)
Performance Standard: None
Groundwater Gauge Plot
Monitoring Year 5 ‐ 2023
Buckwater Mitigation Site
DMS Project No. 97084
St
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8 max consecutive days
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
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‐50
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Monitoring Year 5 ‐2023
Daily Precipitation Gauge #1 Criteria Level Soil Surface 30‐Day Rolling Precip Total 30th & 70th Percentile
Buckwater Groundwater Gauge #1
Barotroll malfunctioned
9/1/2023. Replaced
on 11/13/2023.
Groundwater Gauge Plot
Monitoring Year 5 ‐ 2023
Buckwater Mitigation Site
DMS Project No. 97084
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8 max consecutive days
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
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‐50
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Monitoring Year 5 ‐2023
Daily Precipitation Gauge #2 Criteria Level Soil Surface 30‐Day Rolling Precip Total 30th & 70th Percentile
Buckwater Groundwater Gauge #2
Barotroll malfunctioned
9/1/2023. Replaced
on 11/13/2023.
Groundwater Gauge Plot
Monitoring Year 5 ‐ 2023
Buckwater Mitigation Site
DMS Project No. 97084
St
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101 max consecutive days
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
0
1
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9
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‐60
‐50
‐40
‐30
‐20
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Monitoring Year 5 ‐2023
Daily Precipitation Gauge #3 Criteria Level Soil Surface 30‐Day Rolling Precip Total 30th & 70th Percentile
Buckwater Groundwater Gauge #3
Barotroll malfunctioned
9/1/2023. Replaced
on 11/13/2023.
APPENDIX E. Project Timeline and Contact Info
DMS Project No. 97084
DMS Project No. 97084
Raleigh, NC 27609
919.851.9986
Beaver Removal February & November 2023
Monitoring, POC Jason Lorch
919.851.9986
Monitoring Performers Wildlands Engineering, Inc.
Year 6 Monitoring December 2024
Year 7 Monitoring Stream Survey 2025 December 2025Vegetation Survey 2025
Construction Contractor
Ecotone, Inc.
2120 High Point Rd
Forest Hill, MD 21050
Table 15. Project Contact Table
Buckwater Mitigation Site
Monitoring Year 5 - 2023
Designer
Nicole Macaluso Millns, PE
Wildlands Engineering, Inc.
312 West Millbrook Road, Suite 225
December 2023
Supplemental Planting November 2022Year 4 Monitoring December 2022October 2022Follow-Up Delineation
Sweetgum Thinning February 2023
Invasive Treatment March 2023
Soil Amendments & Ring Sprays April 2023
Stream Survey March 2023
Vegetation Survey October 2023
Year 5 Monitoring
Repair Area & Encroachment Planting November 2023
Stream Repairs August 2023
Vegetation Survey October 2021
February 2021
March 2021
Stream Survey
Replanting & Soil Amendments
Ring Sprays
April 2020
Vegetation Survey September 2020
Stream Survey May 2021
April 2019
August 2019
April 2020
August 2020
October 2019
Baseline Monitoring Document (Year 0)Stream Survey April 2019 July 2019Vegetation Survey April 2019
As-Built Survey Completed May 2021 May 2021
Table 14. Project Activity and Reporting History
Buckwater Mitigation Site
Monitoring Year 5 - 2023
Activity or Deliverable Data Collection Complete Task Completion or Deliverable
Submission
Project Instituted NA March 2016
Mitigation Plan Approved December 2017 December 2017
Year 3 Monitoring December 2021
December 2020
August 2020
Stream Survey October 2019
Vegetation Survey October 2019Year 1 Monitoring December 2019In-stream repairs
Invasive Treatment
Stream Bank Repairs
Soil Amendments
In-stream Vegetation Treatment
Year 2 Monitoring
Construction (Grading) Completed April 2018-April 2019 April 2019
Planting Completed April 2018-April 2019
APPENDIX F. Additional Documentation
MEMORANDUM
TO: 401 Permit Reviewer
FROM: Carolyn Lanza, Wildlands Engineering
DATE: July 7, 2023
RE: Project Repair Plan ‐ Supporting Documentation
BUCKWATER MITIGATION SITE
Orange County, NC
On behalf of the North Carolina Department of Mitigation Services (NCDMS), Wildlands Engineering, Inc.
(Wildlands) is requesting a new water quality certification for an existing stream mitigation project in
Orange County, NC. The Buckwater Mitigation Site was originally permitted in March of 2018 under the
NC Division of Water Resources (NCDWR) Water Quality General Certification Number 4134 and the US
Army Corps of Engineers (USACE) Nationwide Permit Number 27. The project was constructed between
April of 2018 and April of 2019.
Minor repairs are now needed for this mitigation site and the previous water quality certification for the
project has expired. The repairs are relatively minor and will be permitted by the USACE under the
Nationwide Permit Number 3. However, we have been informed by NCDWR that a new water quality
certification will be needed. A repair plan for the project site is attached to this memo. Most of the
repairs are simply replacing structures that were originally constructed but have become damaged and
repairing bank erosion. In total, the repairs will be constructed on 238 linear feet of the project. The
total length of the original project is 16,276 LF (MY0 Annual Report, September 2019).
We hope this water quality certification for the repair work can be processed in a timely manner. If you
have additional questions or need more information about the repair plan to issue the new water
quality certification, please do not hesitate to contact me at 313‐969‐7318 or at
clanza@wildlandseng.com should you have any questions.
Sincerely,
Carolyn Lanza
Environmental Scientist
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Reach Start Station End Station Length (LF)Description Planned 2023 Management Action
314+20 314+30 10
Piping rock sill; souring left bank. Riffle
upstream of piping sill is stable and providing
grade control.
Remove rock sill and tamp down left bank.
314+40 314+70 30
Piping angled log riffle due to log sills being
improperly keyed in. Riffle material is
providing grade control.
Remove angled log riffle, rebuild as native riffle.
N/A Perched culvert due to piping rock sills
below.
408+42 409+20 78
Nine piping rock sills. Original construction of
rock sills were built upstream to downstream
preventing proper sealing of structures.
451+40 451+70 30
Six piping rock sills. Original construction of
rock sills were built upstream to downstream
preventing proper sealing of structures.
Rebuild rock sill structures downstream to
upstream.
453+00 453+50 50
Four piping log sills and two piping rock sills
due to erosion around log sills.
Rebuild structures and remove boulder toe along
banks.
T6 Reach 3 517+80 518+20 40
Four piping log sills due to erosion around
log sill.Remove log sills and replace with boulder sills.
Not applicable (N/A): Lengths not associated with instances (points)
Table 1. Areas of Concern and Management Actions
T4
T4B Reach 1
T3 Reach 2
408+42
Rebuild rock sill structures downstream to
upstream and remove boulder toe along banks.
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Figure 1. Integrated Current Condition Plan View
Buckwater Mitigation Site
DMS Project No. 97084
Monitoring Year 5 - 2023
Orange County, NC
¹0 800400 Feet
2021 Aerial Photography
Conservation Easement
Internal Crossing
Existing Wetlands
^treaŵ ApproaĐh
Restoration
Enhancement I
Enhancement II
No Credit
Stream Areas of Concern
Utility Easement
!(Reach Breaks
Piping Log Sills
Piping Log Sills Piping Rock Sills and
Perched Culvert
Piping Rock Sills
Piping Log and
Rock SillsPiping Rock Sill
Stream Area of Concern Photographs
T3 R2 STA 314+20 - 314+30 – Piping Rock Sill (3/24/2023) T3 R2 STA 314+40 - 314+70 – Piping Angled Log Riffle
(3/24/2023)
T3 R2 STA 314+40 - 314+70 – Piping Angled Log Riffle
(3/24/2023)
T3 R2 STA 314+40 - 314+70 – Piping Angled Log Riffle
(3/24/2023)
T4 STA 408+42 – Perched Culvert (3/24/2023) T4 STA 408+42 – 409+20 – Piping Rock Sills (3/24/2023)
T4 STA 408+42 – 409+20 – Piping Rock Sills (3/24/2023) T4B R1 STA 451+40 – 451+70 – Piping Rock Sills (3/24/2023)
T4B R1 STA 451+40 – 451+70 – Piping Rock Sills (3/24/2023) T4B R1 STA 451+40 – 451+70 – Piping Rock Sills (3/24/2023)
T4B R1 STA 453+00 – 453+50 – Piping Log and Rock Sills
(3/24/2023)
T4B R1 STA 453+00 – 453+50 – Piping Log and Rock Sills
(3/24/2023)
T6 R3 STA 517+80 – 518+20 – Piping Log Sills (3/24/2023) T6 R3 STA 517+80 – 518+20 – Piping Log Sills (3/24/2023)
T6 R3 STA 517+80 – 518+20 – Piping Log Sills (3/24/2023)
Stream Repair Area Photographs
T4 STA 408+42 – 409+20 – Repaired Reach (8/22/2023) T4B R1 STA 453+00 – 453+50 – Repaired Area (8/22/2023)
T4B R1 STA 451+40 – 451+70 – Repaired Area (8/22/2023) T3 R2 STA 314+20 – 314+30 – Repaired Area (8/22/2023)
T6 R3 STA 517+80 – 518+20 – Repaired Area (8/22/2023)
Wildlands Engineering, Inc. page 1
Buckwater Mitigation Site
MEETING SUMMARY
MEETING: MY5 IRT Site Walk
Buckwater Mitigation Site
Neuse 03020201; Orange County, NC
DEQ Contract No. 006829
DMS Project No. 97084
USACE ID: 2016-0406
DATE: On-Site Meeting: Thursday, October 12, 2023
Meeting Notes Distributed: Wednesday, October 17, 2023
Attendees
Todd Tugwell, USACE
Casey Haywood, USACE
Jeremiah Dow, DMS
Danielle Mir, DMS
Chris Roessler, Wildlands
Jason Lorch, Wildlands
Neil Curtis, Wildlands
Meeting Notes
• General Site Notes
o All repair areas were seen during the site walk. The IRT asked that photographs of the repair areas
be included in future monitoring reports. Also, the IRT would like to see evidence of flow for the
repair areas on T4 and T4B. This can be either flow gauge data or trail camera pictures, and site
walk photos from throughout the year.
o Add random vegetation plots to supplementally planted areas and priority 2 areas where cut was
completed during construction.
• Buckwater Creek
o Several small beaver dams were present on Buckwater Creek downstream of Walnut Hill Drive.
The USDA has been contacted and will remove the beaver and their dams.
• T4A
o A tree had fallen across the internal crossing on T4A. Wildlands will work with the tenant farmer
to remove the tree and repair the fences that were damaged by the tree.
• T6
o The internal ford crossing on T6 was discussed. Wildlands explained that the landowner would
like to upgrade the crossing to access a future home that is being planned on the north side of T6.
The landowner is planning on adding rock to the current ford crossing to improve access to the
future home. It should be a mixture of different size stone and be close to the as-built elevations.
Wildlands Engineering, Inc. page 2
Buckwater Mitigation Site
o The recent clearing encroachment along the power line easement was walked and Wildlands
stated that they would add two extra conservation easement signs to shorten the gap in between
the current signs and add approximately a dozen containerized trees to the impacted area. The
IRT agreed with this approach.
o The repair area at the bottom of T6 was seen and there was a discussion about rock versus log sills
on intermittent channels. The IRT prefers to see rock sills in intermittent channels for long-term
stability purposes. There is concern about the long-term stability of log sills due to them rotting.
Containerized trees will be added to the areas affected during the repairs.