HomeMy WebLinkAbout20171157 Ver 1_Year 2 Monitoring Report_2021_20220119ID#* 20171157
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Erin Davis
Initial Review Completed Date 01/19/2022
Mitigation Project Submittal - 1/19/2022
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Stream Wetlands Buffer Nutrient Offset
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Matthew Reid
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ID#:* 20171157
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Project Type: DMS Mitigation Bank
Project Name: Shake Rag
County: Madison
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matthew.reid@ncdenr.gov
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Mitigation Monitoring Report
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MONITORING YEAR 2
ANNUAL REPORT
Final
SHAKE RAG MITIGATION SITE
Madison County, NC
DEQ Contract No. 7190
DMS Project No. 100018
USACE Action ID No. SAW-2017-01570
DWR Certification No. 17-1157
French Broad River Basin
HUC 06010105
Data Collection Period: April — October 2021
Draft Submission Date: November 30, 2021
Final Submission Date: January 13, 2022
PREPARED FOR:
NC Department of Environmental Quality
Division of Mitigation Services
1652 Mail Service Center
Raleigh, NC 27699-1652
PREPARED BY:
Wkw
W ILDLANDS
E N G I N E E R I N G
1430 South Mint Street, Suite 104
Charlotte, NC 28203
Phone: 704.332.7754
Fax: 704.332.3306
k rV
WILDLANDS
E N G I N E E R I N G
January 13, 2022
Mr. Matthew Reid
Western Project Manager
Division of Mitigation Services
5 Ravenscroft Dr., Suite 102
Asheville, NC 28801
RE: Shake Rag Mitigation Site — Monitoring Year 2 Report Response to DMS Comments
French Broad River Basin — CU# 06010105 — Madison County
DMS Project ID No. 100018
Contract # 7190
Dear Mr. Reid:
Wildlands Engineering, Inc. (Wildlands) has reviewed the Division of Mitigation Services (DMS)
comments from the Draft Monitoring Year (MY) 2 report for the Shake Rag Mitigation Site. DMS'
comments are noted below in bold. Wildlands' responses to those comments are noted in italics.
DMS comment: The report indicates repairs are planned for the winter of 2021-2022 on page 1-4.
Table 2 shows repairs/maintenance was completed in November/December 2021. Were stream
repairs completed in MY2? If so, section 1.2.5 needs to be updated, and the repairs need to be
discussed in detail. The CCPV should also be updated and repair areas shown on the map. If repairs
have not occurred, please update the Activity/Dates on Table 2.
Wildlands' response: The repairs have not yet occurred and are planned for early 2022. The report text in
Section 1.2.5 and table 2 has been updated.
DMS' comment: Section 1.2.5 should describe and reflect what is shown on the CCPV. Please revise
this section with the level of detail necessary to inform reviewers of site conditions. Please quantify
and describe problem areas. Include number, locations, type (rock/log) of piping structures, length
and locations of eroding banks, etc. The text describes "reconfiguring boulders and riffle stone around
problematic structures", but Table 6 lists engineered structures as functioning at 100% the majority of
the time. Please review and revise the CCPV and Table 6 as necessary.
Wildlands' response: Text has been added to Section 1.2.5 to better quantify and describe the areas of
concern. An additional appendix (Appendix 6) has also been added with a table summarizing locations,
type, length (if applicable), and planned management activity by stream reach. The majority of the issues
identified as "headcut/do wn cutting" on the CCPV figures are located within sections of cascading riffles
(as shown on the Shake Rag Record Drawings from as -built) that include many drops and riffles.
Therefore, a few instances of "headcut/downcutting" associated with structures within the cascading
riffle sections did not seem to warrant the failure of the entire cascading riffle since it's counted as one
structure in the engineered structures category in Table 6.
Wildlands Engineering, Inc. • phone 704-332-7754 • fax 704-332-3306 • 1430 S. Mint Street, # 104 • Charlotte, NC 28203
% �6-
11�0
WILDLANDS
DMS' comment: There are 11 headcuts shown on the CCPV and not discussed in the report. Please add
a discussion of these areas in the report.
Wildlonds' response: Text has been added to Section 1.2.5.
DMS' comment: The level of repairs described in the report may require an Adaptive Management
Plan. Has the IRT been notified of potential repairs? DMS recommends coordinating with the IRT prior
to implementing any repairs.
Wildlonds' response: Repair work will be discussed with regulatory staff prior to commencement.
DMS' comment: Tables 6a-h and Table 7: Please include dates of when assessment work was
completed on each table. The IRT requested this information be included for these tables at the 2021
Credit Release Meeting.
Wildlonds' response: The 2021 visual assessment dotes hove been added to the top of Tables 6o-h and
Table 7.
DMS' comment: Please ensure the Monitoring Phase Performance Bond has been updated and
approved by Kristie Corson before invoicing for Task 8.
Wildlonds' response: The Monitoring Bond was received and approved by Kristie Corson on 11712022.
Electronic Support Files:
DMS' comment: Please change the Year —observed field in the SAOC and VAOC feature classes to years
observed (e.g. MY1, MY2, etc.) for clarity.
Wildlonds' response: This field has been updated in the SAOC and VAOC feature classes.
Enclosed please find two (2) hard copies and one (1) electronic copy on USB of the Final Monitoring
Report. Please contact me at 828-545-3865 if you have any questions.
Sincerely,
#11�y- (
Jake McLean
Project Manager
jmclean@wildlandseng.com
Wildlands Engineering, Inc. • phone 704-332-7754 • fax 704-332-3306 • 1430 S. Mint Street, # 104 • Charlotte, NC 28203
EXECUTIVE SUMMARY
Wildlands Engineering, Inc. (Wildlands) implemented a full -delivery stream mitigation project at the
Shake Rag Mitigation Site (Site) for the North Carolina Department of Environmental Quality (DEQ)
Division of Mitigation Services (DIMS). The project restored, enhanced, and preserved a total of 9,273
linear feet (LF) of perennial and intermittent stream in Madison County, NC. The Site is located within
the DIMS targeted watershed for the French Broad River Basin Hydrologic Unit Code (HUC)
06010105110020 and the NC Division of Water Resources (NCDWR) Subbasin 04-03-04. The project is
providing 6,655.600 stream mitigation units (SMUs) for the French Broad River Basin HUC 06010105
(French Broad 05).
The watershed has a long history of agricultural activity and most of the stressors to stream functions
are related to historic and current land use practices. Prior to construction, the major stream stressors
for the Site were livestock trampling and fecal coliform inputs, stream bed incision and bank scour, a
lack of stabilizing stream bank and riparian vegetation, and ditching and/or piping from agricultural
activities. The effects of these stressors resulted in degraded water quality and habitat throughout the
Site's watershed when compared to reference conditions. The project approach for the Site focused on
evaluating the Site's existing functional condition, its potential for recovery, and need for intervention.
The project goals defined in the mitigation plan (Wildlands, 2019) were established with careful
consideration of 2009 French Broad River Basin Restoration Priorities (RBRP) goals and objectives to
address stressors identified in the watershed. The established project goals include:
• Improve stream channel stability,
• Exclude livestock from stream channels,
• Reconstruct channels and flood -prone areas with appropriate geomorphology,
• Improve in -stream habitat,
• Reduce sediment and nutrient input from adjacent cattle pastures and unpaved roads,
• Restore and enhance native riparian and upland vegetation, and
• Permanently protect the Site from harmful uses.
The Site construction and as -built surveys were completed between December 2019 and February 2020.
Monitoring Year (MY) 2 assessments and site visits were completed between April and October 2021 to
evaluate the current conditions of the project.
Overall, the Site has met the required stream, vegetation, and hydrology success criteria for MY2. The
average planted stem density for the Site is 486 stems per acre and is on track to meet the MY3
requirement of 320 stems per acre. Geomorphic surveys indicate that cross-section bankfull dimensions
closely match the baseline monitoring with some minor adjustments, and most of the streams are
functioning as intended. At least one bankfull event was documented on all project reaches in MY2. The
MY2 visual assessments revealed a reduction in areas of invasive plant species while other areas of
concern such as isolated areas of bed and bank scour and structure piping are present on the Site.
Wildlands will continue to monitor these areas, and adaptive management will be implemented as
necessary throughout the seven-year monitoring period to sustain the ecological health of the Site.
WShake Rag Mitigation Site
Monitoring Year 2 Annual Report - FINAL
SHAKE RAG MITIGATION SITE
Monitoring Year 2 Annual Report
TABLE OF CONTENTS
Section 1: PROJECT OVERVIEW.....................................................................................................1-1
1.1 Project Goals and Objectives............................................................................................1-1
1.2 Monitoring Year 2 Data Assessment.................................................................................1-2
1.2.1 Vegetation Assessment.............................................................................................1-2
1.2.2 Vegetation Areas of Concern and Management Activity.............................................1-3
1.2.3 Stream Assessment...................................................................................................1-3
1.2.4 Stream Hydrology Assessment..................................................................................1-4
1.2.5 Stream Areas of Concern and Management Activity...................................................1-4
1.3 Monitoring Year 2 Summary.............................................................................................1-5
Section2: METHODOLOGY............................................................................................................2-1
Section3: REFERENCES.................................................................................................................3-1
APPENDICES
Appendix 1 General Figures and Tables
Figure 1
Project Vicinity Map
Figure 2
Project Component/Asset Map
Table 1
Mitigation Assets and Components
Table 2
Project Activity and Reporting History
Table 3
Project Contacts Table
Table 4
Project Information and Attributes
Table 5a-b
Monitoring Component Summary
Appendix 2
Visual Assessment Data
Figure 3.0 — 3.4
Current Condition Plan View Maps (Key — Sheet 4)
Table 6
Visual Stream Morphology Stability Assessment Table
Table 7
Vegetation Condition Assessment Table
Stream Photographs
Vegetation Plot Photographs
Appendix 3
Vegetation Plot Data
Table 8
Vegetation Plot Criteria Attainment
Table 9
CVS Permanent Vegetation Plot Metadata
Table 10a-c
Planted and Total Stem Counts
Appendix 4
Morphological Summary Data and Plots
Table 11a-b
Baseline Stream Data Summary
Table 11c
Reference Reach Data Summary
Table 12a-b
Morphology and Hydraulic Summary (Dimensional Parameters - Cross -Section)
Table 13a-h
Monitoring Data — Stream Reach Data Summary
Cross -Section Plots
Reachwide Pebble Count Plots
Appendix 5 Hydrology Summary Data and Plots
Table 14 Verification of Bankfull Events
Table 15 Verification of Consecutive Flow Days
Stream and Crest Gage Plots
Monthly Rainfall Data
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Monitoring Year 2 Annual Report - FINAL ii
Appendix 6 Adaptive Management
Table 16 Areas of Concern and Management Actions
Representative Stream Areas of Concern Photo Log
WShake Rag Mitigation Site
Monitoring Year 2 Annual Report - FINAL iii
Section 1: PROJECT OVERVIEW
The Shake Rag Mitigation Site (Site) is located in Madison County approximately 19 miles north of
Asheville and 4 miles northeast of the town of Mars Hill in the French Broad River Basin HUC
06010105110020 and NCDWR Subbasin 04-03-04 (Figure 1). Located in the Blue Ridge belt within the
Blue Ridge physiographic province (NCGS, 1985), the project watershed is dominated by agricultural and
steep forested land.
The Site encompasses three primary drainage areas including Shake Rag Branch (SRB), UT1, and UT6, all
of which are comprised of smaller valleys. All project stream reaches within these drainages originate
from steep, forested headwater valleys before transitioning to open pastureland situated in wider valley
bottoms further downstream. The valley of Shake Rag Branch begins as a steep, colluvial, V-shaped
valley, which gradually widens into a moderately confined alluvial bottom as it moves downstream.
UT1A, UT3, UT4, and UT8 have steep valleys with much broader valley bottoms, while UT1, UT2, UT5,
UT6, and UT7 flow through steep, colluvial, V-shaped valleys for their entire length in the project area.
Shake Rag Branch drains 163 acres, UT1 drains 70 acres, and UT6 drains 43 acres of rural land.
Prior to construction activities, the Site was in hay production in the valley bottom, with cattle grazing
along valley side slopes and access to the steeper forested areas. Riparian buffers were absent except in
the steepest upper portions of the Site. The streams throughout the Site were in various stages of
impairment related to the current and historical agricultural uses. Many of the streams were buried in
rock -lined channels or pipes approximately 50 years ago. Pre -construction conditions are outlined in
Table 4 of Appendix 1 and Table 11 of Appendix 4.
The final mitigation plan was submitted and accepted by DIMS in January of 2019 and the IRT in March of
2019. Construction activities were completed in January 2020 by Baker Grading & Landscaping, Inc. Kee
Mapping & Surveying, PLLC. completed the as -built survey in February 2020. Planting was completed
following construction in the January 2020 by Bruton Natural Systems, Inc. A conservation easement has
been recorded and is in place on 18 acres. The project is providing 6,655.600 SMUs for the French Broad
River Basin HUC 06010105 (French Broad 05). Annual monitoring will be conducted for seven years with
close-out anticipated to commence in 2027 given the success criteria are met.
Directions and a map of the Site are provided in Figure 1 and project components are illustrated for the
Site in Figure 2.
1.1 Project Goals and Objectives
The Site is providing numerous ecological benefits within the French Broad River Basin. The project goals
were established with careful consideration to address stressors that were identified in the RBRP (EEP,
2009).
The following project specific goals and objectives outlined in the mitigation plan (Wildlands, 2019)
include:
WShake Rag Mitigation Site
Monitoring Year 2 Annual Report - FINAL 1-1
Goals
Objectives
Reconstruct stream channels slated for restoration with stable
Improve the stability of stream channels.
dimensions and appropriate depth relative to the existing flood -
prone area. Add bank revetments and in -stream structures to
protect restored/enhanced streams.
Exclude livestock from stream channels.
Install livestock fencing and watering systems as needed to
exclude livestock from stream channels and riparian areas.
Daylight buried or piped streams, remove man-made
Reconstruct channels and flood prone areas
impoundments, and restore historic valley profiles. Reconstruct
with appropriate geomorphology.
stream channels with bankfull dimensions and construct flood -
prone areas consistent with reference reach findings.
Install habitat features such as cascading riffle -pool sequences,
Improve instream habitat.
lunker logs, and brush toes on restored reaches. Add woody
materials to channel beds. Construct pools of varying depth.
Remove online farm pond.
Construct one step -pool conveyance BMP to treat contributing
Reduce sediment and nutrient input from
17-acre drainage area that is subject to nutrient and fecal
adjacent cattle grazing areas and unpaved
coliform loading from cattle. Relocate unpaved roads outside of
roads.
riparian corridor. Grade and plant forested buffer with native
vegetation.
Convert active hay fields and cattle pasture to forested riparian
Restore and enhance native riparian and
buffers along all Site streams, which will slow and treat runoff
upland vegetation.
from adjacent agriculture before entering streams. Protect and
enhance existing forested riparian buffers. Treat invasive species.
Permanently protect the Site from harmful
Establish a conservation easement on the Site. Exclude livestock
uses.
from Site streams.
1.2 Monitoring Year 2 Data Assessment
Annual monitoring for MY2 was conducted between April and October 2021 to assess the condition of
the project. The stream, vegetation, and hydrologic success criteria for the Site follows the approved
success criteria presented in the Shake Rag Mitigation Plan (Wildlands, 2019).
1.2.1 Vegetation Assessment
Vegetation plot monitoring is being conducted in post -construction monitoring years 1, 2, 3, 5, and 7.
Permanent plots are monitored in accordance with the guidelines and procedures developed by the
Carolina Vegetation Survey-EEP Level 2 Protocol (Lee et al., 2008) and the 2016 USACE Stream and
Wetland Mitigation Guidance to assess the vegetation success. A total of 5 permanent vegetation plots
were established within the project easement area. All of the permanent plots were established as
either a 10 meter by 10 meter square plot or 5 meter by 20 meter rectangular plot. In addition, 4 mobile
vegetation plots were established in monitoring year 1 throughout the planted conservation easement
to evaluate the random vegetation performance for the Site. These plots will be subsequently
WShake Rag Mitigation Site
Monitoring Year 2 Annual Report - FINAL 1-2
reestablished in different random locations in monitoring years 2, 3, 5, and 7. Mobile vegetation plot
assessments will document stems, species, and height using a circular or 100 meter square/rectangular
plot. The final vegetative performance standard will be the survival of 210 planted stems per acre in the
planted riparian areas at the end of the required seven-year monitoring period. The interim measure of
vegetative success for the Site will be the survival of at least 320 planted stems per acre at the end of
MY3 and at least 260 stems per acre at the end of MY5. In NC mountain counties, planted trees must
average 6 feet in height at the end of MY5 and 8 feet in height at the end of MY7.
The MY2 vegetation survey was completed in August 2021, resulting in an average planted stem density
of 486 stems per acre for all monitored permanent and mobile vegetation plots. The Site is on track to
meet the interim MY3 requirement of 320 planted stems per acre, with all 5 permanent plots (100%)
and 3 out 4 mobile plots (75%) exceeding this requirement. One mobile plot (MP3) did not meet the
MY3 density requirement but remains on track to meet the MY5 density requirement. A survival rate of
roughly 96% from MY1 was observed in the permanent vegetation plots. About 20% of the monitored
stems were documented with a vigor of 2, signaling fair plant health with some damage present. This
lower vigor rating is due to damage from dry soil conditions, deer herbivory, insects, and suffocation
from dense herbaceous cover. Approximately 76% of the planted stems in permanent plots are thriving
with a vigor of 3 or greater indicating plant health ranging from good to excellent and damage is rare.
Natural volunteer trees species that were observed on the Site include sycamore (Platanus occidentalis),
tulip poplar (Liriodendron tulipifera), honey locust (Gleditsia triacanthos), and red maple (Acer rubrum).
Please refer to Appendix 2 for vegetation plot photographs and Appendix 3 for vegetation data tables.
1.2.2 Vegetation Areas of Concern and Management Activity
MY2 visual assessments reveal that over 99% of the conservation easement is unaffected by invasive
plant populations. Invasive species found on the Site include multiflora rose (Rosa multiflora), princess
tree (Paulownia tomentosa), tree of heaven (Ailanthus altisima), silver grass (Miscanthus sinensis), and
wineberry (Rubus phoenicolasius). Populations of wineberry and multiflora have been reduced below
the mapping threshold, therefore are not depicted on the Current Condition Plan View (CCPV) Figures.
Invasive species treatments occurred in June 2021 with efforts focusing on areas near the upper reaches
of UT1, UT2, and Shake Rag Branch. Foliar ring sprays around planted woody stems also occurred to
treat fescue (Festuca sp.) in areas where it was overcrowding the stems. Additional treatments will
continue as needed to help manage and eliminate remaining invasive species populations on the Site.
Overall, the herbaceous cover has continued to become well established throughout the Site. Small and
infrequent areas of poor herbaceous cover were noted on steeper side slopes along UT3 and Shake Rag
Branch. In MY1, small sections of mowing overreach were observed inside the conservation easement.
Wildlands successfully notified the landowner of the error and installed additional posts to clarify the
easement boundary. The encroachment is no longer an active issue and supplemental plantings are not
warranted at this time.
These vegetation areas of concern are documented on Table 7 and shown on the CCPV Figures 3.0 — 3.4
in Appendix 2.
1.2.3 Stream Assessment
Riffle cross -sections on the restoration and enhancement I reaches are stable and show minimal change
in bankfull area, maximum depth ratio, and width -to -depth ratio. All riffle cross -sections should fall
within the parameters defined for the designated stream type. Any significant deviations will be
evaluated to assess possible signs of stream channel instability. Indicators most often include a vertically
incising thalweg and/or eroding channel banks. Remedial action would not be taken if channel changes
indicate a movement toward stability. As noted in the approved Mitigation Plan (Wildlands, 2019),
WShake Rag Mitigation Site
Monitoring Year 2 Annual Report - FINAL 1-3
Shake Rag Reach 5 is expected to have wider flood -prone widths and entrenchment ratios greater than
2.2. This is also evident for UT8 considering the existing landscape in the wider valley bottom.
Morphological surveys for MY2 were conducted in June 2021. Cross-section survey results indicate that
channel dimensions are stable and functioning as designed on all restoration and enhancement I
reaches with minimal adjustments. Minor changes occurring include localized bed scour, narrowing of
pools and riffles, and alluvial deposition with the channel. Low bank height ratios seem to have
stabilized since MY1 at cross-section 1 along UT1 Reach 2 and cross-section 9 along Shake Rag Branch
Reach 3. The difference between the low bank height and bankfull max depth for both cross -sections is
roughly 0.1 feet; therefore, slight changes in bank heights on very small streams tend to exaggerate
ratio comparisons and, in this case, is not considered a sign of instability. Conversely, at riffle cross-
section 3, the max depth has doubled since MYO and is representative of riffle scour and channel
downcutting in isolated areas along UT3. See Section 1.2.5 for further discussion about stream areas of
concern along UT3 and Shake Rag Branch.
Reachwide pebble counts along all restoration and enhancement I reaches indicate maintenance of
coarser materials in riffle features and finer particles in the pool features. Please refer to Appendix 2 for
the visual stability assessment tables, CCPV Figures 3.0 — 3.4, and reference photographs, and Appendix
4 for the morphological tables and plots.
1.2.4 Stream Hydrology Assessment
Automated pressure transducers were installed to document stream hydrology within restoration
and/or enhancement level I mitigation reaches throughout the seven-year monitoring period.
Henceforth, these devices are referred to as "crest gages (CG)" for those recording bankfull events and
"stream gages (SG)" for those recording baseflow.
Bankfull Events
At the end of the seven-year monitoring period, four or more bankfull flow events must have occurred
in separate years within the restoration reaches. A total of 5 CGs were installed along restoration and
enhancement I reaches. At as -built, the pressure transducers in the CGs were programmed to record
data every 2 hours. This interval was likely too long to capture all bankfull events in the steep and flashy
project streams, so the transducers were reprogrammed in MY1 to record data every 30 minutes. In
MY2, at least one bankfull event was recorded on all reaches and was documented by either crest gage
data and/or debris wracklines observed along the floodplain.
Baseflow Monitoring
Consistent flow must be documented in the restored intermittent channel (UT8) at the Site. Under
periods of normal rainfall, stream flow must be documented to occur every year for at least 30
consecutive days during the seven-year monitoring period. An automated SG was installed within the
upper third of UT8 to monitor baseflow. On UT8, 292 consecutive days were documented in MY2
indicating that this channel exceeded the success criteria for intermittent channels.
Please refer to Appendix 5 for hydrology summary data and plots.
1.2.5 Stream Areas of Concern and Management Activity
MY2 stream and visual assessments revealed mostly stable channels with only localized instances of bed
and bank instability, and structure issues; with these being typically inter -related. The majority of these
have been identified on the CCPV Figures as "headcut/downcutting" or "bed instability', however issues
are generally isolated issues of piping and/or bed material movement within cascading riffles (which
includes many drops and riffles). Typical examples of stream areas of concern are provided in the
photolog in Appendix 6. Numerous large storm events occurred in August 2021, with several exhibiting
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Monitoring Year 2 Annual Report - FINAL 1-4
single day rainfall totals greater than 2 inches (CRONOS Mars Hill 2.2 SSE, 2021). The Site was resilient to
these large storm events. Instances of piping, and bed and bank scour at structures within cascading
riffles are planned to be addressed by repairs planned for early 2022; repair work will be discussed with
regulatory staff prior to commencement. Please refer to Appendix 6 for a table summarizing planned
repair work and locations. In areas where stream stability or function may be compromised, proposed
actions will plug piping areas, reconfigure boulders and riffle stone around problematic structures, and
re -grade or provide toe protection to vulnerable banks. Sod mats will be used to quickly re-establish
vegetation wherever possible. Stream areas of minor concern outside of the repair areas will continue to
be monitored in future years for signs of instability. Please refer to Appendix 2 for stream stability tables
and CCPV Figures 3.0-3.4.
1.3 Monitoring Year 2 Summary
Overall, the Site has met the required stream, vegetation, and hydrology success criteria for MY2. The
average planted stem density for the Site is 486 stems per acre and is on track to meet the MY3
requirement of 320 stems per acre. Geomorphic surveys indicate that cross-section bankfull dimensions
closely match the baseline monitoring with some minor adjustments, and most of the streams are
functioning as intended. At least one bankfull event was documented on all project reaches in MY2. The
MY2 visual assessments revealed a reduction in areas of invasive plant species while other areas of
concern such as isolated areas of bed and bank scour and structure piping are present on the Site.
Wildlands will continue to monitor these areas, and adaptive management will be implemented as
necessary throughout the seven-year monitoring period to sustain the ecological health of the Site.
WShake Rag Mitigation Site
Monitoring Year 2 Annual Report - FINAL 1-5
Section 2: METHODOLOGY
Geomorphic data were collected following the standards outlined in The Stream Channel Reference Site:
An Illustrated Guide to Field Techniques (Harrelson et al., 1994) and in the Stream Restoration: A Natural
Channel Design Handbook (Doll et al., 2003). All Integrated Current Condition Mapping was recorded
using a Trimble handheld GPS with sub -meter accuracy and processed using Pathfinder and ArcGIS.
Stream gages were installed in riffles and monitored quarterly. Hydrologic monitoring instrument
installation and monitoring methods are in accordance with the United States Army Corps of Engineers
(USACE, 2003) standards. Vegetation monitoring protocols followed the Carolina Vegetation Survey-EEP
Level 2 Protocol (Lee et al., 2008).
WShake Rag Mitigation Site
Monitoring Year 2 Annual Report - FINAL 2-1
Section 3: REFERENCES
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, Cheryl C; Rawlins, C.L.; Potyondy, John 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, Michael T., Peet, Robert K., Steven D., Wentworth, Thomas R. 2008. CVS-EEP Protocol for Recording
Vegetation Version 4.2. Retrieved from: http://cvs.bio.unc.edu/protocol/cvs-eep-protocol-v4.2-lev1-
2.pdf North Carolina Division of Mitigation Services. 2009. French Broad River Basin Restoration
Priorities.
North Carolina Climate Retrieval and Observations Network of the Southeast Database (NCCRONOS).
2021. State Climate Office of North Carolina. Version 2.7.2. Station ID Mars Hill 2.2 SSE, NC. Accessed
October 2021.
North Carolina Division of Mitigation Services (DIMS), June 2017. DMS Annual Monitoring and Closeout
Reporting Template.
North Carolina Division of Mitigation Services (DIMS), June 2017. DMS Stream and Wetland Mitigation
Plan Template and Guidance.
North Carolina Division of Water Resources. 2011. French Broad Basinwide Water Quality Plan.
North Carolina Division of Water Resources (NCDWR), 2015. Surface Water Classifications.
http://portal.ncdenr.org/web/wq/ps/csu/classifications
North Carolina Ecosystem Enhancement Program. 2009. French Broad River Basin Restoration Priorities.
North Carolina Geological Survey (NCGS), 1985. Geologic Map of North Carolina: North Carolina Survey,
General Geologic Map, scale 1:500,000. https://deq.nc.gov/about/divisions/energy-mineral-land-
resources/north-carolina-geological-survey/ncgs-maps/1985-geologic-map-of-nc4
Rosgen, D. L. 1994. A classification of natural rivers. Catena 22:169-199.
Rosgen, D.L. 1996. Applied River Morphology. Pagosa Springs, CO: Wildland Hydrology Books.
United States Army Corps of Engineers (USACE), October 2016. Stream Mitigation Guidelines. USACE,
NCDENR-DWQ, USEPA, NCWRC.
Wildlands Engineering, Inc (Wildlands), 2019. Shake Rag Mitigation Site Mitigation Plan. DIMS, Raleigh,
NC.
Wildlands Engineering, Inc (Wildlands), 2020. Shake Rag Mitigation Site As -Built Baseline Monitoring
Report. DMS, Raleigh, NC.
WShake Rag Mitigation Site
Monitoring Year 2 Annual Report - FINAL 3-1
APPENDIX 1. General Figures and Tables
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The subject project site i
the North Carolina Depar....
Division of Mitigation Services (DMS) and is encompassed
by a recorded conservation easement, but is bordered
by land under private ownership. Accessing the site
may require traversing areas near or along the easement
boundary and therefore access by the general public is not
permitted. Access by authorized personnel of state and
federal agencies or their designees/contractors involved in
the development, oversight,and stewardship of the restoration
site is permitted with in the terms and timeframes of their
defined roles. Any intended site visitation or activity by
any person outside of these previously sanctioned roles
and activities requires prior coordination with DMS.
06010105110010�0' 4
Directions to Site:
From Asheville: Head north on 1-26 W towards Mars
Hill. Take exit 9 and turn right on US-19 N/US-23A N
towards Burnsville/Spruce Pine and continue for 3 miles.
Turn left onto Shake Rag Road and continue for about
06010105080020"�I`
1 mile onto the Site.
Figure 1 Project Vicinity Map
0 1 2 Miles Shake Rag Mitigation Site
I t I t I DMS Project No. 100018
W I L D LANDS
Monitoring Year 2 - 2021
, Y E N G I N E E R I N G Madison County, NC
�.-_�
Conservation Easement
Internal Culvert Crossing
r '9
Internal Waterline Crossing
Existing Wetland
Stream Restoration
Stream Enhancement I
-
Stream Enhancement II
Stream Preservation a
Not for Credit Stream
Non -Project Stream
w`
Stormwater BMP
`.
`� •
Q Reach Break
WILDLANDS
E N G I N E E R I N G rk
Figure 2 Project Component/Asset Map
0 250 500 Feet Shake Rag Mitigation Site
I i I i I DMS Project No. 100018
Monitoring Year 2 - 2021
Madison County, NC
Table 1. Mitigation Assets and Components
Shake Rag Mitigation Site
DMS Project No. 100018
Monitoring Year 2 - 2021
Project
Project Area/Reach
Existing Footage
1
(LF)or Acreage
Mitigation PlanMitigation
Footage/
Acreage
Category
Components
Restoration Level
Priority Level
Mitigation
Ratio (X:1)
As -Built Footage/
z
Acreage
Comments
Shake Rag Branch R1
312
312
Cold
Preservation
N/A
10.000
312
N/A
Shake Rag Branch R2
175
175
Cold
Enhancement II
N/A
2.500
175
N/A
Shake Rag Branch R3
1,451
1,393
Cold
Restoration
P1
1.000
1,391
N/A
Shake Rag Branch R4
385
385
Cold
Enhancement I
N/A
1.500
385
N/A
Shake Rag Branch R5
1,216
1,134
Cold
Restoration
P1, P2
1.000
1,134
N/A
UT1 R1
934
907
Cold
Enhancement 11
N/A
2.500
907
N/A
UT1 R2
255
278
Cold
Enhancement I
N/A
1.500
278
N/A
UT1A
100
100
Cold
Enhancement 11
N/A
2.500
100
N/A
UT2 R1
164
164
Cold
Enhancement 11
N/A
2.500
164
N/A
UT2 R2
296
304
Cold
Restoration
P1
1.000
304
N/A
UT3 R1
426
426
Cold
Enhancement 11
N/A
2.500
426
N/A
UT3 R2
1,387
1,019
Cold
Restoration
P1
1.000
1,019
N/A
UT4
910
930
Cold
Restoration
P1
1.000
930
N/A
UT5
483
439
Cold
Enhancement 11
N/A
2.500
444
N/A
UT6
707
673
Cold
Enhancement 11
N/A
2.500
670
N/A
UT7
428
428
Cold
Preservation
N/A
10.000
428
N/A
UT8
210
206
Cold
Restoration
P1
1.000
206
N/A
Project
Restoration Level
Credits
Stream
Riparian Wetland
Non -Riparian
Wetland
Coastal Marsh
Warm
Cool
Cold
Riverine
Non-Riv
Restoration
N/A
N/A
4,986.000
N/A
N/A
N/A
N/A
Re-establishment
N/A
N/A
N/A
N/A
Rehabilitation
N/A
N/A
N/A
N/A
Enhancement
N/A
N/A
N/A
N/A
Enhancement
N/A
N/A
442.000
Enhancement II
N/A
N/A
1,153.600
Creation
N/A
N/A
N/A
N/A
Preservation
N/A
N/A
74.000
N/A
N/A
N/A
Totals
N/A
N/A
6,655.600
N/A
N/A
N/A
N/A
Notes:
1. Some or all of SRB Reach 3, UT3 Reach 2, UT4, and UT8 were previously buried in rock -lined channels or pipes. Reported exiting lengths are estimates based upon land owner communication,
remote sensing, and field verification to approximate the subsurface location and alignment.
The Site contains 12 internal easement crossings. This value excludes the affected length of proposed stream centerline within each crossing.
Table 2. Project Activity and Reporting History
Shake Rag Mitigation Site
DMS Project No. 100018
Monitoring Year 2 - 2021
ReportActivity or
Institution Date
Data Collection Complete
N/A
Completion or Delivery
May 2017
404 Permit
June 2019
June 2019
Mitigation Plan
February - October 2018
March 2019
Final Design - Construction Plans
June 2019
June 2019
Construction
July 2019 -January 2020
January 2020
Bare root and live stake plantings for reach/segments
December 2020
December 2020
Baseline Monitoring Document (Year 0)
December 2019 - March 2020
April 2020
Stream Repair/Maintenance
Spring 2020 & November 2020
November 2020
Year 1 Monitoring
Stream Survey
October 2020
November 2020
Vegetation Survey
October 2020
Invasive Species Treatment
June 2021
June 2021
Year 2 Monitoring
Stream Survey
June 2021
November 2021
Vegetation Survey
August 2021
Year 3 Monitoring
Stream Survey
Vegetation Survey
Year 4 Monitoring
Stream Survey
Vegetation Survey
Year 5 Monitoring
Stream Survey
Vegetation Survey
Year 6 Monitoring
Stream Survey
Vegetation Survey
Year 7 Monitoring
Stream Survey
Vegetation Survey
Table 3. Project Contact Table
Shake Rag Mitigation Site
DMS Project No. 100018
Monitoring Year 2 - 2021
Designers
Wildlands Engineering, Inc.
Jake McLean, PE, CFM
1430 South Mint Street, Suite 104
Charlotte, NC 28203
704.332.7754
Construction Contractors
Baker Grading & Landscaping, Inc.
1000 Bat Cave Road
Old Fort, NC 28762
Planting Contractor
Bruton Natural Systems, Inc.
PO Box 1197
Freemont, NC 27830
Seeding Contractor
Baker Grading & Landscaping, Inc.
Seed Mix Sources
Baker Grading & Landscaping, Inc.
Nursery Stock Suppliers
Bare Roots
Bruton Natural Systems, Inc.
Live Stakes
Herbaceous Plugs
Performers
Wildlands Engineering, Inc.
Eontoring
toring, POC
Kristi Suggs
704.332.7754 Ext. 110
%
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APPENDIX 2. Visual Assessment Data
Figure 3.0 Current Condition Plan View Map (Key)
0 300 600 Feet Shake Rag Mitigation Site
I I I
DMS Project No. 100018
WILDLANDS rk
Monitoring Year 2-2021
ENGINEERING 1 Madison County, NC
Figure 3.1 Monitoring Plan View Map
0 100 200 Feet Shake Rag Mitigation Site
I i I i I DMS Project No. 100018
WILDLANDS rk
Monitoring Year 2-2021
ENGINEERING 1 Madison County, NC
\ I✓�t5*a
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0 150 300 Feet
I I I
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NGINEERING rk q�
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IZZ Internal Culvert Crossing
=Existing Wetland
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.............Top of Bank
- - Structures
_t Q Reach Break
0 Photo Point (PP)
_ 0 Barotroll(BT)
Crest Gage (CG)
— Cross Section (XS)
Permanent Vegetation Plots (VP) - MY2
=Criteria Met
Mobile Vegetation Plots (MP) - MY2
._ 0Criteria Met
Vegetation Areas of Concern - MY2
Bare/poor herbaceous cover
®Silver Grass
Stream Areas of Concern - MY2
Headcut/downcutting
Bank instability
-- Bed instability
Deposition
12J
2018 - , Photography
Figure 3.2 Monitoring Plan View Map
Shake Rag Mitigati
on Site
DMS Project No. 100018
Monitoring Year 2 - 2021
Madison County, NC
I +50 t•
� qp0
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1
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i
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-
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0 100 200 Feet
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/ Figure 3.3 Monitoring Plan View Map
Shake Rag Mitigation Site
DMS Project No. 100018
Monitoring Year 2 - 2021
Madison County, NC
27ee
y100
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2600
/ Figure 3.4 Monitoring Plan View Map
0 75 150 Feet / Shake Rag Mitigation Site
I i I i I DMS Project No. 100018
WILDLANDS nk�
Monitoring Year 2-2021
ENGINEERING Madison County, NC
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Stream Photographs
MY2
Photo Point 1— UT1 Reach 1, view upstream (0612912021) 1 Photo Point 1— UT1 Reach 1, view downstream (06/29/2021) 1
Photo Point 2 — UT1 Reach 1, view upstream (0612912021) 1 Photo Point 2 — UT1 Reach 1, view downstream (0612912021) 1
Photo Point 3 — UT1A, view upstream (0612912021) 1 Photo Point 3 — UT1A, view downstream (0612912021) 1
Photo Point 4— UT1 Reach 2, view upstream (0612912021) 1 Photo Point 4— UT1 Reach 2, view downstream (0612912021) 1
Photo Point 5 — UT2 Reach 1, view upstream (0612912021) 1 Photo Point 5 — UT1 Reach 1, view downstream (0612912021) 1
Photo Point 6 — UT2 Reach 2, view upstream (0612912021) 1 Photo Point 6 — UT2 Reach 2, view downstream (0612912021) 1
Photo Point 7 — UT3 Reach 1, view upstream (0612912021) 1 Photo Point 7 — UT3 Reach 1, view downstream (0612912021) 1
Photo Point 8 — UT3 Reach 2, view upstream (0612912021) 1 Photo Point 8 — UT3 Reach 2, view downstream (0612912021) 1
Photo Point 9 — UT3 Reach 2, view upstream (1012012021) 1 Photo Point 9 — UT3 Reach 2, view downstream (0612912021) 1
Photo Point 10 — UT3 Reach 2, view upstream (1012012021) 1 Photo Point 10 — UT3 Reach 2, view downstream (1012012021) 1
Photo Point 11— UT4, view upstream (1012012021) 1 Photo Point 11— UT4, view downstream (1012012021) 1
Photo Point 12 — UT4, view upstream (1012012021) 1 Photo Point 12 — UT4, view downstream (1012012021) 1
Photo Point 13 — UT4, view upstream (1012012021) 1 Photo Point 13 — UT4, view downstream (1012012021) 1
Photo Point 14 — UT8, view upstream (1012012021) 1 Photo Point 14— UT8, view downstream (1012012021) 1
Photo Point 15 — UT7, view upstream (0612912021) 1 Photo Point 15 — UT7, view downstream (0612912021) 1
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Photo Point 16 — SRB Reach 1, view upstream (0612912021)
Photo Point 16 —
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Photo Point 18 —
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Photo Point 19 — SRB Reach 3, view upstream (0612912021) 1 Photo Point 19 — SRB Reach 3, view downstream (0612912021) 1
Photo Point 20 —SRB Reach 3, view upstream (1012012021) 1 Photo Point 20 —SRB Reach 3, view downstream (1012012021) 1
Photo Point 21—SRB Reach 3, view upstream (1012012021) 1 Photo Point 21—SRB Reach 3, view downstream (1012012021) 1
Photo Point 22 — SRB Reach 3, view upstream (1012012021) 1 Photo Point 22 — UT3 Reach 2, view upstream (1012012021) 1
Photo Point 22 — SRB Reach 3, view downstream (1012012021) 1
Photo Point 23 — SRB Reach 4, view upstream (1012012021) 1 Photo Point 23 — SRB Reach 4, view downstream (1012012021) 1
Photo Point 24 — SRB Reach 4, view upstream (1012012021) 1 Photo Point 24 — SRB Reach 5, view downstream (1012012021) 1
Photo Point 25 —SRB Reach 5, view upstream (1012012021) 1 Photo Point 25 —SRB Reach 5, view downstream (1012012021) 1
Photo Point 26 — SRB Reach 5, view upstream (1012012021) 1 Photo Point 26 — SRB Reach 5, view downstream (1012012021) 1
Photo Point 27 — SRB Reach 5, view upstream (1012012021) 1 Photo Point 27 — SRB Reach 5, view downstream (1012012021) 1
Photo Point 28 — UT6, view upstream (0612912021) 1 Photo Point 28 — UT6, view downstream (0612912021) 1
Photo Point 29 — UT6, view upstream (0612912021) 1 Photo Point 29 — UT6, view downstream (0612912021) 1
Vegetation Plot Photographs
MY2
Permanent Vegetation Plot 1— (0810912021) 1 Permanent Vegetation Plot 2 — (0810912021) 1
Permanent Vegetation Plot 3 — (0810912021) 1 Permanent Vegetation Plot 4 — (0810912021) 1
Permanent Vegetation Plot 5 — (0810912021) 1
Mobile Vegetation Plot 1— North view — (0810912021) 1 Mobile Vegetation Plot 2 — North view — (0810912021) 1
Mobile Vegetation Plot 3 — North view — (0810912021) 1 Mobile Vegetation Plot 4 — North view — (0810912021) 1
APPENDIX 3. Vegetation Plot Data
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APPENDIX 5. Hydrology Summary Data and Plots
Table 14. Verification of Bankfull Events
Shake Rag Mitigation Site
DMS Project No. 100018
Monitoring Year 2 - 2021
Reach
UT1 Reach 2
MY
M Y1
Date of Occurrence
2/13/2020
Date of Data Collection
2/13/2020
AM ethod
Crest Gage
4/13/2020
4/13/2020
MY2
7/19/2021
7/19/2021
8/18/2021
8/18/2021
UT2 Reach 2
M Y1
2/6/2020
2/6/2020
MY2
7/19/2021
7/19/2021
8/13/2021
8/13/2021
8/17/2021
8/17/2021
10/8/2021
10/8/2021
UT3 Reach 2
MY2
7/19/2021
8/9/2021
Debris Wracklinesl
UT4
MY2
7/19/2021
7/19/2021
Crest Gage
8/7/2021
8/7/2021
8/17/2021
8/17/2021
10/8/2021
10/8/2021
Shake Rag Branch Reach 3
MY2
7/19/2021
8/9/2021
Debris Wracklinesl
1Photo documentation of debris wracklines are included in the electronic support files
Table 15. Verification of Consecutive Flow Days
Shake Rag Mitigation Site
DMS Project No. 100018
Monitoring Year 2 - 2021
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MY2
UT3 Reach 2 STA 306+00: typical headcut, structure piping I UT3 Reach 2 STA 307+75: typical bank instability
UT3 Reach 2 STA 311+75: headcut/downcutting I UT3 Reach 2 STA 312+00: typical bed instability
Shake Rag Reach 3 STA 921+50 & 921+75: Typical bed and bank I Shake Rag Reach 3 STA 922+15: Typical minor bank instability
instability
Shake Rag Reach 3 STA 922+50 & 922+75: Typical I Shake Rag Reach 4 STA 923+75: Minor deposition at valley break
headcut/downcutting, riffle material lowered
UT1 Reach 2 STA 112+00: headcut due to structure piping
UT4 STA 404+25: Typical headcut, structure piping