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Lindsay Crocker
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Project Name: Dry Creek
County: Durham
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DRY CREEK MITIGATION SITE
MONITORING YEAR 2 Durham County, NC
ANNUAL REPORT NCDEQ Contract No. 6827
DMS Project No. 97082
Final USACE Action ID No. SAW-2016-00880
NCDWR Project No. 2016-0369
Data Collection Period: January -October 2021
Draft Submission Date: November 3, 2021
Final Submission Date: November 19, 2021
PREPARED FOR:
NC Department of Environmental Quality
Division of Mitigation Services
1652 Mail Service Center
Raleigh, NC 27699-1652
WILDLANDS
ENGINEERING
November 19, 2021
Lindsay Crocker
NC Department of Environmental Quality, Division of Mitigation Services
217 W. Jones Street, Suite 3000
Raleigh, NC 27609-1652
Subject: DMS Comments on Dry Creek MY2
Dry Creek, Project ID #97082, DMS Contract #6827
Dear Ms. Crocker,
We have reviewed the comments on the MY1 Report for the above referenced project dated November
18, 2021 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.
Report Comments:
1. In future reports, you may omit the substrate monitoring per IRT/DMS clarification.
This is noted for future monitoring reports.
2. The mortality between MY1 and 2 on parts of the project and lack of species diversity needs to
be considered. It is understood that Wildlands believes that volunteers matching planted
species will result in all plots being considered successful for the stream credit. The riparian
buffer credit success requirement can be satisfied with appropriate volunteers currently in MY2.
Please consider that in the narrative in the Monitoring Year 2 summary of the buffer report.
Please also consider that DWR expects the site to have a minimum of four native hardwood and
many of your plots are showing 3 species. This was discussed at length in the field and DMS
understands that Wildlands is planning to look closely at this in MY3.
The lack of species diversity will be assessed in future monitoring years.
Digital Comments:
1. Please submit the CVS mdb associated with the MY2 veg data for stream and buffer.
The CVS mdb is now submitted with the final digital files.
2. Note that the total % stable performing as intended in Table 5a is listed as 99%, but it should be
100% based on the reported values.
Table 5 has been updated.
Wildlands Engineering, Inc. (P) 919.851.9986 • 312 West Millbrook Road, Suite 225 • Raleigh, NC 27609
Ow
w
WILDLANDS
ENGINEERING
If you have any questions, please contact me by phone (919) 851-9986, or by email
(jlorch@wildlandseng.com).
Sincerely,
Jason Lorch, Monitoring Coordinator
Wildlands Engineering, Inc. (P) 919.851.9986 • 312 West Millbrook Road, Suite 225 • Raleigh, NC 27609
PREPARED BY:
W
WILDLANDS
E N G INFER I N G
312 West Millbrook Road, Suite 225
Raleigh, NC 27609
Jason Lorch
jlorch@wildlandseng.com
Phone: 919.851.9986
EXECUTIVE SUMMARY
Wildlands Engineering, Inc. (Wildlands) implemented a full delivery project at the Dry Creek Mitigation
Site (Site) for the North Carolina Department of Environmental Quality Division of Mitigation Services
(DMS) to restore a total of 9,811 linear feet of perennial and intermittent streams in Durham County,
NC. The Site will generate 8,457.934 stream credits. All stream lengths were measured along the stream
centerline for credit calculations. UT1 Reach 2 crediting changed after the Mitigation Plan was approved
due to the revised break in the conservation easement associated with a utility line relocation. The Site
is located approximately three miles northwest of Butner, NC and approximately 2 miles west of the
Granville County/Durham County line (Figure 1) in the Neuse River Basin 8-Digit Hydrologic Unit Code
(HUC) 03020201. The Site is located within the Neuse River Targeted Local Watershed (TLW) as
presented in the 2010 Neuse River Basin Restoration Priorities (RBRP) which highlights the importance
of riparian buffers for stream restoration projects (Breeding, 2010). The Site is located in the Neuse
River Basin HUC 03020201010050 and NC Division of Water Resources (NCDWR) Subbasin 03-04-01. The
Site contains Dry Creek and eight unnamed tributaries (UT1-UT7; UT1a) which flow to Lake Michie on
the Flat River and then into Falls Lake. The Flat River is classified as Water Supply Waters (WS-III), and
Nutrient Sensitive Waters (NSW). The downstream drainage area of the Site is 807 acres. The 29.764-
acre Site is protected with a permanent conservation easement.
The project goals established in the Mitigation Plan (Wildlands, 2018) were completed with careful
consideration of goals and objectives described in the Neuse River RBRP. The project goals include:
• Exclude cattle from project streams;
• Stabilize eroding stream banks;
• Improve the stability of stream channels;
• Improve instream habitat;
• Reconnect channels with floodplains and riparian wetlands to allow a natural flooding regime;
• Restore and enhance native floodplain and streambank vegetation; and
• Permanently protect the Site from harmful land uses.
The project will contribute to achieving the goals for the watershed listed in the Neuse River RBRP and
provide ecological benefits within the Neuse River Basin. While benefits such as habitat improvement
and geomorphic stability are limited to the Site, others, such as reduced pollutant and sediment loading,
have farther reaching effects.
Site construction, planting, and as -built surveys were completed in April 2020. Monitoring Year 2 (MY2)
assessments and site visits were completed between January and October 2021. Overall, the Site has
fulfilled the required stream success criteria for MY2. All restored streams are stable and functioning as
designed and the isolated area of bank scour directly downstream of the culvert crossing on Dry Creek
Reach 4 was repaired in March 2021. This area has remained stable since the repairs were made. Native
herbaceous wetland vegetation has established on the Site creating excellent groundcover. This
herbaceous vegetation has hindered some of the planted tree growth, but volunteers are establishing
across the Site and supplementing planted trees. Eight of twelve vegetation monitoring plots met the
interim success criteria with an average stem density of 349 planted stems per acre. Next year volunteer
trees species will be included in the vegetation data and should boost stem density across the Site.
Multiple bankfull events were recorded on each restoration reach during the 2021 annual monitoring
period. Additionally, the flow gages on UT1A, UT2, and UT5 Reach 1 easily exceeded the minimum
requirement of 30 consecutive days of baseflow. Overall, the Site is succeeding with reducing sediment
and nutrient inputs into Neuse River tributaries.
Dry Creek Mitigation Site
Monitoring Year 2 Annual Report - Final
DRY CREEK 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
Vegetative Assessment......................................................................................................1-2
1.2.2
Vegetation Areas of Concern.............................................................................................1-3
1.2.3
Stream Assessment............................................................................................................1-3
1.2.4
Stream Areas of Concern...................................................................................................1-3
1.2.5
Hydrology Assessment.......................................................................................................1-4
1.2.6
Wetland Assessment..........................................................................................................1-4
1.2.7
Adaptive Management Plan...............................................................................................1-4
1.3
Monitoring Year 2 Summary......................................................................................................1-4
Section2:
METHODOLOGY.............................................................................................................2-1
Section 3:
REFERENCES...................................................................................................................3-1
TABLES
Table 1: Mitigation Goals and Objectives — Dry Creek Mitigation Site......................................................1-2
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 Contact Table
Table 4
Project Information and Attributes
Appendix 2
Visual Assessment Data
Figure 3-3b
Integrated Current Condition Plan View
Table 5a-e
Visual Stream Morphology Stability Assessment Table
Table 6
Vegetation Condition Assessment Table
Stream Photographs
Stream Area of Concern Photographs
Stream Crossing Photographs
Vegetation Plot Photographs
Appendix 3
Vegetation Plot Data
Table 7
Vegetation Plot Criteria Attainment Table
Table 8
CVS Vegetation Tables - Metadata
Table 9a
Fixed Plots: Planted and Total Stem Counts
Table 9b
Random Plots: Planted and Total Stem Counts
Dry Creek Mitigation Site
Monitoring Year 2 Annual Report - Final ii
Appendix 4 Morphological Summary Data and Plots
Table 10a-d Baseline Stream Data Summary
Table 11a-b Morphology and Hydraulic Summary (Dimensional Parameters — Cross -Section)
Table 12a-h Monitoring Data — Stream Reach Data Summary
Cross -Section Plots
Reachwide Pebble Count Plots
Appendix 5
Hydrology Summary Data
Table 13
Bankfull Events
Table 14
Rainfall Summary
Table 15
Wetland Gage Summary
Wetland Gage Plots
Table 16
Recorded In -Stream Flow Events Summary
Recorded In -Stream Flow Events Plots
Dry Creek Mitigation Site
Monitoring Year 2 Annual Report - Final
Section 1: PROJECT OVERVIEW
The Dry Creek Mitigation Site (Site) is located in northeastern Durham County, approximately three
miles northwest of Butner, NC and approximately 2 miles west of the Granville County/Durham County
line (Figure 1). The Site contains tributaries to Lake Michie on the Flat River, which flows directly into
Falls Lake. Flat River is classified as Water Supply Waters (WS-III) and Nutrient Sensitive Waters (NSW).
The Site is within Hydrologic Unit Code (HUC) 03020201010050, Subbasin 03-04-01 and is located within
the Neuse River Targeted Local Watershed (Figure 1) and is identified in the 2010 Neuse River Basin
Restoration Priorities (RBRP) (Breeding, 2010). The Site is located in in the Carolina Slate Belt of the
Piedmont Physiographic Province (USGS, 1998). The project watershed consists primarily of agricultural
and wooded land. The drainage area for the Site is 807 acres (1.26 square miles).
The project streams consist of Dry Creek and eight unnamed tributaries. Mitigation work within the Site
included restoration, enhancement I, enhancement II, and preservation of 9,810 linear feet of perennial
and intermittent stream channels. The riparian areas were planted with native vegetation to improve
habitat and protect water quality. The final Mitigation Plan (Wildlands, 2018) was submitted to and
accepted by DMS in October 2018. Construction activities were completed by Land Mechanic Designs,
Inc. in April 2020. Planting and seeding activities were completed by Bruton Natural Systems, Inc. in April
2020. Baseline monitoring (MYO) was conducted between March and April 2020. Annual monitoring will
occur for seven years with the close-out anticipated to commence in 2027 provided the success criteria
are met. Appendix 1 provides additional details on project activity, history, contact information, and
watershed background information for the Site.
Prior to construction activities, cattle were rotationally grazed along UT1, UT1a, and Dry Creek to the
UT3 confluence. Cattle access to these streams resulted in significant ecological impacts. Table 4 in
Appendix 1 and Tables 10a-d in Appendix 4 present the pre -restoration conditions data.
The Site is located on 9 parcels under 6 different landowners and a conservation easement was
recorded on 29.764 acres. The project is expected to provide 8,457.934 stream credits at closeout. A
Project Vicinity Map and directions are provided in Figure 1, and Project Components / Asset Map are
illustrated in Figure 2.
1.1 Project Goals and Objectives
The project is intended to provide numerous ecological benefits. While benefits such as habitat
improvement and geomorphic stability are limited to the Site, reduced nutrient and sediment loading
have farther reaching effects. Table 1 below describes expected outcomes to water quality and
ecological processes and provides project goals and objectives. These goals were established and
completed with careful consideration of goals and objectives described in the RBRP and to meet the
DMS mitigation needs while maximizing the ecological and water quality uplift within the watershed.
Dry Creek Mitigation Site
Monitoring Year 2 Annual Report - Final 1-1
Table 1: Mitigation Goals and Objectives — Dry Creek Mitigation Site
Goals
Objectives
Expected Outcomes
Install fencing around project areas
Reduce and control sediment inputs. Reduce
Exclude cattle from
adjacent to cattle pastures or remove
and manage nutrient inputs. Contribute to
project streams.
cattle from the Site.
protection of or improvement to a Water
Supply Waterbody.
Reconstruct stream channels slated for
restoration with stable dimensions.
Stabilize eroding
Create stable tie-ins for tributaries
Reduce sediment inputs. Contribute to
stream banks.
joining restored channels. Add bank
protection of or improvement to a Water
revetments and in -stream structures to
Supply Waterbody.
reaches to protect restored/enhanced
streams.
Construct stream channels that will
Improve the
maintain a stable pattern and profile
Reduce and control sediment inputs.
stability of stream
considering the hydrologic and sediment
Contribute to protection of or improvement
channels.
inputs to the system, the landscape
to a Water Supply Waterbody.
setting, and the watershed conditions.
Install habitat features such as
constructed riffles, cover logs, and brush
Improve instream
toes into restored/enhanced streams.
Improve aquatic communities in project
habitat.
Add woody materials to channel beds.
streams.
Construct pools of varying depth.
Reduce and control sediment inputs. Reduce
Reconnect channels
Reconstruct stream channels with
and manage nutrient inputs. Contribute to
with floodplains.
appropriate bankfull dimensions and
protection of or improvement to a Water
depth relative to the existing floodplain.
Supply Waterbody. Enhance hydration of
riparian wetlands.
Reduce and control sediment inputs. Reduce
Restore and
and manage nutrient inputs. Provide a
enhance native
Plant native tree species in riparian zone
canopy to shade streams and reduce
floodplain
where currently insufficient.
thermal loadings. Contribute to protection
vegetation.
of or improvement to a Water Supply
Waterbody.
Permanently
Ensure that development and agricultural
protect the project
Establish conservation easements on the
uses that would damage the Site or reduce
Site from harmful
Site.
the benefits of the project are prevented.
uses.
1.2 Monitoring Year 2 Data Assessment
Annual monitoring and site visits were conducted during MY2 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, 2018).
1.2.1 Vegetative Assessment
Planted woody vegetation is being monitored in accordance with the guidelines and procedures
developed by the Carolina Vegetation Survey-EEP Level 2 Protocol (Lee et al., 2008). A total of eleven
standard 10 meter by 10 meter and one, 5 meter by 20 meter vegetation plots were established during
Dry Creek Mitigation Site
Monitoring Year 2 Annual Report - Final 1-2
baseline monitoring. Four of the twelve vegetation plots will be relocated randomly on an annual basis
to monitor vegetation health across the Site.
The final vegetation success criteria at the end of MY7 are the survival of 210 planted stems per acre
averaging 10 feet in height. Interim success criteria are the survival of 320 planted stems per acre at the
end of MY3 and 260 planted stems per acre with an average stem height of 7 feet at the end of MYS.
The MY2 vegetative survey was completed in September 2021. Vegetation monitoring resulted in an
average stem density of 349 planted stems per acre, which is above the interim requirement of 320
stems per acre required at MY3 and approximately 34% less than the recorded baseline density (533
planted stems per acre). There is an average of 8 stems per plot as compared to 13 stems per plot in
MYO. Of the 12 vegetation plots, 8 plots individually met the interim success criteria and are on track to
meet the final success criteria required for MY7. Fixed vegetation plots (VP) 5, 6, 7, and 8 do not meet
the interim success criteria of 320 stems per acre. However, fixed vegetation plots 5, 7, and 8 are on
track to meet the final success criteria of 210 stems per acres. Sycamore (Platanus occidentalis)
volunteers were noted in fixed vegetation plots 5, 7, and 8 but will not be counted towards success
criteria until MY3. Due to the high number of volunteers already germinating throughout the Site, no
remedial action is needed at this time. These vegetation plots will continue to be monitored to
determine if remedial action is warranted. Refer to Appendix 2 for Vegetation Plot Photographs and the
Vegetation Condition Assessment Table and Appendix 3 for Vegetation Plot Data.
1.2.2 Vegetation Areas of Concern
The MY2 visual assessment did indicate the vegetation plots are representative of planted trees
throughout the Site, however there are a healthy number of volunteers germinating throughout the
Site. It was assessed that herbaceous vegetation is dense throughout most of the Site hindering planted
tree establishment. The herbaceous vegetation includes native pollinator species and wetland species
indicating 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. Vegetation near fixed plots 5-8 will
be assessed throughout the future monitoring years to determine if replanting is necessary.
1.2.3 Stream Assessment
Morphological surveys for MY2 were conducted in June 2021. All streams within the Site are stable and
functioning as designed. All 19 cross -sections at the Site show little to no change in the bankfull area and
width -to -depth ratio, and bank height ratios are less than 1.2. Substrate measurements indicate the
maintenance of coarser materials in the riffle reaches and finer particles in the pools. Longitudinal
profile surveys are not required on the project unless visual inspection indicates reach wide vertical
instability. Refer to Appendix 2 for the Visual Stream Morphology Stability Assessment Table, Integrated
Current Condition Plan View (CCPV), and Stream Photographs. Refer to Appendix 4 for the
Morphological Summary Data and Plots.
1.2.4 Stream Areas of Concern
Localized bank erosion on the outside bend of a pool directly downstream of the culvert crossing along
Dry Creek Reach 4, was identified during MY1. This area was repaired in March 2021. The stream bank
repair included reshaping the stream bank and installing sod mats and live stakes. After more than six
months and several storm events, the repair is stable, and vegetation is establishing. See before and
after photos of the area in Appendix 2. This area will continue to be monitored to determine the
success of the repair work.
Dry Creek Mitigation Site
Monitoring Year 2 Annual Report - Final 1-3
1.2.5 Hydrology Assessment
By the end of MY7, four bankfull events must have occurred in separate years within the restoration and
enhancement I reaches. Bankfull events were recorded on Dry Creek Reach 2 and 3 along with UT1
Reach 2, UT5 Reach 1 and UT6 Reach 1. Dry Creek Reach 2 and 3, UT1 Reach 2 and UT5 Reach 1 have
partially met the hydrologic success criteria for bankfull events.
In addition, the presence of baseflow must be documented on restored intermittent reaches (UT1A, UT2
and UT5 Reach 1) for a minimum of 30 consecutive days during a normal precipitation year. In -stream
flow gages equipped with pressure transducers were installed to monitor continuity of baseflow. UT1A,
UT2, and UT5 Reach 1 easily exceeded baseflow success criterion for intermittent streams. The
maximum consecutive days ranged from 140 days to 284 days. Refer to Appendix 5 for hydrologic data.
1.2.6 Wetland Assessment
One groundwater gage was installed and monitored within an existing wetland zone at a location
requested by North Carolina Division of Water Resources. The gage was downloaded and maintained
quarterly. The purpose of the gauge is to assess potential effects to wetland hydrology from the
construction of the restored stream channel through this area. The results of this monitoring are not
tied to a success criterion. The measured hydroperiod was 3.5% of the growing season consecutively.
Hydrology associated with the existing wetland currently being monitored was largely the result of the
backwater effect of an impoundment on Dry Creek. By removing the impoundment during stream
restoration activities, Wildlands anticipates an effect on hydrology and the associated gage
results. While the gage results may indicate hydrological impairment, the overall ecological uplift
associated with removal of the man-made impoundment outweighs the potential reduction in
groundwater hydrology.
1.2.7 Adaptive Management Plan
Vegetation around fixed vegetation plots 5-8 will be assessed in future monitoring years to determine if
remedial actions are necessary. Currently no remedial action is needed at this time.
1.3 Monitoring Year 2 Summary
Of the 12 vegetation plots, 8 are on track to meet the MY3 interim requirement of 320 planted stems
per acre. A dense herbaceous layer including wetland and pollinator species has established across the
Site. This layer is great for ground cover and diversity but has hindered planted tree establishment on
parts of the Site. Sycamore and other volunteer woody stems have began establishing throughout the
Site and will be included in MY3 vegetation data. All streams within the Site are stable and functioning
as designed. The localized erosion identified in MY1 on Dry Creek Reach 4 was repaired and is stable.
Multiple bankfull events were documented on all stream reaches partially fulfilling the final bankfull
hydrologic success requirement. Greater than 30 days of consecutive flow were recorded on monitored
intermittent stream reaches UT1a, UT2, and UT5 Reach 1 fulfilling MY2 success requirement. Overall,
the Site is meeting its goals of preventing excess nutrients and sediment from entering the Neuse River
tributaries and is on track to meet final success criteria.
Summary information and data related to the performance of various project and monitoring elements
can be found in the tables and figures in the report appendices. Narrative background and supporting
information formerly found in these reports can be found in the Mitigation Plan (Wildlands, 2018)
available on DMS's website. All raw data supporting the tables and figures in the appendices are
available from DMS upon request.
Dry Creek Mitigation Site
Monitoring Year 2 Annual Report - Final 1-4
Section 2: METHODOLOGY
Geomorphic data was collected following the standards outlined in The Stream Channel Reference Site:
An Illustrated Guide to Field Techniques (Harrelson et al., 1994) and in Stream Restoration: A Natural
Channel Design Handbook (Doll et al., 2003). All Integrated Current Condition Mapping was recorded
using a Trimble handheld GPS with sub -meter accuracy and processed using Pathfinder and ArcGIS.
Crest gages and pressure transducers were installed in riffle cross -sections and monitored throughout
the year. Hydrologic monitoring instrument installation and monitoring methods are in accordance with
the United States Army Corps of Engineers standards (USACE, 2003). Vegetation monitoring protocols
followed the Carolina Vegetation Survey-EEP Level 2 Protocol (Lee et al., 2008).
Dry Creek Mitigation Site
Monitoring Year 2 Annual Report - Final 2-1
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. Retrieved from http://cvs.bio.unc.edu/protocol/cvs-eep-protocol-v4.2-lev1-5.pdf.
Rosgen, D. L. 1994. A classification of natural rivers. Catena 22:169-199.
Rosgen, D.L. 1996. Applied River Morphology. Pagosa Springs, CO: Wildland Hydrology Books.
Rosgen, D.L. 1997. A Geomorphological Approach to Restoration of Incised Rivers. Proceedings of the
Conference on Management of Landscapes Disturbed by Channel Incision. Center For
Computational Hydroscience and Bioengineering, Oxford Campus, University of Mississippi, Pages
12-22.
United States Army Corps of Engineers. 2003. Stream Mitigation Guidelines. USACE, NCDENR-DWQ,
USEPA, NCWRC.
United States Geological Survey. 1998. North Carolina Geology.
http://www.geology.enr.state.nc.us/usgs/carolina.htm
Wildlands Engineering, Inc. (2018). Dry Creek Mitigation Project Mitigation Plan. DMS, Raleigh, NC.
Dry Creek Mitigation Site
Monitoring Year 2 Annual Report - Final 3-1
APPENDIX 1. General Figures and Tables
/
'7k ChuTc Project Location
C,
a;
County Line
..40
03020201010040
r1 Hydrologic Unit Code (14 Digit)
20
:
DIMS Targeted Local Watersheds
N
R .............PF. S2N Person Co.
----------------------------------
DU R H A
6 1 6
M
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>
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0,
03020201040010
03020201010030
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03020201010050
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03020201040020
03020201020040
Directions:
From Raleigh, NC, take U.S. 70 W/NC-50
The subject project site is an environmental restoration site of the
N/Glenwood Avenue. Turn right in 3.9 miles
NCDEQ Division of Mitigation Services (DMS) and is
onto NC-50 N/Creedmoor Rd. Stay on
encompassed by a recorded conservation easement, but is —1
Creedmoor Rd for 15.9 miles. Turn left1C
bordered by land under private ownership. Accessing the site may
onto Old Weaver Trail. Turn right onto
require traversing areas near or along the easement boundary and
Cash Rd in 1.3 miles. Cash Rd turns into
therefore access by the general public is not permitted. Access by
Gate 2 Rd, which turns into Central Ave.
authorized personnel of state and federal agencies or their
Turn left onto 33rd St and then take
designees/contractors involved in the development, oversight,
and stewardship of the restoration site is permitted within the terms
and immediate left onto Old NC 75. In
and timeframes of their defined roles. Any intended site visitation or
0.4 miles turn right onto Range Rd. Turn
N
activity by any person outside of these previously sanctioned roles
J left onto Hampton Rd in 4.0 miles. The
and activities requires prior coordination with DMS.
1 project ect will be on the left in 0.3 miles.
�WILDLANDS
ENGINEERING
Figure 1. Project Vicinity Map
Dry Creek Mitigation Site
0 0.5 1 Miles
t DMS Project No. 97082
Monitoring Year 2 - 2021
Durham County, NC
t r�
' Y 7Yt � • rj
Valk
VA
f
J of 8
t, V _
+1
I_
! *t
i
� r
�A
�4
.r
+`
• .—,; � ---� Conservation Easement
Y �`atl Internal Crossing
S
•� � 'f 5 � �� ®Existing Wetlands
to s = Fencing
Utility Right of Way
Tt,&b ; �� I� '. Y •" Stream Restoration
II . Stream Enhancement I
I
Stream Enhancement II
i' _ •� —Stream Preservation
t Y _
� + 4rza Q9 � � t _ —Not For Credit
,.
.p Reach Breaks
Figure 2. Project Component / Asset Map
�A W I L D L A N D S Dry Creek Mitigation Site
\�/ ENGINEERING
0 350 700 Feet DMS Project No. 97082
I i I i I Monitoring Year 2- 2021
Durham County, NC
Table 1. Mitigation Assets and Components
Dry Creek Mitigation Site
DMS Project No. 97082
Monitoring Year 2 - 2021
Mitigation
Reach IPlan
7,oisting
otage
Footage
Mitigation
Category
Restoration
Level
Priority Level
Mitigation
Ratio
(X:1)
Project
Credits
As -Built
Footage
Comments
STREAMS
Pond Removal, Full Channel
Dry Creek Reach 1
999
1,278
Warm
R
P1
1
1,278.000
1,247
Restoration, Planted Buffer, Fencing
Out Livestock
81
Warm
R
P1
1
81.000
84
Full Channel Restoration, Planted
Buffer, Fencing Out Livestock
Dry Creek Reach 2
2,104
1,681
Warm
R
1
1,681.000
1,656
Full Channel Restoration, Planted
Buffer, Fencing Out Livestock
85
Warm
R
P1
1
85.000
75
Full Channel Restoration, Planted
Buffer, Fencing Out Livestock
Dry Creek Reach 3
1,955
1,603
Warm
R
P1
1
1,603.000
1,583
Full Channel Restoration, Invasive
Removal
241
Warm
R
P1
1
241.000
243
Full Channel Restoration, Invasive
Removal
Dry Creek Reach 4
1,495
813
Warm
R
P1
1
813.000
807
Full Channel Restoration, Invasive
Removal
216
Warm
Ell
N/A
2.5
86.400
215
Bank Repairs, Fencing Out Livestock,
Planted Buffer
UT1 Reach 1
456
205
Warm
Ell
N/A
2.5
82.000
202
Bank Repairs, Fencing Out Livestock,
Planted Buffer
Pond Removal, Full Channel
631
Warm
R
P1
1
631.000
627
Restoration, Planted Buffer, Fencing
Out Livestock
N/A
Culvert Crossing, Utility Relocati,
Easement Bra=
UT1 Reach 2
945
436
Warm
R
P1
1
436.000
426
Full Channel Restoration, Planted
Buffer, Fencing Out Livestock
UT1A
90
166
Warm
El
N/A
1.5
110.667
165
Grade Control Structures, Fencing
UT2
72
151
Warm
Ell
N/A
2.5
60.400
135
Bank Repairs, Fencing Out Livestock
UT3
153
156
Warm
Ell
N/A
2.5
62.400
160
Bank Repairs, Fencing Out Livestoc
UT4
110
115
Warm
P
N/A
10
11.500
114
Conservation Easement
UT5 Reach 1
371
298
Warm
El
N/A
1.5
198.667
285
Grade Control Structures, Invasive
Removal, Planted Buffer
Cul Break
UT5 Reach 21
135
119
Warm
R
P1
1
104.000
112
Full Channel Restoration
UT6 Reach 1
582
617
Warm
R
P1
1
617.000
612
Full Channel Restoration, Invasive
Removal
UT6 Reach 2
209
209
Warm
P
N/A
10
20.900
209
Conservation Easement
UT6 Reach 3
58
89
Warm
R
P1
1
89.000
89
Full Channel Restoration, Invasive
Removal
367
415
Warm
Ell
N/A
2.5
166.000
408
Bank Repairs
1. No credit proposed for UT5 Reach 2 Station 705+61 to 705+76 due to easement width being less than 15 feet wide.
PROJECTIL
Restoration Level
Stream
Riparian Wetland
Non -Riparian
Wetland
Coastal
Marsh
Warm
Cool
Cold
Riverine
Non-Riverine
Restoration
7,659.000
Enhancement 1
309.334
Enhancement 11
457.200
Preservation
32.400
Re -Establishment
Rehabilitation
Enhancement
Creation
Totals
8,457.934
Table 2. Project Activity and Reporting History
Dry Creek Mitigation Site
DIMS Project No. 97082
Monitoring Year 2 - 2021
Activity or Report
Mitigation Plan
Data Collection Complete
October 2018
Completion or Scheduled Delivery
October 2018
Final Design - Construction Plans
November 2019
November 2019
Construction
October 2019 - April 2020
April 20, 2020
Temporary S&E mix applied to entire project area 1
October 2019 - April 2020
April 20, 2020
Permanent seed mix applied to reach/segments'
October 2019 - April 2020
April 20, 2020
Bare root and live stake plantings for reach/segments
April 2020
April 24, 2020
Baseline Monitoring Document (Year 0)
Stream Survey
April 30,2020
August 2020
Vegetation Survey
April 27, 2020
Year 1 Monitoring
Stream Survey
November 4, 2020
December 2020
Vegetation Survey
November 4, 2020
Manual Bank Repair
March 2021
Year 2 Monitoring
Stream Survey
June 10, 2021
December 2021
Vegetation Survey
September 16, 2021
Year 3 Monitoring
Stream Survey
2022
December 2022
Vegetation Survey
2022
Year 4 Monitoring
December 2023
Year 5 Monitoring
Stream Survey
2024
December 2024
Vegetation Survey
2024
Year 6 Monitoring
December 2025
Year 7 Monitoring
Stream Survey
2026
December 2026
Vegetation Survey
2026
'Seed and mulch is added as each section of construction is completed.
Table 3. Project Contact Table
Dry Creek Mitigation Site
DIMS Project No. 97082
Monitoring Year 2 - 2021
Wildlands Engineering, Inc.
Designer
312 West Millbrook Road, Suite 225
Nicole Macaluso Millns, PE
Raleigh, NC 27609
919.851.9986
Land Mechanic Designs, Inc.
Construction Contractor
126 Circle G Lane
Willow Spring, NC 27592
Bruton Natural Systems, Inc
Planting Contractor
P.O. Box 1197
Fremont, NC 27830
Land Mechanic Designs, Inc.
Seeding Contractor
126 Circle G Lane
Willow Spring, NC 27592
Seed Mix Sources
Garrett Wildflower Seed Company
Nursery Stock Suppliers
Dykes and Sons Nursery and Greenhouse
Bare Roots
Live Stakes
Bruton Natural Systems, Inc
Monitoring Performers
Wildlands Engineering, Inc.
Jason Lorch
Monitoring, POC
919.851.9986
Table 4. Project Information and Attributes
Dry Creek Mitigation Site
DMS Project No. 97082
Monitoring Year 2 - 2021
PROJECT• •
Project Name Dry Creek Mitigation Site
County
IDurham County
Project Area (acres)
29.764
Planted (acres)
114.040
Project Coordinates (latitude and longitude)
36' 11' 07.92" N, 78' 49' 39.00" W
Physiographic Province
PROJECT• SUMMARY INFORMATION
Carolina Slate Belt ofthe Piedmont Physiographic Province
River Basin
Neuse River
USGS Hydrologic Unit 8-digit
03020201
USGS Hydrologic Unit 14-digit
03020201010050
D W R Sub -basin
03-04-01
Project Drainiage Area (acres)
807
Project Drainage Area Percentage of Impervious Area
Q%
CGIA Land Use Classification
50%Forested,
REACH
40%Cultivated, 9%Residential Area
SUMMARY INFORMATION
Parameters
Dry Creek
UT1
UT1a
UT2 UT3 UT4 UTS UT6 UT7
Length of Reach (linear feet) - Post -Restoration
5,883
1,559
165
135 160 114 397 910 408
Drainage Area (acres)
807
85
22
4 17 33 40 17 64
NCDWR Stream Identification Score
50.5
32.25
27.5
24.5 26 24 1 25.5 1 36 1 35.5
NCDWR Water Quality Classification
WS-III (NSW)
Morphological Desnption (stream type)
Perennial Intermittent Perennial
Evolutionary Trend (Simon's Model) - Pre -Restoration
IV: Degradation and Widening
III
Chan nelized
I Premodified
IV Degradation and Widening
Underlying Mapped Soils
Chewacla loam, Herndon silt Ioam,Tatum silt loam
Drainage Class
Soil Hydric Status
Slope
FEMA Classification
Zone X
Native Vegetation Community
Piedmont Bottomland Forest
Percent Composition Exotic Invasive Vegetation - Post -Restoration
Regulation
0%
REGULATORY• • •
Applicable? Resolved? Supporting Documentation
Waters ofthe United States -Section 404
Yes
Yes
USACE Nationwide Permit No. 27 and DWQ 401 Water Quality Certification No. 4134.
Waters ofthe United States- Section 401
Yes
Yes
Division of Land Quality (Dam Safety)
N/A
N/A
N/A
Endangered Species Act
Yes
Yes
Dry Creek Mitigation Plan; Wildlands determined "no effect" on Orange County listed endangered
species. The USFWS responded on May 5, 2016 and concurred with NCWRC stating that "the proposed
action is not likely to adversely affect any federally -listed endangered or threatened species, their
formally designated critical habitat, or species currently proposed for listing under the Act."
Historic Preservation Act
Yes
Yes
Correspondence from SHPO on April 26, 2016 indicating they were not aware of any historic resource
that would be affected by the project.
Coastal Zone Management Act (CZMA)/Coastal Area Management Act
(CAMA)
N/A
N/A
N/A
FEMA Floodplain Compliance
Yes
Yes
Durham County Floodplain Development Permit No. 19800028 was obtained on August 1, 2019
Essential Fisheries Habitat
N/A
N/A
N/A
APPENDIX 2. Visual Assessment Data
Figure 3. Integrated Current Condition Plan View (Key)
�A W I L D L A N D S Dry Creek Mitigation Site
\�/ ENGINEERING
0 350 700 Feet DMS Project No. 97082
1 1 1 1 I t
Monitoring Year 2- 2021
Durham County, NC
�Ilk
one= an
mar
d:
70
Y
�ti. o� �• �, � 109+0. nY
r213 ,.
,ly �
�
(2� Y
�S`00 113+00
'kS 6
3
27
♦ � rri
t
Reach^2
2020 Aerial Photography
4.,WILDLANDS
NGINEERING
0 200 400 Feet
I I I I I
1
Conservation Easement
Existing Wetlands
--
Structures
Fixed Vegetation Plot Condition - MY2
- Criteria Met
- Criteria Not Met
Random Vegetation Plot Condition - MY2
t
Criteria Met
Fencing
--- Utility Right of Way
- Stream Restoration
Stream Enhancement I
- Stream Enhancement 11
- Stream Preservation
- Not For Credit
Top of Bank
Cross -Sections
Q Reach Breaks
♦ Barotroll
® Groundwater Well
♦ Crest Gauge
♦ Flow Gauge
Photo Points
Figure 3a. Integrated Current Condition Plan View
Dry Creek Mitigation Site
DIMS Project No. 97082
Monitoring Year 2 - 2021
Durham County, NC
i / Ica*uu
y
ti.-5:�i�. � �. .may �►'
! • O• 133+pp • -
� 1
� � �i t35+pp• i � 'l`�� 4
10
. r #A
Y r /
-59
I
I i
' i . ,moo ► � �. 12 •
r
oak /
Reach 4
— Conservation Easement
« Existing Wetlands
- Structures
Fixed Vegetation Plot Condition - MY2
Criteria Met
Criteria Not Met
Random Vegetation Plot Condition - MY2
Q Criteria Met
_ Fencing
--- Utility Right of Way
Stream Restoration
Stream Enhancement I
Stream Enhancement II
Stream Preservation
Not For Credit
Top of Bank
Cross -Sections
Stream Area of Concern - MY2
Stream Repair
•Q Reach Breaks
Crest Gauge
Flow Gauge
Photo Points
O
Figure 3b. Integrated Current Condition Plan View
�A W I L D L A N D S Dry Creek Mitigation Site
\�/ ENGINEERING
0 200 400 Feet DIMS Project No. 97082
I i I i I Monitoring Year 2- 2021
Durham County, NC
Table Sa. Visual Stream Morphology Stability Assessment Table
Dry Creek Mitigation Site
DIMS Project No. 97082
Monitoring Year 2 - 2021
Dry Creek Reach 1-4: 5,883 LF
M
.nnel
ciry
r.r1eg
1. Bed
Number
Stahl Total Number
Channel Sub -Category Metric as
Perform ieng in As -Built
Intended 11101IMi
1. Vertical Stability Aggradation
Number wit Footage with Adjust %for
INumberofl Annountof Stahl St I"
Unstable Unstable Performing a ell
Woo Y Wo dy Woody
Segments Intended Vegetationj Veget'aticm Vegetation_
0 0 100%
(Riffle and Run Units) Degradation
0 0 100%
2. Riffle Condition Texture/Substrate 55
55
100%
100%
3. Meander Pool Depth Sufficient 58
58
Condition Length Appropriate 58
100%
58
Thalweg centering at upstream of 55
55
4. Thalweg Position meander bendRunThalweg
HOO'/'
55
centering at downstream of 55
meander bend Glide
2. Bank
Bank lacking vegetative cover resulting
1. Scoured/Eroded
simply from poor growth and/or scour
0
0
100%
n/a
n/a
n/a
and erosion.
Banks undercut/overhanging to the
extent that mass wasting appears likely.
2. Undercut
Does NOT include undercuts that are
0
0
100%
n/a
n/a
n/a
modest, appear sustainable and are
providing habitat.
3. Mass Wasting
Bank slumping, caving, or collapse.
0
0
100%
n/a
n/a
n/a
Totals
0
0
100%
n/a
n/a
n/a
3. Engineered
Structures'
Structures physically intact with no
1. Overall Integrity
dislodged boulders or logs.
12
12
100%
Grade control structures exhibiting
2. Grade Control
maintenance of grade across the sill.
12
12
100%
Structures lacking any substantial flow
2a. Piping
underneath sills or arms.
12
12
100%
Bank erosion within the structures
3. Bank Protection
extent of influence does not exceed
36
36
100%
15%.
Pool forming structures maintaining
4. Habitat
—Max Pool Depth : Bankfull Depth >_ 1.6
36
36
100%
Rootwads/logs providing some cover at
baseflow.
Excludes constructed riffles since they are evaluated In section 1.
Table 5b. Visual Stream Morphology Stability Assessment Table
Dry Creek Mitigation Site
DIMS Project No. 97082
Monitoring Year 2 - 2021
UTl Reach 2: 1,053 LF
Major haInnel
,diry
Cater
1. Bed
Nu her
I St or le, Total Number
hannel Sub -Category Metric o -Built
Perf not ng a in As
Intended 11101IMi
1. Vertical Stability Aggradation
Numbe
INumberofl Annountof Stahl S. ,,rwit Footage with Adjust %for
Unstable Unstable Performing a ell
Woo Y Woody Woody
Segments Intended Vegetationj Vegetation Vegetation
0 0 100%
(Riffle and Run Units) Degradation
0 0 100%
2. Riffle Condition Texture/Substrate 22
22
100%
100%
3. Meander Pool Depth Sufficient 21
21
Condition Length Appropriate 21
100%
21
100%
Thalweg centering at upstream of 22
22
4. Thalweg Position mea nder bend Run
22
Thalweg centering at downstream of 22
meander bend Glide
100%
2. Bank
Bank lacking vegetative cover resulting
1. Scoured/Eroded
simply from poor growth and/or scour
0
0
100%
n/a
n/a
n/a
and erosion.
Banks undercut/overhanging to the
extent that mass wasting appears likely.
2. Undercut
Does NOT include undercuts that are
0
0
100%
n/a
n/a
n/a
modest, appear sustainable and are
providing habitat.
3. Mass Wasting
Bank slumping, calving, or collapse
0
0
100%
n/a
n/a
n/a
Totals
0
0
100%
n/a
n/a
n/a
3. Engineered
Structures'
Structures physically intact with no
1. Overall Integrity
dislodged boulders or logs.
3
3
100%
2. Grade Control
Grade control structures exhibiting
3
3
100%
maintenance of grade across the sill.
Structures lacking any substantial flow
2a. Piping
underneath sills or arms.
3
3
100%
Bank erosion within the structures
3. Bank Protection
extent of influence does not exceed
10
10
100%
15%.
Pool forming structures maintaining
4. Habitat
—Max Pool Depth : Bankfull Depth >_ 1.6
10
10
100%
Rootwads/logs providing some cover at
baseflow.
'Excludes constructed riffles since they are evaluated In section 1.
Table Sc. Visual Stream Morphology Stability Assessment Table
Dry Creek Mitigation Site
DIMS Project No. 97082
Monitoring Year 2 - 2021
UT1A: 165 LF
Number
Major Channel Stable ' Total Number
Channel Sub -Category Metric
Category Performing as in As -Built
Intended
1. Bed Aggradation
1. Vertical Stability
Number wit Foot ge with Adjust %for
Numberofl Annountof % Stahl e. Stabilizing Stahilizing Stabilizing
Unstable Unstable Performing a 'di
Woo Y Woody Woody
Segments Intended Vegetationj Vegetation Vegetation
0 0 100%
(Riffle and Run Units) Degradation
0 0 100%
2. Riffle Condition Texture/Substrate 5 5
100%
100%
3. Meander Pool Depth Sufficient 5
5
Condition Length Appropriate 5
100%
100%
5
Thalweg centering at upstream of 5
5
4. Thalweg Position meander bend Run
5
Thalweg centering at downstream of 5
meander bend Glide
100%
2. Bank
Bank lacking vegetative cover resulting
1. Scoured/Eroded
simply from poor growth and/or scour
0
0
100%
n/a
n/a
n/a
and erosion.
Banks undercut/overhanging to the
extent that mass wasting appears likely.
2. Undercut
Does NOT include undercuts that are
0
0
100%
n/a
n/a
n/a
modest, appear sustainable and are
providing habitat.
3. Mass Wasting
Bank slumping, calving, or collapse
0
0
100%
n/a
n/a
n/a
Totals
0
0
100%
n/a
n/a
n/a
3. Engineered
Structures'
1. Overall Integrity
Structures physically intact with no
0
0
N/A
dislodged boulders or logs.
2. Grade Control
Grade control structures exhibiting
0
0
N/A
maintenance of grade across the sill.
2a. Piping
Structures lacking any substantial flow
0
0
N/A
underneath sills or arms.
Bank erosion within the structures
3. Bank Protection
extent of influence does not exceed
1
1
100%
15%.
Pool forming structures maintaining
4. Habitat
—Max Pool Depth : Bankfull Depth >_ 1.6
1
1
100%
Rootwads/logs providing some cover at
baseflow.
'Excludes constructed riffles since they are evaluated In section 1.
Table Scl. Visual Stream Morphology Stability Assessment Table
Dry Creek Mitigation Site
DIMS Project No. 97082
Monitoring Year 2 - 2021
UTS Reach 1-2: 397 LF
Number
Major Channel Stable ' Total Number
Channel Sub -Category Metric
Category Performing as in As -Built
Intended
1. Bed Aggradation
1. Vertical Stability
Number wit Foot ge with Adjust %for
Numberofl Annountof % Stahl e. Stabilizing Stahilizing Stabilizing
Unstable Unstable Performing a 'dl
Woo Y Woody Woody
Segments Intended Vegetationj Vegetation Vegetation
0 0 100%
(Riffle and Run Units) Degradation
0 0 100%
2. Riffle Condition Texture/Substrate 10 10
100%
100%
3. Meander Pool Depth Sufficient 11
11
Condition Length Appropriate 11
100%
100/
11
Thalweg centering at upstream of 10
10
4. Thalweg Position meander bend Run
10
Thalweg centering at downstream of 10
meander bend Glide
100%
2. Bank
Bank lacking vegetative cover resulting
1. Scoured/Eroded
simply from poor growth and/or scour
0
0
100%
n/a
n/a
n/a
and erosion.
Banks undercut/overhanging to the
extent that mass wasting appears likely.
2. Undercut
Does NOT include undercuts that are
0
0
100%
n/a
n/a
n/a
modest, appear sustainable and are
providing habitat.
3. Mass Wasting
Bank slumping, calving, or collapse
0
0
100%
n/a
n/a
n/a
Totals
0
0
100%
n/a
n/a
n/a
3. Engineered
Structures'
1. Overall Integrity
Structures physically intact with no
0
0
N/A
dislodged boulders or logs.
2. Grade Control
Grade control structures exhibiting
0
0
N/A
maintenance of grade across the sill.
2a. Piping
Structures lacking any substantial flow
0
0
N/A
underneath sills or arms.
Bank erosion within the structures
3. Bank Protection
extent of influence does not exceed
6
6
100%
15%.
Pool forming structures maintaining
4. Habitat
—Max Pool Depth : Bankfull Depth >_ 1.6
6
6
100%
Rootwads/logs providing some cover at
baseflow.
'Excludes constructed riffles since they are evaluated In section 1.
Table Se. Visual Stream Morphology Stability Assessment Table
Dry Creek Mitigation Site
DIMS Project No. 97082
Monitoring Year 2 - 2021
UTb Reach 1 & 3: 701 LF
.nne
ciry
MC.Ieg
1. Bed
Nu her
St or le, Total Number
hannel Sub -Category Metric o
Perf not ng a in As -Built
Intended 11101IMi
1. Vertical Stability Aggradation
Numbe
INumberofl Annountof Stahl S. ,,rwit Footage with Adjust %for
Unstable Unstable Performing a ell
Woo Y Woody Woody
Segments Intended Vegetationj Vegetation Vegetation
0 0 100%
(Riffle and Run Units) Degradation
0 0 100%
2. Riffle Condition Texture/Substrate 34
34
100%
100%
3. Meander Pool Depth Sufficient 32
32
Condition Length Appropriate 32
100%
32
100%
Thalweg centering at upstream of 34
34
4. Thalweg Position mea nder bend Run
34
Thalweg centering at downstream of 34
meander bend Glide
100%
2. Bank
Bank lacking vegetative cover resulting
1. Scoured/Eroded
simply from poor growth and/or scour
0
0
100%
n/a
n/a
n/a
and erosion.
Banks undercut/overhanging to the
extent that mass wasting appears likely.
2. Undercut
Does NOT include undercuts that are
0
0
100%
n/a
n/a
n/a
modest, appear sustainable and are
providing habitat.
3. Mass Wasting
Bank slumping, calving, or collapse
0
0
100%
n/a
n/a
n/a
Totals
0
0
100%
n/a
n/a
n/a
3. Engineered
Structures'
1. Overall Integrity
Structuresphysically intact with no
0
0
N/A
dislodged boulders or logs.
2. Grade Control
Grade control structures exhibiting
0
0
N/A
maintenance of grade across the sill.
2a. Piping
Structures lacking any substantial flow
0
0
N/A
underneath sills or arms.
Bank erosion within the structures
3. Bank Protection
extent of influence does not exceed
17
17
100%
15%.
Pool forming structures maintaining
4. Habitat
—Max Pool Depth : Bankfull Depth >_ 1.6
17
17
100%
Rootwads/logs providing some cover at
baseflow.
'Excludes constructed riffles since they are evaluated In section 1.
Table 6. Vegetation Condition Assessment Table
Dry Creek Mitigation Site
DMS Project No. 97082
Monitoring Year 2 - 2021
Planted Acreage 14.04
Vegetation Category D• . .
NumberMapping
Polygons
Acreage
Acreage
Very limited cover of both woody and herbaceous
Bare Areas 0.1
0
0
o
0/
material.
Low Stem Density Woody stem densities clearly below target levels
0.1
0
0
o
0/
Areas based on MY3, 4, or 5 stem count criteria.
Total
0
0
0%
Areas of Poor Growth
Areas with woody stems of a size class that are
0.25 Ac
0
0
o
0/
Rates or Vigor
obviously small given the monitoring year.
Cumulative Total
0
0.0
0%
STREAM PHOTOGRAPHS
PHOTO POINT 1 Dry Creek R1— upstream (41212021) 1 PHOTO POINT 1 Dry Creek R1— downstream (41212021) 1
PHOTO POINT 2 Dry Creek R1— upstream (41212021)
PHOTO POINT 3 Dry Creek R1— upstream (41212021)
PHOTO POINT 2 Dry Creek R1— downstream (41212021)
PHOTO POINT 3 Dry Creek R1— downstream (41212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
PHOTO POINT 4 Dry Creek R1— upstream (41212021)
PHOTO POINT 5 Dry Creek R2 — upstream (41212021)
PHOTO POINT 6 Dry Creek R2 — upstream (41212021)
PHOTO POINT 4 Dry Creek R1— downstream (41212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
,ate �'•h
C
a't
PHOTO POINT 7 Dry Creek R2 — upstream (41212021)
PHOTO POINT 8 Dry Creek R2 — upstream (41212021)
PHOTO POINT 7 Dry Creek R2 — downstream (41212021)
PHOTO POINT 8 Dry Creek R2 — downstream (41212021)
PHOTO POINT 9 Dry Creek R2 — upstream (41212021) PHOTO POINT 9 Dry Creek R2 — downstream (41212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
PHOTO POINT 10 Dry Creek R3 — upstream (41212021) 1 PHOTO POINT 10 Dry Creek R3 — downstream (41212021) 1
PHOTO POINT 11 Dry Creek R3 — upstream (41212021)
PHOTO POINT 12 Dry Creek R3 — upstream (41212021)
PHOTO POINT 11 Dry Creek R3 — downstream (41212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
PHOTO POINT 13 Dry Creek R3 — upstream (41212021) 1 PHOTO POINT 13 Dry Creek R3 — downstream (41212021) 1
PHOTO POINT 14 Dry Creek R3 — upstream (41212021) 1 PHOTO POINT 14 Dry Creek R3 — downstream (41212021) 1
PHOTO POINT 15 Dry Creek R4 — upstream (41212021)
PHOTO POINT 15 Dry Creek R4 — downstream (41212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
PHOTO POINT 16 Dry Creek R4 — upstream (41212021) PHOTO POINT 16 Dry Creek R4 — downstream (41212021)
PHOTO POINT 17 UT1 R1— upstream (41212021)
PHOTO POINT 18 UT1 R2 — upstream (41212021)
PHOTO POINT 17 UT1 R1— downstream (41212021)
PHOTO POINT 18 UT1 R2 — downstream (41212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
PHOTO POINT 19 UT1 R2 — upstream (41212021)
PHOTO POINT 20 UT1 R2 — upstream (41212021)
PHOTO POINT 21 UT1 R2 — upstream (41212021)
PHOTO POINT 19 UT1 R2 — downstream (41212021)
PHOTO POINT 20 UT1 R2 — downstream (41212021)
PHOTO POINT 21 UT1 R2 — downstream (41212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
PHOTO POINT 22 UT1a — upstream (41212021) 1 PHOTO POINT 22 UT1a — downstream (41212021) 1
PHOTO POINT 23 UT2 — upstream (41212021)
PHOTO POINT 24 UT3 — upstream (41212021)
PHOTO POINT 23 UT2 — downstream (41212021)
PHOTO POINT 24 UT3 — downstream (41212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
PHOTO POINT 25 UT4—upstream (41212021)
PHOTO POINT 25 UT4 — downstream (41212021)
PHOTO POINT 26 UT5 R1— upstream (41212021) 1 PHOTO POINT 26 UT5 R1— downstream (41212021) 1
PHOTO POINT 27 UT5 R1— upstream (41212021)
PHOTO POINT 28 UT5 R2 — downstream (41212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
PHOTO POINT 29 UT6 R1— upstream (41212021)
PHOTO POINT 29 UT6 R1— downstream (41212021)
PHOTO POINT 30 UT6 R1— upstream (41212021) 1 PHOTO POINT 30 UT6 R1— downstream (41212021) 1
PHOTO POINT 31 UT6 R2 — upstream (41212021)
PHOTO POINT 31 UT6 R2 — downstream (41212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Stream Photographs
Stream Area of Concern Photographs
Dry Creek Reach 4
Before — Localized Erosion (11/4/2020)
After —Repaired Localized Erosion (04/2/2021)
Before — Localized Erosion (11/4/2020)
After — Repaired Localized Erosion (04/2/2021)
After — Repaired Localized Erosion (09/16/2021) 1 After —Repaired Localized Erosion (09/16/2021) 1
STREAM CROSSING PHOTOGRAPHS
Dry Creek Reach 2 - Looking Upstream (1011212021) 1 Dry Creek Reach 2 - Looking Downstream (1011212021) 1
Dry Creek Reach 2 - Looking Upstream (1011212021)
Dry Creek Reach 2 - Looking Downstream (1011212021)
Dry Creek Reach 4 - Looking Upstream (1011212021) I Dry Creek Reach 4 - Looking Downstream (1011212021) I
1 Dry Creek Mitigation Site
4- ' Appendix 2: Visual Assessment Data -Stream Crossing Photographs
UT1 Reach 1- Looking Upstream (1011212021) 1 UT1 Reach 1- Looking Downstream (1011212021) 1
UT1 Reach 2 - Looking Upstream (1011212021)
UT5 - Looking Upstream (1011212021)
UT1 Reach 2 - Looking Downstream (1011212021)
UT5 - Looking Downstream (1011212021
1 Dry Creek Mitigation Site
4- ' Appendix 2: Visual Assessment Data -Stream Crossing Photographs
VEGETATION PLOT PHOTOGRAPHS
FIXED VEG PLOT 1 (911612021) 1 FIXED VEG PLOT 2 (911612021) 1
FIXED VEG PLOT 3 (911612021) 1 FIXED VEG PLOT 4 (911612021) 1
FIXED VEG PLOT 5 (911612021)
FIXED VEG PLOT 6 (1011212021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Vegetation Plot Photographs
FIXED VEG PLOT 7 (911612021) 1 FIXED VEG PLOT 8 (911612021) 1
RANDOM VEG PLOT 9 (911612021) 1 RANDOM VEG PLOT 10 (911612021) 1
RANDOM VEG PLOT 11 (911612021)
RANDOM VEG PLOT 12 (911612021)
Dry Creek Mitigation Site
Appendix 2: Visual Assessment Data —Vegetation Plot Photographs
APPENDIX 3. Vegetation Plot Data
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