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Stream Wetlands Buffer Nutrient Offset
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Jeremiah Dow
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Project Type: • DMS Mitigation Bank
Project Name: Catfish Pond Mitigation Site
County: Durham
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CATFISH PONDMITIGATION SITE
MONITORING YEAR 3
DurhamCounty, NC
ANNUAL BUFFER REPORT
NCDEQ Contract No.007424
DMS ProjectNo.100039
FINAL
NCDWR Project No.2018-0196
RFPNo.16-007279
NeuseRiver Basin
HUC 03020201
Data Collection Period: September 2022
Draft Submission Date: November2022
Final Submission Date: 202
PREPARED FOR:
NC Department of Environmental Quality
Division of Mitigation Services
1652 Mail Service Center
Raleigh, NC 27699-1652
PREPARED BY:
Wildlands Engineering, Inc.
312 West Millbrook Road, Suite 225
Raleigh, NC 27609
Jason Lorch
jlorch@wildlandseng.com
Phone: (919) 851-9986
CATFISH POND MITIGATION SITE
Monitoring Year 3 Buffer Report
TABLE OF CONTENTS
Section 1: PROJECT OVERVIEW .......................................................................................................... 1
1.1 Project Summary ........................................................................................................................... 1
1.2 Project Goals and Objectives ........................................................................................................ 1
1.3 Monitoring Year 3 Data Assessment ............................................................................................. 2
1.3.1 Vegetative Assessment ......................................................................................................... 2
1.3.2 Vegetation Areas of Concern ................................................................................................ 3
1.4 Monitoring Year 3 Summary ......................................................................................................... 3
Section 2: REFERENCES ...................................................................................................................... 4
APPENDICES
Appendix 1 General Figures and Tables
Figure 1 Project Vicinity Map
Figure 2 Service Area Map
Figure 3 Project Component/Asset Map
Figure 4 Catfish Pond II Mitigation Bank Parcel Site Map
Table 1 Buffer Project Areas and Assets
Table 2 Project Activity and Reporting History
Table 3 Project Contact Table
Table 4 Project Information and Attributes
Table 5 Adjacent Forested Areas Existing Tree and Shrub Species
Table 6 Planted Tree Species
Appendix 2 Visual Assessment Data
Figure 5-5b Monitoring Plan View Maps
Table 7 Vegetation Condition Assessment Table
Vegetation Plot Photographs
Overview Photographs
Appendix 3 Vegetation Plot Data
Table 8 Vegetation Plot Criteria Attainment Table
Table 9 Vegetation Plot Data
Table 10 Vegetation Performance Standards Summary Table
Catfish Pond Mitigation Site
Monitoring Year 3 Annual Buffer Report - FINALi
Section 1:PROJECT OVERVIEW
1.1Project Summary
Wildlands Engineering, Inc. (Wildlands) implemented a full delivery project at the Catfish Pond
Mitigation Site (Site) for the North Carolina Department of Environmental Quality Division of Mitigation
Services (DMS). A total of 7,140 linear feet of perennial and intermittent streams were restored and
enhanced in Durham County, NC. A conservation easement comprised of 20.73 acres along Catfish Creek
and three unnamed tributaries in the Neuse River Basin are included in the project. A total of 18.22
2
acres (793,207 ft) of riparian buffer have been restored or enhanced and are expected to generate
523,358.865 riparian buffer credits, with potential to convert some buffer credits to nutrient offset
credits dependent on the need. The Site is located approximately 12 miles north of the City of Durham
and approximately 3 miles east of the Orange County/Durham County border (Figure 1). The project
resides within Hydrologic Unit Code 03020201020040 and North Carolina Department of Water
Resources (NCDWR) Sub-basin 03-04-01. Two unnamed tributaries (UT1 and UT2) drain to Catfish Creek,
which drains to Mountain Creek, and one unnamed tributary (Mountain Tributary) drains directly to
Mountain Creek. Mountain Creek flows into Little River, the Eno River, and then Falls Lake. Falls Lake is
classified as Water Supply Waters (WS-IV) and Nutrient Sensitive Waters (NSW).
Work at the Site was planned, designed, and constructed per the Catfish Pond Mitigation Site – Riparian
Buffer Mitigation Plan (Wildlands, 2019) and the Consolidated Buffer Mitigation Rule 15A NCAC 02B
.0295 (effective November 1, 2015). The purpose of the riparian buffer restoration is to provide riparian
buffer credits to compensate for buffer impacts within the Hydrologic Unit Code 03020201 and the Falls
Lake Watershed. The service area for the riparian buffer credits is depicted in Figure 2. The mitigation
credits generated from the Site are included in Table 1 and illustrated in Figure 3 located in Appendix 1.
With the addition of Catfish Pond II Mitigation Bank Parcel (Catfish Pond II, DWR Project Number 2018-
0196v2), it is not necessary to deduct credits for lack of diffuse flow where Ditch D enters the DMS
conservation easement. The Catfish Pond II conservation easement completely encompasses Ditch D
allowing for diffuse flow through the riparian buffer. Fencing has been installed around Catfish Pond II
(Appendix 1, Figure 4).
1.2Project Goals and Objectives
Prior to construction, the primary degradation of Catfish Creek was the creation of Catfish Pond
sometime between 1940 and 1955. Within the same period, extensive logging and farm road
construction took place. Aerial photographs from 1972 suggest that UT1 had been straightened for
agricultural purposes. Catfish Creek above and below the pond, UT2, and Mountain Tributary showed
few signs of channel manipulation.
The major goals of the riparian restoration project are to provide ecological and water quality
enhancements to the Neuse River Watershed within the Falls Lake Water Supply Watershed by creating
a functional riparian corridor and restoring the riparian area. The project supports specific goals
identified in the 2010 Neuse River Basin Restoration Priorities (RBRP) for the Neuse River Targeted Local
Watershed, which highlights the importance of riparian buffers for stream restoration projects
(Breeding, 2010). Forested riparian areas immobilize and retain nutrients and suspended sediment. The
RBRP also supports the Falls Lake Nutrient Management Strategy (NCDWR, 2011). Falls Lake is the
receiving water supply water body downstream of the Site and is classified as WS-IV and NSW. Specific
enhancements to water quality and ecological processes are outlined below:
Exclude cattle from project streams – Fencing has been installed around project areas adjacent
to cattle pastures.
Catfish Pond Mitigation Site
Monitoring Year 3 Annual Buffer Report - FINAL1
Decrease nutrient levels – Filtering runoff from the agricultural fields through restored native
riparian zones. The off-site nutrient input is absorbed on-site by filtering flood flows through
restored floodplain areas, where flood flows can disperse through native vegetation.
Decrease water temperature and increase dissolved oxygen concentrations – Riparian areas will
create additional long-term shading of the channel flow to reduce thermal pollution.
Restore and enhance native floodplain vegetation – Planted native tree species in riparian zone
where tree growth was insufficient.
Permanently protect the project Site from harmful uses – Established a conservation easement
on the site.
The 20.73-acre Site is protected with a permanent conservation easement. Of the 20.73 acres, Neuse
riparian buffer credits were generated by restoring 5.92 acres and enhancing 12.30 acres. No buffer
credit will be generated from the remaining 2.51 acres. In general, riparian buffer restoration area
widths on streams extend out to 50 feet from top of bank on each side of the stream channel. Figure 3
and Table 1 in Appendix 1 detail the buffer credit generation.
1.3Monitoring Year 3 Data Assessment
The Mitigation Plan (Wildlands, 2019) was submitted and accepted by DMS in July 2019. Construction
activities by Main Stream Earthwork, Inc. and tree planting by Bruton Natural Systems, Inc. were both
completed in March 2020. The baseline as-built survey was completed by Kee Mapping and Surveying in
April 2020. Refer to Appendix 1 for detailed project activity, history, contact information, and
watershed/site background information.
Vegetative performance for buffer restoration areas will be in accordance with 15A NCAC 02B
.0295(n)(2)(B), and (n)(4) (effective November 1, 2015). To meet success criteria, areas generating buffer
mitigation credits shall include a minimum of four native hardwood tree species, where no one species
is greater than 50 percent of stems, and shall have a survival of at least 260 stems per acre at the end of
the required five-year monitoring period. For monitoring to be completed and buffer credit to be
awarded, NCDWR must provide written approval of successful revegetation of buffer restoration areas.
Year 3 monitoring (MY3) was conducted to assess the condition of the vegetation in September 2022.
1.3.1Vegetative Assessment
The quantity of monitoring vegetation plots was determined in accordance with the Carolina Vegetative
Sampling Protocol (Lee et al., 2008) such that at least 2 percent of the Site is encompassed in monitoring
plots. A total of 7 vegetation plots (each 100 square meters) were established within the conservation
easement boundaries. The plot corners have been marked and are recoverable either through field
identification or with the use of a GPS unit. Reference photographs are taken at the origin looking
diagonally across the plot to the opposite corner on an annual basis. Trees will be marked annually with
flagging tape. Species composition, vigor, height, density, and survival rates will be evaluated by plot on
an annual basis. The extent of invasive species coverage will also be monitored and controlled as
necessary.
The 2022 annual vegetation monitoring resulted in an average survival of 508 stems per acre of
Mitigation Plan Approved species, which exceeds the final requirement of 260 stems per acre at the end
of Monitoring Year 5. Plot stem densities range from 324 to 607 stems per acre and each plot includes at
least four planted species. Volunteer stems have begun to establish themselves and include desirable
species such as American persimmon (Diospyros virginiana), eastern redbud (Cercis canadensis), and
sycamore (Platanus occidentalis). The Site is on track to surpass the final success criteria. Refer to
Appendix 2 for the vegetation condition assessment table, the monitoring plan view map, vegetation
Catfish Pond Mitigation Site
Monitoring Year 3 Annual Buffer Report - FINAL2
plot and overview photographs. Appendix 3 contains vegetation plot data and the vegetation
performance summary table.
1.3.2Vegetation Areas of Concern
While planted trees are growing well, pasture grasses are still thick. To ensure planted trees remain
competitive, herbicide ring sprays were applied around the base of trees where necessary in April 2022.
Invasive species at Catfish Pond have been greatly reduced by past treatments throughout the site.
However, Wildlands recognizes that multiple treatments are typically needed for effective invasive plant
control. Sporadic patches of multiflora rose (Rosa multiflora) and blackberry (Rubus spp.) on the
upstream portion of UT1 had begun to compete with planted trees and were treated in May 2022 with a
foliar spray application of triclopyr herbicide. Intermittent resprouts of multiflora rose, Chinese Privet
(Ligustrum sinense), and tree-of-heaven (Alianthus altissima), were also treated along Catfish Creek with
triclopyr and glyphosate using situation and plant appropriate forms of application.
1.4Monitoring Year 3 Summary
Vegetation across the Parcel is exceeding performance standards. Monitoring Year 3 data shows an
average density of 508 stems per acre across vegetation plots. The Parcel is on track to achieve the final
success criteria of 260 stems per acre at the end of Monitoring Year 5. In addition, desirable volunteer
species such as American persimmon (Diospyros virginiana) and eastern redbud (Cercis canadensis) are
establishing themselves. Sporadic resprouts of invasive vegetation were treated and herbicide ring
sprays were applied around trees in Monitoring Year 3. Wildlands will continue to monitor and treat as
necessary. Additional herbicide ring sprays will be applied as needed around the base of trees in areas of
thick herbaceous competition in spring 2023.
Summary information/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, 2019)
available on DMS’s website. All raw data supporting the tables and figures in the appendices are
available from DMS upon request.
Catfish Pond Mitigation Site
Monitoring Year 3 Annual Buffer Report - FINAL3
Section 2:REFERENCES
Breeding, R. 2010. Neuse River Basin Restoration Priorities. North Carolina Ecosystem Enhancement
Program. Accessed at:
https://files.nc.gov/ncdeq/Mitigation%20Services/Watershed_Planning/Neuse_River_Basin/FINAL%2
0RBRP%20Neuse%202010_%2020111207%20CORRECTED.pdf
Lee, M.T., Peet, R.K., Roberts, S.D., & Wentworth, T.R. 2008. CVS-EEP Protocol for Recording Vegetation
Version 4.2. Accessed at: http://cvs.bio.unc.edu/protocol/cvs-eep-protocol-v4.2-lev1-2.pdf
North Carolina Department of Environmental Quality, Division of Mitigation Services (NCDMS). 2017.
Riparian Buffer and Nutrient Offset Buffer Baseline and Annual Monitoring Report Template version
2.0 Accessed at:
https://files.nc.gov/ncdeq/Mitigation%20Services/Document%20Management%20Library/Guidance%
20and%20Template%20Documents/RB_NO_Base_Mon_Template_2.0_2017_5.pdf
North Carolina Department of Environmental Quality, Division of Water Resources (NCDWR). 2000. 15A
NCAC 02B .0233 Neuse River Basin: Nutrient Sensitive Waters Management Strategy: Protection and
Maintenance of Existing Riparian Buffers. Accessed at:
http://reports.oah.state.nc.us/ncac/title%2015a%20-
%20environmental%20quality/chapter%2002%20-
%20environmental%20management/subchapter%20b/15a%20ncac%2002b%20.0233.pdf
North Carolina Department of Environmental Quality, Division of Water Resources (NCDWR). 2011. Falls
Lake Nutrient Management Strategy. Accessed at: https://deq.nc.gov/about/divisions/water-
resources/water-planning/nonpoint-source-planning/falls-lake-nutrient-strategy
North Carolina Department of Environmental Quality, Division of Water Resources (NCDWR). 2015. 15A
NCAC 02B .0295 Mitigation Program Requirements for Protection and Maintenance of Riparian
Buffers. Accessed at: http://reports.oah.state.nc.us/ncac/title%2015a%20-
%20environmental%20quality/chapter%2002%20-
%20environmental%20management/subchapter%20b/15a%20ncac%2002b%20.0295.pdf
North Carolina Department of Environmental Quality, Division of Water Resources (NCDWR). 2011.
Surface Water Classifications. Accessed at: https://deq.nc.gov/about/divisions/water-
resources/planning/classification-standards/classifications#DWRPrimaryClassification
Wildlands Engineering, Inc. 2019. Catfish Pond Mitigation Site – Riparian Buffer Mitigation Plan. North
Carolina Department of Environmental Quality, Division of Mitigation Services (NCDMS), Raleigh, NC.
Catfish Pond Mitigation Site
Monitoring Year 3 Annual Buffer Report - FINAL4
———
3.573
847.231
Nutrient
Delivered
Offset: P (lbs)
———
55.469
N (lbs)
Delivered
13,154.184
Nutrient Offset:
NoNoNo
YesYes
Offset?
Nutrient
Convertible to
0.0000.0000.000
Credits
CreditsCredits
350.790636.075
4,369.000
252,086.000265,917.000256,805.790266,553.075523,358.865
Riparian Buffer
00
—
YesYesYesYesYes
Buffer?
257,518535,689793,207
Riparian
to Riparian
Convertible
Square FeetSquare Feet
Buffer Credits
Nitrogen:
1.000001.000003.030302.000006.06061
Ratio (x:1) Ratio (x:1)
Final Credit Final Credit
Phosphorus:
TOTAL NUTRIENT OFFSET MITIGATION
Restoration:
Preservation:
TOTAL AREA OF BUFFER MITIGATION (TABM)
Enhancement:
Mitigation TotalsMitigation Totals
33%33%
100%100%100%
Offset:
Total Riparian Buffer:
Nutrient
% Full Credit% Full Credit
11122
Ratio (x:1)Ratio (x:1)
Initial Credit Initial Credit
))
22
0
0.0%0.0%
Total Total
4,3691,0633,855
252,086531,834793,207264,402
(Creditable) (Creditable)
Area of Buffer
Mitigation (ftArea for Buffer Mitigation (ft
):):
22
)
2
4,3691,0633,855
252,086531,834793,207
Total Area (sf)
Total Area (ft
Totals:
Eligible for Preservation (ft
Preservation Area Subtotal (ft
UT1UT1
Mountain TribMountain Trib
Feature NameFeature Name
Catfish Creek, UT1
Catfish Creek, UT1, UT2, Catfish Creek, UT1, UT2,
/pound)
Preservation as % Total Area of Buffer Mitigation:
/pound)
2
2
0-50
0-1000-100
101-200101-200
Width (ft)Width (ft)
Ephemeral Reaches as % Total Area of Buffer Mitigation:
Min-Max Buffer Min-Max Buffer
RestorationRestorationRestoration
Preservation
Cattle ExclusionCattle Exclusion
Enhancement via Enhancement via
Mitigation ActivityMitigation Activity
Project AreaN Credit Conversion Ratio (ftP Credit Conversion Ratio (ft
I / PI / PI / PI / PI / P
Feature TypeFeature Type
)
1
YesYesYesYesYes
NO if
ditch
Subject?
ephemeral or
Subject? (enter
19.16394
297.54099
RuralRuralRuralRuralRural
793207
LocationLocation
Neuse 03020201 - Upper Falls Lake
0
BufferBufferBufferBufferBufferBuffer
793207
Credit TypeCredit Type
Table 1. Buffer Project Areas and Assets Catfish Pond Mitigation SiteDMS Project No. 100039 Monitoring Year 3 - 2022Enter Preservation Credits Below last updated 01/17/2020
Table 2. Project Activity and Reporting History
Catfish Pond Mitigation Site
DMS Project No. 100039
Monitoring Year 3 - 2022
Activity or Report
Data Collection CompleteCompletion or Scheduled Delivery
Mitigation Plan
July 2019July 2019
Final Design - Construction PlansAugust 2019August 2019
Construction
February-March 2020March 2020
1
March 2020March 2020
Temporary S&E mix applied to entire project area
1
April 2020April 2020
Permanent seed mix applied to reach/segments
Bare root and live stake plantings for reach/segmentsMarch 2020March 2020
Baseline Monitoring Document (Year 0)
March 2020June 2020
2
April-May 2020
Competitive Vegetation Treatment
Invasive Vegetation Treatment
May & September 2020
Year 1 MonitoringOctober 2020December 2020
Invasive Vegetation Treatment
September 2021
Year 2 MonitoringSeptember 2021December 2021
2
April 2022
Competitive Vegetation Treatment
Invasive Vegetation TreatmentMay 2022
Year 3 Monitoring
September 2022ember 2022
Year 4 Monitoring
2023December 2023
Year 5 Monitoring
2024December 2024
1
Seed and mulch is added as each section of construction is completed.
2
Herbicide ring sprays around the base of planted stems.
Table 3. Project Contact Table
Catfish Pond Mitigation Site
DMS Project No. 100039
Monitoring Year 3 - 2022
Wildlands Engineering, Inc.
Designer
497 Bramson Ct, Suite 104
Daniel Johnson, PE
Mt. Pleasant, SC 29464
843.277.6221
Main Stream Earthwork, Inc.
Construction Crew
631 Camp Dan Valley Rd
Reidsville, NC 27320
Bruton Natural Systems, Inc
Planting Contractor
P.O. Box 1197
Fremont, NC 27830
Canady's Landscaping & Erosion
Seeding Contractor
256 Fairview Acres Rd
Lexington, NC 27295
Seed Mix SourcesGarrett Wildflower Seed Farm
1591 Cleveland Rd
Smithfield, NC 27577
Ernst Conservation Seeds, Inc.
8884 Mercer Pike
Meadville, PA 16335
Dykes and Sons Nursery and Greenhouse
Nursery Stock Suppliers
825 Maude Etter Rd
Bare Roots
McMinnville, TN 37110
Bruton Natural Systems, Inc
Live Stakes
Foggy Mountain Nursery
797 Helton Creek Rd
Lansing, NC 28643
Monitoring PerformersWildlands Engineering, Inc.
Jason Lorch
Monitoring, POC
919.851.9986
Table 4. Project Information and Attributes
Catfish Pond Mitigation Site
DMS Project No. 100039
Monitoring Year 3 - 2022
PROJECT INFORMATION
Project NameCatfish Pond Mitigation Site
CountyDurham County
Project Coordinates (latitude and longitude)36° 9’ 48.03” N, 78° 54’ 37.66” W
Project Area (acres)20.73
Planted Acreage (acres of woody stems planted)8.00
PROJECT WATERSHED SUMMARY INFORMATION
Physiographic ProvinceCarolina Slate Belt of the Piedmont Physiographic Province
River BasinNeuse River
USGS Hydrologic Unit 8-digit03020201
USGS Hydrologic Unit 14-digit03020201020040
DWR Sub-basin03-04-01
Project Drainiage Area (acres)227 (Catfish Creek - 197, Mountain Tributary - 30)
Project Drainage Area Percentage of Impervious Area0.0%
CGIA Land Use Classification45.6% forested, 54.2% cultivated, 0.2% wetland
Table 5. Adjacent Forested Areas Existing Tree and Shrub Species
Catfish Pond Mitigation Site
DMS Project No. 100039
Monitoring Year 3 - 2022
Wetland Indicator
Common NameScientific Name
Status
Black Willow Salix nigra PCM
Eastern Red Cedar Juniperus virginiana GBDV
Green Ash Fraxinus pennsylvanica GBDX
Hazel Alder Alnus serrulata PCM
Paw Paw Asimina triloba GBD
Red Maple Acer rubrum GBD
Sweet Gum Liquidambar styraciflua GBD
Sycamore Platanus occidentalis GBDX
White Oak Quercus alba GBDV
Yellow Poplar Liriodendron tulipifera GBDV
Table 6. Planted Tree Species
Catfish Pond Mitigation Site
DMS Project No. 100039
Monitoring Year 3 - 2022
Number
Common NameScientific Name% of Total
Planted
Arrowwood Viburnum Viburnum dentatum 551.0%
Green Ash Fraxinus pennsylvanica 64611.5%
Overcup Oak Quercus lyrata 3656.5%
River Birch Betula nigra 92716.5%
Shumard Oak Quercus shumardii 64611.5%
Smooth Serviceberry Amelanchier laevis 551.0%
Swamp Chestnut Oak Quercus michauxii 64611.5%
Sycamore Platanus occidentalis 1,20721.5%
White Oak Quercus alba 3656.5%
Willow Oak Quercus phellos 64611.5%
Yellow Buckeye Aesculus flava 551.0%
Table 7. Vegetation Condition Assessment Table
Catfish Pond Mitigation Site
DMS Project No. 100039
Monitoring Year 3 - 2022
Planted Acreage8.00
Mapping
Combined % of Planted
Vegetation CategoryDefinitions
Threshold
AcreageAcreage
(ac)
Bare Areas Very limited cover of both woody and herbaceous material.0.1000%
Low Stem Density Woody stem densities clearly below target levels based on MY3, 4, or 5 stem count
00%
0.10
Areas criteria.
Total
0.000%
Areas of Poor Growth Areas with woody stems of a size class that are obviously small given the monitoring
0.2500%
Rates year.
Cumulative Total
0.000%
Visual assessment was completed October 18, 2022.
Easement Acreage20.73
Mapping % of
Combined
Vegetation CategoryDefinitions
Threshold Easement
Acreage
(ac)Acreage
Invasive Areas of
00%
Areas of points (if too small to render as polygons at map scale).0.10
Concern
0 Encroachments Noted
Easement
Areas of points (if too small to render as polygons at map scale).
none
/ 0 ac
Encroachment Areas
Visual assessment was completed October 18, 2022.
VEGETATION PLOT PHOTOGRAPHS
VEG PLOT 1 ΛЉВΉЉЊΉЋЉЋЋΜ VEG PLOT 2 ΛЉВΉЋЋΉЋЉЋЋΜ
VEG PLOT 3 ΛЉВΉЋЋΉЋЉЋЋΜ VEG PLOT 4 ΛЉВΉЋЋΉЋЉЋЋΜ
VEG PLOT 5 ΛЉВΉЋЋΉЋЉЋЋΜ VEG PLOT 6 ΛЉВΉЋЋΉЋЉЋЋΜ
Catfish Pond Mitigation Site
Appendix 2: Visual Assessment Data Vegetation Plot Photographs
VEG PLOT 7 ΛЉВΉЉЊΉЋЉЋЋΜ
Catfish Pond Mitigation Site
Appendix 2: Visual Assessment Data Vegetation Plot Photographs
OVERVIEW PHOTOGRAPHS
Catfish Pond Mitigation Site
Appendix 2: Visual Assessment Data – Overview Photographs
Catfish Pond Mitigation Site
Appendix 2: Visual Assessment Data – Overview Photographs
Catfish Pond Mitigation Site
Appendix 2: Visual Assessment Data – Overview Photographs
Catfish Pond Mitigation Site
Appendix 2: Visual Assessment Data – Overview Photographs
Table 8. Vegetation Plot Criteria Attainment Table
Catfish Pond Mitigation Site
DMS Project No. 100039
Monitoring Year 3 - 2022
Plot Success Criteria Met*Tract Mean
Yes
1
Yes
2
Yes
3
4Yes
100%
Yes
5
Yes
6
7Yes
*Based on the target stem density for MY5 of 260 stems per acre.
63050
41 21 54
2
111411461446
445567
Total
Veg Plot 7 F
416
1111
Planted
62
1213 2 680780
151715401740
607688
Total
Veg Plot 6 F
16221
1212
Planted
32333550550
1
141414201420
567567
Total
Veg Plot 5 F
32332
1313
Planted
28112 1 590690
1
141514531553
526567
Total
Veg Plot 4 F
8112
1212
Planted
13228 5 8460550
13381338
324526
Total
Veg Plot 3 F
132288
Planted
262115050
1212125010125010
486486
Total
Veg Plot 2 F
26211
1212
Planted
17511 1 540640
151615471647
607648
Total
Veg Plot 1 F
1441
1010
Planted
FACFAC FAC
OBL OBL
FAC
FACUFACU FACUFACU
FACWFACWFACWFACWFACW
Status FACW
Indicator
% Invasives% Invasives
Stems/AcreStems/Acre
Species CountSpecies Count
Proposed Standard
TreeTreeTreeTreeTreeTreeTreeTreeTreeTreeTree
TreeTreeTreeTreeTree
Tree
Tree/
Shrub
Performance Standard
Average Plot Height (ft.)Average Plot Height (ft.)
Current Year Stem CountCurrent Year Stem Count
Dominant Species Composition (%)Dominant Species Composition (%)
8.00
0.0247
green ash
white oak
river birch
willow oak
sweetgum
2020-03-252022-09-22 hazel alder
black willow
black walnut
Shumard's oak swamp tupelo
cherrybark oak
yellow buckeye
Common Name eastern redbud
American sycamore
swamp chestnut oak
common persimmon
American black elderberry
Salix nigra
Betula nigra
Quercus alba
Juglans nigraNyssa biflora
Aesculus flava
Scientific Name Alnus serrulata
Quercus phellos
Quercus pagoda
Cercis canadensis
Quercus michauxii
Quercus shumardii
Platanus occidentalis Diospyros virginiana
Sambucus canadensis
Fraxinus pennsylvanica
Liquidambar styraciflua
SumSumPlan
Species
StandardStandard
Approved
Included in
Plan Species
Performance Performance
Mitigation PlanPost Mitigation Mitigation Plan Post Mitigation
Table 9. Vegetation Plot Data Catfish Pond Mitigation SiteDMS Project No. 100039 Monitoring Year 3 - 2022 Planted AcreageDate of Initial PlantDate of Current SurveyPlot size (ACRES)1).
Bolded species are proposed for the current monitoring year, italicized species are not approved, and a regular font indicates that the species has been approved.2). The "Species Included
in Approved Mitigation Plan" section contains only those species that were included in the original approved mitigation plan. The "Post Mitigation Plan Species" section includes species
that are being proposed through a mitigation plan addendum for the current monitoring year (bolded) , species that have been approved in prior monitoring years through a mitigation
plan addendum (regular font), and species that are not approved (italicized).3). The "Mitigation Plan Performance Standard" section is derived only from stems included in the original
mitigation plan, whereas the "Post Mitigation Plan Performance Standard" includes data from mitigation plan approved, post mitigation plan approved, and proposed stems.
00000000
% Invasives% Invasives
45666556
# Species# Species
Veg Plot 3 FVeg Plot 6 F
64338432
Av. Ht. (ft)Av. Ht. (ft)
324405486486607567567607
Stems/Ac.Stems/Ac.
00000000
% Invasives% Invasives
55665555
# Species# Species
Veg Plot 2 FVeg Plot 5 F
6435432
10
Av. Ht. (ft)Av. Ht. (ft)
486526607607567526526526
Stems/Ac.Stems/Ac.
000000000000
% Invasives% Invasives% Invasives
545554443555
# Species# Species# Species
Veg Plot 1 FVeg Plot 4 FVeg Plot 7 F
433397445433
Av. Ht. (ft)Av. Ht. (ft)Av. Ht. (ft)
607405567567526405405405445526648648
Stems/Ac.Stems/Ac.Stems/Ac.
Monitoring Year 7Monitoring Year 5Monitoring Year 3Monitoring Year 2Monitoring Year 1Monitoring Year 0Monitoring Year 7Monitoring Year 5Monitoring Year 3Monitoring Year 2Monitoring Year
1Monitoring Year 0Monitoring Year 7Monitoring Year 5Monitoring Year 3Monitoring Year 2Monitoring Year 1Monitoring Year 0
Table 10. Vegetation Performance Standards Summary Table Catfish Pond Mitigation SiteDMS Project No. 100039 Monitoring Year 3 - 2022