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HomeMy WebLinkAbout20180198 Ver 1_Sassarixa_100040_MY3_2023_20240209    MONITORING YEAR 3  ANNUAL REPORT  Final    February 2024    SASSARIXA SWAMP MITIGATION SITE   Johnston County, NC  Neuse River Basin   HUC 03020201  DMS Project No. 100040  DMS Contract No. 7425  DMS RFP No. 16‐007279  USACE Action ID No. 2018‐00432  DWR Project No. 2018‐0198    Data Collection Dates: January‐November 2023   PREPARED FOR:        NC Department of Environmental Quality  Division of Mitigation Services  1652 Mail Service Center  Raleigh, NC 27699‐1652    Wildlands Engineering, Inc.   (P) 919.851.9986  •  312 West Millbrook Road, Suite 225  •  Raleigh, NC 27609 February 7, 2024    Jeremiah Dow  Project Management Supervisor – Eastern Region  North Carolina DEQ Division of Mitigation Services   217 West Jones Street, Raleigh, NC 27603    RE:  DMS Comments on the MY3 Report   Sassarixa Swamp, Project ID #100040, DMS Contract 7425     Dear Mr. Dow:    We have reviewed the comments on the Monitoring Year 3 Report for the above referenced project  dated December 19, 2023 and have revised the report based on these comments. The revised  documents are submitted with this letter. Below are responses to each of your comments. For your  convenience, the comments are reprinted with our response in italics.     Stream Report:     1. Section 2.2 – incomplete sentence in second paragraph reads “Chinese privet in MY4.” Please  correct.   Response: The incomplete sentence was removed.      2. The meeting minutes from the May 18, 2023 IRT site visit indicate that a piping log sill on T3 was  observed and would be manually repaired. Was this work completed?   Response: The piping log sill on T3 naturally sealed itself by the time Wildlands stewardship team  was going to manually repair it. Wildlands has completed various site walks since then and has  not observed any additional piping.       If you have any questions, please contact me by phone (919) 851‐9986, or by email  (jlorch@wildlandseng.com).  Sincerely,     Jason Lorch, Monitoring Coordinator                                          PREPARED BY:                     312 West Millbrook Road, Suite 225  Raleigh, NC 27609    Jason Lorch  jlorch@wildlandseng.com  Phone: 919.851.9986      Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final i  SASSARIXA SWAMP MITIGATION SITE  Monitoring Year 3 Annual Report    TABLE OF CONTENTS  Section 1: PROJECT OVERVIEW ........................................................................................................ 1‐1  1.1 Project Quantities and Credits ................................................................................................... 1‐1  1.2 Project Goals and Objectives ..................................................................................................... 1‐2  1.3 Project Attributes ....................................................................................................................... 1‐4  Section 2: MONITORING YEAR 3 DATA ASSESSNENT ........................................................................ 2‐1  2.1 Vegetative Assessment .............................................................................................................. 2‐1  2.2 Vegetation Areas of Concern and Management ....................................................................... 2‐1  2.3 Stream Assessment .................................................................................................................... 2‐1  2.4 Stream Areas of Concern and Management .............................................................................. 2‐2  2.5 Hydrology Assessment ............................................................................................................... 2‐2  2.6 Wetland Assessment .................................................................................................................. 2‐2  2.7 Monitoring Year 3 Summary ...................................................................................................... 2‐2  Section 3: REFERENCES .................................................................................................................... 3‐1    TABLES  Table 1: Project Quantities and Credits ..................................................................................................... 1‐1  Table 2: Goals, Performance Criteria, and Functional Improvements ...................................................... 1‐3  Table 3: Project Attributes ......................................................................................................................... 1‐5    FIGURES  Figure 1a‐c  Current Condition Plan View    APPENDICES  Appendix A Visual Assessment Data  Table 4 Visual Stream Morphology Stability Assessment Table  Table 5 Vegetation Condition Assessment Table   Stream Photographs   Stream Crossing Photographs   Vegetation Plot Photographs  Appendix B Vegetation Plot Data  Table 6 Vegetation Plot Data  Table 7a Vegetation Performance Standards Summary Table  Table 7b  Supplementally Planted Tree Species and Quantities  Appendix C Stream Geomorphology Data   Cross‐Section Plots  Table 8 Baseline Stream Data Summary  Table 9 Cross‐Section Morphology Monitoring Summary  Appendix D Hydrology Data  Table 10 Bankfull Events  Table 11 Rainfall Summary   Bankfull Events Visual Observations  Table 12 Groundwater Gauge Summary    Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final ii   Groundwater Gauge Plot  Table 13 Recorded In‐Stream Flow Events Summary   Recorded In‐Stream Flow Events Plot  Appendix E Project Timeline and Contact Info  Table 14 Project Activity and Reporting History  Table 15 Project Contact Table     Appendix F Additional Documentation   IRT MY2 Site Visit Meeting Minutes      Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final 1‐1  Section 1: PROJECT OVERVIEW  The Sassarixa Swamp Mitigation Site (Site) is located in Johnston County, approximately six miles  southwest of Smithfield and five miles north of Four Oaks. The Site drains to Holts Lake, which drains to  the Neuse River. Holts Lake is a recreational lake classified as a Nutrient Sensitive Water (NSW) and the  Neuse River is a water supply for the City of Goldsboro. Table 3 presents information related to the  project attributes.   1.1 Project Quantities and Credits  The Site is located on 10 parcels under 7 different landowners and a conservation easement was  recorded on 65.06 acres. Mitigation work within the Site included restoration, enhancement II, and  preservation of perennial and intermittent stream channels. Table 1 below shows stream credits by  reach and the total amount of stream credits expected at closeout.   Table 1: Project Quantities and Credits   PROJECT MITIGATION QUANTITIES  Project  Segment  Mitigation  Plan  Footage  As‐Built  Footage  Mitigation  Category  Restoration  Level  Mitigation  Ratio  (X:1)  Credits Comments  Stream  Sassarixa  Creek R1‐R3 2,631 2,631 Warm EII 2.5 1,052.400 Ford Crossing, Fencing Out  Livestock  T1 R1 570 570 Warm EII 2.5 228.000 Bank Stabilization, Fencing  Out Livestock  T1 R2 824 810 Warm R 1.0 824.000 Full Channel Restoration,  Fencing Out Livestock  T1 R3 509 507 Warm R 1.0 509.000 Full Channel Restoration,  Fencing Out Livestock  T1 R4 252 252 Warm EII 2.5 100.800 Fencing Out Livestock  T1A 358 356 Warm EII 2.5 143.200 Fencing Out Livestock  T1B 275 276 Warm EII 2.5 110.000 Fencing Out Livestock  T1C 307 307 Warm EII 2.5 122.800 Fencing Out Livestock  T2 1,010 1,006 Warm R 1.0 1,010.000 Pond Removal, Fencing Out  Livestock  T3 R1 1,053 1,041 Warm R 1.0 1,053.000 Full Channel Restoration,  Fencing Out Livestock  T3 R2 61 61 Warm P 10.0 6.100 Conservation Easement  T4 R1 206 206 Warm EII 2.5 82.400 Ford Crossing, Fencing Out  Livestock  T4 R2 398 399 Warm EII 2.5 159.200 Bank Stabilization, Fencing  Out Livestock  T4 R3 1,509 1,510 Warm P 10.0 150.900 Culvert Crossing,  Conservation Easement  T5 R1 670 642 Warm EII 2.5 268.000 Bank Stabilization  T5 R2 885 874 Warm R 1.0 885.000 Full Channel Restoration,  Fencing Out Livestock    Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final 1‐2  PROJECT MITIGATION QUANTITIES  Project  Segment  Mitigation  Plan  Footage  As‐Built  Footage  Mitigation  Category  Restoration  Level  Mitigation  Ratio  (X:1)  Credits Comments  Stream  T5 R3 965 961 Warm EII 4.0 241.250 Culvert Crossing, Bank  Stabilization  T5A 1,026 1,018 Warm EII 2.5 410.400 Bank Stabilization, Fencing  Out Livestock  T5B 580 580 Warm EII 2.5 232.000 Fencing Out Livestock  T5C1 588 588 Warm EII 2.5 235.200 Fencing Out Livestock  T6 R1 381 383 Warm R 1.0 381.000 Full Channel Restoration,  Fencing Out Livestock  T6 R2 1,035 1,037 Warm EII 2.5 414.000  Culvert Crossing, Bank  Stabilization. Fencing Out  Livestock  Total: 8,618.650    1.  T5C Credited using the Headwater Stream guidance method of the valley length.     Blue = Restoration Orange = Enhancement II Green = Preservation                          1.2 Project Goals and Objectives  The project is intended to provide numerous ecological benefits. Table 2 below describes expected  outcomes to water quality and ecological processes and provides project goals and objectives.  Restoration Level Stream  Warm Cool Cold  Restoration 4,662.000    Enhancement I ‐‐    Enhancement II 3,799.650    Preservation 157.000    Totals 8,618.650    Total Stream Credit 8,618.650    Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final 1‐3  Table 2: Goals, Performance Criteria, and Functional Improvements  Goal Objective/ Treatment Likely Functional  Uplift  Performance  Criteria Measurement  Cumulative  Monitoring  Results  Improve the  stability of  stream  channels.  Construct stream  channels that will  maintain stable cross‐ sections, patterns,  and profiles over  time.  Reduce sediment  inputs from bank  erosion. Reduce  shear stress on  channel boundary.   ER stays over 2.2  and BHR below  1.2 with visual  assessments  showing  progression  towards stability.  Cross‐section  monitoring will be  assessed during  MY1, MY2, MY3,  MY5, and MY7  and visual  inspections will  be assessed  annually.  Cross‐section  surveys show the  channels are  stable. Visual  observations  indicate the  majority of  channels are  performing as  intended. An  additional cross‐ section was added  to determine if  the upper third of  T2 is transitioning  into a linear  wetland   Improve     in‐stream  habitat.  Install habitat  features such as  constructed riffles,  lunker logs, and brush  toes into  restored/enhanced  streams. Add woody  materials to channel  beds. Construct pools  of varying depth.  Increase and  diversify available  habitats for  macroinvertebrates,  fish, and  amphibians leading  to colonization and  increase in  biodiversity over  time.   There is no  required  performance  standard for this  metric.  N/A N/A  Reconnect  channels  with  floodplains  to allow a  natural  flooding  regime.  Reconstruct stream  channels with  designed bankfull  dimensions and depth  based on reference  reach data. Remove  pond above T2.  Allow more  frequent flood  flows to disperse on  the floodplain.   Four bankfull  events in  separate years  within  monitoring  period.   30 consecutive  days of flow for  intermittent  channels.   Crest gauges  and/or pressure  transducers  recording flow  elevations.  Bankfull event  documented on  T1 R3, T2, and T5  R2 during MY3; T3  R1 did not meet  during MY3.  Greater than 30  consecutive days  of flow recorded  on all intermittent  streams during  MY3.     Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final 1‐4  Goal Objective/ Treatment Likely Functional  Uplift  Performance  Criteria Measurement  Cumulative  Monitoring  Results  Restore and  enhance  native  floodplain  and  streambank  vegetation.  Plant native tree and  understory species in  riparian zones and  plant native shrub and  herbaceous species  on streambanks.  Reduce sediment  inputs from bank  erosion and runoff.  Increase nutrient  cycling and storage  in floodplain.  Provide riparian  habitat. Add a  source of LWD and  organic material to  stream.   Survival rate of  320 stems per  acre at MY3, 260  planted stems  per acre at MY5,  and 210 stems  per acre at MY7.  Height  requirement is 7  feet at MY5 and  10 feet at MY7.  One hundred  square meter  vegetation plots  are placed on 2%  of the planted  area of the Site  and monitored  during MY1, MY2,  MY3, MY5, and  MY7.  9 out of 11  vegetation plots  have a planted  stem density  greater than 320  stems per acre. A  small  supplemental  planting occurred  along T1 in  February 2023.    Permanently  protect the  project Site  from  harmful  uses.  Establish conservation  easements on the  Site.   Protect the Site  from encroachment  on the riparian  corridor and direct  impact to streams  and wetlands.  Prevent  easement  encroachment.  Visually inspect  the perimeter of  the Site to ensure  no easement  encroachment is  occurring.  No easement  encroachments.  1.3 Project Attributes  The project includes several adjacent properties that have been owned and operated as a livestock farm  by a single family since 1850, where livestock were continually rotated through all fields with access to  the project streams. Based on aerial photos from 1950 to 2012 onsite streams have existed in their  approximate locations with very little change to riparian buffer extents since 1950. Two alterations to  the Site visible from historical aerial photography were the addition of the pond on T2 between 1964  and 1973, and the addition of the large pond below T5A, T5B, and T5C between 1950 and 1961.  According to the landowners, in the 1960’s and early 1970’s a hog yard was located at the upstream end  of T4 and T5, where the streams were diverted to make a hog wallow area. The hogs were moved to a  hog house in the early 1970’s, however goats, horses, and cattle had continuous access to this portion of  the site until Hurricane Matthew struck in September 2016. The floods from the storm destroyed much  of the fencing around T4 and T5 and livestock have been rotated in other fields since that time while  fencing was being repaired. Other portions of the site had not seen significant changes in land use with  livestock or crop rotations from existing activities. Table 3 below and Table 9 in Appendix C present  additional information on pre‐restoration conditions.                        Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final 1‐5  Table 3: Project Attributes       PROJECT INFORMATION  Project Name Sassarixa Swamp  Mitigation Site  County Johnston County  Project Area (acres)  65.06  Project Coordinates  35.472153, ‐78.436000  PROJECT WATERSHED SUMMARY INFORMATION  Physiographic Province Rolling Coastal Plain  River Basin Neuse River  USGS HUC 8‐digit  03020201  USGS HUC 14‐digit 03020201130030  DWR Sub‐basin 03‐04‐04  Land Use Classification 66% agriculture, 27%  forested, 7% developed  Project Drainage Area (acres) 5,024  Percentage of Impervious Area 0.9%   RESTORATION TRIBUTARY SUMMARY INFORMATION  Parameters T1 T2 T3 T5 T6  Pre‐project length (feet) 2,202 348 1,098 2,544 1,342  Post‐project (feet) 2,155 1,010 1,114 2,553 1,451  Valley confinement (Confined, moderately confined,  unconfined) Unconfined Moderately Confined to Unconfined  Drainage area (acres) 45 25 26 41.25 38.25  Perennial, Intermittent, Ephemeral Intermittent Perennial  DWR Water Quality Classification C, NSW B, NSW  Dominant Stream Classification (existing) G5 G5 B5/G5 E5 G5/E5  Dominant Stream Classification (proposed) C5b/E5b C5b/E5b C5b/E5b C5/E5 C5/E5  Dominant Evolutionary class (Simon) if applicable Stage III Stage IV Stage III Stage IV  REGULATORY CONSIDERATIONS  Parameters Applicable? Resolved? Supporting Documentation  Water of the United States ‐ Section 404 Yes Yes USACE Nationwide Permit No. 27  and DWQ 401 Water Quality  Certification No. 4134. Water of the United States ‐ Section 401 Yes Yes  Endangered Species Act Yes Yes Categorical Exclusion in Mitigation  Plan (Wildlands, 2019)  Historic Preservation Act Yes Yes  Coastal Zone Management Act (CZMA or CAMA) N/A N/A N/A  Essential Fisheries Habitat N/A N/A N/A    Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final 2‐1  Section 2: MONITORING YEAR 3 DATA ASSESSNENT  Annual monitoring and site visits were conducted during MY3 to assess the condition of the project. The  vegetation and stream success criteria for the Site follow the approved success criteria presented in the  Mitigation Plan (Wildlands, 2019). Performance criteria for vegetation, stream, and hydrologic  assessment are located in Section 1.2 Table 2: Goals, Performance Criteria, and Functional  Improvements. Methodology for annual monitoring is presented in the MY0 Annual Report (Wildlands,  2021).    2.1 Vegetative Assessment  The MY3 vegetative survey was completed in September 2023. Vegetation monitoring resulted in a stem  density range of 243 to 567 planted stems per acre and the average stem density was 427 planted stems  per acre.  Out of the eleven vegetation plots, nine met the success criteria of 320 stems per acres, while  vegetation plots 1 and 2 have 283 and 243 stems per acres, respectively. Mortality is contributed to  competition from dense herbaceous grass and a dry spring when the trees were originally planted in  2021.  Refer to Appendix A for Vegetation Plot Photographs and the Vegetation Condition Assessment  Table and Appendix B for Vegetation Plot Data.   There were a significant number of mature hardwood trees that were left untouched from construction.  A visual site assessment in September 2022 indicated that some mature trees are starting to decline  after construction. Further observations throughout 2023 did not show a significant change in the  condition of the mature hardwoods left onsite. Planted trees and volunteer species are growing  throughout the Site and starting to fill in an understory that will eventually become a mature hardwood  forest.   2.2 Vegetation Areas of Concern and Management  Approximately 0.55 acres along T1 was identified as an area of low stem density in MY2. A supplemental  planting of the area was approved in MY2 and conducted in February 2023 (Figure 1a). The  supplementally planted species were the same from the approved Mitigation Plan (Table 7b). Ring  sprays were completed throughout the supplementally planted area and soil amendments were applied  locally to replanted trees to reduce competition and aid in planted stem success. Ring sprays and soil  amendments will be competed in MY4 in the supplementally planted areas as well as any areas where  the herbaceous vegetation is affecting tree growth.   An invasive species treatment was completed in May 2023 to address a dense population of Chinese  privet (Ligustrum sinense) along Sassarixa Creek Reach 3 and scattered stems throughout the remainder  of the Site. A combination of methods included foliar and cut stump applications. Approximately 4.97  acres at the downstream reach of Sassarixa Creek was treated and may require additional treatment in  MY4 if resprouting occurs. The Site will continue to be monitored for invasive species and follow up  treatments will occur if necessary.  A dense stand of sweetgum (Liquidambar styraciflua) and loblolly pine (Pinus taeda) covering  approximately 0.70 acres became established along T1 and T1B. This area was treated, and individuals  of both species were thinned in May 2023 by brush cutting. The Site will continue to be monitored for  additional dense populations of sweetgum and loblolly pine and follow up treatments will occur if  necessary.   2.3 Stream Assessment  Morphological surveys for MY3 were conducted in March 2023. All streams within the Site are stable  and functioning as designed. All 10 cross‐sections at the Site show little to no change in the bankfull area  and width‐to‐depth ratio, and bank height ratios are less than 1.2. Refer to Appendix A for the Visual    Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final 2‐2  Stream Morphology Stability Assessment Table and Stream Photographs. Refer to Appendix C for Stream  Geomorphology Data.  2.4  Stream Areas of Concern and Management  Due to concern over the upper third of T2 appearing to be turning into a linear wetland, the NCIRT  requested that an additional cross‐section be installed at the upstream end of T2. During and  immediately following construction of the Site, sediment entered the top of T2 and began accumulating  in the channel. This allowed in‐stream vegetation to become established, which resulted in channel  constriction and flow restriction. The additional cross‐section (XS 11) was installed in May 2023 and a  cross‐section survey was taken to document geomorphology of the channel before being raked out. At  the end of June 2023, approximately 545 linear feet of channel was raked out to remove in‐stream  vegetation and sediment (Figure 1a). An additional cross‐section survey was completed immediately  after the stream was raked out, and then again four months later. While the cross‐sectional area  experienced little change between the initial survey on May 31, 2023, and when it was resurveyed on  July 20, 2023 after the raking, the max depth increased. The third survey on November 14, 2023,  indicated minimal changes in cross‐sectional area, bankfull elevations, thalweg elevation, and max  depth. This indicates that the stream stable and moving sediment through the system. The upper third  of T2 will continue to be monitored for further sediment accumulation or vegetation growth in the  channel.  2.5 Hydrology Assessment  By the end of MY7, four bankfull events must have occurred in separate years within the restoration  reaches. At least one bankfull event was recorded on all stream restoration reaches except T3 Reach 1.  While a bankfull event was not recorded on the T2 flow gauge, evidence of a bankfull event was visually  observed and documented. The hydrologic success criterion for bankfull events has been partially met in  MY3.   In addition, the presence of baseflow must be documented on restored intermittent reaches (T1 Reach  2, T2 and T3 Reach 1) for a minimum of 30 consecutive days during a normal precipitation year. In‐ stream flow gauges equipped with pressure transducers were installed to monitor continuity of  baseflow. All intermittent reaches in MY3 exceeded baseflow success criteria. The maximum  consecutive days ranged from 45 days to 75 days. Refer to Appendix 5 for hydrologic data.   2.6 Wetland Assessment  One groundwater gauge was installed and monitored within an existing wetland zone along T3 at a  location requested by North Carolina Division of Water Resources. The purpose of the gauge is to assess  potential effects to wetland hydrology from the construction of the restored stream channel through  this area.  The results of this monitoring are not tied to any success criteria. Results from the  groundwater gauge, during MY3, show that the existing wetland maintained free groundwater within 12  inches of the ground surface for 39.1% of the defined growing season (March 1 to November 16).  2.7 Monitoring Year 3 Summary  Overall, the Site has met the success criteria for MY3. Nine out of eleven veg plots are on track to meet  the MY3 interim success criteria. A supplemental planting on 0.55 acres was completed in February 2023  to accommodate for tree mortality along T1. Some mature trees that were avoided during construction  were starting to decline in 2022, however their condition was stable in 2023 and a new understory layer  is continuing to establish. An approximately 4.97 acre dense stand of Chinese privet along Sassarixa  Creek Reach 3, as well as scattered stems throughout the remainder of the Site were treated in May  2023. Chinese privet throughout the Site will continue to be monitored and treated as necessary. The  upper reach of T2 was raked to clear excessive sedimentation and vegetation from the channel and    Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final 2‐3  continue to be monitored for changes in channel condition and dimension. Bankfull events were  documented on all stream restoration reaches except T1 Reach 3, partially fulfilling the final bankfull  hydrologic success requirement. Greater than 30 days of consecutive flow were recorded on monitored  intermittent stream reaches T1 Reach 2, T2, and T3 Reach 1 fulfilling MY3 success requirement. The Site  boundary was walked, and fences are in good condition and are keeping livestock out, and all crossings  are stable and in good condition. Overall, the Site is meeting its goals of preventing excess nutrients and  sediment from entering the Neuse River tributaries and is on track to meet final success criteria.  Summary information and data related to the performance of various project and monitoring elements  can be found in the tables and figures in the report appendices. All raw data supporting the tables and  figures in the appendices are available from DMS upon request.   Sassarixa Swamp Mitigation Site  Monitoring Year 3 Annual Report ‐ Final 3‐1  Section 3:  REFERENCES  Breeding, R. 2010. Neuse River Basin Restoration Priorities 2010. NCEEP, NC  Doll, B.A., Grabow, G.L., Hall, K.A., Halley, J., Harman, W.A., Jennings, G.D., and Wise, D.E. 2003. Stream  Restoration A Natural Channel Design Handbook.  Harrelson, C.C., Rawlins, C.L., Potyondy, J.P. 1994. Stream Channel Reference Sites: An Illustrated Guide  to Field Technique. Gen. Tech. Rep. RM‐245. Fort Collins, CO:  U.S. Department of Agriculture, Forest  Service, Rocky Mountain Forest and Range Experiment Station. 61 p.  Rosgen, D. L. 1994. A classification of natural rivers. Catena 22:169‐199.  Rosgen, D.L. 1996. Applied River Morphology. Pagosa Springs, CO: Wildland Hydrology Books.  Rosgen, D.L. 1997. A Geomorphological Approach to Restoration of Incised Rivers. Proceedings of the  Conference on Management of Landscapes Disturbed by Channel Incision. Center For  Computational Hydroscience and Bioengineering, Oxford Campus, University of Mississippi, Pages  12‐22.  North Carolina Division of Water Resources (DWR). 2015. Neuse 01 CU Update. River Basin Restoration  Priorities Transition Approach.  North Carolina Interagency Review Team (NCIRT). 2016. Wilmington District Stream and Wetland  Compensatory Mitigation Update. Accessed at: https://saw‐ reg.usace.army.mil/PN/2016/Wilmington‐District‐Mitigation‐Update.pdf  United States Army Corps of Engineers. 2003. Stream Mitigation Guidelines. USACE, NCDENR‐DWQ,  USEPA, NCWRC.  United States Geological Survey. 1998. North Carolina Geology.   Wildlands Engineering, Inc. (2019). Sassarixa Swamp Mitigation Project Mitigation Plan. DMS, Raleigh,  NC.    T2 T 5 A T5C T 5 B T1A T1 C T 1 B T4 S a s s a r i x a C r e e k T3 T6 T5 T1 T1DT1 Reach 1 Reach 1 Reach 2 Reach 1 Reach 1 Reach 2 Reach 3 Reach 2 Reach 3 Reach 3Reach 4 Reach 2 Reach 3 Reach 2 Reach 1 Reach 1 Reach 2 Figure 1. Current Condition Plan View Key Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 - 2023 2019 Aerial Photography 0 1,200600 Feet Johnston County, NC Conservation Easement Internal Crossing Existing Wetlands Utility Easement Vegetation Plot Condition - MY3 Criteria Met - Fixed Criteria Not Met - Fixed Criteria Met - Random Vegetation Area of Concern - MY3 Chinese Privet Removal Supplemental Planting (February 2023) Sweetgum & Loblolly Thinning Cross-Sections Stream Restoration Stream Enhancement II Stream Preservation Not for Credit Non-Project Streams Stream Area of Concern - MY3 Stream Raking & Vegetation Removal Fencing Gates Photo Points Reach Break Figure 1a. Figure 1b. Figure 1c. T2 T1A T1 C T 1 B S a s s a r i x a C r e e k T3 T1 T1D T1 4 1 0 + 0 0 4 0 5 + 0 0 4 0 0 + 0 0 310+10 3 0 5 + 0 0 3 0 0 + 0 0 26 0 + 0 0 241+ 0 0 22 0 + 0 0 221+0 0 2 1 5 + 0 0 210+00 2 0 5 + 0 0 2 0 0 + 0 0 125+ 0 0 120 + 0 0 115+00 110+00 105+00 Reach 1 Reach 1 Reach 2 Reach 3Reach 4 Reach 2 Reach 3 Reach 2 Reach 1 X S 3 XS1 XS 7 XS2 X S 5 X S 6 X S 4 X S 1 1 PP9 PP7 PP8 PP5 PP4 PP3 PP2 PP1 P P 2 4 P P 2 5 P P 2 6 P P 2 7 P P 2 8 P P 2 9 PP23 P P 2 2 P P 2 0 P P 1 9 PP10 PP18 PP17 PP16 PP15 PP12 PP14 PP13 PP11 P P 2 1 PP6 3 6 4 2 7 5 1 11 Figure 1a. Current Condition Plan View Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 - 2023 2021 Aerial Photography 0 400200 Feet Johnston County, NC Conservation Easement Internal Crossing Existing Wetlands Vegetation Plot Condition - MY3 Criteria Met - Fixed Criteria Not Met - Fixed Criteria Met - Random Vegetation Area of Concern - MY3 Chinese Privet Removal Supplemental Planting (February 2023) Sweetgum & Loblolly Thinning Stream Restoration Stream Enhancement II Stream Preservation Not for Credit Non-Project Streams As-Built Top of Bank Structures Fencing Cross-Sections Stream Area of Concern - MY3 Stream Raking & Vegetation Removal Gates Barotroll Crest Gauge Flow Gauge Groundwater Well Photo Points Reach Break T4 T6 T5 710+ 0 0 70 4 + 0 0 700+ 0 0 620+00 615+00 610+00 605+00 600+ 0 0 520+00 515+00 510+00 505+00 501 + 0 0 6 2 5 + 0 0 Reach 1 Reach 1 Reach 2 Reach 3 Reach 2 Reach 3 Reach 1 Reach 2 XS 8 XS9 X S 1 0 PP40 PP38 PP36 PP54 PP53 PP50 PP43 PP34 PP42 PP41 PP33 PP39 PP37 PP35 PP32 PP31 PP30 PP51 PP52 8 10 Figure 1b. Current Condition Plan View Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 - 2023 2021 Aerial Photography 0 600300 Feet Johnston County, NC Conservation Easement Internal Crossing Utility Easement Existing Wetlands Vegetation Plot Condition - MY3 Criteria Met - Fixed Stream Restoration Stream Enhancement II Stream Preservation Not for Credit Non-Project Streams As-Built Top of Bank Structures Fencing Cross-Sections Gates Crest Gauge Photo Points Reach Break T 5 A T5C T 5 B 6 6 4 + 0 0 66 0 + 0 0 645+00 640+0 0 63 0 + 2 6 625+00 620+00 PP45 PP48PP49 PP47 PP46 PP44 9 Figure 1c. Current Condition Plan View Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 - 2023 0 200100 Feet Johnston County, NC 2021 Aerial Photography Conservation Easement Existing Wetlands Vegetation Plot Condition - MY3 Criteria Met - Fixed Stream Enhancement II Not for Credit Non-Project Streams As-Built Top of Bank Structures Fencing Gates Photo Points APPENDIX A. VISUAL ASSESSMENT DATA Table 4. Visual Stream Morphology Stability Assessment Table Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 - 2023 T1 R2 810 1,620 Surface Scour/ Bare Bank Bank lacking vegetative cover resulting simply from poor growth and/or surface scour.0 100% Toe Erosion Bank toe eroding to the extent that bank failure appears likely. Does NOT include undercuts that are modest, appear sustainable and are providing habitat. 0 100% Bank Failure Fluvial and geotechnical - rotational, slumping, calving, or collapse.0 100% 0 100% Grade Control Grade control structures exhibiting maintenance of grade across the sill. 00 N/A Bank Protection Bank erosion within the structures extent of influence does not exceed 15%. 27 27 100% T1 R3 507 1,014 Surface Scour/ Bare Bank Bank lacking vegetative cover resulting simply from poor growth and/or surface scour.0 100% Toe Erosion Bank toe eroding to the extent that bank failure appears likely. Does NOT include undercuts that are modest, appear sustainable and are providing habitat. 0 100% Bank Failure Fluvial and geotechnical - rotational, slumping, calving, or collapse.0 100% 0 100% Grade Control Grade control structures exhibiting maintenance of grade across the sill. 00 N/A Bank Protection Bank erosion within the structures extent of influence does not exceed 15%. 14 14 100% Visual assessment was completed on 11/14/2023. Structure Major Channel Category Metric Number Stable, Performing as Intended Total Number in As-built Amount of Unstable Footage Assessed Stream Length Assessed Bank Length Bank Totals: % Stable, Performing as Intended Assessed Stream Length Assessed Bank Length Bank Totals: Structure Visual assessment was completed on 11/14/2023. % Stable, Performing as Intended Major Channel Category Metric Number Stable, Performing as Intended Total Number in As-built Amount of Unstable Footage Table 4. Visual Stream Morphology Stability Assessment Table Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 - 2023 T2 1,006 2,012 Surface Scour/ Bare Bank Bank lacking vegetative cover resulting simply from poor growth and/or surface scour.0 100% Toe Erosion Bank toe eroding to the extent that bank failure appears likely. Does NOT include undercuts that are modest, appear sustainable and are providing habitat. 0 100% Bank Failure Fluvial and geotechnical - rotational, slumping, calving, or collapse.0 100% 0 100% Grade Control Grade control structures exhibiting maintenance of grade across the sill. 34 34 100% Bank Protection Bank erosion within the structures extent of influence does not exceed 15%. 18 18 100% T3 R1 1,041 2,082 Surface Scour/ Bare Bank Bank lacking vegetative cover resulting simply from poor growth and/or surface scour.0 100% Toe Erosion Bank toe eroding to the extent that bank failure appears likely. Does NOT include undercuts that are modest, appear sustainable and are providing habitat. 0 100% Bank Failure Fluvial and geotechnical - rotational, slumping, calving, or collapse.0 100% 0 100% Grade Control Grade control structures exhibiting maintenance of grade across the sill. 00 N/A Bank Protection Bank erosion within the structures extent of influence does not exceed 15%. 30 30 100% Visual assessment was completed on 11/14/2023. Structure Major Channel Category Metric Number Stable, Performing as Intended Total Number in As-built Amount of Unstable Footage Assessed Stream Length Assessed Bank Length Bank Totals: % Stable, Performing as Intended Assessed Stream Length Assessed Bank Length Bank Totals: Structure Visual assessment was completed on 11/14/2023. % Stable, Performing as Intended Major Channel Category Metric Number Stable, Performing as Intended Total Number in As-built Amount of Unstable Footage Table 4. Visual Stream Morphology Stability Assessment Table Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 - 2023 T5 R2 874 1,748 Surface Scour/ Bare Bank Bank lacking vegetative cover resulting simply from poor growth and/or surface scour.0 100% Toe Erosion Bank toe eroding to the extent that bank failure appears likely. Does NOT include undercuts that are modest, appear sustainable and are providing habitat. 0 100% Bank Failure Fluvial and geotechnical - rotational, slumping, calving, or collapse.0 100% 0 100% Grade Control Grade control structures exhibiting maintenance of grade across the sill. 00 N/A Bank Protection Bank erosion within the structures extent of influence does not exceed 15%. 20 20 100% T6 R1 383 766 Surface Scour/ Bare Bank Bank lacking vegetative cover resulting simply from poor growth and/or surface scour.0 100% Toe Erosion Bank toe eroding to the extent that bank failure appears likely. Does NOT include undercuts that are modest, appear sustainable and are providing habitat. 0 100% Bank Failure Fluvial and geotechnical - rotational, slumping, calving, or collapse.0 100% 0 100% Grade Control Grade control structures exhibiting maintenance of grade across the sill. 00 N/A Bank Protection Bank erosion within the structures extent of influence does not exceed 15%. 5 5 100% Visual assessment was completed on 11/14/2023. Visual assessment was completed on 11/14/2023. Totals: Structure % Stable, Performing as Intended Assessed Stream Length Assessed Bank Length Bank Major Channel Category Metric Number Stable, Performing as Intended Total Number in As-built Amount of Unstable Footage Assessed Stream Length Assessed Bank Length Totals: Bank Structure % Stable, Performing as Intended Major Channel Category Metric Number Stable, Performing as Intended Total Number in As-built Amount of Unstable Footage Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 ‐ 2023 Planted Acreage 13.03 Vegetation Category Definitions Mapping  Threshold  (ac) Combined  Acreage % of Planted  Acreage Bare Areas Very limited cover of both woody and herbaceous material.0.10 0 0% Low Stem Density  Areas Woody stem densities clearly below target levels based on current MY stem count  criteria.0.10 0.55 4% 0.55 4% Areas of Poor Growth  Rates Planted areas where average height is not meeting current MY Performance  Standard.0.10 0 0% 0.55 4% Easement Acreage 65.06 Vegetation Category Definitions Mapping  Threshold  (ac) Combined  Acreage % of  Easement  Acreage Invasive Areas of  Concern Invasives may occur outside of planted areas and within the easement and will  therefore be calculated against the total easement acreage. Include species with the  potential to directly outcompete native, young, woody stems in the short‐term or  community structure for existing communities.  Invasive species included in  summation above should be identified in report summary.   0.10 4.97* 8% Easement  Encroachment Areas Encroachment may be point, line, or polygon. Encroachment to be mapped consists of any violation of restrictions specified in the conservation easement. Common encroachments are mowing, cattle access, vehicular access. Encroachment has no threshold value as will need to be addressed regardless of impact area.  none *Chinese privet (Ligustrum sinense ) resprouted throughout an existing mautre canopy forest along Sassarixa Creek and was treated March 2023. Table 5.  Vegetation Condition Assessment Table Total Cumulative Total 0 Encroachments Noted/ 0 Ac *Supplemental planting occurred in February 2023.  STREAM PHOTOGRAPHS Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 1 T1 R1 – upstream (2/7/2023) PHOTO POINT 1 T1 R1 – downstream (2/7/2023) PHOTO POINT 2 T1 R2 – upstream (2/7/2023) PHOTO POINT 2 T1 R2 – downstream (2/7/2023) PHOTO POINT 3 T1 R2 – upstream (2/7/2023) PHOTO POINT 3 T1 R2 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 4 T1 R2 – upstream (2/7/2023) PHOTO POINT 4 T1 R2 – downstream (2/7/2023) PHOTO POINT 5 T1 R3 – upstream (2/7/2023) PHOTO POINT 5 T1 R3 – downstream (2/7/2023) PHOTO POINT 6 T1 R3 – upstream (2/7/2023) PHOTO POINT 6 T1 R3 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 7 T1 R3 – upstream (2/7/2023) PHOTO POINT 7 T1 R4 – downstream (2/7/2023) PHOTO POINT 8 T1 R4 – upstream (2/7/2023) PHOTO POINT 8 T1 R4 – downstream (2/7/2023) PHOTO POINT 9 T1A – upstream (2/7/2023) PHOTO POINT 9 T1A – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 10 T1B – upstream (2/7/2023) PHOTO POINT 10 T1B – downstream (2/7/2023) PHOTO POINT 11 T1B – upstream (2/7/2023) PHOTO POINT 11 T1B – downstream (2/7/2023) PHOTO POINT 12 T1C – upstream (2/7/2023) PHOTO POINT 12 T1C – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 13 Sassarixa Creek R2 – upstream (2/7/2023) PHOTO POINT 13 Sassarixa Creek R2 – downstream (2/7/2023) PHOTO POINT 14 Sassarixa Creek R2 – upstream (2/7/2023) PHOTO POINT 14 Sassarixa Creek R2 – downstream (2/7/2023) PHOTO POINT 15 Sassarixa Creek R2 – upstream (2/7/2023) PHOTO POINT 15 Sassarixa Creek R2 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 16 Sassarixa Creek R2 – upstream (5/31/2023) PHOTO POINT 16 Sassarixa Creek R2 – downstream (5/31/2023) PHOTO POINT 17 Sassarixa Creek R3 – upstream (2/7/2023) PHOTO POINT 17 Sassarixa Creek R3 – downstream (2/7/2023) PHOTO POINT 18 Sassarixa Creek R3 – upstream (5/31/2023) PHOTO POINT 18 Sassarixa Creek R3 – downstream (5/31/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 19 T2 – upstream (2/7/2023) PHOTO POINT 19 T2 – downstream (2/7/2023) PHOTO POINT 20 T2 – upstream (2/7/2023) PHOTO POINT 20 T2 – downstream (2/7/2023) PHOTO POINT 21 T2 – upstream (2/7/2023) PHOTO POINT 21 T2 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 22 T2 – upstream (2/7/2023) PHOTO POINT 22 T2 – downstream (2/7/2023) PHOTO POINT 23 T2 – upstream (2/7/2023) PHOTO POINT 23 T2 – downstream (2/7/2023) PHOTO POINT 24 T3 R1 – upstream (2/7/2023) PHOTO POINT 24 T3 R1 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 25 T3 R1 – upstream (2/7/2023) PHOTO POINT 25 T3 R1 – downstream (2/7/2023) PHOTO POINT 26 T3 R1 – upstream (2/7/2023) PHOTO POINT 26 T3 R1 – downstream (2/7/2023) PHOTO POINT 27 T3 R1 – upstream (2/7/2023) PHOTO POINT 27 T3 R1 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 28 T3 R1 – upstream (2/7/2023) PHOTO POINT 28 T3 R1 – downstream (2/7/2023) PHOTO POINT 29 T3 R2 – upstream (2/7/2023) PHOTO POINT 29 T3 R2 – downstream (2/7/2023) PHOTO POINT 30 T4 R1 – upstream (2/7/2023) PHOTO POINT 30 T4 R1 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 31 T4 R2 – upstream (2/7/2023) PHOTO POINT 31 T4 R2 – downstream (2/7/2023) PHOTO POINT 32 T4 R3 – upstream (2/7/2023) PHOTO POINT 32 T4 R3 – downstream (2/7/2023) PHOTO POINT 33 T4 R3 – upstream (2/7/2023) PHOTO POINT 33 T4 R3 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 34 T4 R3 – upstream (2/7/2023) PHOTO POINT 34 T4 R3 – downstream (2/7/2023) PHOTO POINT 35 T5 R1 – upstream (2/7/2023) PHOTO POINT 35 T5 R1 – downstream (2/7/2023) PHOTO POINT 36 T5 R1 – upstream (2/7/2023) PHOTO POINT 36 T5 R1 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 37 T5 R2 – upstream (2/7/2023) PHOTO POINT 37 T5 R2 – downstream (2/7/2023) PHOTO POINT 38 T5 R2 – upstream (2/7/2023) PHOTO POINT 38 T5 R2 – downstream (2/7/2023) PHOTO POINT 39 T5 R2 – upstream (2/7/2023) PHOTO POINT 39 T5 R2 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 40 T5 R2 – upstream (2/7/2023) PHOTO POINT 40 T5 R3 – downstream (2/7/2023) PHOTO POINT 41 T5 R3 – upstream (2/7/2023) PHOTO POINT 41 T5 R3 – downstream (2/7/2023) PHOTO POINT 42 T5 R3 – upstream (2/7/2023) PHOTO POINT 42 T5 R3 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 43 T5 R3 – upstream (2/7/2023) PHOTO POINT 43 T5 R3 – downstream (2/7/2023) PHOTO POINT 44 T5A – upstream (2/7/2023) PHOTO POINT 44 T5A – downstream (2/7/2023) PHOTO POINT 45 T5A – upstream (2/7/2023) PHOTO POINT 45 T5A – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 46 T5B – upstream (2/7/2023) PHOTO POINT 46 T5B – downstream (2/7/2023) PHOTO POINT 47 T5B – upstream (2/7/2023) PHOTO POINT 47 T5B – downstream (2/7/2023) PHOTO POINT 48 T5C – upstream (2/7/2023) PHOTO POINT 48 T5C – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 49 T5C – upstream (2/7/2023) PHOTO POINT 49 T5C – downstream (2/7/2023) PHOTO POINT 50 T6 R1 – upstream (2/7/2023) PHOTO POINT 50 T6 R1 – downstream (2/7/2023) PHOTO POINT 51 T6 R2 – upstream (2/7/2023) PHOTO POINT 51 T6 R2 – downstream (2/7/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Photographs PHOTO POINT 52 T6 R2 – upstream (2/7/2023) PHOTO POINT 52 T6 R2 – downstream (2/7/2023) PHOTO POINT 53 T6 R2 – upstream (2/7/2023) PHOTO POINT 53 T6 R2 – downstream (2/7/2023) PHOTO POINT 54 T6 R2 – upstream (2/7/2023) PHOTO POINT 54 T6 R2 – downstream (2/7/2023) STREAM CROSSING PHOTOGRAPHS Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Crossing Photographs Sassarixa Creek Reach 2 – Looking Upstream (11/14/2023) Sassarixa Creek Reach 2 – Looking Downstream (11/14/2023) T1 Reach 1 – Looking Upstream (11/14/2023) T1 Reach 1 – Looking Downstream (11/14/2023) T4 Reach 3 – Looking Upstream (11/14/2023) T4 Reach 3 – Looking Downstream (11/14/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Stream Crossing Photographs T5 Reach 3 – Looking Upstream (11/14/2023) T5 Reach 3 – Looking Downstream (11/14/2023) T6 Reach 2 – Looking Upstream (11/14/2023) T6 Reach 2 – Looking Downstream (11/14/2023) VEGETATION PLOT PHOTOGRAPHS Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Vegetation Plot Photographs FIXED VEG PLOT 1 (9/14/2023) FIXED VEG PLOT 2 (9/14/2023) FIXED VEG PLOT 3 (9/19/2023) FIXED VEG PLOT 4 (9/19/2023) FIXED VEG PLOT 5 (9/19/2023) FIXED VEG PLOT 6 (9/19/2023) Sassarixa Swamp Mitigation Site Appendix A: Visual Assessment Data – Vegetation Plot Photographs FIXED VEG PLOT 7 (9/19/2023) FIXED VEG PLOT 8 (9/19/2023) FIXED VEG PLOT 9 (9/19/2023) FIXED VEG PLOT 10 (9/20/2023) RANDOM VEG PLOT 11 (9/20/2023) APPENDIX B. VEGETATION PLOT DATA Table 6.  Vegetation Plot Data Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 ‐ 2023 13.03 2021‐03‐05 2023‐02‐13 2023‐09‐21 0.0247 Scientific Name Common Name Planted Total Planted Total Planted Total Planted Total Planted Total Acer negundo boxelderTreeFAC11 111111 Betula nigra river birchTreeFACW22 441122 Magnolia virginiana sweetbayTreeFACW 11 1111 Platanus occidentalis American sycamoreTreeFACW1111442233 Populus deltoides eastern cottonwoodTreeFAC 33 1111 Quercus michauxii swamp chestnut oakTreeFACW11 223311 Quercus nigra water oakTreeFAC1111 11 Quercus phellos willow oakTreeFACW11 333322 Sum 7766141413131111 Liquidambar styraciflua sweetgum Tree FAC Sum 7766141413131111 7 6 14 13 11 283 243 567 526 445 64587 29 50 29 23 27 23313 00000 7 6 14 13 11 283 243 567 526 445 64587 29 50 29 23 27 23313 00000 Post Mitigation  Plan  Performance  Standard Current Year Stem Count Stems/Acre Species Count Dominant Species Composition (%) Average Plot Height (ft.) % Invasives Species Included  in Approved  Mitigation Plan Post Mitigation  Plan Species Mitigation Plan  Performance  Standard Performance Standard Proposed Standard Veg Plot 5 FIndicator  Status Veg Plot 1 FVeg Plot 2 FVeg Plot 3 FVeg Plot 4 F Date of Current Survey Plot size (ACRES) Tree/S hrub Planted Acreage Date of Initial Plant Date(s) of Supplemental Plant(s) Current Year Stem Count Stems/Acre Species Count Dominant Species Composition (%) Average Plot Height (ft.) % Invasives Table 6.  Vegetation Plot Data Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 ‐ 2023 13.03 2021‐03‐05 2023‐02‐13 2023‐09‐21 0.0247 Scientific Name Common Name Acer negundo boxelder Tree FAC Betula nigra river birch Tree FACW Magnolia virginiana sweetbay Tree FACW Platanus occidentalis American sycamore Tree FACW Populus deltoides eastern cottonwood Tree FAC Quercus michauxii swamp chestnut oak Tree FACW Quercus nigra water oak Tree FAC Quercus phellos willow oak Tree FACW Sum Liquidambar styraciflua sweetgum Tree FAC Sum Post Mitigation  Plan  Performance  Standard Current Year Stem Count Stems/Acre Species Count Dominant Species Composition (%) Average Plot Height (ft.) % Invasives Species Included  in Approved  Mitigation Plan Post Mitigation  Plan Species Mitigation Plan  Performance  Standard Performance Standard Proposed Standard Indicator  Status Date of Current Survey Plot size (ACRES) Tree/S hrub Planted Acreage Date of Initial Plant Date(s) of Supplemental Plant(s) Current Year Stem Count Stems/Acre Species Count Dominant Species Composition (%) Average Plot Height (ft.) % Invasives Veg Plot  11 R Planted Total Planted Total Planted Total Planted Total Planted Total Total 22111111 1 2222112211 111111 221 22332244226 11 2 3333221133 11 4 331111 11 1313131388889914 1 1313131388889914 13 13 8 8 9 14 526 526 324 324 364 567 686455 23 23 25 50 33 40 122211 000000 13 13 8 8 9 14 526 526 324 324 364 567 686455 23 23 25 50 33 40 122211 000000 Veg Plot 10 FVeg Plot 6 FVeg Plot 7 FVeg Plot 8 FVeg Plot 9 F Table 7a.  Vegetation Performance Standards Summary Table Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 ‐ 2023 Stems/Ac. Av. Ht. (ft) # Species % Invasives Stems/Ac. Av. Ht. (ft) # Species % Invasives Stems/Ac. Av. Ht. (ft) # Species % Invasives 283 2 6 0 243 3 4 0 567 3 5 0 324 1 6 0 283 1 5 0 567 2 5 0 364 1 6 0 243 1 3 0 607 1 6 0 567 1 8 0 445 1 5 0 607 1 6 0 Stems/Ac. Av. Ht. (ft) # Species % Invasives Stems/Ac. Av. Ht. (ft) # Species % Invasives Stems/Ac. Av. Ht. (ft) # Species % Invasives 526 1 8 0 445 3 7 0 526 1 6 0 526 1 8 0 486 2 7 0 526 1 6 0 567 1 8 0 486 1 7 0 526 1 6 0 607 1 8 0 486 1 7 0 567 1 6 0 Stems/Ac. Av. Ht. (ft) # Species % Invasives Stems/Ac. Av. Ht. (ft) # Species % Invasives Stems/Ac. Av. Ht. (ft) # Species % Invasives 526 2 8 0 324 2 6 0 324 2 4 0 526 1 8 0 364 1 6 0 364 1 5 0 567 1 8 0 567 1 7 0 607 1 7 0 567 1 8 0 567 1 7 0 648 1 7 0 Stems/Ac. Av. Ht. (ft) # Species % Invasives Stems/Ac. Av. Ht. (ft) # Species % Invasives 364 1 5 0 567 1 5 0 567 1 6 0 486 1 7 0 891 1 8 0 486 1 8 0 607 1 8 0 648 1 8 0 *Each monitoring year represents a different plot for the random vegetation plot "groups". Random plots are denoted with an R, and fixed plots with an F. Veg Plot 3 F Veg Plot 4 F Veg Plot 5 F Veg Plot 6 F Veg Plot 7 F Veg Plot 8 F Veg Plot 9 F Monitoring Year 2 Monitoring Year 1 Monitoring Year 0 Veg Plot 1 F Veg Plot 2 F Veg Plot 10 F Veg Plot Group 11 R Monitoring Year 1 Monitoring Year 0 Monitoring Year 7 Monitoring Year 5 Monitoring Year 3 Monitoring Year 0 Monitoring Year 7 Monitoring Year 5 Monitoring Year 3 Monitoring Year 2 Monitoring Year 7 Monitoring Year 5 Monitoring Year 3 Monitoring Year 2 Monitoring Year 1 Monitoring Year 0 Monitoring Year 7 Monitoring Year 5 Monitoring Year 3 Monitoring Year 2 Monitoring Year 1 Table 7b. Supplementally Planted Tree Species and Quantities  Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 ‐ 2023 Scientific Name Common Name Number Planted % of Total Type  Quercus phellos Willow Oak 367 15%Bare Root Platanus occidentalis Sycamore 490 20%Bare Root Betula nigra River Birch 490 20%Bare Root Quercus michauxii Swamp Chestnut Oak 367 15%Bare Root Quercus nigra Water Oak 172 7%Bare Root Acer negundo Box Elder 245 10%Bare Root Populus deltoides Eastern Cottonwood 172 7%Bare Root Magnolia virginiana Sweetbay Mangolina 147 6%Bare Root 2,450 100% * A total area of 8.51 acres were supplemented with trees in February 2023 along T1, the ditch above T3, T4, T5A, and T5C. Of that, 0.55 acres were within the Sassarixa Swamp Mitigation Site along T1.  Total APPENDIX C. Stream Geomorphology Data                         Cross‐Section Plots                                                Sassarixa Swamp Mitigation Site  Appendix C: Stream Geomorphology Data – Cross‐Section Plots       Downstream (03/07/2023)    MY0 MY1 MY2 MY3 MY5 MY7  Bankfull Elevation ‐ Based  on AB‐Bankfull Area 149.35 149.41 149.28 149.27  Bank Height Ratio ‐ Based  on AB‐Bankfull Area 1.00 0.93 1.03 1.01  Thalweg Elevation 148.45 148.62 148.34 148.28  LTOB Elevation 149.35 149.36 149.31 149.28  LTOB Max Depth 0.90 0.74 0.97 1.00  LTOB Cross‐Sectional Area 2.47 2.16 2.63  2.51         Sassarixa Swamp Mitigation Site  Appendix C: Stream Geomorphology Data – Cross‐Section Plots       Downstream (03/07/2023)    MY0 MY1 MY2 MY3 MY5 MY7  Bankfull Elevation ‐ Based  on AB‐Bankfull Area N/A N/A N/A N/A     Bank Height Ratio ‐ Based  on AB‐Bankfull Area N/A N/A N/A N/A     Thalweg Elevation 147.78 147.58 147.67 147.87  LTOB Elevation 148.82 148.77 148.83 148.79    LTOB Max Depth 1.04 1.19 1.16 0.92    LTOB Cross‐Sectional Area 3.20 2.84 2.91  2.79         Sassarixa Swamp Mitigation Site  Appendix C: Stream Geomorphology Data – Cross‐Section Plots       Downstream (03/07/2023)    MY0 MY1 MY2 MY3 MY5 MY7  Bankfull Elevation ‐ Based  on AB‐Bankfull Area 130.69 130.77 130.75 130.68    Bank Height Ratio ‐ Based  on AB‐Bankfull Area 1.00 0.91 0.94 1.08    Thalweg Elevation 130.04 130.24 130.12 130.02    LTOB Elevation 130.69 130.72 130.71 130.73    LTOB Max Depth 0.64 0.48 0.59 0.71    LTOB Cross‐Sectional Area 1.67 1.45 1.50  1.93      Sassarixa Swamp Mitigation Site  Appendix C: Stream Geomorphology Data – Cross‐Section Plots       Downstream (03/07/2023)    MY0 MY1 MY2 MY3 MY5 MY7  Bankfull Elevation ‐ Based  on AB‐Bankfull Area 141.46 141.52 141.49 141.51    Bank Height Ratio ‐ Based  on AB‐Bankfull Area 1.00 0.94 0.95 0.91    Thalweg Elevation 140.66 140.78 140.77 140.77    LTOB Elevation 141.46 141.47 141.46 141.45    LTOB Max Depth 0.80 0.69 0.69 0.68    LTOB Cross‐Sectional Area 1.99 1.76 1.80  1.65         Sassarixa Swamp Mitigation Site  Appendix C: Stream Geomorphology Data – Cross‐Section Plots       Downstream (03/07/2023)    MY0 MY1 MY2 MY3 MY5 MY7  Bankfull Elevation ‐ Based  on AB‐Bankfull Area N/A N/A N/A N/A    Bank Height Ratio ‐ Based  on AB‐Bankfull Area N/A N/A N/A N/A    Thalweg Elevation 139.53 139.50 139.51 139.67    LTOB Elevation 141.12 141.10 141.07 141.06    LTOB Max Depth 1.58 1.60 1.56 1.39    LTOB Cross‐Sectional Area 4.88 4.82 4.57 4.65           Sassarixa Swamp Mitigation Site  Appendix C: Stream Geomorphology Data – Cross‐Section Plots       Downstream (03/07/2023)    MY0 MY1 MY2 MY3 MY5 MY7  Bankfull Elevation ‐ Based  on AB‐Bankfull Area N/A N/A N/A N/A    Bank Height Ratio ‐ Based  on AB‐Bankfull Area N/A N/A N/A N/A    Thalweg Elevation 126.70 127.32 127.31 127.31    LTOB Elevation 128.16 128.35 128.31 128.33    LTOB Max Depth 1.46 1.03 1.00 1.02    LTOB Cross‐Sectional Area 3.25 2.57 2.40  2.27         Sassarixa Swamp Mitigation Site  Appendix C: Stream Geomorphology Data – Cross‐Section Plots       Downstream (03/07/2023)    MY0 MY1 MY2 MY3 MY5 MY7  Bankfull Elevation ‐ Based  on AB‐Bankfull Area 127.58 127.56 127.54 127.57  Bank Height Ratio ‐ Based  on AB‐Bankfull Area 1.00 1.10 1.09 0.99  Thalweg Elevation 127.06 126.89 126.89 126.91  LTOB Elevation 127.58 127.63 127.59 127.56  LTOB Max Depth 0.52 0.74 0.70 0.65  LTOB Cross‐Sectional Area 1.50      1.82 1.77  1.48         Sassarixa Swamp Mitigation Site  Appendix C: Stream Geomorphology Data – Cross‐Section Plots       Downstream (03/07/2023)    MY0 MY1 MY2 MY3 MY5 MY7  Bankfull Elevation ‐ Based  on AB‐Bankfull Area 133.06 133.12 133.08 133.10    Bank Height Ratio ‐ Based  on AB‐Bankfull Area 1.00 0.85 1.02 1.00    Thalweg Elevation 132.36 132.42 132.40 132.36    LTOB Elevation 133.06 133.02 133.10 133.10    LTOB Max Depth 0.70 0.60 0.70 0.74    LTOB Cross‐Sectional Area 2.49 1.95 2.60  2.48         Sassarixa Swamp Mitigation Site  Appendix C: Stream Geomorphology Data – Cross‐Section Plots       Downstream (03/07/2023)    MY0 MY1 MY2 MY3 MY5 MY7  Bankfull Elevation ‐ Based  on AB‐Bankfull Area N/A N/A N/A N/A   Bank Height Ratio ‐ Based  on AB‐Bankfull Area N/A N/A N/A N/A   Thalweg Elevation 131.03 131.50 131.69 131.69   LTOB Elevation 132.53 132.46 132.55 132.50   LTOB Max Depth 1.50 0.96 0.86 0.81   LTOB Cross‐Sectional Area 6.97 3.86 4.66  4.02         Sassarixa Swamp Mitigation Site  Appendix C: Stream Geomorphology Data – Cross‐Section Plots       Downstream (03/07/2023)      MY0 MY1 MY2 MY3 MY5 MY7  Bankfull Elevation ‐ Based  on AB‐Bankfull Area 156.43 156.50 156.48 156.49     Bank Height Ratio ‐ Based  on AB‐Bankfull Area 1.00 0.88 0.96 0.99     Thalweg Elevation 155.62 155.69 155.67 155.67  LTOB Elevation 156.43 156.40 156.45 156.48    LTOB Max Depth 0.81 0.71 0.78 0.81    LTOB Cross‐Sectional Area 2.69 2.20 2.51  2.64       Sassarixa Swamp Mitigation Site Appendix C: Stream Geomorphology Data – Cross-Section Plots Downstream (07/20/2023) MY3 (5/31/2023) MY3 (7/20/2023) MY3 (11/14/2023) MY4 MY5 MY7 Bankfull Elevation - Based on AB-Bankfull Area 94.62 94.52 94.57 Bank Height Ratio - Based on AB-Bankfull Area 1.00 1.00 1.00 Thalweg Elevation 94.13 93.88 93.98 LTOB Elevation 94.62 94.52 94.57 LTOB Max Depth 0.49 0.64 0.60 LTOB Cross-Sectional Area 1.69 1.68 1.69 Table 8. Baseline Stream Data Summary Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 ‐ 2023 Parameter Riffle Only Min Max n Min Max Min Max n Bankfull Width (ft)1 1 Floodprone Width (ft)1 1 Bankfull Mean Depth (ft)1 1 Bankfull Max Depth (ft)1 0.4 0.5 1 Bankfull Cross Sectional Area (ft2)11 Width/Depth Ratio 1 1 Entrenchment Ratio 1 1 Bank Height Ratio 1 1.0 1.2 1 Max particle size (mm) mobilized at bankfull Rosgen Classification Bankfull Discharge (cfs) Sinuosity Water Surface Slope (ft/ft) 0.0190 0.0300 2 0.0250 0.0410 Other Parameter Riffle Only Min Max n Min Max Min Max n Bankfull Width (ft)1 1 Floodprone Width (ft)1 1 Bankfull Mean Depth (ft)1 1 Bankfull Max Depth (ft)1 0.4 0.6 1 Bankfull Cross Sectional Area (ft2)11 Width/Depth Ratio 1 1 Entrenchment Ratio 1 1 Bank Height Ratio 1 1.0 1.2 1 Max particle size (mm) mobilized at bankfull Rosgen Classification Bankfull Discharge (cfs) Sinuosity Water Surface Slope (ft/ft) 0.0190 0.0300 2 0.0092 0.0250 Other 12.0 0.4 0.6 1.7 9.0 1.20 90 0.4 4.2 ‐‐‐ 0.0322 11.0 1.0 ‐‐‐ 34.6 4.9 2.2 C5b/E5b ‐‐‐ 3.08.8 1.20 1.20 ‐‐‐ ‐‐‐‐‐‐‐‐‐ 3.4 8 1 0.7 2.5 1.20 1.20 1.20 0.0181 G5 C5/E5 C5/E5 8.8 3.5 4.3 ‐‐‐‐‐‐‐‐‐ 4.9 2.2 3.0 >2.2 11.1 21.9 1.0 1.5 0.7 2.5 ‐‐‐ T1 R3 3.4 8 1 >9.2 4.3 MONITORING BASELINE  (MY0) 3.6 11.0 1.2 0.3 200 0.4 0.9 2.5 PRE‐EXISTING  CONDITIONS ‐‐‐ G5 C5b/E5b 3.0 T1 R2 >7.9 >2.2 5.2 DESIGN Table 8. Baseline Stream Data Summary Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 ‐ 2023 Parameter Riffle Only Min Max n Min Max Min Max n Bankfull Width (ft)1 1 Floodprone Width (ft)1 1 Bankfull Mean Depth (ft)1 1 Bankfull Max Depth (ft)1 1 Bankfull Cross Sectional Area (ft2)11 Width/Depth Ratio 1 1 Entrenchment Ratio 1 1 Bank Height Ratio 1 1.0 1.2 1 Max particle size (mm) mobilized at bankfull Rosgen Classification Bankfull Discharge (cfs) Sinuosity Water Surface Slope (ft/ft)1 0.0051 0.0064 Other Parameter Riffle Only Min Max n Min Max Min Max n Bankfull Width (ft) 3.2 4.2 2 1 Floodprone Width (ft) 5 24 2 1 Bankfull Mean Depth (ft) 0.42 0.5 2 1 Bankfull Max Depth (ft) 0.7 0.56 2 0.4 0.5 1 Bankfull Cross Sectional Area (ft2)21 Width/Depth Ratio 6.4 10 2 1 Entrenchment Ratio 1.1 7.1 2 1 Bank Height Ratio 2.7 7.0 2 1.0 1.2 1 Max particle size (mm) mobilized at bankfull Rosgen Classification Bankfull Discharge (cfs) 6.2 6.9 2 Sinuosity Water Surface Slope (ft/ft)1 0.0280 0.0330 Other 1.5 14.8 7.4 1.0 75 0.4 0.8 2.0 15.7 13.4 0.0312 ‐‐‐‐‐‐‐‐‐ 0.0340 0.0290 2.5 4.5 1.16 1.20 1.20 ‐‐‐‐‐‐‐‐‐ B5/G5 C5/E5b C5/E5b 12.0 >2.2 >7.9 0.3 1.7 1.0 35 0.3 0.5 0.0147 ‐‐‐‐‐‐‐‐‐ T3 R1 3.6 4.7 5.4 2.0 4.3 1.14 1.40 1.40 ‐‐‐‐‐‐‐‐‐ G5 C5b/E5b C5b/E5b 6 12.0 1.2 >2.2 6.5 1.0 4 >9.2 0.5 0.4 0.6 1.5 1.5 0.5 PRE‐EXISTING  CONDITIONS DESIGN MONITORING BASELINE  (MY0) T2 3 4.2 5.6 Table 8. Baseline Stream Data Summary Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 ‐ 2023 Parameter Riffle Only Min Max n Min Max Min Max n Bankfull Width (ft)1 1 Floodprone Width (ft)1 1 Bankfull Mean Depth (ft)1 1 Bankfull Max Depth (ft)1 0.6 0.8 1 Bankfull Cross Sectional Area (ft2)11 Width/Depth Ratio 1 1 Entrenchment Ratio 1 1 Bank Height Ratio 1 1.0 1.2 1 Max particle size (mm) mobilized at bankfull Rosgen Classification Bankfull Discharge (cfs) Sinuosity Water Surface Slope (ft/ft)1 0.0086 0.0170 Other Parameter Riffle Only Min Max n Min Max Min Max n Bankfull Width (ft)1 1 Floodprone Width (ft)1 1 Bankfull Mean Depth (ft)1 1 Bankfull Max Depth (ft)1 0.5 0.7 1 Bankfull Cross Sectional Area (ft2)11 Width/Depth Ratio 1 1 Entrenchment Ratio 1 1 Bank Height Ratio 1 1.0 1.2 1 Max particle size (mm) mobilized at bankfull Rosgen Classification Bankfull Discharge (cfs) Sinuosity Water Surface Slope (ft/ft)1 0.0049 0.0150 Other 90 0.4 0.8 2.7 13.3 15.1 170 0.4 0.7 2.5 14.0 16.9 0.0107 ‐‐‐‐‐‐‐‐‐ 0.0120 0.0086 12.8 5.5 5.9 1.10 1.20 1.20 ‐‐‐‐‐‐‐‐‐ G5 C5/E5 C5/E5 3.7 12.0 1.7 >2.2 2.0 1.0 7 >14 1.1 0.41 1.5 4.4 3.3 0.0111 ‐‐‐‐‐‐‐‐‐ T6 R1 4.1 6.4 6.0 10.9 6.0 5.4 1.20 1.40 1.40 ‐‐‐‐‐‐‐‐‐ E5 C5/E5 C5/E5 2.8 12.0 8.7 >2.2 1.6 1.0 27 >11 1.1 0.5 1.4 3.5 2.7 PRE‐EXISTING  CONDITIONS DESIGN MONITORING BASELINE  (MY0) T5 R2 3.1 5.6 5.9 Sassarixa Swamp Mitigation Site DMS Project No. 100040 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area 149.35 149.41 149.28 149.27 N/A N/A N/A N/A 130.69 130.77 130.75 130.68 141.46 141.52 141.49 141.51 Bank Height Ratio ‐ Based on AB Bankfull1 Area 1.00 0.93 1.03 1.01 N/A N/A N/A N/A 1.00 0.91 0.94 1.08 1.00 0.94 0.95 0.91 Thalweg Elevation 148.45 148.62 148.34 148.28 147.78 147.58 147.67 147.87 130.04 130.24 130.12 130.02 140.66 140.79 140.77 140.77 LTOB2 Elevation 149.35 149.36 149.31 149.28 148.82 148.77 148.83 148.79 130.69 130.72 130.71 130.73 141.46 141.48 141.46 141.45 LTOB2 Max Depth (ft)0.90 0.74 0.97 1.00 1.04 1.19 1.16 0.92 0.64 0.48 0.59 0.71 0.80 0.69 0.69 0.68 LTOB2 Cross Sectional Area (ft 2)2.47 2.16 2.63 2.51 3.20 2.84 2.91 2.79 1.67 1.45 1.50 1.93 1.99 1.76 1.80 1.65 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area N/A N/A N/A N/A N/A N/A N/A N/A 127.58 127.56 127.54 127.57 133.06 133.12 133.08 133.10 Bank Height Ratio ‐ Based on AB Bankfull1 Area N/A N/A N/A N/A N/A N/A N/A N/A 1.00 1.10 1.09 0.99 1.00 0.85 1.02 1.00 Thalweg Elevation 139.53 139.51 139.51 139.67 126.70 127.32 127.31 127.31 127.06 126.89 126.89 126.91 132.36 132.42 132.40 132.36 LTOB2 Elevation 141.12 141.11 141.07 141.06 128.16 128.35 128.31 128.33 127.58 127.63 127.59 127.56 133.06 133.02 133.10 133.10 LTOB2 Max Depth (ft)1.58 1.60 1.56 1.39 1.46 1.03 1.00 1.02 0.52 0.74 0.70 0.65 0.70 0.60 0.70 0.74 LTOB2 Cross Sectional Area (ft 2)4.88 4.82 4.57 4.65 3.25 2.57 2.40 2.27 1.50 1.82 1.77 1.48 2.49 1.95 2.60 2.48 MY0 MY1 MY2 MY3 MY5 MY7 MY0 MY1 MY2 MY3 MY5 MY7 Bankfull Elevation (ft) ‐ Based on AB‐Bankfull1 Area N/A N/A N/A N/A 156.43 156.50 156.48 156.49 Bank Height Ratio ‐ Based on AB Bankfull1 Area N/A N/A N/A N/A 1.00 0.88 0.96 0.99 Thalweg Elevation 131.03 131.50 131.69 131.69 155.62 155.69 155.67 155.67 LTOB2 Elevation 132.53 132.46 132.55 132.50 156.43 156.40 156.45 156.48 LTOB2 Max Depth (ft)1.50 0.96 0.86 0.81 0.81 0.71 0.78 0.81 LTOB2 Cross Sectional Area (ft 2)6.97 3.86 4.66 4.02 2.69 2.20 2.51 2.64 1Bank Height Ratio (BHR) takes the As‐built bankful area as the basis for adjusting each subsequent years bankfull elevation.   Table 9.  Cross‐Section Morphology Monitoring Summary Cross‐Section 1 (Riffle)Cross‐Section 2 (Pool)Cross‐Section 3 (Riffle) Cross‐Section 7 (Riffle) T6 Reach 1 T2 Cross‐Section 8 (Riffle) T1 Reach 3 Monitoring Year 3 ‐ 2023 T1 Reach 2 Cross‐Section 5 (Pool) 2LTOB Area and Max depth ‐ These are based on the LTOB elevation for each years survey (The same elevation used for the LTOB in the BHR calculation).  Area below the LTOB elevation will be used and tracked for each year as above.  The difference between the LTOB elevation and the  thalweg elevation (same as in the BHR calculation) will be recroded and tracked above as LTOB max depth.  T5 Reach 2 Cross‐Section 4 (Riffle) T2 T3 Reach 1 Cross‐Section 6 (Pool) T5 Reach 2 Cross‐Section 10 (Riffle)Cross‐Section 9 (Pool) Sassarixa Swamp Mitigation Site DMS Project No. 100040 MY3* (5/31/2023) MY3* (7/20/2023) MY3* (11/14/2023)MY4 MY5 MY7 Bankfull Elevation (ft) - Based on AB-Bankfull1 Area 94.61 94.52 94.62 Bank Height Ratio - Based on AB Bankfull1 Area 1.00 1.00 1.00 Thalweg Elevation 94.13 93.88 93.98 LTOB2 Elevation 94.62 94.52 94.62 LTOB2 Max Depth (ft)0.50 0.64 0.60 LTOB2 Cross Sectional Area (ft2)2.00 1.68 1.50 1Bank Height Ratio (BHR) takes the As-built bankful area as the basis for adjusting each subsequent years bankfull elevation. T2 Cross-Section 11 (Riffle) Table 9. Cross-Section Morphology Monitoring Summary Monitoring Year 3 - 2023 2LTOB Area and Max depth - These are based on the LTOB elevation for each years survey (The same elevation used for the LTOB in the BHR calculation). Area below the LTOB elevation will be used and tracked for each year as above. The difference between the LTOB elevation and the thalweg elevation (same as in the BHR calculation) will be recroded and tracked above as LTOB max depth. * An additional cross-section on the upper reach of T2 was requested by the NCIRT to monitor sedimentation and vegetation accumulating within the channel. The cross- section was installed in May 2023. The cross-section was surveyed to establish baseline conditions before vegetation and sedimentation were raked out to clear the stream. The cross-section was then surveyed after raking was completed, and then surveyed again 6 months later to observe any changes in channel stability. APPENDIX D. Hydrology Data Reach MY1 (2021) MY2 (2022) MY3 (2023)* MY4 (2024) MY5 (2025) MY6 (2026) MY7 (2027) T1 Reach 3 2/16/2021 7/28/2021 3/12/2022  5/23/2022 9/10/2022 12/27/2022 6/22/2023 T2 7/27/2021 10/9/2021 N/A 6/30/20231 T3 Reach 1 7/28/2021 1/18/2022 12/27/2022 N/A T5 Reach 2 1/24/2021 7/28/2021 9/10/2022 8/15/2023 MY1 (2021) MY2 (2022) MY3 (2023) MY4 (2024) MY5 (2025) MY6 (2026) MY7 (2027) Annual Precip  Total 34.14 28.44 38.24* WETS 30th  Percentile 44.35 44.67 44.91 WETS 70th  Percentile 52.31 52.62 52.91 Normal LL* Annual Precipitation Source: Smithfield Station, Johnston County, NC, State Climate Office (Approximately 6 miles northeast of the Site).  30 Year Average Precipitation Source: Smithfield Station, Johnston County, NC, AgCIS (Approximately 6 miles northeast of the Site).  *Annual precipitation total was collected up until 11/14/2023. Data will be updated in MY4.  Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 ‐ 2023 Table 10. Bankfull Events Sassarixa Swamp Mitigation Site DMS Project No. 100040 Monitoring Year 3 ‐ 2023 Table 11. Rainfall Summary * Data was collected 1/1/2023 to 11/14/2023. Data from the remainder of MY3 will be updated in MY4. 1. Bankfull event recorded based on visual observations                           BANKFULL EVENTS  VISUAL OBSERVATIONS                                          Sassarixa Swamp Mitigation Site  Appendix D: Hydrology Data – Bankfull Events Visual Observations     T2 (6/30/2023) T2 (6/30/2023)    Table 12. Groundwater Gauge Summary Sassarixa Swamp Mitigation Site Monitoring Year 3 - 2023 MY1 (2021) MY2 (2022) MY3 (2023)* MY4 (2024) MY5 (2025) MY6 (2026) MY7 (2027) 1 124 Days (47.5%) 96 Days (36.8%) 102 Days (39.1%) *Data was collected from 3/1/2023 to 11/14/2023 (258 Days). Gauge Max. Consecutive Hydroperiod (Percentage) DMS Project No. 100040 WETS Station: Smithfield 2 North Growing Season: 3/1/2023 to 11/16/2023 (260 Days) Performance Standard: None Groundwater Gauge Plot Monitoring Year 3 - 2023 Sassarixa Swamp Mitigation Site DMS Project No. 100040 St a r t o f G r o w i n g S e a s o n 3/ 1 / 2 0 2 3 En d o f G r o w i n g S e a s o n 11 / 1 6 / 2 0 2 3 102 max consecutive days Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec 0 2 4 6 8 10 -60 -50 -40 -30 -20 -10 0 10 Pr e c i p i t a t i o n ( i n ) Wa t e r L e v e l ( i n ) Monitoring Year 3 - 2023 Daily Precipitation Gauge #1 Criteria Level Soil Surface 30-Day Rolling Precip Total 30th & 70th Percentile Sassarixa Swamp Groundwater Gauge #1 Possible gauge malfunction early morning of 7/25/23. Transducer replaced mid-day on 7/25/23. Sassarixa Swamp Mitigation Site DMS Project No. 100040 MY1 (2021) MY2 (2022) MY3 (2023)** MY4 (2024) MY5 (2025) MY6 (2026) MY7 (2027) T1 Reach 2 44 Days/ 122 Days 86 Days/ 147Days 45 Days/ 152 Days T2 103 Days/ 192 Days 87 Days/ 156 Days 75 Days/ 169 Days T3 Reach 1 108 Days/ 190 Days 63 Days/ 130 Days 54 Days/ 158 Days **Data was colleted through 11/14/2023. Data will be updated in MY4. *Success criteria is 30 consecutive days of flow. Table 13. Recorded In-Stream Flow Events Summary Monitoring Year 3 - 2023 Reach Max Consecutive Days/Total Days Meeting Success Criteria* Recorded In-Stream Flow Events Plot Monitoring Year 3 - 2023 Sassarixa Swamp Mitigation Site DMS Project No. 100040 45 days of consecutive stream flow Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov 0 2 4 6 8 10 159 160 161 162 163 164 Pr e c i p i t a t i o n ( i n ) El e v a t i o n ( f t ) Monitoring Year 3 - 2023 Daily Precipitation Water Level Thalweg Bankfull 30-Day Rolling Precip Total 30th & 70th Percentile Sassarixa Swamp: T1 Reach 2 Recorded In-Stream Flow Events Plot Monitoring Year 3 - 2023 Sassarixa Swamp Mitigation Site DMS Project No. 100040 75 days of consecutive stream flow Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov 0 2 4 6 8 10 137 138 139 140 141 Pr e c i p i t a t i o n ( i n ) El e v a t i o n ( f t ) Monitoring Year 3 - 2023 Daily Precipitation Water Level Thalweg Bankfull 30-Day Rolling Precip Total 30th & 70th Percentile Sassarixa Swamp: T2 Recorded In-Stream Flow Events Plot Monitoring Year 3 - 2023 Sassarixa Swamp Mitigation Site DMS Project No. 100040 54 days of consecutive stream flow Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov 0 2 4 6 8 10 149 150 151 152 153 Pr e c i p i t a t i o n ( i n ) El e v a t i o n ( f t ) Monitoring Year 3 - 2023 Daily Precipitation Water Level Thalweg Bankfull 30-Day Rolling Precip Total 30th & 70th Percentile Sassarixa Swamp: T3 Reach 1 APPENDIX E. Project Timeline and Contact Info DMS Project No. 100040 DMS Project No. 100040 Table 14. Project Activity and Reporting History Sassarixa Swamp Mitigation Site Monitoring Year 3 - 2023 Activity or Deliverable Data Collection Complete Task Completion or Deliverable Submission Project Instituted NA January 2018 Mitigation Plan Approved NA November 2019 As-Built Survey Completed NA Febuary 2021 Construction (Grading) Completed NA January 2021 Planting Completed NA March 2021 March 2023 Vegetation Survey September 2023 December 2022 Easement Encroachment December 2021 April 2021 Supplemental Planting February 2022 Invasive Species Treatment May 2023 Sweetgum & Loblolly Thinning May 2023 Year 5 Monitoring Stream Survey 2025 December 2025Vegetation Survey 2025 Year 6 Monitoring December 2026 Year 7 Monitoring Stream Survey 2027 December 2027Vegetation Survey 2027 Construction Contractor Land Mechanic Designs, Inc. 126 Circle G Lane Willow Spring, NC 27592 Table 15. Project Contact Table Sassarixa Swamp Mitigation Site Monitoring Year 3 - 2023 Designer Angela Allen, PE Wildlands Engineering, Inc. 312 West Millbrook Road, Suite 225 Raleigh, NC 27609 919.851.9986 Monitoring, POC Jason Lorch 919.851.9986 Monitoring Performers Wildlands Engineering, Inc. July 2021 September 2021 Stream Survey March 2022 Year 1 Monitoring Stream Survey July 2021 Vegetation Survey September 2021 Baseline Monitoring Document (Year 0) In-Stream Vegetation Treatment Stream Survey January 2021 Vegetation Survey March 2021 December 2024 Instaled XS 11 May 2023 Year 2 Monitoring September 2022 March - July 2022Invasive Species Treatment Vegetation Survey Year 3 Monitoring Supplemental Planting February 2023 Year 4 Monitoring Sediment Removal Along T2 June 2023 December 2023 Stream Survey APPENDIX F. Additional Documentation   Wildlands Engineering, Inc.    page 1  Sassarixa Swamp Mitigation Site MEETING MINUTES MEETING:  MY2 IRT Site Visit        Sassarixa Swamp Mitigation Site        Neuse River Basin 03020201; Johnston County, NC        NCDMS Project No. 100040        USACE ID: SAW‐2018‐00432        NCDEQ Contract No. 7425               DATE:    On‐site Meeting: Thursday, May 18, 2023      Meeting Notes Distributed: Friday, May 19, 2023      Attendees  Kim Browning, USACE  Casey Haywood, USACE  Jeremiah Dow, NC Division of Mitigation Services  Emily Dunnigan, NC Division of Mitigation Services  Angela Allen, Wildlands Engineering  Carolyn Lanza, Wildlands Engineering   Andrew Radecki, Wildlands Engineering    Meeting Notes   T2  o The upper third of T2 has sediment accumulated in the channel due to erosion from the valely  side slopes during construction. The IRT is concerned this segment will eventually trend towards  a linear wetland. Wildlands will install one riffle cross‐section along the upper third of T2 to  show signs of stream stability. After the cross‐section is installed and surveyed, Wildlands will  remove the instream vegetation and sediment deposition from the erosion and then continue to  monitor the cross‐section in subsequent monitoring years. Wildlands will also plant several  container trees in the current bare areas around the BMP to prevent further erosion.   o The IRT gave suggestions that in future areas where rock is utilized to stabilize an erosive slope  that it’s preferable that rock be more embedded into the ground.   o The IRT is not concerned with flow along T2 and a flow gauge is not needed in the upper third of  the stream.    T3  o Wildlands will manually repair the one log sill that was piping.   o Overall, the IRT was happy with the stability of T3.     Vegetation    Wildlands Engineering, Inc.    page 2  Sassarixa Swamp Mitigation Site  o Overall, the IRT was happy with the vegetation being established across the Site. The IRT would  like Wildlands to be mindful of the area surrounding Vegetation Plot 2, since that was the only  plot not meeting MY3 success criteria.