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HomeMy WebLinkAbout20141149 Ver 9_Year 2 Monitoring Report Final_2019_20200317ID#* 20141149 Version* 9 Select Reviewer:* Katie Merritt Initial Review Completed Date 03/18/2020 Mitigation Project Submittal - 3/17/2020 Is this a Prospectus, Technical Proposal or a New Site?* r Yes r No Type of Mitigation Project:* r Stream r Wetlands W Buffer V Nutrient Offset (Select all that apply) Project Contact Information Contact Name:* Raymond Holz Project Information .................................................................................................................................................................. ID#:* 20141149 Existing IDr Project Type: r DMS r Mitigation Bank Project Name: Benton Branch County: Caswell Document Information Email Address:* rholz@restorationsystems.com Version: *9 Existing Version Mitigation Document Type:* Mitigation Monitoring Report File Upload: Final Benton Branch Buffer-NutOff 2019MY2 DWR 23.47MB 20141149 v9_.pdf Rease upload only one RDFof the corrplete file that needs to be subrritted... Signature Print Name:* Raymond Holz Signature:* Restoration Systems, LLC 1101 Haynes St. Suite 211 Raleigh, North Carolina Ph: (919) 755-9490 Fx: (919) 755-9492 1101 Haynes St., Suite 211 • Raleigh, NC 27604 • www.restorationsystems.com • Ph 919.755.9490 • Fx 919.755.9492 March 17, 2020 Attn: Ms. Katie Merritt NC Department of Environment and Natural Resources Division of Water Resources - Wetland and Stormwater Branch 1650 Mail Service Center Raleigh, NC 27699-1650 Subject: Benton Branch Yr. 2 (2019) Monitoring Report Comment Reponses – DWR 20141149 v9 Katie - Below are the responses from Restoration Systems to all comments received on the Draft Benton Branch buffer and nutrient offset monitoring report. DWR comments are in black, and RS responses are in blue. Please do not hesitate to reach out if you would like to discuss. Sincerely, Raymond Holz Restoration Systems Comments Received & Responses 1. No stem height data is provided. This is required for all vegetation data under 0295 and is part of the Qualitative data expected by DWR. Please provide the height data if you have it, and make sure this is included in all future monitoring reports. If you don’t have it, please justify why this data wasn’t recorded. Dataforms for planted stems are included as an Appendix F, and include data related to height and vigor. 2. 20% of plots failed. However, there is no reasoning provided as to why the plots had poor survivorship. Last year’s data suggests that plot 12 had 14 volunteer sycamores and 4 volunteer winged elms. However, all of those are gone when comparing the plot data for this report. Additionally, Plot 14 had 4 black walnut volunteers last year, and now all those are gone. Explain what may have happened for such a large amount of stems to be missing. Competition from dense herbaceous vegetation is the likely culprit for the lack of planted and volunteer stems in these plots. The following sentence was added into the 2020 Maintenance Summary section: “Herbaceous vegetation in these plots is dense and is likely the reason for the mortality of both planted and naturally recruited stems.” Furthermore, RS ran 11 temporary vegetation plots around the site in February and plans to replant in some areas. This data has been added to the end of the report as Appendix F. RS will provide a detailed report of replanted areas, including species and amounts, once the work is completed. Page 2 of 2 3. Is the data for the failed plots representative of the areas around them? Yes and no, RS ran 11 temporary vegetation plots around the site in February and plans to replant in some areas. This data has been added to the end of the report as Appendix F. 4. Based on the information provided in the report, DWR will not require a supplemental planting at this time. However, RS intends to establish 4 transects around the failed plots (3, 12- 15). Depending on the transect data you collect and provide in the 2020 monitoring report for Year 3, additional planting may be required by DWR. Updated sentence in the 2020 Maintenance Section to include the following “4 random vegetation plots in the areas surrounding Plots 3, and 12-15” 5. Bond for this site expired January 2020. Since no replanting is required at this time and no major issues were noted in the report, DWR will authorize a 20% bond reduction in the current bond amount for the Benton Branch site. However, in order to receive bond reduction approvals in the future, DWR will require the height data be submitted in the report for all planted stems in the plots. Understood. RS has requested the Yr. 3 monitoring bond and will provide an original to DWR once received. YEAR 2 (2019) MONITORING REPORT Benton Branch Bank Parcel DWR# 20141149 version 9 Pursuant to: Restoration Systems’ Phase One Haw River WS Umbrella Banking Instrument for Riparian Buffer and Nutrient Offset Mitigation Credits PREPARED BY: RESTORATION SYSTEMS, LLC 1101 HAYNES STREET, SUITE 211 RALEIGH, NORTH CAROLINA 27604 AND AXIOM ENVIRONMENTAL, INC. 218 SNOW AVENUE RALEIGH, NORTH CAROLINA 27603 February 2019 Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Executive Summary page i Phase One Haw River WS Umbrella Bank Restoration Systems, LLC EXECUTIVE SUMMARY Restoration Systems, LLC (RS) established the Benton Branch Bank Parcel (Parcel), as part of the RS’ Phase One Haw River WS Umbrella Banking Instrument (Banking Instrument) signed October 25th, 2017 between RS, and the North Carolina Division of Water Resources (DWR). Per the Jordan Lake Water supply Nutrient Strategy, Consolidated Mitigation Rule, and Nutrient Offset Payments (15A NCAC 02B .0267, 15A NCAC 02B .0268, 15A NCAC 02B .0295, & 15A NCAC 02B .0240), this Parcel is designed to provide riparian buffer and nutrient offset mitigation credits for unavoidable impacts due to development within the Haw River Sub-watershed of Jordan Lake in the Cape Fear River Basin. Supporting figures are included in Appendix B. The Parcel was evaluated on January 16th, 2015 by Sue Homewood of DWR. Ms. Homewood’s evaluation was part of an inter-agency review, including the US Army Corps of Engineers, to determine if stream features located within the site are applicable to provide compensatory stream mitigation under Restoration Systems’ Cape Fear 02 Phase One Umbrella Banking Instrument, (Benton Branch USACE Action ID SAW-2015-01701). Riparian areas adjacent to features within the parcel providing compensatory mitigation for stream impacts were restored and provide riparian buffer mitigation and nutrient off-set credit. The Parcel was planned and designed according to the Banking Instrument with DWR, 15A NCAC 02B .0240, and the Consolidated Mitigation Rule 15A NCAC 02B.0295, which became effective on November 1, 2015. The Parcel was designed in concurrence with the Benton Branch Stream and Wetland Mitigation Bank (SAW# 2015-01701). The mitigation plan for the Benton Branch Stream and Wetland Mitigation Bank along with the Stream and Wetland Umbrella Mitigation Banking Instrument was approved by the Interagency Review Team on July 6th, 2017. The Section 404 (Clean Water Act, 33 USC 1344) was granted by the U.S. Army Corps of Engineers on June 30th, 2017, the corresponding Section 401 Water Quality Certification was granted on June 28th, 2017 and the land quality letter of approval was granted June 20th, 2017. Project construction and planting was completed between February 14 and March 14th, 2018, with baseline monitoring conduction between mid-and late March 2018. Benton Branch Nutrient Offset and Riparian Buffer Bank, the Parcel involved restoring and enhancing riparian buffers and other riparian areas adjacent to mitigated streams onsite in order to help reduce non-point source contaminant discharges to downstream waters in the Haw River sub-watershed of Jordan Lake. All riparian areas were assessed by DWR during an onsite visit to determine viability for buffer mitigation and nutrient offset. Approximately 33.14 acres will be protected with a permanent conservation easement. Of those 33.14 acres, 10.45 acres will be restored for Jordan riparian buffer credit, 0.08 acre will be restored for nutrient offset credit, 9.40 acres will be enhanced by the removal of cattle from the streams and riparian areas for Jordan riparian buffer credit, and 5.005 acres will be preserved for Jordan riparian buffer credit. In general, riparian restoration/enhancement area widths on streams will extend out to a maximum of 100 feet from the top of bank with a minimum width of 20 from top of banks. Riparian buffer enhancement and preservation credits generated on this Bank Parcel are allowed pursuant to 15A NCAC 02B .0295 (o). Neither the enhancement credits nor the preservation credits can be used to generate nutrient offset credits. Additionally, no riparian restoration areas that are less than 50 feet wide from Top of Banks can be used to generate nutrient offset credit, and no riparian restoration areas that are less than 20 feet wide from Top of Banks can be used to generate riparian buffer credit. Therefore, the maximum acreage of riparian restoration on this site that is able to be converted into nutrient offset credits if needed by RS, is 10.44 acres. Figure 3 (Appendix B) shows the Credit Determination Map and Section 2.0 provides details of the mitigation determination on the Bank Parcel. Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Executive Summary page ii Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Year 2 (2019) vegetation sampling occurred on October 1, 2019. Stem density across the Parcel was above the required average density with 447 planted tree stems per acre (excluding livestakes) surviving in year 2 (2019). Each individual plot exceeded success criteria with the exception of Plots 3,4,9 and 13-15. Plot 13 contained no live woody stems due to poor soil conditions and an extremely dense herbaceous layer. The herbaceous layer consists of abnormally dense knotweed (Polygonum sp.), Japanese stiltgrass (Microstegium vimineum), and ragweed (Ambrosia sp.). Restoration Systems conducted a Site review of the Benton Branch Stream and Wetland Restoration project on 11/5/19 with USACE representative Sam Dailey with no outstanding issues. 2019 Maintenance Summary; Lack of surviving planted stems in and around the upper portions of UT-3 (Plot 13), UT-2 and UT-1 were observed during the as-built walkthrough with DWR in July of 2018. The herbaceous layer consists of abnormally dense knotweed (Polygonum sp.), Japanese stiltgrass (Microstegium vimineum), and ragweed (Ambrosia sp.). These areas were specifically treated in July of 2019 as part of the annual maintenance program (Table 7, Appendix C). Based on field observations and Yr. 1 (2018) monitoring data, RS did implement a replanting of target areas (UT-3 (Plot 13), UT-2 and UT-1) at an approximate density of 400 stems per acre. Species planted and their quantity are detailed in Table 5 of Appendix C. RS Staff performed the replant in March of 2019. Typically, RS will not replant vegetation monitoring plots so that original bare-root planting can be indecently monitored. Unfortunately, in this case, vegetation plot 13 should have received additional planting given its Year 1 monitoring results of zero planted stems per acre. Additional field observations made by RS staff in the Fall of 2019, conclude that originally and replanted stems are surviving within the target areas. RS will establish four additional random transects (5m x 20m), within the in and around those monitoring plots that did not meet success criteria this monitoring year. RS will esta blish these transects in early spring, and re-survey the transects during the typical vegetation monitoring period. 2020 Maintenance Summary; Herbaceous vegetation in plots with low planted stems, is dense and is likely the reason for the mortality of both planted and naturally recruited stems. RS will establishment 4 random vegetation plots in the areas surrounding Plots 3, and 12-15 will assist in showing a more comprehensive range of the Site and provide insight into how restoration areas adjacent to failing monitoring plots are doing. RS ran 11 temporary vegetation plots around the site in February (2020) and plans to replant in some areas. This data has been added to the end of the report as Appendix F. RS will provide a detailed report to DWR of replanted areas, including species and amounts once the work is completed. RS will continue with routine vegetation management activities in accordance with Section 4.2 (Parcel Maintenance) of the Bank Parcel Development Plan to facilitate continued success. These activities will include mechanical and chemical control of competing herbaceous vegetation in targeted areas beginning early in the 3rd year (2020). In areas of intensive treatment, a short-term nurse-crop seed mix may be planted to suppress weedy herbaceous competition. RS believes these management activities will ensure the continued survival of the planted stems as well as the establishment of natural recruits. Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Table of Contents page i Phase One Haw River WS Umbrella Bank Restoration Systems, LLC TABLE OF CONTENTS EXECUTIVE SUMMARY ........................................................................................................................... i 1.0 PROJECT GOALS, BACKGROUND, AND ATTRIBUTES ......................................................... 1 1.1 Location and Setting .............................................................................................................. 1 1.2 Project Goals and Objectives ................................................................................................. 1 2.0 MITIGATION POTENTIAL ............................................................................................................ 1 3.0 MONITORING AND MAINTENANCE PLAN .............................................................................. 3 3.1 Monitoring Protocol ............................................................................................................... 3 3.2 Parcel Maintenance ................................................................................................................ 4 4.0 REFERENCES ................................................................................................................................. 5 APPENDICES Appendix A. Background Tables Table 2. Project Activity and Reporting History Table 3. Project Contacts Table Table 4. Project Baseline Information & Attributes Appendix B. Figures Figure 1. Site Location & Service Area Figure 2. Current Conditions Plan View Figures 3 and 3A-3f. Credit Determination Figure 4. Potential Conversion of Wetland Credit to Riparian Buffer Credit Figures 5A and 5B. Credit Determination (Changes from BPDP to As-built) Figure 6. Potential Conversion of Wetland Credit to Riparian Buffer Credit Appendix C. Vegetation Data Table 5. Planted Bare Root Woody Vegetation Table 6. Total Planted Stems by Plot and Species Table 7. Herbicide Application Logs Vegetation Plot Photographs Appendix D. Delivered Credit Yield Table for Jordan Sub Watersheds Appendix E. Vegetation Monitoring Datasheets Appendix F. Additional Vegetation Survey Work (02-28-2020) Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Page 1 Phase One Haw River WS Umbrella Bank Restoration Systems, LLC 1.0 PROJECT GOALS, BACKGROUND, AND ATTRIBUTES 1.1 Location and Setting Restoration Systems, LLC has established the Benton Branch Bank Parcel (Parcel), proposed as part of the Restoration Systems’ Phase One Haw River WS Umbrella Banking Instrument (Banking Instrument) signed October 25th, 2017 between Restoration Systems, and the North Carolina Division of Water Resources (DWR). The Site encompasses 33 acres of land located on both sides of Milesville Road at the intersection of Massey Road. Prior to construction, the Site was characterized by agricultural land utilized for beef cattle production and municipal effluent disposal, with scattered disturbed forest. Located in the South Atlantic/Gulf Region approximately 12 miles north of Burlington, NC in southwest Caswell County (Figure 1, Appendix B), the Parcel is hydrologically situated within the USGS 14-digit HUC 03030002030030 of the Cape Fear River Basin and Jordan Lake’s Haw Sub-Watershed (North Carolina Division of Water Quality Subbasin Number 03-06-02). The main hydrologic features include Benton Branch, six unnamed tributaries (UT) to Benton Branch, and adjacent floodplains. Directions to the Parcel (from Burlington): • Take Holt St./NC-62 toward N. Fishe St. – 0.1 mile • Continue on Rauhut St./NC-62 – 3.2 miles • Turn left on Union Ridge Rd. – 6.0 miles • Turn left on Stoney Mountain Rd. – 2.3 miles • Stoney Mountain Rd becomes Stoney Creek Mountain Rd. – 0.9 mile • Stoney Creek Mountain Rd. becomes Milesville Rd. – 1.4 miles • Turn left on Massey Rd. Parcel Coordinates: 36.278744, -79.419371 1.2 Project Goals and Objectives According to the Final Cape Fear River Basin Restoration Priorities (NCEEP 2009), this watershed should be targeted for restoration to protect the nutrient-sensitive waters that ultimately drain into the nutrient- sensitive water supply of Jordan Lake. Overall, the purposes of the Benton Branch Buffer and Nutrient Offset Bank is to restore, enhance, and preserve riparian buffers and other riparian areas adjacent to mitigated streams onsite. The riparian restoration and enhancement work will result in improved water quality within the Parcel and the downstream watershed. The Parcel is located in a region of the state dominated by agriculture and livestock; restoration of the riparian buffer is expected to result in immediate water quality benefits within the vicinity of the Parcel through the removal of livestock access to Parcel streams. Primary goals focus on 1) improving water quality, 2) enhancing flood attenuation and hydrology, 3) improving aquatic resources, and 4) restoring riparian habitat. Proposed mitigation activities will provide floodplain connectivity, floodplain resistance, stream stability, sediment transport, surface and subsurface storage, and retention, in-stream habitat, riparian habitat and structure, thermal regulation, floodplain biogeochemical processing, and pollutant filtration as well as remove sources of pollutants. 2.0 MITIGATION POTENTIAL The Benton Branch Bank will provide Jordan buffer mitigation credits and nutrient offset mitigation credits for development impacts within the Haw River Sub-watershed of Jordan Lake (Figures 5-6, Appendix B). The width of the credit generation areas begins at the most landward limit of the top of bank or t he rooted Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Page 2 Phase One Haw River WS Umbrella Bank Restoration Systems, LLC herbaceous vegetation and extends landward a maximum distance of 200 feet where Restoration Systems was able to secure an easement. No buffer mitigation credit generation areas are less than 20 feet in width and no nutrient offset credit generating areas are less than 50 feet from TOB. Buffer Mitigation credits generated from riparian restoration in non-forested pasture areas on this Bank Parcel with a minimum width of 50 feet from TOB, can be converted and transferred from Riparian Buffer Credits to Nutrient Offset Credits and from Nutrient Offset Credit to Riparian Buffer Credits upon written approval from DWR. A maximum of 10.44 acres of riparian restoration on this site is able to be converted and transferred from Riparian Buffer Credits to Nutrient Offset Credits and from Nutrient Offset Credit back to Riparian Buffer Credits upon approval. The Sponsor must submit a written request and receive written approval from DWR prior to any credit conversions and transfers to the buffer and nutrient credit ledgers. All delivery factors shall be applied to nutrient offset credits before requesting a conversion. According to the nutrient reduction goals for the Haw River arm of Jordan Lake, the generated nitrogen credits per acre in the Haw Sub-watershed for riparian restoration on agriculture land is 2249.36 pounds and the generated phosphorus credit per acre is 143.81 pounds. The delivery factors applied to this parcel are 25 percent for nitrogen and 8 percent for phosphorus (Appendix D). Delivered credits are calculated by applying the delivery factors and the acreage of riparian restoration to the generated credits per acre stated above. Proposed areas for Jordan riparian buffer and nutrient offset (Nitrogen and Phosphorus) credits for the Benton Bank Parcel are summarized in Table 1 and Figures 5-6 (Appendix B). Table 1. Jordan Lake: Haw River Sub-Watershed Credit Determination Table 14 Digit Watershed ID: 03030002030030 Riparian Buffer Mitigation Units *Buffer Width Credit Type Total Area Mitigation Ratio Percentage of Full Credit Mitigation Units TOB-29 ft Restoration (located on the right bank of the upper reach of Benton Branch [Figure 5A, Appendix B]) 261.40 ft2 (0.006 ac) 1:1 75% 196.05 ft2 (0.004 ac) TOB-100 ft Restoration 454,860.87 ft2 (10.44 ac) 1:1 100% 454,860.87 ft2 (10.44 ac) TOB-100 ft Enhancement via Cattle Exclusion (15A NCAC 02B .0295 (o)(6) 406,754.51 ft2 (9.33 ac) 2:1 100% 203,377.25 ft2 (4.66 ac) 101-200 ft Enhancement via Cattle Exclusion (15A NCAC 02B .0295 (o)(6) 3,385.53 ft2 (0.07 ac) 2:1 33% 558.61 ft2 (0.01 ac) TOB-100 ft Preservation (Rural Subject Streams) 218,084.72 ft2 (5.00 ac) 10:1 100% 21,808.47 ft2 (0.50 ac) TOB-29 ft Preservation (Rural Subject Streams) 254.87 ft2 (0.005 ac) 10:1 75% 19.11 ft2 (0.0004 ac) Total Riparian Buffer Mitigation Units 680,820.36 ft2 (15.62 ac) Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Page 3 Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Table 1. Jordan Lake: Haw River Sub-Watershed Credit Determination Table (continued) Nutrient Offset Credits **Buffer Width Credit Type Mitigation Type Total Acreage Generated Credits per Acre Generated Credits Delivery Factor Delivered Credits 101-200 ft Nitrogen Restoration 0.08 2249.36 179.95 25% 44.99 101-200 ft Phosphorus Restoration 0.08 143.81 11.50 8% 0.92 * TOB-20 ft = Buffer is less than 20 ft from the TOB and therefore qualifies for no credit. TOB-29 ft = Buffer width is contiguous from TOB, is a minimum of 20 ft from the TOB and a maximum of 29 ft from the TOB and qualifies for 75% credit. TOB-100 ft = Buffer width is contiguous from TOB, is a minimum of 29 ft f rom the TOB and a maximum of 100 ft from the TOB and qualifies for 100% credit. 101-200’ = Buffer width is contiguous from TOB, is a minimum of 101 ft from the TOB and a maximum of 200 ft from the TOB, and qualifies for 33% credit. **Buffer mitigation credits are sought from top of bank to 100 feet. Beyond buffer credit generating areas, RS is proposing nutrient offset credits out to a maximum of 200 feet for a contiguous riparian restoration from top of bank to 200 feet where possible. The Sponsor will maintain 4 credit ledgers for the Parcel under the Banking Instrument and BPDP: (1) for buffer restoration mitigation credits in both square feet and acres, (1) for buffer enhancement mitigation credits in square feet and acres, (1) accounting for nitrogen offset credits in pounds and acres, and (1) accounting for phosphorus offset credits in pounds and acres. The Sponsor may elect to use riparian areas for either buffer mitigation credit or wetland mitigation credit, but not both. The Sponsor must submit a written request and receive written approval from DWR prior to any credit conversions and transfers to the buffer credit ledger. As part of that request, the Sponsor must provide DWR with a written acceptance letter from the USACE, accompanied by suppo rting documents, for any wetlands that they want removed from the wetland mitigation bank. Only riparian areas that fail to qualify to generate wetland credit may be viable for generating riparian buffer credit. Figure 3 (Appendix B) depicts riparian areas that could potentially generate riparian buffer credit if they don't qualify to generate wetland mitigation credits, and Figure 5 (Appendix B) depicts the potential conversion of failed wetland mitigation credits to riparian buffer credits. Any areas proposed for buffer mitigation credit must meet the performance standards detailed in 15A NCAC 02B .0295. 3.0 MONITORING AND MAINTENANCE PLAN 3.1 Monitoring Protocol Restoration monitoring procedures for riparian vegetation will include periodic visual inspection and annual plant survival and species diversity survey reports. Quantitative sampling of vegetation will be performed as outlined in the CVS Level 1-2 Protocol for Recording Vegetation, Version 4.2 (Lee et al. 2008). Photos will be taken from all photo points each monitoring year and provided in the annual reports. All planted stems in the plots will be marked with flagging tape and recorded. Detailed qualitative and quantitative monitoring is proposed for vegetated riparian areas; marsh treatment areas will be visually inspected periodically and reported qualitatively within the annual monitor report, which will include photographic record of the Parcel’s assets. Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Page 4 Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Monitoring of the restoration efforts will be performed for five years or until success criteria are fulfilled. Restoration Systems shall submit an annual monitoring report to DWR, no later than December 31st of each year. Quantitative monitoring includes measurements of 20-10x10 meter, permanent vegetation plots (2.0% of riparian buffer mitigation and nutrient offset credit areas). Plots were randomly placed throughout the planted riparian areas and are representative of credit generating areas. Sampling of vegetation will be performed in October of each year; monitoring data can be found in Appendix C. During the first year, vegetation will received a cursory, visual evaluation on a periodic basis to ascertain the degree of overtopping of planted elements by nuisance species. Success criteria within the riparian buffer and nutrient offset restoration areas will be based on the survival of planted species at a density of 260 stems per acre after five years of monitoring. A minimum of four native, hardwood tree and shrub species must be present, with no one species representing greater than 50% of the stems. In addition, appropriate volunteer stems of native hardwood tree and shrub species may be included to meet the final performance standard of 260 stems per acre upon DWR approval. A visual assessment of the cattle exclusion and preservation areas within the conservation easement will also be performed each year to confirm: • Fencing is in good condition throughout the site; • No cattle access within the conservation easement area; • No encroachment has occurred; • Diffuse flow is being maintained in the conservations easement area; and • There has not been any cutting, clearing, filling, grading, or similar activities that would negatively affect the functioning of the buffer. 3.2 Parcel Maintenance 2019 Maintenance Summary; Lack of surviving planted stems in and around the upper portions of UT-3 (Plot 13), UT-2 and UT-1 were observed during the as-built walkthrough with DWR in July of 2018. The herbaceous layer consists of abnormally dense knotweed (Polygonum sp.), Japanese stiltgrass (Microstegium vimineum), and ragweed (Ambrosia sp.). These areas were specifically treated in July of 2019 as part of the annual maintenance program (Table 7, Appendix C). Based on field observations and Yr. 1 (2018) monitoring data, RS did implement a replanting of target areas (UT-3 (Plot 13), UT-2 and UT-1) at an approximate density of 400 stems per acre. Species planted and their quantity are detailed in Table 5 of Appendix C. RS Staff performed the replant in March of 2019. Typically, RS will not replant vegetation monitoring plots so that original bare-root planting can be indecently monitored. Unfortunately, in this case, vegetation plot 13 should have received additional planting given its Year 1 monitoring results of zero planted stems per acre. Additional field observations made by RS staff in the Fall of 2019, conclude that originally and replanted stems are surviving within the target areas. RS will establish four additional random transects (5m x 20m), within the in and around those monitoring plots that did not meet success criteria this monitoring year. RS will establish these transects in early spring, and re-survey the transects during the typical vegetation monitoring period. 2020 Maintenance Summary; Herbaceous vegetation in plots with low planted stems, is dense and is likely the reason for the mortality of both planted and naturally recruited stems. RS will establishment 4 random vegetation plots in the areas surrounding Plots 3, and 12-15 will assist in showing a more comprehensive range of the Site and provide insight into how restoration areas adjacent to failing monitoring plots are doing. Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Page 5 Phase One Haw River WS Umbrella Bank Restoration Systems, LLC RS ran 11 temporary vegetation plots around the site in February (2020) and plans to replant in some areas. This data has been added to the end of the report as Appendix F. RS will provide a detailed report to DWR of replanted areas, including species and amounts once the work is completed. RS will continue with routine vegetation management activities in accordance with Section 4.2 (Parcel Maintenance) of the Bank Parcel Development Plan to facilitate continued success. These activities will include mechanical and chemical control of competing herbaceous vegetation in targeted areas beginning early in the 3rd year (2020). In areas of intensive treatment, a short-term nurse-crop seed mix may be planted to suppress weedy herbaceous competition. RS believes these management activities will ensure the continued survival of the planted stems as well as the establishment of natural recruits. 4.0 REFERENCES Griffith, G.E., J.M. Omernik, J.A. Comstock, M.P. Schafale, W.H. McNab, D.R. Lenat, T.F. MacPherson, J.B. Glover, and V.B. Shelbourne. 2002. Ecoregions of North Carolina and South Carolina. U.S. Geological Survey, Reston, Virginia. Jordan Lake Water Supply Watershed Buffer Rules 15A NCAC 02B .0267, 15A NCAC 02B .0268, and 15A NCAC 02B .0295 Lee, M.T., R.K. Peet, S.D. Roberts, and T.R. Wentworth. 2008. CVS-EEP Protocol for Recording Vegetation, Level 1-2 Plot Version 4.2. Ecosystem Enhancement Program, North Carolina Department of Environment and Natural Resources. North Carolina Division of Water Quality (NCDWQ). 2005. Cape Fear River Basinwide Water Quality Plan. Available: http://portal.ncdenr.org/c/document_library/get_file?uuid=2eddbd59-b382-4b58- 97ed-c4049bf4e8e4&groupId=38364. North Carolina Department of Environment and Natural Resources, Raleigh, North Carolina. North Carolina Ecosystem Enhancement Program (NCEEP 2009). Cape Fear River Basin Restoration Priorities 2009 (online). Available: http://portal.ncdenr.org/c/document_library/get_file?uuid= 864e82e8-725c-415e-8ed9-c72dfcb55012&groupId=60329 Schafale, M.P. and A.S. Weakley. 1990. Classification of the Natural Communities of North Carolina: Third Approximation. North Carolina Natural Heritage Program, Division of Parks and Recreation, N.C. Department of Environment, Health, and Natural Resources. Raleigh, North Carolina. Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Appendix A. Background Tables Table 2. Project Activity and Reporting History Table 3. Project Contacts Table Table 4. Project Baseline Information & Attributes Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Table 2: Project Activity and Reporting History Activity / Milestone BPDP Proposed Date Actual Date BPDP Approved NA January 22, 2018 Parcel Protection via conservation easement NA December 8, 2015 Easement Assignment to Land Trust NA August 17, 2017 Cattle exclusion / fence construction NA March 2018 Planting NA March 14, 2018 As-Built Data Collection NA March 5th – 23rd, 2018 As-Built Report Submittal NA December 2018 Year 1 (2018) Monitoring October 2018 December 2018 Year 2 (2019) Monitoring October 2019 October 2019 Table 3: Project Contacts Table Firm POC & Address Bank Sponsor Restoration Systems, LLC 1101 Haynes Street, Suite 211 Raleigh, North Carolina 27604 George Howard and John Preyer 919.755.9490 Designer: Axiom Environmental, Inc. Grant Lewis; 919.215.1693 218 Snow Ave. Raleigh, NC 27603 Construction Contractor: Strader Fencing Inc Lloyd Glover; 919.422.3392 780 Landmark Road Willow Spring, NC 27592-7756 Planting Contractor: Carolina Silvics Mary-Margaret McKinney 252.482.8491 908 Indian Trail Road Edenton, NC 27932 Seeding Contractor: Land Mechanics, Inc. Lloyd Glover; 919.422.3392 780 Landmark Road Willow Spring, NC 27592-7756 Nursery Stock Suppliers: ArborGen 1.888.888.7158 Baseline Data Collection & Annual Monitoring Axiom Environmental, Inc. Grant Lewis; 919.215.1693 218 Snow Ave. Raleigh, NC 27603 Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Table 4: Project Baseline Information & Attributes Table Project Information Project Name Benton Branch County Caswell Project Area (acres) 33.14 Project Coordinates (latitude and longitude) Latitude: 36°16’33.3”N , Longitude: 79°25’26.3”W Project Watershed Summary Information Physiographic Province Piedmont River Basin Cape Fear USGS Hydrologic Unit 8-digit 03030002 USGS Hydrologic Unit 14-digit 03030002030030 DWQ Sub-basin 03-06-02 Project Drainage Area, Total Outfall (miles) 9.06 mi² Project Drainage Area Percentage of Impervious Area < 5% CGIA Land Use Classification Pasture and Forest Land Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Appendix B. Figures Figure 1. Site Location & Service Area Figure 2. Current Conditions Plan View Figures 3 and 3A-3f. Credit Determination Figure 4. Potential Conversion of Wetland Credit to Riparian Buffer Credit Figures 5A and 5B. Credit Determination (Changes from BPDP to As-built) Figure 6. Potential Conversion of Wetland Credit to Riparian Buffer Credit Copyright:© 20 14 DeLo rme FIGURE Dra wn by : Dat e: Sca le: Pro jec t N o.: KRJ AUG 2016 1:3500 16-017 Tit le: Pro jec t: Pre pa red fo r: Cas we ll C ou nty, NC BENTON BRANCHBANK PARCEL SITE LOCATIO NANDSERVICE AREA 1 Not es : 0 10 20 30 405Miles Legend Jor dan La ke 14 -dig it U SG S HU Cs Par cel Se rvic e A re a - Ha w R ive r S ubw at ers hed Haw R ive r S ubw at ers hed New H op e C ree k S ub wa ters he d ³ 1. Bac kground Im agery Source:DeLorme Wo rld Basem ap(20 14) ^ Bank Parcel LocationUSGS 14-digit HUC03030002030030 1587 Mas sey RoadElon, NC 27244 36.278744°N, 79.419371°W 3 6 2 1 11 15 12 25 21 22 13 24 16 10 23 17 19 14 18 20 NCCGIA FIGURE Dra wn by : Dat e: Sca le: Pro jec t N o.: KRJ APR 2018 1:4700 16-017 Tit le: Pro jec t: Pre pa red for : Caswell County, NC BEN TON BRANCHBANKPARCEL CURRENTCONDITIONSPLAN VIEW 2 ³ Legend Bento n Branc h Eas ement = 3 3.1 2 ac Stream Cha nnel CVS Plots 0 500 1,000 1,500 2,000250FeetBentonBranchUT-5 UT-4UT-4AU T-4 BUT-1UT-2U T - 3 UT-2B UT-6UT-5A 632111151225212213241610231719141820Milesville RdMassey RdNCCGIAFIGUREDrawn by:Date:Scale:Project No.:KRJ/CLFNOV 20181:500016-017Title:Project:Prepared for:Caswell County, NCBENTON BRANCHBANK PARCELCREDITDETERMINATION3Notes:01,0002,000500FeetLegendConservation Easement = 33.14 acStream Channel = 3.41 acRiparian Buffer Restoration (TOB-100 ft) = 10.44 ac (454,860.87 sq ft)Riparian Buffer Restoration (TOB-29 ft) = 0.006 ac (261.40 sq ft)Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) = 9.33 ac (406,754.51 sq ft)Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) = 0.07 ac (3,385.53 sq ft)Riparian Buffer Preservation on Rural Subject Stream (TOB-29 ft) = 0.005 ac (254.87 sq ft)Riparian Buffer Preservation on Rural Subject Stream (TOB-100 ft) = 5.00 ac (218,084.72 sq ft)Nutrient Offset Credit Area (101-200 ft) = 0.08 ac (3,600.73 sq ft)Wetland Mitigation Credit Area = 4.56 acConstructed BMP Footprint (no credit) = 0.02 acCVS PlotsPreviously Fenced Area (fencing removed)NCDOT Roads³1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council)UT-6NOTE: No riparian buffer credit isgiven in areas with buffer width of lessthan 20 ft. Additionally, no nutrientoffset credit is given in areas withbuffer width less than 50 ft.NOTE ABOUT BUFFER WIDTHS:TOB-20 ft = Buffer is less than 20 ft from the TOB andtherefore qualifies for no credit.TOB-29 ft = Buffer width is contiguous from TOB, is aminimum of 20 ft from the TOB and a maximum of 29 ftfrom the TOB, and qualifies for 75% credit.TOB-100 ft = Buffer width is contiguous from TOB, is aminimum of 29 ft from the TOB and a maximum of 100 ftfrom the TOB, and qualifies for 100% credit.101-200’ = Buffer width is contiguous from TOB, is aminimum of 101 ft from the TOB and a maximum of 200 ftfrom the TOB, and qualifies for 33% credit.UT-4BUT-4AFigure 3FFigure 3EFigure 3DFigure 3AFigure 3BFigure 3CBenton BranchUT-5UT-4UT-1UT-2UT-3UT-2B 19 18 Milesville RdMassey Rd NCCGIA FIGURE Drawn by: Date: Scale: Project No.: KRJ/CLF NOV 2018 1:1200 16-017 Title: Project: Prepared for: Caswell County, NC BENT ON BRANCHBANK PARCEL CREDITDET ERMINAT ION 3A Notes: 0 200 400100Feet Legen d Conservation Easement = 33.14 ac Stream Channel = 3.41 ac Riparian Buffer Restoration (TOB-100 ft) = 10.44 ac (454,860.87 sq ft) Riparian Buffer Restoration (TOB-29 ft) = 0.006 ac (261.40 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) = 9.33 ac (406,754.51 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) = 0.07 ac (3,385.53 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-100 ft) = 5.00 ac (218,084.72 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-29 ft) = 0.005 ac (254.87 sq ft) Nutrient Offset Credit Area (101-200 ft) = 0.08 ac (3,600.73 sq ft) Wetland Mitigation Credit Area = 4.56 ac 50 feet from TOB 100 feet from TOB 200 feet from TOB Constructed BMP Footprint (no credit) = 0.02 ac CVS Plots Previously Fenced Area (fencing removed) NCDOT Roads ³ 1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council) NOT E: No riparian buffer credit isgiven in areas w ith buffer w idth of lessthan 20 ft. Addition ally, n o n utrien toffset credit is given in areas w ithbuffer width less than 50 ft. NOT E ABOUT BUFFER WIDT HS:T OB-20 ft = Buffer is less than 20 ft from the T OB an dtherefore qualifies for n o credit.T OB-29 ft = Buffer width is con tiguous from T OB, is am in im um of 20 ft from the T OB an d a m axim um of 29 ftfrom the T OB, an d qualifies for 75% credit.T OB-100 ft = Buffer w idth is con tiguous from T OB, is am in im um of 29 ft from the T OB an d a m axim um of 100 ftfrom the T OB, an d qualifies for 100% credit.101-200’ = Buffer w idth is con tiguous from T OB, is am in im um of 101 ft from the T OB an d a m axim um of 200 ftfrom the T OB, an d qualifies for 33% credit. Ben ton Bran ch No credit generated bybuffer less than 20 ft. 22 20 Milesville RdNCCGIA FIGURE Drawn by: Date: Scale: Project No.: KRJ/CLF NOV 2018 1:1200 16-017 Title: Project: Prepared for: Caswell County, NC BENT ON BRANCHBANK PARCEL CREDITDET ERMINAT ION Notes: 0 200 400100Feet Legen d Conservation Easement = 33.14 ac Stream Channel = 3.41 ac Riparian Buffer Restoration (TOB-100 ft) = 10.44 ac (454,860.87 sq ft) Riparian Buffer Restoration (TOB-29 ft) = 0.006 ac (261.40 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) = 9.33 ac (406,754.51 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) = 0.07 ac (3,385.53 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-100 ft) = 5.00 ac (218,084.72 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-29 ft) = 0.005 ac (254.87 sq ft) Nutrient Offset Credit Area (101-200 ft) = 0.08 ac (3,600.73 sq ft) Wetland Mitigation Credit Area = 4.56 ac 50 feet from TOB 100 feet from TOB 200 feet from TOB Constructed BMP Footprint (no credit) = 0.02 ac CVS Plots Previously Fenced Area (fencing removed) NCDOT Roads ³ 1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council) NOT E: No riparian buffer credit isgiven in areas w ith buffer w idth of lessthan 20 ft. Addition ally, n o n utrien toffset credit is given in areas w ithbuffer width less than 50 ft. NOT E ABOUT BUFFER WIDT HS:T OB-20 ft = Buffer is less than 20 ft from the T OB an dtherefore qualifies for n o credit.T OB-29 ft = Buffer width is con tiguous from T OB, is am in im um of 20 ft from the T OB an d a m axim um of 29 ftfrom the T OB, an d qualifies for 75% credit.T OB-100 ft = Buffer w idth is con tiguous from T OB, is am in im um of 29 ft from the T OB an d a m axim um of 100 ftfrom the T OB, an d qualifies for 100% credit.101-200’ = Buffer w idth is con tiguous from T OB, is am in im um of 101 ft from the T OB an d a m axim um of 200 ftfrom the T OB, an d qualifies for 33% credit. Ben ton Bran ch UT -5 UT -4 No credit generated bybuffer less than 20 ft. 3B 25 21 22 24 23 20 NCCGIA FIGURE Drawn by: Date: Scale: Project No.: KRJ/CLF NOV 2018 1:1200 16-017 Title: Project: Prepared for: Caswell County, NC BENT ON BRANCHBANK PARCEL CREDITDET ERMINAT ION 3C Notes: 0 200 400100Feet Legen d Conservation Easement = 33.14 ac Stream Channel = 3.41 ac Riparian Buffer Restoration (TOB-100 ft) = 10.44 ac (454,860.87 sq ft) Riparian Buffer Restoration (TOB-29 ft) = 0.006 ac (261.40 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) = 9.33 ac (406,754.51 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) = 0.07 ac (3,385.53 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-100 ft) = 5.00 ac (218,084.72 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-29 ft) = 0.005 ac (254.87 sq ft) Nutrient Offset Credit Area (101-200 ft) = 0.08 ac (3,600.73 sq ft) Wetland Mitigation Credit Area = 4.56 ac 50 feet from TOB 100 feet from TOB 200 feet from TOB CVS Plots Previously Fenced Area (fencing removed) ³ 1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council) NOT E: No riparian buffer credit isgiven in areas w ith buffer w idth of lessthan 20 ft. Addition ally, n o n utrien toffset credit is given in areas w ithbuffer width less than 50 ft. NOT E ABOUT BUFFER WIDT HS:T OB-20 ft = Buffer is less than 20 ft from the T OB an dtherefore qualifies for n o credit.T OB-29 ft = Buffer width is con tiguous from T OB, is am in im um of 20 ft from the T OB an d a m axim um of 29 ftfrom the T OB, an d qualifies for 75% credit.T OB-100 ft = Buffer w idth is con tiguous from T OB, is am in im um of 29 ft from the T OB an d a m axim um of 100 ftfrom the T OB, an d qualifies for 100% credit.101-200’ = Buffer w idth is con tiguous from T OB, is am in im um of 101 ft from the T OB an d a m axim um of 200 ftfrom the T OB, an d qualifies for 33% credit. UT -5 UT -4 UT -4A UT -4B This area was previously fenced andlivestock had no access; therefore, nocredit is generated 101-200 ft from TOB. 6 311 12 13 NCCGIA FIGURE Drawn by: Date: Scale: Project No.: KRJ/CLF NOV 2018 1:1200 16-017 Title: Project: Prepared for: Caswell County, NC BENT ON BRANCHBANK PARCEL CREDITDET ERMINAT ION Notes: 0 200 400100Feet Legen d Conservation Easement = 33.14 ac Stream Channel = 3.41 ac Riparian Buffer Restoration (TOB-100 ft) = 10.44 ac (454,860.87 sq ft) Riparian Buffer Restoration (TOB-29 ft) = 0.006 ac (261.40 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) = 9.33 ac (406,754.51 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) = 0.07 ac (3,385.53 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-100 ft) = 5.00 ac (218,084.72 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-29 ft) = 0.005 ac (254.87 sq ft) Nutrient Offset Credit Area (101-200 ft) = 0.08 ac (3,600.73 sq ft) Wetland Mitigation Credit Area = 4.56 ac 50 feet from TOB 100 feet from TOB 200 feet from TOB Constructed BMP Footprint (no credit) = 0.02 ac CVS Plots Previously Fenced Area (fencing removed) ³ 1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council) NOT E: No riparian buffer credit isgiven in areas w ith buffer w idth of lessthan 20 ft. Addition ally, n o n utrien toffset credit is given in areas w ithbuffer width less than 50 ft. NOT E ABOUT BUFFER WIDT HS:T OB-20 ft = Buffer is less than 20 ft from the T OB an dtherefore qualifies for n o credit.T OB-29 ft = Buffer width is con tiguous from T OB, is am in im um of 20 ft from the T OB an d a m axim um of 29 ftfrom the T OB, an d qualifies for 75% credit.T OB-100 ft = Buffer w idth is con tiguous from T OB, is am in im um of 29 ft from the T OB an d a m axim um of 100 ftfrom the T OB, an d qualifies for 100% credit.101-200’ = Buffer w idth is con tiguous from T OB, is am in im um of 101 ft from the T OB an d a m axim um of 200 ftfrom the T OB, an d qualifies for 33% credit. UT -1UT -2 UT -3 UT -2B 3D 3 2 1 11 12 10 NCCGIA FIGURE Drawn by: Date: Scale: Project No.: KRJ/CLF NOV 2018 1:1200 16-017 Title: Project: Prepared for: Caswell County, NC BENTON BRANCHBANK PARCEL CREDITDETERMINATION 3E Notes: 0 200 400100Feet Legen d Conservation Easement = 33.14 ac Stream Channel = 3.41 ac Riparian Buffer Restoration (TOB-100 ft) = 10.44 ac (454,860.87 sq ft) Riparian Buffer Restoration (TOB-29 ft) = 0.006 ac (261.40 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) = 9.33 ac (406,754.51 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) = 0.07 ac (3,385.53 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-100 ft) = 5.00 ac (218,084.72 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-29 ft) = 0.005 ac (254.87 sq ft) Nutrient Offset Credit Area (101-200 ft) = 0.08 ac (3,600.73 sq ft) Wetland Mitigation Credit Area = 4.56 ac 50 feet from TOB 100 feet from TOB 200 feet from TOB CVS Plots ³ 1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council) NOTE: No riparian buffer credit isgiven in areas with buffer width o f lessthan 20 ft. Additio n ally, n o n utrien to ffset credit is given in areas withbuffer width less than 50 ft. NOTE ABOU T BU FFER WIDTHS:TOB-20 ft = Buffer is less than 20 ft fro m the TOB an dtherefo re qualifies fo r n o credit.TOB-29 ft = Buffer width is co n tiguo us fro m TOB, is am in im um o f 20 ft fro m the TOB an d a m axim um o f 29 ftfro m the TOB, an d qualifies fo r 75% credit.TOB-100 ft = Buffer width is co n tiguo us fro m TOB, is am in im um o f 29 ft fro m the TOB an d a m axim um o f 100 ftfro m the TOB, an d qualifies fo r 100% credit.101-200’ = Buffer width is co n tiguo us fro m TOB, is am in im um o f 101 ft fro m the TOB an d a m axim um o f 200 ftfro m the TOB, an d qualifies fo r 33% credit. U T-1 U T-2 U T-3 U T-2B 15 16 17 14 NCCGIA FIGURE Drawn by: Date: Scale: Project No.: KRJ/CLF NOV 2018 1:1200 16-017 Title: Project: Prepared for: Caswell County, NC BENTON BRANCHBANK PARCEL CREDITDETERMINATION 3F Notes: 0 200 400100Feet Legend Conservation Easement = 33.14 ac Stream Channel = 3.41 ac Riparian Buffer Restoration (TOB-100 ft) = 10.44 ac (454,860.87 sq ft) Riparian Buffer Restoration (TOB-29 ft) = 0.006 ac (261.40 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) = 9.33 ac (406,754.51 sq ft) Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) = 0.07 ac (3,385.53 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-100 ft) = 5.00 ac (218,084.72 sq ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-29 ft) = 0.005 ac (254.87 sq ft) Nutrient Offset Credit Area (101-200 ft) = 0.08 ac (3,600.73 sq ft) Wetland Mitigation Credit Area = 4.34 ac 50 feet from TOB 100 feet from TOB 200 feet from TOB CVS Plots ³ 1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council) NOTE: No riparian buffer credit isgiven in areas with buffer width of lessthan 20 ft. Additionally, no nutrientoffset credit is given in areas withbuffer width less than 50 ft. NOTE ABOUT BUFFER WIDTHS :TOB-20 ft = Buffer is less than 20 ft from the TOB andtherefore qualifies for no credit.TOB-29 ft = Buffer width is contiguous from TOB, is am inim um of 20 ft from the TOB and a m axim um of 29 ftfrom the TOB, and qualifies for 75% credit.TOB-100 ft = Buffer width is contiguous from TOB, is am inim um of 29 ft from the TOB and a m axim um of 100 ftfrom the TOB, and qualifies for 100% credit.101-200’ = Buffer width is contiguous from TOB, is am inim um of 101 ft from the TOB and a m axim um of 200 ftfrom the TOB, and qualifies for 33% credit. UT-6 Milesville RdMassey Rd NCCGIA FIGURE Drawn by: Date: Scale: Project No.: KRJ/CLF APR 2018 1:5000 16-017 Title: Project: Prepared for: Caswell County, NC BENTON BRANCHBANK PARCEL POTENTIALCONVERS IONOF WETLANDCREDIT TO RIPARIAN BUFFERCREDIT 4 Notes: 0 1,000 2,000500Feet Legend Conservation Easement = 33.12 ac Restored Stream Channel = 3.53 ac Riparian Buffer Restoration (TOB-100 ft) Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) Riparian Buffer Preservation on Rural Subject Streams (TOB-100 ft) Nutrient Offset Credit Area (101-200 ft) Constructed BMP Footprint (no credit) = 0.02 ac NCDOT Roads 50 feet from TOB 100 feet from TOB 200 feet from TOB ³ 1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council) NOTE: Riparian areas th at fail to qualifyto generate w etland mitigation credit may beviable for generating riparian buffer crdit. Anyareas proposed for buffer mitigation credit mustmeet standards detailed in 15A NCAC 0213.0295. UT-4 Benton Branch UT-4A UT-4B UT-5 UT-2 UT-1 UT-3 UT-6 UT-2B NOTE ABOUT BUFFER WIDTHS :TOB-20 ft = Buffer is less th an 20 ft from th e TOB andth erefore qualifies for no credit.TOB-29 ft = Buffer width is contiguous from TOB, is aminimum of 20 ft from th e TOB and a max imum of 29 ftfrom th e TOB, and qualifies for 75% credit.TOB-100 ft = Buffer w idth is contiguous from TOB, is aminimum of 29 ft from th e TOB and a max imum of 100 ftfrom th e TOB, and qualifies for 100% credit.101-200’ = Buffer w idth is contiguous from TOB, is aminimum of 101 ft from th e TOB and a max imum of 200 ftfrom th e TOB, and qualifies for 33% credit. 14 Digit Watershed ID: 03030002030030 Potential Conversion of Riparian Buffer Mitigation Units Buffer Width Credit Type Total Area Mitigation Ratio Percentage of Full Credit Mitigation Units TOB-100 ft Restoration 93,993.42 ft2 (2.16 ac) 1:1 100% 93,993.42 ft2 (2.16 ac) 101-200 ft Restoration 28,354.37 ft2 (0.65 ac) 1:1 33% 9451.46 ft2 (0.22 ac) TOB-100 ft Enhancement via Cattle Exclusion (15A NCAC 02B .0295 (o)(6) 44,955.54 ft2 (1.03 ac) 2:1 100% 22,477.77 ft2 (0.52 ac) 101-200 ft Enhancement via Cattle Exclusion (15A NCAC 02B .0295 (o)(6) 5999.15 ft2 (0.14 ac) 2:1 33% 999.86 ft2 (0.02 ac) TOB-100 ft Preservation (Rural Subject Streams) 15,837.59 ft2 (0.36 ac) 10:1 100% 1583.76 ft2 (0.04 ac) Total Potential Riparian Buffer Mitigation Units 128,506.27 ft2 (2.96 ac) NCCGIANCCGIA FIGURE Drawn by: Date: Scale: Project No.: KRJ/CLF OCT 2018 1:760 16-017 Title: Project: Prepared for: Caswell County, NC BENTON BRANCHBANK PARCEL CREDITDETERMINATION(CHANGES FROMBPDP TO AS-BUILT) 5A Notes: 0 100 20050Feet Legend Conservation Easement Restored Stream Channel Riparian Buffer Restoration (TOB-100 ft) Riparian Buffer Restoration (TOB-29 ft) Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-100 ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-29 ft) Nutrient Offset Credit Area (101-200 ft) Wetland Mitigation Credit Area 50 feet from TOB 100 feet from TOB 200 feet from TOB ³ 1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council) As-Built BPDP UT-2 UT-2 Riparian buffer and nutrient offset credit amountschanged slightly due to a shift in the easement and theaddition of wetland mitigation within the old pond beds.The easement shift was a result of the final, post-construction surveyed easement and did not result inany changes to the stream and wetland credits asproposed in the mitigation plan and constructed.Additionally, there was an oversight in the BPDP whereall riparian buffer restoration and enhancement wasgiven full credit (rather than 50%). During as-built, it wasdecided to pursue nutrient offset credit in the areas 101-200 ft where buffer vegetation was restored. NCCGIANCCGIA FIGURE Drawn by: Date: Scale: Project No.: KRJ/CLF OCT 2018 1:760 16-017 Title: Project: Prepared for: Caswell County, NC BENTON BRANCHBANK PARCEL CREDITDETERMINATION(CHANGES FROMBPDP TO AS-BUILT) 5B Notes: 0 100 20050Feet Legend Conservation Easement Restored Stream Channel Riparian Buffer Restoration (TOB-100 ft) Riparian Buffer Restoration (TOB-29 ft) Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-100 ft) Riparian Buffer Preservation on Rural Subject Stream (TOB-29 ft) Nutrient Offset Credit Area (101-200 ft) Wetland Mitigation Credit Area 50 feet from TOB 100 feet from TOB 200 feet from TOB ³ 1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council) As-Built BPDP UT-1 UT-1 Riparian buffer and nutrient offset credit amountschanged slightly due to a shift in the easement and theaddition of wetland mitigation within the old pond beds.The easement shift was a result of the final, post-construction surveyed easement and did not result inany changes to the stream and wetland credits asproposed in the mitigation plan and constructed.Additionally, there was an oversight in the BPDP whereall riparian buffer restoration and enhancement wasgiven full credit (rather than 50%). During as-built, it wasdecided to pursue nutrient offset credit in the areas 101-200 ft where buffer vegetation was restored. Milesville RdMassey Rd NCCGIA FIGURE Drawn by: Date: Scale: Project No.: KRJ/CLF APR 2018 1:5000 16-017 Title: Project: Prepared for: Caswell County, NC BENTON BRANCHBANK PARCEL POTENTIALCONVERS IONOF WETLANDCREDIT TO RIPARIAN BUFFERCREDIT 6 Notes: 0 1,000 2,000500Feet Legend Conservation Easement = 33.12 ac Restored Stream Channel = 3.53 ac Riparian Buffer Restoration (TOB-100 ft) Riparian Buffer Enhancement via Cattle Exclusion (TOB-100 ft) Riparian Buffer Enhancement via Cattle Exclusion (101-200 ft) Riparian Buffer Preservation on Rural Subject Streams (TOB-100 ft) Nutrient Offset Credit Area (101-200 ft) Constructed BMP Footprint (no credit) = 0.02 ac NCDOT Roads 50 feet from TOB 100 feet from TOB 200 feet from TOB ³ 1. Background Imagery Source:2014 aerial photographyprovided by the NC OneMapprogram (online, provided bythe NC Geographic InformationCoordination Council) NOTE: Riparian areas th at fail to qualifyto generate w etland mitigation credit may beviable for generating riparian buffer crdit. Anyareas proposed for buffer mitigation credit mustmeet standards detailed in 15A NCAC 0213.0295. UT-4 Benton Branch UT-4A UT-4B UT-5 UT-2 UT-1 UT-3 UT-6 UT-2B NOTE ABOUT BUFFER WIDTHS :TOB-20 ft = Buffer is less th an 20 ft from th e TOB andth erefore qualifies for no credit.TOB-29 ft = Buffer width is contiguous from TOB, is aminimum of 20 ft from th e TOB and a max imum of 29 ftfrom th e TOB, and qualifies for 75% credit.TOB-100 ft = Buffer w idth is contiguous from TOB, is aminimum of 29 ft from th e TOB and a max imum of 100 ftfrom th e TOB, and qualifies for 100% credit.101-200’ = Buffer w idth is contiguous from TOB, is aminimum of 101 ft from th e TOB and a max imum of 200 ftfrom th e TOB, and qualifies for 33% credit. 14 Digit Watershed ID: 03030002030030 Potential Conversion of Riparian Buffer Mitigation Units Buffer Width Credit Type Total Area Mitigation Ratio Percentage of Full Credit Mitigation Units TOB-100 ft Restoration 93,993.42 ft2 (2.16 ac) 1:1 100% 93,993.42 ft2 (2.16 ac) 101-200 ft Restoration 28,354.37 ft2 (0.65 ac) 1:1 33% 9451.46 ft2 (0.22 ac) TOB-100 ft Enhancement via Cattle Exclusion (15A NCAC 02B .0295 (o)(6) 44,955.54 ft2 (1.03 ac) 2:1 100% 22,477.77 ft2 (0.52 ac) 101-200 ft Enhancement via Cattle Exclusion (15A NCAC 02B .0295 (o)(6) 5999.15 ft2 (0.14 ac) 2:1 33% 999.86 ft2 (0.02 ac) TOB-100 ft Preservation (Rural Subject Streams) 15,837.59 ft2 (0.36 ac) 10:1 100% 1583.76 ft2 (0.04 ac) Total Potential Riparian Buffer Mitigation Units 128,506.27 ft2 (2.96 ac) Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Appendix C. Vegetation Data Table 5. Planted Woody Vegetation Table 6. Total Planted Stems by Plot and Species Table 7: 2019 Herbicide Application Log Vegetation Plot Photographs Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Table 5. Planted Bare Root Woody Vegetation Species Quantity 2019 Replant River birch (Betula nigra) 2550 500 Buttonbush (Cephalanthus occidentalis) 250 -- Eastern redbud (Cercis canadensis) 1100 -- Silky dogwood (Cornus amomum) 2325 -- Green ash (Fraxinus pennsylvanica) 3900 500 Tulip poplar (Liriodendron tulipifera) 600 -- Sycamore (Platanus occidentalis) 3800 -- Black gum (Nyssa sylvatica var. sylvatica) 2000 -- Water oak (Quercus nigra) 2800 -- Willow oak (Quercus phellos) 3000 -- Black willow (Salix nigra) 1225 -- Elderberry (Sambucus canadensis) 550 -- Persimmon (Diospyros virginiana) -- 250 Black cherry (Prunus serotine) -- 400 White oak (Quercus alba) -- 500 American elm (Ulmus americana) -- 500 TOTAL 24,100 2,650 Table 7: 2019 Herbicide Application Log Date: Herbicide\ Surfactant: Rate/Amount: Total: Target Species: Method: Applicator: 7/11/19 Roundup® Custom (glyphosate) Agri-Dex® .3% 10.8 fl oz .5% 17.25 fl oz 27 Gallons Microstegium Foliage ATV- Broadcast Joshua G Merritt (NC 026-33717) Table 6.  Total and Planted Stems by Plot and SpeciesProject Code 1500702.  Project Name: Benton BranchPnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all TBetula nigra river birch Tree 11 11 11111111888888333555Carya hickory TreeCarya glabra pignut hickory TreeCephalanthus occidentalis common buttonbush Shrub111Cercis canadensis eastern redbud Tree111222Cornus amomum silky dogwood ShrubDiospyros virginiana common persimmon TreeFraxinus pennsylvanica green ash Tree111338111 222 444111444Juglans nigra black walnut TreeLiriodendron tulipifera tuliptree Tree 1 1 1 1 1 1Nyssa sylvatica blackgum Tree14 14 14 5 5 5Platanus occidentalis American sycamore Tree666666222333Quercus oak TreeQuercus alba white oak Tree11Quercus lyrata overcup oak TreeQuercus nigra water oak Tree 1 1 1111Quercus phellos willow oak Tree111555Quercus rubra northern red oak TreeSalix nigra black willow TreeUlmus alata winged elm TreeUnknown Shrub or Tree1818181111166661717179910171718777000555444999333444555444223334222000222222222728.4 728.4 728.4 445.2 445.2 647.5 242.8 242.8 242.8 688 688 688 364.2 364.2 404.7 688 688 728.4 283.3 283.3 283.3 0 0 0 202.3 202.3 202.3 161.9 161.9 161.9 364.2 364.2 364.2Color for DensityPnoLs = Planted excluded livestakesExceeds requirements by 10% P‐all = Planted included live stakes Exceeds requirements, but by less than 10% T = All planted and natural recruits including livestakesFails to meet requirements, by less than 10% T includes natural recruitesFails to meet requirements by more than 10%1500702‐01‐0013 1500702‐01‐0014 1500702‐01‐0015 1500702‐01‐001610.0210.02Stem countScientific Name Common Name Species Type1500702‐01‐0001 1500702‐01‐0002 1500702‐01‐0003 1500702‐01‐0006 1500702‐01‐0010 1500702‐01‐0011 1500702‐01‐001210.0210.0210.0210.0210.0210.0210.02Stems per ACREsize (ACRES)Species countsize (ares)10.02Current Plot Data (MY2 2019)10.02 Table 6.  Total and Planted Stems by Plot and Species (continued)Project Code 1500702.  Project Name: Benton BranchPnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all T PnoLS P‐all TBetula nigra river birch Tree 6 6 62 2 2 45 45 45 62 62 62 84 84 84Carya hickory Tree4Carya glabra pignut hickory Tree6Cephalanthus occidentalis common buttonbush Shrub111111Cercis canadensis eastern redbud Tree 3 3 3111333444222 161616191919 111Cornus amomum silky dogwood Shrub111333555 999111111161616Diospyros virginiana common persimmon Tree1Fraxinus pennsylvanica green ash Tree 4 4 4 4 4 4111222333333333338333336414141Juglans nigra black walnut Tree6Liriodendron tulipifera tuliptree Tree222444 666Nyssa sylvatica blackgum Tree11111 1222111444 222 303030333333373737Platanus occidentalis American sycamore Tree333222 3332525252222134242424Quercus oak Tree 1 1 11 1 1 10 10 10 26 26 26Quercus alba white oak Tree 1 1 1113Quercus lyrata overcup oak Tree111Quercus nigra water oak Tree11122 2777888 111111333333282828363636434343Quercus phellos willow oak Tree11144 4111222333333 555444292929272730262626Quercus rubra northern red oak Tree 1 1 1111Salix nigra black willow Tree13Ulmus alata winged elm Tree4Unknown Shrub or Tree1 1 1 20 20 2014 14 14 11 11 11 11 11 11 16 16 16 14 14 14 14 14 14 12 12 12 11 11 11 15 15 15 221 221 228 260 260 412 324 324 32466655 5444555555666555333555131313131319111111566.6 566.6 566.6 445.2 445.2 445.2 445.2 445.2 445.2 647.5 647.5 647.5 566.6 566.6 566.6 566.6 566.6 566.6 485.6 485.6 485.6 445.2 445.2 445.2 607 607 607 447.2 447.2 461.3 526.1 526.1 833.7 655.6 655.6 656Color for DensityPnoLs = Planted excluded livestakesExceeds requirements by 10% P‐all = Planted included live stakes Exceeds requirements, but by less than 10% T = All planted and natural recruits including livestakesFails to meet requirements, by less than 10% T includes natural recruitesFails to meet requirements by more than 10%0.49Annual MeansMY1 (2018)201500702‐01‐0017 1500702‐01‐00181500702‐01‐00251500702‐01‐0019 1500702‐01‐0020 1500702‐01‐0021 1500702‐01‐0022 1500702‐01‐0023 1500702‐01‐002410.0210.0210.0210.0210.0210.02Scientific Name Common Name Species TypeStem countMY2 (2019) MY0 (2018)Stems per ACRESpecies countCurrent Plot Data (MY1 2018)200.49200.4910.0210.0210.02size (ares)size (ACRES) Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Benton Branch Year 1 Vegetation Monitoring Photographs Taken October 2019 Plot 1 Plot 2 Plot 10 Plot 6 Plot 3 Plot 11 Plot 12 Plot 13 Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Benton Branch Year 1 Vegetation Monitoring Photographs Taken October 2019 Plot 16 Plot 21 Plot 19 Plot 17 Plot 20 Plot 14 Plot 15 Plot 18 Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Benton Branch Year 1 Vegetation Monitoring Photographs Taken October 2019 Plot 22 Plot 25 Plot 24 Plot 23 Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Appendix D. Delivered Credit Yield Table for Jordan Sub Watersheds Jordan Water Supply Nutrient Strategy Delivered Credit Yield Table for Jordan Sub Watersheds Updated 12/20/2012 Page 1 of 2 Attachment B Delivered credit yields for buffer acres in Jordan small watersheds. Watershed ID Jordan Subwatershed Delivery Factors TN Credit TP Credit TN TP (lbs/30yrs) (lbs/30yrs) 03030002010010 Haw 25% 10% 562.34 14.38 03030002010020 Haw 37% 36% 832.26 51.77 03030002010030 Haw 44% 40% 989.72 57.52 03030002010040 Haw 49% 44% 1102.19 63.27 03030002010050 Haw 55% 48% 1237.15 69.03 03030002020010 Haw 15% 4% 337.40 5.75 03030002020020 Haw 22% 12% 494.86 17.26 03030002020030 Haw 48% 43% 1079.69 61.84 03030002020040 Haw 32% 33% 719.80 47.46 03030002020050 Haw 32% 32% 719.80 46.02 03030002020060 Haw 47% 42% 1057.20 60.40 03030002020070 Haw 54% 47% 1214.66 67.59 03030002030010 Haw 60% 56% 1349.62 80.53 03030002030020 Haw 44% 31% 989.72 44.58 03030002030030 Haw 25% 8% 562.34 11.50 03030002030040 Haw 42% 30% 944.73 43.14 03030002030050 Haw 64% 62% 1439.59 89.16 03030002030060 Haw 39% 19% 877.25 27.32 03030002030070 Haw 36% 18% 809.77 25.88 03030002030080 Haw 73% 64% 1642.04 92.04 03030002040010 Haw 30% 14% 674.81 20.13 03030002040020 Haw 28% 14% 629.82 20.13 03030002040030 Haw 71% 63% 1597.05 90.60 03030002040040 Haw 32% 15% 719.80 21.57 03030002040050 Haw 52% 50% 1169.67 71.90 03030002040060 Haw 54% 51% 1214.66 73.34 03030002040070 Haw 67% 60% 1507.07 86.28 03030002040080 Haw 53% 51% 1192.16 73.34 03030002040090 Haw 54% 51% 1214.66 73.34 03030002040100 Haw 75% 65% 1687.02 93.47 03030002040110 Haw 66% 60% 1484.58 86.28 03030002050010 Haw 74% 68% 1664.53 97.79 03030002050020 Haw 81% 74% 1821.98 106.42 03030002050030 Haw 42% 17% 944.73 24.45 03030002050040 Haw 80% 73% 1799.49 104.98 Jordan Water Supply Nutrient Strategy Delivered Credit Yield Table for Jordan Sub Watersheds Updated 12/20/2012 Page 2 of 2 Watershed ID Jordan Subwatershed Delivery Factors TN Credit TP Credit TN TP (lbs/30yrs) (lbs/30yrs) 03030002050050 Haw 71% 67% 1597.05 96.35 03030002050060 Haw 79% 73% 1777.00 104.98 03030002050070 Haw 78% 72% 1754.50 103.54 03030002050080 Haw 80% 73% 1799.49 104.98 03030002050090 Haw 79% 73% 1777.00 104.98 03030002050100 Haw 81% 75% 1821.98 107.85 03030002060010 Haw 81% 74% 1821.98 106.42 03030002060020 Haw 95% 97% 2136.90 139.49 03030002060030 Haw 88% 91% 1979.44 130.86 03030002060040 Haw 97% 98% 2181.88 140.93 03030002060050 Haw 92% 95% 2069.41 136.61 03030002060062 Haw 98% 99% 2204.38 142.37 03030002060070 UNH 40% 19% 867.70 27.32 03030002060080 UNH 59% 45% 1279.86 64.71 03030002060100 UNH 69% 63% 1496.79 90.60 03030002060110 UNH 61% 58% 1323.25 83.41 03030002060120 UNH 69% 63% 1496.79 90.60 03030002060140 UNH 85% 89% 1843.87 127.99 03030002060130 UNH 69% 63% 1496.79 90.60 03030002060160 LNH 85% 90% 1932.07 131.76 03030002060090* UNH 92% 94% 1995.71 135.18 03030002060090* LNH 92% 94% 2091.18 137.62 03030002060060* UNH 94% 96% 2039.10 138.05 03030002060060* LNH 94% 96% 2136.64 140.54 03030002060150* UNH 88% 91% 1908.94 130.86 03030002060150* LNH 88% 91% 2000.26 133.22 *Watershed is located in both the Upper New Hope (UNH) and Lower New Hope (LNH) Subwatersheds. Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Appendix E. Vegetation Monitoring Datasheets Plot (continued): 1500702-01-0001 Oct 2018 Data o ' THIS YEAR'S DATA map source X Y ddh Height DBH ddb Height DBH Re- Vigor* Damage* Notes ID Species char (m) (m) (mm) (cm) (cm) * (mm) (cm) (cm) sprout Vegetation Monitoring Data (VMD) Datasheet Please fill in any missing data and correct any errors. Plot 1500702-01-0001 VMD Year (1-5): ❑� Date: Taxonomic Standard: Taxonomic Standard DATE: Latitude or UTM-N: (dec.deg. or in) Longitude or UTM-E: Coordinate Accuracy (m): conk ,� Zo Icy Datum: NAD83/W 79.424005 j UTM Zone: Y157 1 X-Axis bearing (deg): Plot Dimensions: X: 10 Y Party: Kole: Ro c Jk" IP L Date last planted: New I nting date m/yy? Check box if plot was not Notes: sampled, specify reason below 101 ❑ Plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data o THIS YEAR'S DATA Map Source* X Sr Height DBH * Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m O.lm Icm* 1 cm lcm* 1 cm sprout 15800 Betula nigra ® R 1.5 0.3 Missing ❑ 15801 Betula nigra ® R 1.5 1.8 91.0 ❑ 15802 Betula nigra R 1.6 3.6 80.0 ❑ 15803 Betula nigra R 2.0 5.6 89.0 ❑ 15804 Betula nigra ® R 1.9 6.9 72.0 ❑ 15805 Betula nigra 0 R 2.9 8.0 92.0 ❑ 15806 Betula nigra Oj R 4.3 6.3 100.0 ❑ 15807 Betula nigra O R 4.2 4.8 132.0 DBH? ❑ 15808 Platanus occidentalis ® R 3.3 1.0 107.0 DBH? ❑ 15809 Betula nigra ® R 3.6 2.1 10.0 ❑ 15810 Platanus occidentalis O v 3.6 3.8 105.0 DBH? ❑ 15811 Platanus occidentalis O R 5.5 0.4 50.0 ❑ 15812 Betula. nigra ® R 5.0 2.2 91.0 ❑ 15813 Platanus occidentalis R 5.3 3.7 108.0 DBH? ❑ 15814 Fraxinus pennsylvanica R 5.6 5.2 42.0 ❑ 15815 Betula nigra ® R 5.6 6.7 78.0 ❑ 15816 Betula nigra 0 It 5.8 8.2 92.0 ❑ 15817 Platanus occidentalis O R 6.0 9.6 125.0 DBH? ❑ 15819 Betula nigra © R 8.7 5.5 92.0 ❑ 15820 Betula nigra O R 8.2 3.3 110.0 DBH? ❑ 15822 Betula nigra O R 9.3 0.2 22.0 ❑ 16462 Platanus occidentalis Q R 3.8 8.0 82.0 ❑ om"N mm =u©�� mmm Mal mmn©M� KI S WM©_� m -mm_-mwlvlwm_ # stems: 22 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: X Y Height DBH Species Name Source* (in) (in) 1 cm* 1 cm Vigor* Damage* Notes I *SOURCE: Tr-Tran tan L=Live stake B=Ball and burlap. P=Potted. Tu=Tublin R=bare Root M=Mechanics U=Unknown n- *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LPJESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. i Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 1 Ocm if>2.5m and 50cm if>4m. Printed in the CPS-EEP Entry Toot ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Please fill in any missing data and correct any errors. Plot 150 2-01- 02 VMD Year (1-5): T Date: tp / V / i 0[ Taxonomic Standard: 1nf ea�C l Taxonomic Standard DATE: Latitude or UTM-N: L36.275860 Datum: NAD83/W(dec.deg. or m) 423365 UTM Zone: Longitude or UTM-E: C rd' t Acc rac (m)• 1 X-Axis bearing (deg): 4 Date last planted: New lanting date m/yy? Check box if plot was not specity reason Detow 00 tna e u y Plot Dimensions: X: 10 Y: F 10 ❑ plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data Map Source* X Y Height DBH ID Species Name char _ 0.1m O.lm lcm* I cm 15824 Betula nigra ® R 3.9 2.3 69.0 ❑ 15825 Platanus occidentalis O R 0.6 4.1 130.0 DBH? 15826 Platanus occidentalis ® R 1.7 7.2 111.0 DBH? 15827 Platanus occidentalis O R 4.6 9.7 110.0 DBH? 15828 Liriodendron tulipifera O R 4.7 7.4 34.0 El 15829 Fraxinus pennsylvanica ® R 6.0 1.7 61.0 11 15831 Platanus occidentalis ® R 6.7 5.5 130.0 DBH? ❑ 15832 Fraxinus pennsylvanica 0 R 9.0 7.4 74.0 El 15833 Fraxinus pennsylvanica Q F, 7.7 5.7 60.0 ❑ 15834 Platanus occidentalis 0 R 8.9 5.6 49.0 El 15835 Betula nigra R 9.7 0.3 31.0 16463 Platanus occidentalis 0 2.4 4.4 88.0 ❑ THIS YEAR'S DATA Height DBH Re- Vigor* Damage* Notes 1 cm* 1 cm sprout ®mmm_� ®®® mmu amp # stems: 11 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Source* X Y Height DBH m Vigor* Damage* Notes Species Name (m) (m) *SOURCE: Tr -Transplant, L=Live stake B=J�D d burl P=Potted, Tu=Tublin R=bare Root M=Mechanica U=Unknown • 4 *VIGOR: 4=excellent, 3=good, 2=fair, AMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown I�nlikely to survive year, 0=dead, IMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if >4m. Printed in the CVSEEP Entry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Please fill in any missing data and correct any errors. Plot 1500702-01-0003 Part : Role: Date last planted: �, a�e� t` pL New lanting date m/yy? I� VMD Year (1-5): � Date: �p / 1 / - / / _ ^ Check box if plot was not Taxonomic Standard: w f p� S - t Taxonomic Standard DATE: 20 to Latitude or UTM-N: 36.276271 Datum: NAD83/W (dec.deg. or m) Longitude or UTM-E: Coordinate Accuracy (m): ` 79.423282 UTM Zone: 1 X-Axis bearing (deg): 38 reason below Plot Dimensions: X: 10 Y: 10 ❑ plot hasreverse orientation for X and Y axis (Y is 90 degrees to the right of X F-Oct 2018 Data z THIS YEAR'S DATA 0 Map Source* X Y Height DBH Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m 0.1m lcm* I cm * lcm* 1 cm sprout 15837 Quercus nigm O R 1.2 1.1 50.0 ❑ 15838 Quercus sp. ® R 1.2 3.4 10.0 ❑ 15839 Quercus sp. ® R 0.9 6.0 25.0 ❑ 15840 Quercus sp. O R 0.3 8.4 53.0 ❑ 15841 Fraxinus pennsylvanica O R 3.7 7.3 78.0 ❑ 15842 Quercus phellos O R 4.0 2.2 40.0 ❑ 15843 Cercis canadensis ® R 4.0 5.5 Missing ❑ 15844 Fraxinus pennsylvanica ® R 4.3 3.0 Missing ❑ 15845 Betula nigra 0 F. 6.5 1.6 78.0 ❑ 15846 Quercus nigra O R 6.4 3.6 Missing ❑ 15848 Betula nigm ® R 9.7 9.1 93.0 ❑ 15849 Platanus occidentalis O R 9.7 6.6 52.0 ❑ 15851 Platanus occidentalis Q R 9.7 1.7 110.0 DBH? ❑ # stems: 13 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: X Y Height DBH Species Name Source* (m) (m) 1 cm* 1 cm Vigor* Damage* Notes *SOURCE: Tr -Transplant L=Live stake, B=Ball and burlap,_P=Potted, Tu=TublinR, R=bare Root, M=Mechanically, U=Unknown P. 7 *VIGOR: 4--excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVcr, DEER, RODents, INSects, GAME, LNESTock, Other/Unknown 1 --unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CYS-EEPEntry Tool ver.1.3.0 Vegetation Monitoring Data (VMD) Datasheet Plot 1500702-01-0006 VMD Year (1-5): F Date: 0 Taxonomic Standard: Weak'�. Taxonomic Standard DATE: 2d 1 Q Latitude or UTM-N: 36.276455 Datum: NAD83/W (dec.deg. or m) Longitude or UTM-E: 79.423750 UTM Zone: 1 Coordinate Accuracy (m): 1 X-Axis bearing (deg): 50 Please fill in any missing data and correct any errors. Ya : Role: I Plot Dimensions: X: 10 Y; 10 ❑ plot has reverse orientation for X and Y axis ID Species Name Map Source* X Y char 0.1 m 0.1 m Date last planted: New lanting date m/yy? 0 Check box if plot was not Notes: sampled, specify reason below is 90 degrees to the right of X Oct 2018 Data Z THIS YEAR'S DATA 0 Height DBH * Height DBH Re- Vigor* Damage* Notes 1 cm* 1 cm 1 cm* 1 cm sprout 15882 Platanus occidentalis O K 1.3 2.1 111.0 DBH? ❑ 15883 Betula nigra O R 3.9 2.3 52.0 ❑ 15884 Cephalanthus occidentalis O R 1.7 6A 58.0 ❑ 15885 Quercus sp. P4,115 Q R 0.0 8.0 63.0 El 15886 Quercus phellos ® R 1.5 7.8 72.0 ❑ 15887 Quercus phellos ® R 0.4 9.8 15.0 ❑ 15888 Betula nigra O R 2.7 7.5 62.0 ❑ 15889 Betula nigra ® R 3.3 6.4 90.0 ❑ 15890 Platanus occidentalis O R 4.6 0.0 82.0 ❑ 15891 Betula nigra ® R 5.8 7.9 98.0 15892 Betula nigra O R 5.0 5.9 40.0 ❑ 15893 Quercus sp. )qW1tle J O R 4.9 8.9 40.0 ❑ 15894 Betula nigra O a( 4.4 7.5 62.0 ❑ 15896 Betula nigra O R 6.2 3.2 70.0 ❑ 15897 Platanus occidentalis @ R 8.2 2.3 82.0 ❑ 15899 Quercus phellos O R 9.8 8.5 52.0 ❑ 15900 Betula nigra 0 i . 8.4 8.5 Missing ❑ 15901 Betula nigra ® R 7.1 8.2 70.0 ❑ 15902 Quercus phellos R 6.4 9.3 58.0 ❑ mil■�©�� �1�1©mom. # stems: 19 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: X Y Height DBH Species Name Source* (m) (m) 1 cm* 1 cm Vigor* Damage* Notes *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1--unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE Missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CVS-EEPEntry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Please fill in any missing data and correct any errors. Plot 15 702-01-0010 VMD Year (1-5): Ifl Date: )io Taxonomic Standard: Taxonomic Standard DATE: 2 Latitude or UTM-N: 36.275605 Datum: NAD83/W (dec.deg. or m) _79.424279 j Longitude or UTM-E: UTM Zone: Coordinate Accuracy (m): I X-Axis bearing (deg): 26 Date last planted: New lanting date m/yy? 0 Check box if plot was not Notes: sampled, specify reason below Plot Dimensions: X: 10 y; 10 ElPlot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data z THIS YEAR'S DATA 5 Map Source* X Y Height DBH * Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m 0.1m lcm* 1 cm lcm* 1 cm sprout 15934 Liriodendron tulipifera O R 1.5 0.4 11.0 15935 Liriodendron tulipifera ® R 3.6 0.4 10.0 15936 Betula nigra O R 2.0 2.9 60.0 15937 Betula nigra O R 4.4 2.7 52.0 15938 Betula nigra O R 1.2 6.8 73.0 15939 Betula nigra ® k 3.0 6.7 108.0 DBH? 15940 Liriodendron tulipifera ® R 1.3 8.2 28.0 15941 Betula nigra O R 1.2 9.7 25.0 15942 Betula nigra Q R 2.9 8.7 61.0 ❑ 15944 Betula nigra O R 5.3 6.0 62.0 15945 Betula nigra O R 6.4 3.7 111.0 DBH? 15946 Betula nigra ® R 7.9 1.8 60.0 ❑ 15947 Betula nigra Q R 8.6 4.6 90.0 ❑ 15948 Betula nigra © R 5.8 9.9 81.0 ❑ ©-lml0_- =-lm,w_- VOW W lmm- # stems: 14 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* X Y Height DBH (m) (m) 1 cm* 1 cm Vigor* Damage* Notes *SOURCE: Tr-TransplantTr-Transplant L=Live stake B=Ball and burlap. P=Potte Tu--Tublinz R=bare Root M=Mechanically_U=Unknown o. 27 *VIGOR: 4=excellent, 3=good, 2--fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if >2.5m and 50cm if >4m. Printed in the CVS-EEP Entry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Plot 1500702-01-0011 VMD Year (1-5): ❑2 Date: - / / Taxonomic Standard: Taxonomic Standard DATE: o Latitude or UTM-N: 36.276309 Datum: NAD83/W (dec.deg. or m) Longitude or UTM-E:-79.424594 UTM Zone: Coordinate Accuracy (m): 1 X-Axis bearing (deg): q358 Please fill in any missing data and correct any errors. Role: Date last planted: DECIG t rL New lanting date m/yy? `- Check box if plot was not Notes: sampled, specify reason below Plot Dimensions: X: 10 Y; 10 Plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data Z THIS YEAR'S DATA 0 Map Source* X Y Height DBH y Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.lm 0.lm lcm* 1 cm °F lcm* 1 cm sprout g g 15951 Nyssa sylvatica O R 2.0 1.5 50.0 ❑ 15952 Cercis canadensis © R 1.2 4.1 50.0 ❑ 15953 Nyssa sylvatica O R 0.6 6.0 60.0 El 15954 Fraxinus pennsylvanica ® R 1.4 9.3 70.0 15955 Fraxinus pennsylvanica ® R 2.9 9.5 70.0 ❑ 15956 Nyssa sylvatica O R 4.7 8.3 63.0 ❑ 15957 Nyssa sylvatica O R 2.6 7.1 52.0 ❑ 15958 Nyssa sylvatica ® R 2.9 5.0 52.0 ❑ 15959 Nyssa sylvatica R 4.0 2.5 62.0 ❑ 15960 Nyssa sylvatica O R 6.3 0.8 58.0 15962 Nyssa sylvatica O R 6.4 6.8 60.0 ❑ 15963 Nyssa sylvatica ® R 6.9 9.1 52.0 ❑ 15964 Nyssa sylvatica ® R 9.2 10.0 40.0 El 15965 Nyssa sylvatica O R 9.9 7.9 51.0 ❑ 15966 Nyssa sylvatica @ R 7.6 4.6 53.0 ❑ 15967 Nyssa sylvatica ® R 8.5 1.9 61.0 ❑ 15968 Nyssa sylvatica R 8.0 6.8 45.0 ❑ 16467 Nyssa sylvatica ® R 0.8 0.1 62.0 ❑ uz-lw1©_- mmlmlm_m m-mm_- wa-mm_- m-mm_- WA-INIM - MINIMM� ©=Fffllvm� i i -m©_- mmumm� ®emu©mom # stems: 18 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* X Y Height DBH p (m) (m) 1 cm* 1 cm Vigor* Damage* Notes *SOURCE: Tr--Transplant,L=Live stake B=Bz 11 and burls P=Potted, Tu=Tubling, R=bare Root, M=Mechanically, U=Unknown P. 30 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CVS-EEP Entry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Plot 15QO702-01-0012 VMD Year (1-5): ❑� Date: / / Taxonomic Standard: Taxonomic Standard DATE: ap Latitude or UTM-N: 36.276457 Datum: NAD831W (dec.deg. or m) Longitude orUTM-E: 79.425015 UTM Zone: Coordinate Accuracy (m): 1 X-Axis bearing (deg): 26 Please fill in any missing data and correct any errors. Role: Date last planted: New lanting date m/yy? s Wit New box if plot was not Notes: sampled, specify reason below Plot Dimensions: X: 10 Y: 10❑ Plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data z THIS YEAR'S DATA 0 Map Source* X Y Height DBH Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m 0.1m lcm* 1 cm lcm* 1 cm sprout g g 15972 Cercis canadensis Q R 1.5 9.0 60.0 El 15973 Nyssa sylvatica ® R 3.3 8.1 57.0 El 15974 Nyssa sylvatica O R 3.4 3.7 50.0 El 15975 Nyssa sylvatica ® I: 4.0 1.2 62.0 15976 Cercis canadensis O R 5.7 2.5 45.0 El 15977 Nyssa sylvatica ® R 8.0 4.2 30.0 El 15978 Nyssa sylvatica O R 5.4 6.7 30.0 ❑ mMu©■�■� mmlwl©_- # stems: 7 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* X Y Height DBH (m) (m) 1 cm* 1 cm Vigor* Damage* Notes I' of anation of cutoff Natural Woody Stems - tallied by species s subsamiginsc**: _lei! ht Cut -Off (All stems shorter than this are ignored. If>10cm, explain why to the right): ❑ 1 tic m ❑ 50cm ❑ 106FC m ❑ 1 _ em Species Name 010 c50 LINGS - HEIGHT CLASSES SAPLINGS - DBH TREES - DBH hSeed cm em 50 cm 100 em 100 cm- 137 cm Sub- sap] 0-1 cm 1-2.5 2.5- 5- =10 (write DBH) "Required ifcutoff>]Ocmorsubsample?100%. 417 :2 +: g 0*4 !fa 6 ::10 Form WS2, ver 9.1 *SOURCE: Tr--TranspIpA L=Live stake, B=Be ll and burls P=PottTu--TublinZ R=bare Roo M=MechanicallU=Unlmown p, 33 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CVS-EEP Entry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Please fill in any missing data and correct any errors. Plot 1500702-01-0013 PaTv : Role: Date last planted: VMD Year (1-5): 2� Date: i Q / / i o - Taxonomic Standard: (/1%tAI' It Taxonomic Standard DATE: to Latitude or UTM-N: i36.277680 i Datum: NAD831W (dem) Longitude or UTM-TM-E: -79.425754 UTM Zone: Coordinate Accuracy (m): 1 I X-Axis bearing (deg): 146 Plot Dimensions: X: New Ianting date m/yy? Check box if plot was not Notes: sampled, specify reason below Y: 10 ❑ Plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data c THIS YEAR'S DATA Map Source* X Y HeighDBH y Height DBH Re- Vi or* Dama e* Notes t ID Species Name char 0.1m 0.1m lcm* I cm Icm* 1 cm sprout g g 15981 Platanus occidentalis O R 0.7 0.5 Missing ❑ M 15983 Quercus sp. ® R 1.2 5.4 Missing ❑ 15985 Nyssa sylvatica 0 R 3.1 5.4 Missing ❑ M 15988 Quercus sp. ® R 7.2 0.2 Missing ❑ M # stems: 4 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: X Y Height DBH Species Name Source* (m) (m) 1 cm* 1 cm Vigor* Damage* Notes Eacolanadon of cut-off" Natural Woody Stems - tallied by species & subsamaline *: ligiv ht Cut -Off (All stems shonerthan thisare ignored. If>10cm, explain why to theright): ❑ 10cm ❑ 50cm ❑ 1 m ❑ 137cm SEEDLINGS — HEIGHT CLAjcm SAPLINGS — DBH TREES — DBH Species Name Q Sub- 10 cm 50 cm 10Sub- =10 c Seed 50 cm 100 cm 13saps 1 0-1 cm 1 1-2.5 2.5- 1 5- (write DBH) **Required ifcrt-off>l0cm or subsample? 100%. 01 !2 ■ 3 a •4 ! #5 6 0 Form WS2, ver 9.1 "wUxCl : '1'r Trans lanL=Live stake B=Ball and burlap,P=Potted,,Tu=Tubling, R=bare Root, M=Mechanical] U=Unknown 1= 35 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CVS-EEP Entry Toot ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Plot 1500702-01-0014 VMD Year (1-5): a Date: Taxonomic Standard: Taxonomic Standard DATE: Latitude or UTM-N: (dec.deg. or m) Longitude or UTM-E: Coordinate Accuracy (m): Plot Dimensions: X: W�tic 1.e ZD1d 36.271527 Datum: INAD83/W L`C'A -79.429882 UTM Zone: 1 X-Axis bearing (deg): 76 Please fill in any missing data and correct any errors. Date last planted: New lanting date m/yy? Check box if plot was not Notes: sampled, specify reason below 10 Y: ]0 ❑ Plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Kole: l TL Oct 2018 Data z THIS YEAR'S DATA 0 Map Source* X Y Height DBH * Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m O.lm lcm* 1 cm lcm* 1 cm sprout 15992 Quercus sp. h S� Q R 1.5 2.5 62.0 ❑ 15993 Betula nigra ® R 3.8 1.4 20.0 ❑ 15994 Fraxinus pennsylvanica O R 4.0 7.9 55.0 ❑ 15995 Fraxinus pennsylvanica 0 R 3.2 6.2 60.0 ❑ 15996 Betula nigra O R 6.3 1.3 Missing ❑ 15997 Fraxinus pennsylvanica ® R 6.6 7.4 48.0 ❑ 15998 Betula nigra ® R 10.0 7.9 Missing ❑ 15999 Betula nigra O R 9.8 9.5 Missing ❑ 16000 Fraxinus pennsylvanica O k 8.8 7.0 Missin g ❑ 16001 Fraxinus pennsylvanica O R 8.2 4.1 63.0 ❑ 16002 Fraxinus pennsylvanica (R) R 6.8 4.1 60.0 ❑ # stems: 11 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* (m) (m) lI cm eight 1DBm Vigor* Damage* Notes *SOURCE: Tr -Transplant L=Live stake B=N 11 and burls P=Potted Tu­-TublinjL R=bare Root, M=Mechanically, U=Unknown 1-. 37 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown ]=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CYSEEPEntry Toot ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Please fill in any missing data and correct any errors. Plot 1500702-01-0015 VMD Year (1-5): 2 Date: / / / / Taxonomic Standan : Taxonomic Standard DATE: 20 l0 Latitude or UTM-N: 36.271883 Datum: NAD83/W (dec.deg. or m) Longitude or UTM-E: -79 429571 j UTM Zone: Coordinate Accuracy (m): I X-Axis bearing (deg): 16 Date last planted: New lanting date m/yy? 0 Check box if plot was not Notes: sampled, specify reason below Plot Dimensions: X: 10 Y: ! 101 ❑ Plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data Z THIS YEAR'S DATA 0 Map Source* X Y Height DBH I * Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m O.lm Icm* I cm 1 lcm* 1 cm sprout 16004 Betula nigra O R 3.6 5.9 50.0 ❑ 16005 Betula nigra 0 R 2.2 8.3 82.0 ❑ 16006 Betula nigra ® R 4.3 8.7 121.0 DBH? ❑ 16007 Fraxinus pennsylvanica O R 9.3 1.5 Missing ❑d 16008 Betula nigra O R 6.1 6.3 Missing ❑ 16009 Betula nigra O d : 6.8 9.4 111.0 DBH? ❑ 16010 Betula nigra © R 9.0 9.5 MissingEl 16011 Betula nigra ® R 8.0 7.1 72.0 ❑ 16012 Fraxinus pennsylvanica ® R 3.1 0.6 32.0 ❑ �-lm,©_- m-"©_- m o -w©_- # stems: 9 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* (m) (m) I cm* DBE Vigor* Damage* Notes *Notes by ID: 16007-Buried alive *SOURCE: Tr=Transplant L=Live stake B=Ball and burla P=Po Tu=Tublin R=bare Root M=Mechanicall} , U=Unknown 1, 40 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1--unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CVS-EEPEnoy Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Plot 1500702-01-0016 VMD Year (1-5): F Date: Taxonomic Standard: Taxonomic Standard DATE: Latitude or UTM-N: (dec.deg. or m) Longitude or UTM-E: Coordinate Accuracy (m): Plot Dimensions: X: i% /I41-1 ZD 10 56.272880 Datum: NAD83/W 79.429170 UTM Zone: 1 X-Axis bearing (deg): 346 Please fill in any missing data and correct any errors. Kole: F Date last planted: New lanting date m/yy? 0 Check box if plot was not Notes: sampled, specify reason below 10 Y: F 1 0 ❑ plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data ' z THIS YEAR'S DATA 0 Map Source* X Y Height DBH * Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m 0.1m lcm* 1 cm lcm* 1 cm sprout 16014 Betula nigra ® k 0.9 1.2 93.0 ❑ 16015 Betula nigra O R 2.6 0.8 45.0 16016 Quercus nigra O R 0.8 3.4 25.0 16017 Fraxinus pennsylvanica O R 2.8 6.5 70.0 ❑ 16018 Quercus phellos O R 0.5 6.7 39.0 11 16019 Betula nigra ® R 1.4 9.6 62.0 ❑ 16020 Betula nigra ® R 2.8 9.4 51.0 ❑ 16021 Fraxinus pennsylvanica ® R 3.1 3.5 45.0 El 16022 Betula nigra O 4.9 0.7 40.0 16023 Betula nigra Ol R 6.9 1.0 82.0 16024 Quercus sp. ® R 9.4 4.8 40.0 16025 Betula nigra O R 9.1 2.0 65.0 16026 Fraxinus pennsylvanica ® R 7.1 4.5 56.0 16027 Quercus phellos O R 7.9 7.6 70.0 ❑ 16028 Betula nigra O R 4.6 9.3 65.0 16474 Fraxinus pennsylvanica O R 5.2 6.8 44.0 mmlxj=_- # stems: 16 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* X Y Height DBH (m) (m) 1 cm* 1 cm Vigor* Damage* Notes *SOURCE: Tr --Transplant L=Live stake B=Ball and burlap, P=Potted, Tu=TublinR. R=bare Root M=Mechanicallx, U=Unlmown p. 43 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 1 Ocm if >2.5m and 50cm if >4m. Printed in the CVS-EEP Entry Toot ver. 2.3.0 # stems: 16 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* X Y Height DBH (m) (m) 1 cm* 1 cm Vigor* Damage* Notes *SOURCE: Tr --Transplant L=Live stake B=Ball and burlap, P=Potted, Tu=TublinR. R=bare Root M=Mechanicallx, U=Unlmown p. 43 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 1 Ocm if >2.5m and 50cm if >4m. Printed in the CVS-EEP Entry Toot ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Please fill in any missing data and correct any errors. Plot 1500702- VMD Year (1-5): Ffl Date: I, b Taxonomic Standard: I W,e°a R- Taxonomic Standard DATE: ZD 10 Latitude or UTM-N: 36.273295 Datum: NAD83/W (dec.deg. or m) Longitude or UTM-E: _79 429498 UTM Zone: Coordinate Accuracy (m): 1 X-Axis bearing (deg): 308 Date last planted: New planting date m/yy? 0 Check box if plot was not Notes: sampled, specify reason below IPlot Dimensions: X: 10 Y: 10 ❑ plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data Z THIS YEAR'S DATA 0 Map Source* X Y Height DBH * Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m 0.1m lcm* 1 cm lcm* 1 cm sprout 16030 Betula nigm ® R 1.2 4.2 92.0 ❑ 16031 Fraxinus pennsylvanica Q R 0.7 8.0 62.0 ❑ 16032 Fraxinus pennsylvanica O R 2.9 7.3 77.0 ❑ 16033 Betula nigra ® R 3.5 3.7 92.0 ❑ 16034 Fraxinus pennsylvanica Q R 1.8 2.7 75.0 ❑ 16035 Quercus lyrata Ql R 6.2 2.3 50.0 ❑ 16036 Betula nigra ® R 6.2 3.4 92.0 ❑ 16037 Quercus nigra 0 R 5.7 7.0 68.0 ❑ 16038 Betaia-nigra � ® R 5.8 9.1 62.0 ❑ 16039 Quercus sp. ® R 3.0 9.9 MissingEl 16040 Fraxinus pennsylvanica O R 4.3 9.1 Missing ❑ 16041 Betula nigra © R 7.2 9.6 80.0 ❑ 16042 Fraxinus pennsylvanica Q R 7.7 8.3 55.0 ❑ 16043 Betula nigra O R 8.8 9.8 70.0 ❑ 16044 Betula nigra ® R 10.0 8.2 102.0 DBH? ❑ 16045 Quercus sp. O R 10.0 9.6 70.0 ❑ 16046 Quercus sp. O R 8.5 7.0 MissingEl 16047 Quercus sp. ® R 8.0 4.3 MissingEl 16048 Quercus sp. O R 9.8 2.3 MissingEl 16049 Fraxinus pennsylvanica (�) R 8.5 0.2 87.0 ❑ 16050 Quercus phellos Q R 9.9 0.4 92.0 ❑ # sterns: 21 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* (m) (m) 1 C. 1 cm X Y Height DBH Vigor* Damage* Notes *SOURCE: T =Trans lanA L=Live stake B=Ball and burlap. P=Potted Tu=Tublinc, R=bare Root. M=Mechanicall}p, U=Unlmown _ �_46 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CVS-EEP Entry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Plot 1500702-01-0018 VMD Year (1-5): ❑2 Date: Taxonomic Standard: Taxonomic Standard DATE: Latitude or UTM-N: (dec.deg. or m) Longitude or UTM-E: Coordinate Accuracy (m): Plot Dimensions: X: ID/ �n%�.wiGi•e 2n ►v 36.278533 Datum: NAD83/W -79.417650 UTZone: X-Axis bearing (deg): 124 Please fill in any missing data and correct any errors. 5W-I Kole: Date last planted: New lanting date m/yy? Check box if plot was not Notes: sampled, specify reason below ]0 Y: 10 ❑ Plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data z THIS YEAR'S DATA 0 Map Source* X Y Height DBH Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m 0.1m lcm* 1 cm lcm* 1 cm sprout g g 15648 Cercis canadensis O R 0.0 0.6 52.0 ❑ 15649 Cercis canadensis ® R 2.8 0.7 40.0 ❑ 15650 Nyssa sylvatica O R 4.4 2.8 41.0 ❑ 15651 Nyssa sylvatica O [t 2.7 2.6 42.0 ❑ 15652 Unknown sp. ® R 0.5 2.6 10.0 ❑ 15653 Quercus phellos n R 0.6 4.6 44.0 ❑ 15654 Quercus phellos O R 2.7 4.6 50.0 ❑ 15655 Cercis canadensis © :• 5.7 0.9 72.0 ❑ 15656 Cercis canadensis R 8.2 1.3 53.0 ❑ 15657 Unknown sp. @ R 8.6 3.1 Missing ❑ 15658 Nyssa sylvatica ® R 6.6 3.0 42.0 ❑ 15659 Quercus phellos ® R 6.9 4.8 50.0 ❑ 15660 Quercus nigra O R 7.8 7.9 Missing ❑ 15661 Quercus nigra O R 5.9 7.7 10.0 ❑ 15662 Quercus nigra ® R 3.8 7.6 48.0 ❑ 15663 Quercus nigra ® k 1.6 7.6 62.0 ❑ 15664 Quercus phellos O R 5.1 4.5 50.0 ❑ # stems: 17 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* X Y Height DBH Il (m) (m) 1 cm* 1 cm Vigor Damage Notes *SOURCE: Tr --Transplant L=Live stake, B=Ball and burlar- P=Potted, Tu=Tubling, R=bare Roo M=MechanicallU=Unknown . 49 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown hmlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if >2.5m and 50cm if>4m. Printed in the CVS-EBPEntry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Please fill in any missing data and correct any errors. Plot 15 702-01-0019 VMD Year (1-5): ❑2 Date: 1 p / , / 1 b _ / / Taxonomic Standard: We-.k\ 2v Taxonomic Standard DATE: Latitude or UTM-N: 136.275203 Datum: NAD83/W (dec.deg. orm) Longitude or UTM-E:-79.418009 UTM Zone: Coordinate Accuracy (m): IFX-Axis bearing (deg): 1241 1N Date last planted: New lanting date m/yy? Check box if plot was not Plot Dimensions: X: 10 Y: 101 ❑ plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Species Name Oct 2018 Data Z THIS YEAR'S DATA o_ Map Source* X Y Height DBH Heigbt DBH Re- Dama Vigor* e* Notes char 0.1m 0.1m ]cm* 1 cm * ]cm* 1 cm sprout g g hoot quercus nigra O R 1.1 0.6 40.0 ❑ 15668 Quercus nigra O R 3.7 0.4 20.0 ❑ 15669 Quercus nigra Q R 2.7 3.0 60.0 ❑ 15670 Quercus nigra (E) R 5.6 3.0 40.0 ❑ 15671 Quercus sp. r 1 �('N O R 6.3 0.2 44.0 ❑ 15672 Quercus sp. n` ` � r�l+ ® R 8.9 0.6 54.0 El 15673 Quercus nigra Q R 8.0 3.2 58.0 ❑ 15675 Quercus nigra O R 5.9 5.0 53.0 ❑ 15676 Nyssa sylvatica O R 6.6 8.0 40.0 ❑ 15677 Nyssa sylvatica ® R 8.8 8.1 38.0 ❑ 15678 Quercus nigca o,\ ® R 1.1 5.2 71.0 ❑ 15679 Quercus nigra ® R 3.1 5.0 Missing ❑ 15680 Quercus sp. Q R 4.2 3.0 MissingEl 15681 Quercus phellos ® R 4.2 8.0 32.0 ❑ # stems: 14 N St mar■�©�� ew ems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* (X) (m) H ig t DBH ViI cotgor* Damage* Notes *SOURCE: Tr=Turns lan L=Live stake, B=Ball and �burlsp Pam=Potted, Tu=Tubling, R=bare Root. M=Mechanically, U=Unknown v 52 *VIGOR: 4=excellent, 3=good, 2=fair, *D� AMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicanc, DISeased, VINE M=rnissing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to IOcm if>2.5m and 50cm if>4m. Printed in the CVSEEP Entry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Plot 1500202-01-0020 VMD Year (1-5): ❑2 Date: p / 1 Taxonomic Standard: W e, ,k t� Taxonomic Standard DATE: 20 � b Latitude or UTM-N: 36.2764 Datum: NAD83/W (dec.deg. or m) Longitude or UTM-E:-79.4175 UTM Zone: Coordinate Accuracy (m): X-Axis bearing (deg): 140 Please fill in any missing data and correct any errors. a4>1GL 1 PL Sw- i 4v, s} Date last planted: New mg date m/yy? 0 Check box if plot was not Notes: sampled, specify reason below Plot Dimensions: X: ] 0 Y: 10 E Plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data c THIS YEAR'S DATA Map Source* X Y Height DBH * Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m 0.1m lcm* 1 cm lcm* 1 cm sprout 15683 Quercus nigra 0 R 0.2 0.6 52.0 15684 Quercus nigra O R 2.0 1.3 60.0 ❑ 15685 Quercus nigra ® R 4.1 1.9 58.0 ❑ 15686 AJ�`) 15687 l���tW ® Quercus � R 6.0 2.8 22.0 El 15688 Quercus nigra O R 5.3 0.2 48.0 El 15690 Cercis canadensis O R 8.1 3.1 62.0 ❑ 15691 Cercis canadensis O R 9.9 4.9 53.0 ❑ 15692 Quercus nigra O R 9.8 6.0 51.0 11 15693 Nyssa sylvatica © R 7.8 6.0 40.0 ❑ 15694 Quercus nigra O R 5.9 5.2 15.0 15695 Fraxinus pennsylvanica ® R 6.5 7.2 40.0 ❑ 15696 Fraxinus pennsylvanica ® R 8.5 7.5 48.0 ❑ 15697 Quercus nigra R 8.7 9.9 58.0 ❑ 15698 Quercus nigra O R 6.3 9.9 38.0 El 15699 Quercus nigra �S ® R 4.3 6.3 62.0 ❑ 15701 Nyssa sylvatica (R-;LA- ;qc, O R 3.9 5.1 50.0 ❑ 15702 Fraxinus pennsylvanica O R 2.2 6.3 30.0 0 15703 Quercus phellos O R 2.2 8A 39.0 ❑ =MINI©�� ®-"© - m-w©_- ®-"©_- mmusm� =-Mm_- m-1 m©_- mmmmm � ®-m©_- MMrEA©M�� m-mm_- ©-m©_- m-m®_- M-I•,Mm- # stems: 19 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* (m) (m) Height DBm Vigor* Damage* Notes *SOURCE: Tr=T last L=Live stale B=Ball and burl P=Potted Tw-Tubb R=bare Root M=Mechanicall U=Unknown V. 55 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unl mown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CVS-EEP Entry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Please fill in any missing data and correct any errors. Plot 1500702-01-0021 VMD Year (1-5): 2 Date: 4o/ Taxonomic Standard: Taxonomic Standard DATE: 2 O Latitude or UTM-N: 36.2759 Datum: NAD83/W (dec.deg. or m) Longitude or UTM-E: -79.4144 LL UTM Zone: Coordinate Accuracy (in): X-Axis bearing (deg): 180 pill Date last planted: New planting date m/yy? Check box if plot was not Notes: sampled, specify reason below Plot Dimensions: X: 10 Y: 10 plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Species Name Oct 2018 Data I o THIS YEAR'S DATA Map Source* X Y Height DBH * Height DBH Re- Vigor* Damage* Notes char 0.lm 0.lm lcm* 1 cm Icm* 1 cm sprout 15704 Quercus nib ��C'�5 O R 0.1 2.6 38.0 ❑ 15705 Cercis canadensis O it 3.4 2.5 53.0 ❑ 15706 Betula nigra O R 5.8 1.8 28.0 ❑ 15707 Quercus nigra R 6.9 3.8 47.0 ❑ 15708 Nyssa sylvatica O R 4.2 4.6 40.0 ❑ 15709 Qusp);eHes R 0.4 4.0 53.0 ❑ 15710 Quercus nigra O R 7.7 6.2 51.0 ❑ 15711 Nyssa sylvatica ® R 5.6 7.4 22.0 ❑ 15712 Nyssa sylvatica ® R 5.0 6.0 41.0 ❑ 15713 Cercis canadensis O R 8.5 8.4 30.0 ❑ 15714 Cercis canadensis R 7.1 9.5 60.0 ❑ 15715 Quercus phellos Q R 2.2 10.0 61.0 ❑ 15716 Platanus occidentalis O R 1.6 8.4 73.0 ❑ 15717 Quercus phellos O R 0.9 7.2 Missing ❑ 15719 Platanus occidentalis O R 2.8 5.4 48.0 ❑ 15720 Comus amomum © R 3.5 7.0 42.0 ❑ 15722 Quercus phellos ® R 2.2 3.3 20.0 ❑ 15723 Quercus phellos O K 1.5 1.3 20.0 ❑ 15724 44 Nyssa sylvatica ® R 2.7 0.8 28.0 ❑ ®■l,©_� s ■IMMAI== mm"M mm� v■rllo=� ®M ■m©_- ®■I"Mm =■I■,M_- m■ n©m� m■n©m�= stems. 19 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* (m) (m) Hight DBHH Vigor* Damage* Notes 'SOURCE: Tr -Trap lan L=Live stake B=Ball and bur P=Potted Tu=Tubling, R=bare Root�M=Mechanically, U=Unknown 3,. 58 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1--unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE Missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if >4m. Printed in the CYSEEP Entry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Plot 150 2- 1- 022 VMD Year (1-5): ff] Date: 10 / ( Taxonomic Standard: wepic Taxonomic Standard DATE: Zp rr a Latitude or UTM-N: 136.2757 Datum: NAD83/W (dec.deg. or m) .-794153 UTM Zone: Longitude or UTM-E: Coordinate Accuracy (m)• X-Axis bearing (deg): 88 Please fill in anv missing data and correct any errors. Date last planted: New lanting date m/yy? Check box if plot was not Notes: sampled, specify reason below Plot Dimensions: X: 10 Y: 10 ❑ Plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X xore: Ed Oct 2018 Data o THIS YEAR'S DATA Map Source* X Y Height DBH * Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m 0.1m lcm* 1 cm Icm* 1 cm sprout 15726 Cercis canadensis O R 1.8 2.9 45.0 ❑ 15727 Cercis canadensis ® R 0.5 0.0 51.0 ❑ 15728 Cercis canadensis ® R 2.7 0.5 75.0 ❑ 15729 Cercis canadensis O R 4.5 0.6 107.0 DBH? ❑ 15730 Cercis canadensis (D 11.. 4.1 3.3 42.0 ❑ 15731 Quercus phellos @ R 6.5 1.2 81.0 ❑ 15732 Quercus nigra @ R 8.7 1.4 102.0 DBH? ❑ 15733 Quercus nigra ® R 8.0 3.9 Missing ❑ 15734 Quercus phellos @ F 7.1 6.6 Missing ❑ 15735 Quercus phellos O R 5.1 5.9 Missing ❑ 15736 Comus amomum @ R 5.4 9.6 50.0 ❑ 15737 Fraxinus pennsylvanica G) R 9.1 8.9 Missing ❑ 15738 Quercus phellos R 9.2 7.3 45.0 ❑ 15739 Quercus phellos O R 2.6 5.3 Missing ❑ 15740 Corpus amomum O R 3.4 9.0 42.0 ❑ 15741 Comus amomum @ R 1.6 8.1 40.0 ❑ 15742 Platanus occidentalis @ R 0.2 9.8 110.0 DBH? ❑ 15743 Fraxinus pennsylvanica ® R 1.5 6.5 50.0 ❑ 15744 Platanus occidentalis @ R 0.5 5.0 Missing ❑ # stems: 19 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: X Y Height DBH Species Name Source* (m) (m) 1 cm* 1 cm Vigor* Damage* Notes *SOURCE: Tr=Trwsplant, =Live stake B=Ball and burls P=Potted Tu-Tubes, R=bare Root, M=Mechanicall U=Unlmown •. 61 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1--unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CVS EEPEntry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Plot 1500702-01-0023 VMD Year (1-5): ❑� Date: Taxonomic Standard: Taxonomic Standard DATE: Latitude or UTM-N: (dec.deg. or m) Longitude or UTM-E: Coordinate Accuracy (m): Plot Dimensions: X: 10/� /1 -zoo 1 6.2753 79.4149 Datum: NAD83/W UTM Zone: X-Axis bearing (deg): 1 140 Please fill in any missing data and correct any errors. Date last planted: New lanting date m/yy? L=� Check box if plot was not Notes: sampled, specify reason below y; 10 ❑ plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data Z THIS YEAR'S DATA 5 Map Source* X Y Height DBH * Height DBH Re- Vigor* Damage* Notes ID Species Name char 0.1m 0.1m lcm* 1 cm Icm* 1 cm sprout 15747 Comus amomum O R 0.3 1.0 52.0 ❑ 15748 Comus amomum O 1i 2.7 1.4 Missing ❑ 15749 Comus amomum ® R 1.1 2.7 53.0 ❑ 15750 Comus amomum ® R 3.6 3.3 58.0 ❑ 15751 Cawvs-anemum �Sh O R 5.7 2.9 44.0 ❑ 15752 Comes ememum � C O H 5.7 2.9 41.0 ❑ 15753 Quercus nigra O R 7.5 2.3 38.0 ❑ 15754 Nyssa sylvatica O R 9.7 2.3 30.0 ❑ 15755 Unknown sp. ® R 7.6 6.8 MissingEl 15756 Quercus nigra R 9.8 7.4 58.0 ❑ 15757 Quercus nigra O R 7.9 8.5 Missing❑ 15758 Cercis canadensis © It 6.0 7.6 41.0 ❑ 15759 Cercis canadensis O R 4.5 9.6 62.0 ❑ 15760 Comus amomum Q R 3.1 9.0 44.0 ❑ 15761 Comus amomum ® R 3.7 5.4 38.0 ❑ 15762 Fraxinus pennsylvanica ® R 1.4 6.3 45.0 ❑ 15763 Fraxinus pennsylvanica O R 1.0 9.4 38.0 ❑ �Mlmlm_- M-I■,©_- ®-l■'®_- ®mu©m� ®-IE,©_-, ®ter■�©�� # stems: 17 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* (m** ) (m) Height I scut Vigor* Damage* Notes *SOURCE: Tr -Transplant. L=Live stak B=Ball and burlap, P=Pottcd�Tu=Tublina R=bare Root M=MechanicallU=Unknown 64 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CVS-EEPEntry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Please fill in any missing data and correct any errors. Plot 1 0702-01- 4 Parrs: Role: Date last planted: VMD Year (1-5): ❑2 Date: Taxonomic Standard: Taxonomic Standard DATE: -Zp Latitude or UTM-N: 36.2748 Datum: NAD83/W (dec.deg. or m) Longitude or UTM-E:-79.4151 UTM Zone: Coordinate Accuracy (m): X-Axis bearing (deg): 190 Plot Dimensions: X: 10 y; 1 10 Plot has reverse orientation for X and Y axis Oct 2018 Data Z 0 Map Source* X Y Height DBH CD ID Species Name char 0.1m 0.1m lcm* 1 cm * 15766 Quercus phellos O R 1.1 3.4 40.0 15767 Quercus phellos Q R 2.9 4.6 62.0 ❑ 15768 Fraxinus pennsylvanica ® R 9.2 0.3 30.0 ❑ 15769 Quercus phellos Q R 6.9 6.1 Missing ❑ 15770 Quercus phellos Q R 8.7 6.8 Missing ❑ 15771 Quercus nigra © R 7.5 9.0 70.0 ❑ 15772 Quercus nigra Q R 6.0 8.0 32.0 El 15773 Quercus phellos ® R 4.9 5.4 48.0 15774 Quercus phellos ® R 4.0 7.2 32.0 ❑ 15775 Quercus > ' n �iS ® R 2.4 6.3 40.0 ❑ 15776 Fraxinus pennsylvanica O R 3.9 9.6 48.0 ❑ 15777 Fraxinus pennsylvanica ® R 0.7 8.0 50.0 ❑ 15778 Quercus nigra O t 0.6 5.6 49.0 ❑ New I rating date m/yy? Check box if plot was not Notes: sampled, specify reason below is 90 degrees to the right of X THIS YEAR'S DATA Height DBH Re- Vigor* Damage* Notes lcm* 1 cm sprout KM-IE,©_- FMI-1E,®_- cn="E mm � =-MM_- # stems: 13 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: Species Name Source* X Y Height DBH P (m) (m) 1 cm* 1 cm Vigor* Damage* Notes d E- - *SOURCE: Tr-Transvlant, L=Live stake, B=Ball and burls P=Po Tu=Tubli R=bare Root, M=Mechanically, U=Unknown p. 67 *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODents, INSects, GAME, LIVESTock, Other/Unknown 1--unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE Missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CVS-EEP Entry Tool ver. 2.3.0 Vegetation Monitoring Data (VMD) Datasheet Please till in any missing data and correct any errors. Plot 1500702-01-0025 VMD Year (1-5): ❑2 Date: Taxonomic Standard: IV f ea)L l v Taxonomic Standard DATE: 20 \V ' Latitude or UTM-N: 36.2743 Datum: NAD83/W (dec.deg. or m) _79.4143 UTM Zone: Longitude or UTM-E: Coordinate Accuracy (m): X-Axis bearing (deg): 1 160 Date last planted: New lanting date m/yy? 0 Check box if plot was not Notes: sampled, specify reason below Plot Dimensions: X: 10 Y: ]0 ❑ Plot has reverse orientation for X and Y axis (Y is 90 degrees to the right of X Oct 2018 Data Z THIS YEAR'S DATA 0 Map Source* X Y Height DBH Height DBH Re- g Vig or* Dama e* Notes ID Species Name char O.lm 0.1m lcm* I cm * 1cm* 1 cm sprout 15781 Quercus phellos ® R 0.8 0.7 62.0 ❑ 15782 Quercus phellos ® R 2.8 0.7 42.0 ❑ 15783 Fraxinus peansylvanica O R 1.6 2.7 Missing ❑ 15784 Fraxinus pennsylvanica ® P 4.0 2.7 Missing ❑ 15785 Quercus nigra O R 9.8 1.2 38.0 ❑ 15786 Betula nigra R 8.1 2.5 Missing ❑ 15787 Fraxinus pennsylvanica Qj R 5.2 1.5 40.0 ❑ 15788 Quercus nigra ® R 6.1 3.9 51.0 ❑ 15789 Betula nigra R 8.7 7.0 95.0 ❑ 15790 Betula nigra ® R 7.1 7.6 75.0 ❑ 15791 Betula nigra © R 5.0 7.3 70.0 ❑ 15792 Quercus phellos O R 7.6 9.6 Missing ❑ 15793 Quercus phellos O R 8.6 9.6 Missing ❑ 15794 Platanus occidentalis O R 4.4 9.4 68.0 ❑ 15795 Fraxinus pennsylvanica ® R 1.4 7.7 52.0 ❑ 15796 Quercus phellos O R 0.9 9.8 42.0 ❑ 15797 Platanus occidentalis O R 0.1 5.6 85.0 ❑ 15798 Quercus nigra O R 2.2 5.3 52.0 ❑ 15799 Platanus occidentalis O R 4.3 5.0 Missing ❑ MWENORMIE1 _- / % -lwj®_- # stems: 19 New Stems, not included last year, but are obviously planted. If more space needed, use blank PWS (Planted Woody Stems) Form: X Y Height DBH Species Name Source* cm* 1 cm Vigor* Damage* Notes *VIGOR: 4=excellent, 3=good, 2=fair, *DAMAGE: REMoval, CUT, MOWing, BEAVer, DEER, RODems, INSects, GAME, LIVESTock, Other/Unknown 1=unlikely to survive year, 0=dead, ANIMal, Human TRAMpled, Site Too WET, Site Too DRY, FLOOD, DROUght, STORM, HURRicane, DISeased, VINE M=missing. Strangulation, UNKNown, specify other. *HEIGHT PRECISION drops to 10cm if>2.5m and 50cm if>4m. Printed in the CYSEEPEnrry Tool ver. 2.3.0 Benton Branch Bank Parcel Year 2 (2019) Monitoring Report Appendices Phase One Haw River WS Umbrella Bank Restoration Systems, LLC Appendix E. Additional Vegetation Survey Work (02-28-2020) Temporary Vegetation Plot Data Benton Branch 020228 Benton Branch Restoration Site Species T-1 (221°) T-2 (182°) T-3 (251°) T-4 (295°) T-5 (44°) T-6 (145°) T-7 (343°) Betula nigra 4122417 Cercis Canadensis 111 Cornus ammomum 1 Diospyros virginiana 13 Fraxinus pennsylvanica 2123716 Platanus occidentalis 13 7447 Nyssa spp.11 Quercus spp.13 Ulmus spp.1 Stems per acre:324 364 243 647 607 283 931 Temporary Vegetation Plot Data Benton Branch 020228 Benton Branch Restoration Site Species T-8 (160°) T-9 (131°) T-10 (282°) T-11 (205°) Betula nigra 5611 Cornus ammomum 1 Stems per acre:243 243 40 40 XS-1XS-2XS-3 XS-4 T 1 1 T10 15 16 17 14 NC Center for Geographic Information & Anaylsis FIGURE Drawn by: Date: Scale: Project No.: KRJ OCT 2019 1:1000 15-007.02 Title: Project: Prepared for: Caswell County, NC BENTON BRANCHMITIGATIONBANK CURRENTCONDITIONSPLAN VIEW 2C³Legend Benton Branch Easement = 33.2 ac Transects 200228 Stream Restoration = 4602 ft Stream Enhancement (Level I) = 480 ft Stream Enhancement (Level II @ 2.5:1) = 1084 ft Stream Enhancement (Level II @ 5:1) = 3517 ft Wetland Restoration = 2.7 ac Wetland Enhancement = 2.3 ac CVS Plots Cross Sections 0 200 400100Feet UT-6 ^_#*#*XS-1 XS-1XS-6XS-6XS-6XS-9XS-9XS-9XS-10XS-10XS-10XS-20XS-20XS-32XS-13XS-13XS-13XS- 3 4 X S -1 6XS-16XS-16XS-12XS-12XS-12X S -1 7 XS - 1 7XS-33XS-11XS-11XS-11XS-31X S-1 5XS-15XS - 1 5XS-24X S - 2 3XS-26XS-27XS-25XS-21XS-18XS- 1 8 XS-22 XS-14 X S-14 XS - 1 4 X S-1 9 X S -1 9XS-28XS-30XS-29XS-8X S -4 XS-8X S -1 X S -1XS-2XS-5XS-8XS-7XS-5 XS-3XS-7X S -4XS-3 XS- 4 XS-2XS-3XS-4XS-5X S -3 XS-2X S -2 XS-75 4 3 1 2 T7T2T4T3 T1 T9T6T 5T86 4 3 2 7 1 8 5 9 11 12 13 10 NC Center for Geographic Information & Anaylsis FIGURE Drawn by: Date: Scale: Project No.: KRJ OCT 2019 1:1600 15-007.02 Title: Project: Prepared for: Caswell County, NC BENTON BRANCHMITIGATIONBANK CURRENTCONDITIONSPLAN VIEW 2B³Legend Benton Branch Easement = 33.2 ac Stream Restoration = 4602 ft Stream Enhancement (Level I) = 480 ft Stream Enhancement (Level II @ 2.5:1) = 1084 ft Stream Enhancement (Level II @ 5:1) = 3517 ft Transects 200228 Wetland Restoration = 2.7 ac Wetland Enhancement = 2.3 ac CVS Plots Cross Sections Groundwater Gauges #*Stream Gauges/Cameras ^_Rain Gauge 0 300 600150Feet UT-1 U T -2 UT-2BUT-3UT-2