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HomeMy WebLinkAboutI-51_Root Dendrogeomorphology Analysis and Results_Final_ReducedA=COM / rn?.K.OLS Root Dendrogeomorphology Analysis and Results FINAL City of Durham Stormwater & GIS Services Division Public Works Department 101 City Hall Plaza, Third Floor CITY OF DURHAM Durham, North Carolina 27701 AECOM / Freese and Nichols, Inc. Table of Contents 1 Introduction..................................................................................................................................................... 1-1 1.1 Background...................................................................................................................................................................................1-1 2 Root Dendrogeomorphology Methodology and Field Data Collection ................................................... 2-1 2.1 Methodology...............................................................................................................................................................................2-1 3 Data Collection................................................................................................................................................. 3-1 3.1 Field Data Collection.................................................................................................................................................................3-1 3.1.1 Bank Site #2 — UT to Ellerbe Creek......................................................................................................................3-2 3.1.2 Bank Site #10 —Third Fork Creek.........................................................................................................................3-4 3.1.3 Bank Site #12 — UT to Little Lick Creek..............................................................................................................3-5 3.1.4 Bank Site #13 — UT to Sandy Creek.....................................................................................................................3-7 3.2 Sample Preparation for Analysis...........................................................................................................................................3-9 4 Data Analysis and Interpretation................................................................................................................... 4-1 4.1 Analysis..........................................................................................................................................................................................4-1 5 Discussion.........................................................................................................................................................5-1 5.1 Interpretation of Results..........................................................................................................................................................5-1 6 Conclusions...................................................................................................................................................... 6-1 7 References........................................................................................................................................................ 7-1 Root Dendrogeomorphology Report AECOM / Freese and Nichols, Inc. List of Figures Figure 2-1 Illustration of Annual Erosion Measurement (Dick et al. 2013)................................................................................2-3 Figure3-1 Bank Site #2: UT to EC..............................................................................................................................................................3-2 Figure 3-2 Locations of Roots 02-A and 02-B prior to sampling from Bank Site #2: UT to EC . ....................................... 3-3 Figure 3-3 Locations of existing bank pins for Bank Site #2: UT to EC.......................................................................................3-3 Figure 3-4 Roots 10-A, 10-B, and 10-C located along Bank #10: TFC.........................................................................................3-4 Figure 3-5 Root 10-D located three feet down the bank from the previously installed bank pins . ................................ 3-5 Figure 3-6 Locations of roots 12-A, 12-B, and 12-C located along the bank site #12: UT to LLC. .................................. 3-6 Figure 3-7 Locations of existing bank pins located along the bank site #12: UT to LLC..................................................... 3-7 Figure 3-8 Location of Roots 13-A and 13-B along Bank Site #13: UT to SC...........................................................................3-8 Figure 3-9 Location of existing bank pins along Bank Site #13: UT to SC.................................................................................3-8 Figure 6-1 Incomplete relationship of BEHI score to estimated root -derived erosion rate . .............................................. 6-2 List of Tables Table 2-1 Root Dendrogeomorphology Stream Bank Erosion Long -Term Monitoring Site..............................................2-2 Table 3-1 Summary of Collected Root Samples & Nomenclature...............................................................................................3-1 Table 3-2 Root Location Measurements at Bank Site #2: UT to EC (n = 3).............................................................................3-2 Table 3-3 Root Location Measurements at Bank Site #10 TFC (n = 4).......................................................................................3-5 Table 3-4 Root Location Measurements at Bank Site #12 UT to LLC (n = 3)...........................................................................3-6 Table 3-5 Root Locations at Bank Site #13 UT to SC (n = 2)...........................................................................................................3-7 Table 4-1 Results of Root Analysis for Estimated Years of Exposure and the Calculated Erosion Rate .........................4-2 Table 5-1 Summary of Results from Collected Root Samples compared to BEHI Erosion Rate Estimates..................5-1 Table 5-2 Summary of Results from Collected Root Samples compared to Bank Pin Data...............................................5-2 List of Appendices A-1 Full -Size Overview Map of Root Dendrogeomorphology Sample Locations A-2 BEHI Forms A-3 Prepared Root Samples and Sample Location Information A-4 Root Dendrogeomorphology Quality Assurance Project Plan (QAPP) A-5 Root Sample Photos (Electronic Submission) Root Dendrogeomorphology Report AECOM / Freese and Nichols, Inc. Acronyms and Abbreviations BEHI............... Bank Erosion Hazard Index City .................. City of Durham EC .................. Ellerbe Creek FNI................. Freese and Nichols, Inc. GIS................... Geographic Information Systems GPS................. Global Position System LLC ............... Little Lick Creek NBS................ Near Bank Stress Root Dendrogeomorphology Report PDF................. Portable Document Format QA................... Quality Assurance QAPP.............. Quality Assurance Project Plan QC ................... Quality Control SC .................. Sandy Creek TFC ................ Third Fork Creek UT ................. Unnamed Tributary WIP................. Watershed Improvement Plan 1 Introduction City of Durham has retained AECOM and Freese and Nichols to assist with applying root dendrogeomorphology methods for estimating erosion rates within selected watersheds at sites previously studied by erosion pins. The scope of work consists of the following tasks: Task 1 Project Management and Quality Assurance (QA)/Quality Control (QC) — December 2020 Task 2 Root Dendrogeomorphology Field Data Collection — June 2020 Task 3 Root Dendrogeomorphology Training Session for City Staff — February 2020 Task 4 Final Report — January 2021 The purpose of this document is to present the associated analysis and results of the root samples collected during Task 2, under Task 9.2 (Root Dendrogeomorphology) of the New Hope Creek and Little Creek Watershed Improvement Plan (WIP) contract in accordance with the Root Dendrogeomorphology Quality Assurance Project Plan (QAPP) developed during Task 1 and finalized in December 2020 (Appendix A-4). Under this task, a dendrogeomorphic study was conducted to determine site -specific annual erosion rates through root -derived methods. This document outlines the project introduction, methods, analysis, results, discussion, and conclusion associated with the Task. The project team consists of Freese and Nichols, Inc (FNI) staff with support from AECOM and the City of Durham (City). This document may be used by the project team as a reference when planning site selection, collecting, preparing, and analyzing field samples of roots for future projects. 1.1 Background Root dendrogeomorphology is a method to determine annual erosion within a fluvial environment using exposed tree roots along eroding stream banks. Tree ring anatomy of the exposed roots change in response to the duration of exposure and these changes can be identified within cross -sectional samples of the root. The annual growth rings of the cross-section are then counted back to the exposure indicator to determine the number of years since the root was exposed. Using the date since exposure and a horizontally measured distance from the bank to the root sample, an average yearly rate of erosion can be determined. This rate can then be used for a variety of applications, although the method is predominantly used to determine the severity of erosion within a system or the urgency for stabilizing the banks to protect nearby infrastructure. Secondary purposes of determining erosion rates include long term planning for Total Maximum Daily Load implementation, evaluation of measurable benefits for stream restoration projects, time -trend analysis of land use change, channel process response to land use change, and forecasting the stability of systems facing land use change (Dick et al., 2017). The primary objective of the Root Dendrogeomorphology Task was to provide the City of Durham with root -derived, site -specific annual erosion rates based on the analysis of data collected from four selected sites (Table 2-1). These rates were estimated by collecting and analyzing exposed root samples at banks representing differing levels of erosion risk, as characterized by Bank Erosion Hazard Index (BEHI) ratings. A digital compound microscope (Celestron Handheld Digital Microscope Pro) was used to identify indicators within a prepared cross -sectional Root Dendrogeomorphology Report 1-1 sample of each collected root that provide insight to the initial date of root exposure or most recent exposure, in the case of roots that have been buried and re -exposed over time. This project collected dendrogeomorphological data along bank locations where bank pins were previously installed with the intent to monitor stream bank erosion. The City of Durham can then compare the dendrogeomorphological annual erosion rate data to the bank pin erosion rates to determine if the observed erosion rates can be validated using the dendrogeomorphological data. This comparison will be completed by Kimley Horn under Task 9.1 of the New Hope Creek and Little Creek Watershed Improvement Plan (WIP) contract. The data may be combined with erosion rates from additional locations to provide the City of Durham with a more comprehensive watershed -scale erosion rate curve for use in future site evaluations. This study additionally validates the use of root dendrogeomorphology as an accepted method to determine annual erosion rates. Root Dendrogeomorphology Report 1-2 2 Root Dendrogeomorphology Methodology and Field Data Collection 2.1 Methodology The root dendrogeomorphology methodology was conducted in accordance with the Root Dendrogeomorphology Quality Assurance Project Plan (QAPP) developed during Task 1 and finalized in December 2020 (Appendix A-4). Typically, erosion rates can be obtained from erosion pins installed within the stream bank, toe pins, annual surveys of the bank, or a time -trend aerial photograph analysis (Lawler, 1993). However, each of these methods has limitations. A time -trend aerial photograph analysis is limited in the level of detail of erosion rates that can be detected between photographs, which is typically crude on forested sites in the Eastern United States. Erosion pins and bank surveys, while considered the most accurate methods, require multiple years of measurements to obtain meaningful results. Erosion pins can undermine (Lawler, 1993), and under some contexts, when soils are predominantly cohesive sediments, they can act as stabilizers (Thorne, 1979, 1981). Direct impacts by survey crews during scheduled bank pin assessment can also impact and skew the data. An exposed root study is an alternative method that allows quick erosion rate estimation for a relatively large number of sample points using exposed tree roots (Dick et al., 2014; Lopez-Saez et al., 2018; Malik and Matyja, 2008). This method is predicated on the fact that the wood structure of a tree root changes when soil loss results in root exposure, resulting in the accumulation of growth features that are commonly found in the trunk and branches. Trees in temperate regions typically manifest growth rings which represent the annual growth. Thus, by identifying the specific growth ring associated with a change in morphology due to the root tissue response to exposure, the number of rings beyond the exposure year can be counted to estimate the duration of exposure. An average annual erosion rate can then be estimated by dividing the distance of exposed roots from the existing streambank by the estimated years of exposure. Collection and analysis of multiple root samples in a given area can yield a large amount of accurate and detailed bank erosion rate data in a relatively short period of time. The City of Durham established 16 stream bank pin monitoring sites across the city in 2014. Sites were chosen that represented higher levels of erosion as determined by BEHI and NBS ratings with a minimum of a 'Moderate' classification. These sites have been monitored regularly since installation (City of Durham, 2018). Four of these sites were selected for inclusion in the current study with the intent of comparing results of erosion rate analysis from these different methodologies; bank pins and dendrogeomorphology (Table 2-1). A site map illustrating the sample locations is included in Appendix A-1. Root Dendrogeomorphology Report 2-1 Table 2-1 Root Dendrogeomorphology Site and Corresponding City of Durham Stream Bank Erosion Long -Term Monitoring Site UT to Ellerbe #2 36.0307 -78.9032 High Very High High Very High Creek (EC) Third Fork #10 35.9664 -78.9130 Extreme Very High High Very High Creek (TFC) UT to Little Lick #12 Creek (LLC) 35.9836 -78.8521 High High Moderate High UT to Sandy #13 Creek (SC) 35.9770 -78.9521 Moderate Moderate Moderate Moderate 2018 BEHI and NBS Rating values were collected as part of the City of Durham Bank Pin Monitoring Report (City of Durham, 2018) In accordance with the December 2020 QAPP (Appendix A-4), root samples shall be collected within 90 feet (30 meters) of the established bank pins where possible, with the stipulation that the sampled bank exhibits the same bank erodibility conditions. A photo was taken of the entire streambank at each root sample location, with a grade rod shown in the image for scale to capture the flagged roots and their relative position to one another. The horizontal distance between the exposed tree root and the bank location was measured in the same manner that an erosion pin would be measured to the current bank slope surface. The location of each root sample was also recorded using a Trimble R1 Global Position System (GPS) with an accuracy of less than one meter. Prior to root collection, a Bank Erosion Hazard Index (BEHI) streambank stability assessment was conducted on the bank being sampled using methodology developed by Rosgen (2006) and included all necessary photo documentation and measurements. BEHI assessments should be conducted every time field work is conducted at a site, as BEHI scores and ratings are subject to change as channel conditions change. Banks may improve if sediment deposition collected along the toe of slope is able to form a floodplain bench, if vegetation increases, or if bank angle decreases. Likewise, bank conditions can worsen if the bank angle steepens, vegetation and protective cover is reduced, or mass failure occurs. Bank height, bankfull height, root density, surface protection, and bank angle were all measured and recorded, using the form included in Appendix A-2. The bank (either right or left looking downstream) and the relative location that the sample was collected on the bank (i.e. height from toe of slope, distance from the bank, etc.) was recorded with the notes. Root samples were labeled in the field using flagging tape. Paper bags for each sample were prepared with the corresponding label written on the bag with a permanent marker. Paper bags reduce the occurrence of mold development, which can destroy the wood tissue and render it difficult or impossible to determine the first year of root exposure. Each label included: • a unique identifier corresponding to the stream where the sample was collected, • the date which it was sampled, and • the sample number for that specific bank. Root Dendrogeomorphology Report 2-2 For example, a sample from the UT to Ellerbe Creek was labelled "060320-UT-EC-01 ", where "060320" indicates the date of sample collect, "UT -EC" is the stream reach identifier, and "-01" signifies the sample location. If more than one sample was collected at a location, the sample was further identified with a letter. Prior to cutting the root, two measurements were taken, as illustrated in Figure 2-1. One measurement was taken from the toe of bank slope to the centroid location of the root to be cut (y- or vertical measurement), and the other from the centroid of the root horizontally to the face of the bank slope (x- or horizontal measurement). These measurements were documented and recorded under the same nomenclature as the flagging for the sample. A photo of each root measurement was taken with a grade rod (Keson 6 ft. pocket rod) indicating the distance to the bank. The locations of the bank pins in this area were also measured and recorded. Using a permanent marker, an arrow was drawn on the root, indicating gravity up. Once all measurements and documentation were completed, a minimum six-inch long root specimen (including the flagging) was cut with a hand saw and placed into the paper bag for transport and storage. As a note, Site 10 was mislabeled as UT to TFC (UT-TFC) during sample collection. The samples were actually collected on the main stem of TFC and all references to UT-TFC are referring to TFC. c r� C rZ a Lateral Measurement '' Annual Growth ring / /Exposed Riverbank Vertical Measurement Distance of exposed root - from riverbank ANATOMICAL :', O c CHANGE INDICATES YEAR m ROOT EXPOSED o O Annual Years of = Erosion Exposure Rate Figure 2-1 Illustration of Annual Erosion Measurement (Dick et al. 2013) Root Dendrogeomorphology Report 2-3 3 Data Collection 3.1 Field Data Collection Sample collection occurred on June 03, 2020, and a total of 12 samples were collected from the four sites. Several root samples were collected at each bank location from different bank elevations to provide an average annual bank erosion rate for that location. The labels on the root samples included a number (which corresponds to the City of Durham's bank pin monitoring nomenclature e.g., 02, 10, etc.) to signify the bank site from which the samples were collected, and were assigned an additional unique identifier (A, B, C, or D) to differentiate the samples taken at the same bank site. The term lateral is used to describe the distance out from the bank (x-axis), the term vertical is used to describe the distance up from the bottom of the channel (y-axis), and the term longitudinal is used to describe the distance between the previously installed bank pins and the sampled roots. The longitudinal distances between the bank pins, installed by the previous study performed by the City in 2018, and the collected root samples were measured and recorded; photographs of the bank pins were also taken. General observations were recorded through notes or photographs. The roots are herein referred to by the final number and letter combination of their unique labels, as illustrated in Table 3-1. Table 3-1 Summary of Collected Root Samples & Nomenclature Black walnut UT-EC-02-A UT to Ellerbe #2 3 Black walnut Right High UT-EC-02-B Creek (EC) Red maple UT-EC-02-C Boxelder UT-TFC-10-A Third Fork Ironwood UT-TFC-10-B #10 Creek TFC 1 ( ) 4 Ironwood Left High UT-TFC-10-C Ironwood UT-TFC-10-D UT to Little Sweetgum UT-LLC-12-A #12 Lick Creek 3 Yellow poplar Left Moderate UT-LLC-12-B (LLC) Beech UT-LLC-12-C UT to Sandy Sweetgum UT-SC-13-A #13 2 Right Moderate Creek (SC) Blackgum UT-SC-13-B Total 12 Site 10 was mislabeled as UT to TFC (UT-TFC) during sample collection. The samples were actually collected on the main stem of TFC. Root Dendrogeomorphology Report 3-1 3.1.1 Bank Site #2 - UT to Ellerbe Creek The three roots collected at Bank Site #2, along the UT to Ellerbe Creek, were cut from the right bank, looking downstream, as shown in Figure 3-1. Figure 3-2 shows the locations from which samples 02-A and 02-B were taken (indicated with flagging). A summary of measurements representing lateral distance of the root sample from the face of the bank (x), and the vertical height of the root from the streambed (y) are shown below in . The upper, middle, and lower bank pins in this area were measured at lateral depths into the bank of 0.45, 1.48, and 1.05 feet, respectively (Figure 3-3). The middle bank pin was located near an area of local scour, measured at 1.96 feet laterally from the bank to the center of the root sample. The BEHI score was calculated, using measurements taken in the field. Using the standard BEHI form, the BEHI score was found to be 39. This yields a rating in the upper end of the adjective range "High". It should be noted that adjective rating is not as useful as using the raw score for development of lateral erosion curves. Future studies should use the numerical score when developing regression relationships of erosion to BEHI or other erosion indices. Table 3-2 Root Location Measurements at Bank Site #2: UT to EC (n = 3) 02-A UT-EC-02-A Black walnut 2.45 2.68 02-B UT-EC-02-B Right Black walnut High 0.3 4.2 02-C UT-EC-02-C Red maple 0.89 1.85 Figure 3-1 Bank Site #2: UT to EC Root Dendrogeomorphology Report 3-2 Middle Bank Pin 'I OBottom Bank Pin 3.1.2 Bank Site #10 -Third Fork Creek The four root samples collected along the left bank (looking downstream) of Third Fork Creek, Bank Site #10, are shown in the photographs below (Figure 3-4 and Figure 3-5). As a note, Site 10 was mislabeled as UT to TFC (UT- TFC) during sample collection. The samples were actually collected on the main stem of TFC. The lateral and vertical locations of the roots along the bank as measured in the field are included in the Table 3-3. The fourth root, 10-D, was taken 3.0 feet from the bank pins. The bank pins along Bank Site #10 were measured to have lateral depths into the bank of 0.74, 1.62, and 2.35 feet (upper, middle, lower; respectively). Seepage along the bank was observed in this bank location. The BEHI score was calculated, using measurements taken in the field evaluated using the standard BEHI form, and was found to be 38. This yields a rating in the upper end of the adjective range "High". The previous BEHI rating for Bank Site #10, collected in 2018, was in the adjective range of "Extreme". Without the previous BEHI scoring details, it is difficult to determine what influenced the change BEHI score between 2018 and 2020. Generally speaking, BEHI score may improve for a bank if sediment deposition collected along the toe of slope is able to form a floodplain bench, if vegetation increases, or if bank angle lessens. Increases in vegetation influence half of the scoring parameters evaluated when assessing bank erodibility. Figure 3-4 Roots 10-A, 10-B, and 10-C located along Bank #10: TFC. Root Dendrogeomorphology Report 3-4 Figure 3-5 Root 10-D located three feet down the bank from the previously installed bank pins. Table 3-3 Root Location Measurements at Bank Site #10 TFC (n = 4) 10-A UT-TFC-10-A Boxelder 2.18 4.4 10-B UT-TFC-10-B Ironwood 0.71 3.15 10-C UT-TFC-10-C Left Ironwood High 2.34 1.75 10-D UT-TFC-10-D Ironwood 0.68 6.1 Site 10 was mislabeled as UT to TFC (UT-TFC) during sample collection. The samples were actually collected on the main stem of TFC. 3.1.3 Bank Site #12 - UT to Little Lick Creek The roots collected along Bank Site #12, in the UT to Little Lick Creek, were collected along the left bank in the outer meander. The locations of the roots can be seen in Figure 3-6. The bank pins in Figure 3-7 were measured at lateral depths into the bank of 0.11, 1.10, and 0.57 feet (upper, middle, lower; respectively). The lateral and vertical Root Dendrogeomorphology Report 3-5 measurements are included in . The BEHI score was calculated using measurements taken in the field evaluated using the standard BEHI form and was found to be 28. This yields a rating at the high end of the adjective range "Moderate". The previous BEHI rating for Bank Site #12, collected in 2018, was in the adjective range of "High". Without the previous BEHI scoring details, it is difficult to determine what influenced the change BEHI score between 2018 and 2020.Generally speaking, BEHI score may improve for a bank if sediment deposition collected along the toe of slope is able to form a floodplain bench, if vegetation increases, or if bank angle lessens. Increases in vegetation influence half of the scoring parameters evaluated when assessing bank erodibility. Table 3-4 Root Location Measurements at Bank Site #12 UT to LLC (n = 3) 12-A UT-LLC-12-A Sweetgum 0.38 1.15 12-B UT-LLC-12-B Left Yellow poplar Moderate 0.46 3.12 12-C UT-LLC-12-C Beech 0.03 2.55 Figure 3-6 Locations of roots 12-A, 12-B, and 12-C located along the bank site #12: UT to LLC. Root Dendrogeomorphology Report 3-6 Figure 3-7 Locations of existing bank pins located along the bank site #12: UT to LLC. 3.1.4 Bank Site #13 - UT to Sandy Creek The two roots collected along the right bank (looking downstream) of UT to Sandy Creek, at Bank Site #13 are shown in below in Figure 3-8. The bank pins in this area, shown in Figure 3-9, were measured at lateral depths into the bank of 0.62, 0.88, and 0.82 feet (upper, middle, lower; respectively). The measurements of the locations of the root samples are included in . The BEHI score was calculated, using measurements taken in the field evaluated using the standard BEHI form, and was found to be 23. This yields a rating at the low end of the adjective range "Moderate". Table 3-5 Root Locations at Bank Site #13 UT to SC (n = 2) 13 A UT-SC-13-A Sweetgum 0.15 2.40 Right Moderate 13 B UT-SC-13-B Blackgum 0.23 3.35 Root Dendrogeomorphology Report 3-7 Figure 3-8 Location of Roots 13-A and 13-B along Bank Site #13: UT to SC. Photograph taken during measurement of vertical position of root sample on the bank using a pocket rod. Figure 3-9 Location of existing bank pins along Bank Site #13: UT to SC. Root Dendrogeomorphology Report 3-8 3.2 Sample Preparation for Analysis Root samples were initially cleaned with a sharpened wood chisel to remove debris and provide a uniform outer surface. A one -centimeter width disk was cut from the sample, using a Havalon toothless Piranah Knife, for observation under a Celestron handheld digital stereoscope (Schweingruber, 2007). Root samples needing more detailed analysis were prepared for microscopic analysis by cutting a one -centimeter disk with a band saw and then dividing the disk into smaller sections along two perpendicular axes in order to provide a complete cross-section of the root. Prepared root samples for the study locations are included in Appendix A-3. Prepared microscopic sections were permanently mounted on slides for archiving and then photographed. Digital images of each microscopic section were taken using the Celestron handheld digital microscope, and are included in Appendix A-5. The cellular structure was determined by comparing the photo to the Inside Wood Database for Stem -Wood Anatomy developed by the College of Natural Resources at North Carolina State University (Inside Wood, 2020). The total years of exposure was determined by counting the number of growth rings from the first growth ring demarcating exposure to the bark. From this, the average annual erosion was calculated by dividing the recorded distance from the root to the bank by the total years of exposure for each root (Figure 2-1). Root Dendrogeomorphology Report 3-9 4 Data Analysis and Interpretation 4.1 Analysis The roots were prepared for analysis following the methodology included in the December 2020 Root Dendrogeomorphology Quality Assurance Project Plan (QAPP) and established in previous research studies. The samples were analyzed in the laboratory to estimate the years since exposure of the root to the elements and associated mechanical stresses due to a lack of soil covering. The year of exposure was determined by examining a well -prepared cut -root section, evaluating the growth anatomy of the root through a microscope looking for several well -documented indicators of exposure, as described in Dick (2019). Indicators of exposure used for this analysis included: Decrease in cell and vessel size • Changes in the structure of the root to resemble stem -like growth • Eccentricity in the annual growth rings • Occurrence of scars and pith flecks • Bending of ray cells that coincide with the first year of exposure The results of the analysis are shown below in Table 4-1, including estimated annual erosion rate for each sample as well as the average estimated annual erosion rate at each bank site. Note that the erosion rates provided by this study are assumed to be constant and do not account for slope failure, mass wasting, or rapid erosion induced by specific storm events as that is not possible to capture without having samples that bound the years on either side of a specific event or events. Root Dendrogeomorphology QAPP 4-1 Table 4-1 Results of Root Analysis for Estimated Years of Exposure and the Calculated Erosion Rate UT-EC-02-A 2.45 16 0.15 #2 39 High UT-EC-02-B 0.30 13 0.02 0.16 UT-EC-02-C 0.89 3 0.30 UT-TFC-10-A' 2.18 6 0.36 UT-TFC-10-B' 0.71 7 0.10 #10 38 0.21 High UT-TFC-10-Cl 2.34 8 0.29 UT-TFC-10-D' 0.68 7 0.10 UT-LLC-12-A 0.38 9 0.04 #12 29 Moderate UT-LLC-12-B 0.46 9 0.05 0.03 UT-LLC-12-C 0.03 3 0.01 UT-SC-13-A 0.15 11 0.01 #13 23 0.02 Moderate UT-SC-13-B 0.23 10 0.02 ' Site 10 was mislabeled as UT to TFC (UT-TFC) during sample collection. The samples were actually collected on the main stem of TFC. Root Dendrogeomorphology QAPP 4-2 5 Discussion 5.1 Interpretation of Results The average annual erosion rate values for each site, as determined through dendrogeomorphology, provided a range from 0.02 ft/yr at Bank Site #13, located along the UT to Sandy Creek, to 0.21 ft/yr for Bank Site #10, along Third Fork Creek. The spatial distribution of the individual rates at each bank site indicates higher annual rates of erosion typically occurring in the mid to upper portions of the bank slope, while the lower portion of the bank typically has lower annual erosion rates. Additionally, the banks with higher BEHI scores had higher annual erosion rates as compared to the locations with lower BEHI scores. Results validated the relationship, showing that higher erosion rates correlated with higher scores for bank erodibility (BEHI) and likewise, the banks with lower erosion rates were found to have lower BEHI scores. Table 5-1 Summary of Results from Collected Root Samples compared to BEHI Erosion Rate Estimates UT to #2 Ellerbe Right High 0.16 High 0.16 0.16 Creek (EC) Third Fork #10 Creek Left Extreme 0.20 High 0.16 0.21 (TFC)' UT to #12 Little Lick Left High 0.16 Moderate 0.06 0.03 Creek (LLC) UT to #13 Sandy Right Moderate 0.06 Moderate 0.06 0.02 Creek (SC) Site 10 was mislabeled as UT to TFC (UT-TFC) during sample collection. The samples were actually collected on the main stem of TFC. z BEHI rating and BEHI derived erosion rates were determined as part of the bank pin monitoring effort conducted by the City of Durham (City of Durham, 2018). Root Dendrogeomorphology Report 5-1 Table 5-2 Summary of Results from Collected Root Samples compared to Bank Pin Data UT to #2 Ellerbe Right High 0.12 High 0.16 Creek (EC) Third Fork #10 Creek Left Extreme 0.99 High 0.21 (TFC)' UT to Little #12 Lick Creek Left High 0.14 Moderate 0.03 (LLC) UT to #13 Sandy Right Moderate 0.08 Moderate 0.02 Creek (SC) Site 10 was mislabeled as UT to TFC (UT-TFC) during sample collection. The samples were actually collected on the main stem of TFC. z Bank pin derived rates were determined as part of the bank pin monitoring effort conducted by the City of Durham (City of Durham, 2018). Root Dendrogeomorphology Report 5-2 6 Conclusions The goal of this study was to carry out a dendrogeomorphic study to develop root -derived annual erosion rates for the selected bank sites in the City of Durham to augment data gaps for missing or lost bank pin data and to provide an additional methodology for determined erosion rates. The information provides site specific annual erosion rates that can then be compared to existing erosion rate data to serve as data validation for future projects tasks carried out by the City. Erosion rates determined using dendrogeomorphology ranged from 0.02 ft/yr to 0.21 ft/yr, with an average erosion rate of 0.16 ± 0.05 ft/yr, with more erosion occurring on banks with higher BEHI scores, as would be expected. With the inclusion of additional data not collected as part of this Task, this information has the potential to be used to develop an erosion curve. The curve would need associated data sets that encompass the full range of BEHI scores in order to serve as a predictive tool. An incomplete curve was developed to show how future annual erosion rate data collection can be utilized. It should be noted that the example curve shown in Figure 6-1 is not valid until an expanded data set has been incorporated to represent the full range of BEHI values. Once the data set has been expanded, a regression equation and an R2 ("R-squared") value can be determined. An R2 value is one that describes the goodness of fit of a regression equation, or how closely the predictive data points match the observed data points. These values range between 0 and 1, where 1 is an exact match between predictive and observed data points. A p-value can be defined as the probability indictor that the observed relationship between the variables is not due to random chance, and in the context of this study, a p-value of less than 0.05 is considered to have statistical significance. Dick, et al. (2014) demonstrated that roots with less than 10 years of exposure have better correlation with bank erosion rates. The more recent the root is exposed, the more reasonable that a BEHI score collected this year will relate to that of the first year of exposure. An erosion rate curve was created by plotting BEHI score versus root -derived erosion rates for all samples with less than 10 years post -exposure (Dick, et al., 2014). The erosion rates for UT-EC-2A, UT-EC-213, UT-SC-13A, and UT-SC-13B were excluded from the data set because the identified years of exposure were greater than or equal to 10 years. Results indicate that high BEHI scores have a range of erosion rate values which may be influenced by soil variability within the sample locations. However, as BEHI scores increased, erosion rates generally increased linearly. Near bank stress values were not included in the incomplete erosion rate model, as results from Dick (2019) found low correlation between NBS-BEHI comparisons and erosion rate statistical significance. Root Dendrogeomorphology Report 6-1 0.4 0.35 p C).25 0 O W i 0.2 d 0 0 0.15 0.1 0.05 U 0 5 10 15 20 25 30 35 4D 45 BEHI Score Figure 6-1 Incomplete relationship illustrating the potential correlation of BEHI score to estimated root - derived erosion rate using the selected City of Durham stream reaches chosen as part of this Task. Roots identified as having been exposed for 10 years or more were excluded from the graph (Dick et al., 2014). The incomplete erosion rate curve derived from the root dendrogeomorphology analysis is incomplete until additional data sets have been incorporated to reflect the full range of BEHI values. As shown in Figure 6-1, the incomplete erosion rate curve, is limited by the lack of data at the lower end of the BEHI spectrum of scores. The specific BEHI score was used along the x-axis, rather than the BEHI rating, to provide granularity. This curve can be used as a foundation for future site investigations and provides site -specific, ground validated data as opposed to relying on regional trends. The use of root derived erosion rates with BEHI allows an assessor to collect BEHI and quickly estimate bank erodibility from previously developed erosion rate curves have been developed for a watershed. Additional data collection should be undertaken to improve the accuracy and robustness of the curve; as additional watershed analyses are conducted and additional streams are studied, more data can be added to the dataset. By including data from additional local streams, the erosion curve can be further refined and expanded to include the range of BEHI ratings. Fundamentally, this study serves to augment data gaps for missing or lost bank pin data and can be used for data validation to determine if similar erosion rates are determined from root derived approaches vs. measured values. A more complete data set with a range of BEHI scores would be required for the development and use of a strongly correlated erosion curve. This information has the potential to be used to develop an erosion curve. The curve would need associated data sets that encompass the full range of BEHI scores in order to serve as a predictive tool. An incomplete curve was developed to show how future annual erosion rate data collection can be utilized. It should be noted that the example curve shown in is not valid until an expanded data set has been incorporated to represent the full range of BEHI values. Once additional data sets have been incorporated, the expanded erosion curve could serve as a Root Dendrogeomorphology Report 6-2 useful tool to increase the confidence in the estimate of sediment loading and empower City staff to develop management plans that are more accurate with respect to loading rates. This analysis can be used as an example project and as guidance for similar projects in the City. FNI recommends that the City expand the data set and add to the incomplete erosion curve by collecting and analyzing additional root samples on banks that fall within the Low, Moderate, Very High, and Extreme BEHI ranges to strengthen the correlation between BEHI and erosion rate, providing a more accurate predictive tool. Additional study of bank soils is warranted to provide a better understanding of the role bulk density, soil type and other soil variability characteristics have on bank erodibility. Finding ways to further develop watershed erosion prediction models will allow the City to validate sediment production rates more comprehensively and provide a foundation for future erosion reduction action plans. Root Dendrogeomorphology Report 6-3 7 References City of Durham. (2018, July 12). Summary of 3-Year Stream Bank Erosion Monitoring Results and Development of Bank Erosion Rate Curves. Durham, NC: US. Dick, B.M., Hey, R., Peralta, P., Jewell, I., Simon, P. and Peszlen, I., 2014. Estimating annual riverbank erosion rates — a dendrogeomorphic method. River research and applications, 30(7), pp.845-856. Dick, B. M., Peszlen I., & Peralta, P. (2014). Changes in the Anatomy of Exposed Roots of Some Hardwood Species [PowerPoint slides]. Retrieved from https://www.swst.org/wp/meetings/AM14/pdfs/presentations/dick%20pdf.pdf Dick, B. M., & Jewell I. (2017). Living Erosion Pins — Streambank and Hillslope Erosion Rate Assessments using Exposed Tree Roots [PowerPoint slides]. Retrieved from http://northcarolina.apwa.net/Content/Chapters/northcarolina.apwa.net/Documents/3%20Living%20Erosi on%20Pins Bryan%20Dick.pdf Dick, B. (2019). Getting to the Root of Erosion: Dendrogeomorphology as a Streambank Erosion Assessment Tool [PowerPoint slides]. Retrieved from https://www.freese.com/sites/default/files/OCLWA- 2019 Getting%20to%20the%20Root%20of%20Erosion.pdf Dick, B.M. (2019). Diagnostic Testing in the Natural and Built Environment. North Carolina State University. Lawler, D. M. (1993). The Measurement of River Bank Erosion and Lateral Channel Change: A Review. Earth Surface Processes and Landforms, 18, 777-821. Lopez-Saez, J., Corona, C., Morel, P., Rovera, G., Dewez, T. J., Stoffel, M., & Berger, F. (2018). Quantification of Cliff Retreat in Coastal Quaternary Sediments using Anatomical Changes in Exposed Tree Roots. Earth Surface Processes and Landforms, 43, 2983-2997. Malik, I. and Matyja, M., 2008. Bank erosion history of a mountain stream determined by means of anatomical changes in exposed tree roots over the last 100 years (Bila Opava River —Czech Republic). Geomorphology, 98(1-2), pp.126-142. The Inside Wood Database. (n.d.). Retrieved from https:Hinsidewood.lib.ncsu.edu/search?l1 Thorne, C. R. and Lewin, J. 1979. 'Bank processes, bed material movement and planform development in a meandering river', in Rhodes, D. D. and Williams, G. P. (Eds), Adjustments of the Ffuvial System, Kendall/Hunt Pub. Co., Dubuque, Iowa, 117-137. Thorne, C. R. and Tovey, N. K. 1981. 'Stability of composite river banks', Earth Surface Processes and Landforms, 6, 469-484. Rosgen, D. L. (2006). Watershed Assessment of River Stability and Sediment Supply (WARSSS). Wildland Hydrology Books, Fort Collins, Colorado. Root Dendrogeomorphology Report 7-1 Schweingruber, F. H. (2007). Preparation of Wood and Herb Samples for Microscopic Analysis. In Wood Structure and Environment (3-5). Springer Series in Wood Science. Root Dendrogeomorphology Report 7-2 APPENDIX A-1 Sample Location Mapping ia y Crutchfield p+ ` t ; s n Neri aod5 n Location Overview Map sir+•yiry �I I t3bhrar. ty Wt�taia Ave . Shari CI Dearborn Dr y NICNOLS r� 5°pit All, n Rd j' crcedm❑❑r �,re ayr4� 't i Z ,.:..I ; Piper SrT on Raven S! /k1��rrO/II a 0 r "` ° ' Balvi E Sundial Cir Q n Ava w a gip`+q j m a B gtown m o`� 4 CITY OF DURHAM is6i. Ern � d da �.,i. � (n t3erW yn Ave n3J a DEN DROGEOMORPHOLOGY HNlabamyh R.reark i I j - I r aPlew❑°tt STUDY Park r`st• `� -----� - e '' [�-----/-.; ��.� Rock 1�i1 4 r /�_ '-� ❑°dry Quarry ••f. r _ lr-' Park H _ _c Pecan PI Site Locations r �\ y '�_ � S Dear Run _ 9-6C d \ Q _ Z Jo Durham City Limits lu �_ Fbck cM's �a u d \ yen•+, d = Quarry d Ave Op %S a rq �c o r n ■ $G -� b F A� ri�r„r a ❑ Park Yy Dclatsd sT p,Ve +/�� r £ a = n z» rrr� I ❑ub:•''l.rn� ,, tt ? ,A fps.., P Mrsrn;Rd ll A .r Cie ryas r� w Wdey Aveo y Watersheds n rvs=r=ny o ;� Durham r� a 501 E Mu„ �v C h Ra e06.. r >Z F $ k a Ave print r n e►. NX c n �,rn Rivers N Pointe r ° 501kQ ❑ a �.d Rd •. _.:�". 4 titer - /98 y .p E yn all `aQ m o ,,kr,k _ g c µaynardAve Ponds and Lakes � i rd Rd "� 4� M •� �% Site N o • nerd Ave y O Parks 4 I N µcc P Jr pd �' NL „cnd Ad x 4 ye 15 otesrrPG a Leon se o` Hu9p Si N s 1 e° ti, s �� k a o-s❑ N Im Ave County Boundary r_ a 2: UT to CarrbaoCH� t r R a yrr Ave Hammon t °3r 0 2,000 u 4 r �vicMla a> Lavender Ave 'a FI Lavender Ave *, tv 8 c E I I e rb e Creek r n a Feet ? rx A: Sunset Ave °p 7 to e t c G t P i # rr �, ne a a I CO� l `•r v n e qp F` DS. ; ! c y ' EFttet ,tsson G7 ` I F� Lyon tiZn Y e a' Sprun` 4 ❑ ,tya quhY st yn thq]he ` I m U p� �Da ° Occ4 a.Syro - - - �. __ _ � yr ______-__-__-__-_— f • F 7 9 �7� ti "s PershingSt Q v a � I a °, cat e E m r" b .501 o n c E J S. a Gt Il �r•�•R o- ,� Wrlsan SF CA n 1 ti a f ST Spring Cta& nc+ksMrr.ri¢e Morrisville �� a4 '�,, Woodrow Sr Oavid an Ave GJa St k.9a� , - Llnlieidps -�., I yi:, 4. z� W Club Blvd n Bt�d. St Paul St �te� yY pat a a time W club Blvd yy Glut r t+ U Pill 9 'Pr ¢ y Hrgbee S, a » v — 1J7 rewSt hIr all Englewood Ave H rn �_ m y hR a d e v in o m r c d Englewood Ave ' 0 pp rr= E U a _ � ❑ n 5 - Lawndala Ave `. H Q 70 v L) r - o ° _ 3 En Inwood Ave t5 pr ° a e 4 Duke Mnr Flpy' �i a ' o N - H 2 ° i n y g t ?nd v 06 Q Q W Knox St n a ° ~ _ - - D_1t1L tt a o n f r o J3 r in n u _� c 4 Z Everett P - RuYa Faek ! r -- - - L t pve f MEl °`+e d a H N I O� Irtdmon r pt' roll Y `.1 d v v _V rr r a u o ° .s i - us•7p E y al Ave ° D f`� 9 c x O n a '> a b `y W N n x S t Q R i. t" n' t7 Crest St ra 2 ii e m p a v n t_ y;nox t de t* a R WrttQ \, r Faye ❑ Grecn St Demerrus sl Clark Sr ¢ 1;+ h t G$tt+ Winburn Ave E d �Or m �dQtShirie t , • , 6�as Green $t }� TJanL1 ~' L ii ' r Q] N Gre?n S[ i5c,l Cynthia., ❑ U q pr att SS l LSt { ryf U N H O Car rn Elder St ' r E cn W Markham c 14 V'J 1Na[k am Ave Pus Walk Ave i 'o r �a n n e am Ave ' ❑ o r-_-r i °p f a Alf flt W o ° Elba S ° _ �rtner� nuis r Macon St ti `4 � 3 z ; ;' ; fiotlyvr 4J y eo a ry +ff+s et Frytin Rd IL a °tyre IT rC Urban Ave i I AveV 4 rp _o TryD Rr r ^ \ z _ r Newell Sr Sr`t 7 U U rR °rJCr ��r Perry Sr rOn Ds Dacran Ave ❑ y W Lynch s1 L Lynch St ShPill, Monmouth Ave HatQ seer m` fr �c L SccrnSn 51 tryti P Sr ya o u e Chee °rV+ln O W Trinity Ave c t a + .. SRGp Yea+by Ave t` ut N tdS Ct„ y ❑ �~ rLaty Ot L esearc Gqt y Envm h 0errr&r Mrnerva Ave rn z d St :+any a ^ Q4 s rl N10, 8 Dr } Lewis SI c Fork y� DG ens DurMm C W Geer Il c a I& rh r Gloria Ava 2 E Geer St ° ysbriar Naples e t, m y 8 Al e 7 +� j l ..e Rd i N N h+rrrA �j• +;� all?yn Lamond Ave f jl y Cr Co 'a ✓e �i ry r ro N W Corporalion St Lee St y< St a Snip 1 a r4 i1 n Lyric St� r ° C ' 3 4e ! - Durham a k� o ° 4ay t 0 Deaver °� Q° ❑ 10 c o a` Cerdral Wake PI x b- ben aro ``' Aa erh k Piuk Broadway S ° a P ° rtiz ron m` Sr �G Eo ka r al; Dowd St .' ❑ L y ❑ y (utz to c / Ot 7 ° Ch Carrll),r a Ave qy 4, rq`c Hunt St - q # o - arn� ¢ 'a E G,, J -S / • .. °Wer�rc Jfi �, - u Mlkers❑n Ave °i vy W Se I: 4 Gray Avey u . • Gt p t �'� adson St -- m C% i y` W +ra trp rn Roney rna� Etc y V 0 0 . 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Q° n E eror °110, 0 n G' a ' • �r .c ¢ w c E ee Ra ryC Se d n ON �' Q tn Catt:n E ly i n Y r. anL pkwy x' Y o ,. _a. S Ren at5s z Lr o y rG Loves Gry r� a i v s cr ANC.. 4M �C r= ifot�l ❑ c 4+ _ _ o a 1 �d � S'o-at � rpi• Morrell Ln e m G,naP _ 0 v F agtc Vtew Dr b n t�a�5 tstc' Lattirrtor t�Gri o. }(entington Dr x D ur r e 7�. 0. d t4 %% ro U e a ° 0 Cir c rr5 ' °Nt ❑ rndanL n 9Dr Q at Li+•rierlck L cUi °' a' b�❑ �r'aa * ry 4 4P ❑ a o r el parA pt , APPENDIX A-2 BEHI Forms BEHI Variable Worksheet Stream: UT- EC - 2 Reach: UT TO ELLERBE CREEK Cross Section: XS # 2 Observers: BMD, EMD Photos: Date: 06.03.2020 A Bank Ht D Root Depth eanik Helghrdeartktuir Height 6.7 Rooting QepthlE�mnk Height 3.0 3.5 2 __ _ B Bankfull Ht A Bank Ht x a.3 1 1.8 m U.$ 2.5 C (A/B) o.s _— E (D/A) 1.6 — .. — . — 0.2 3.7 t 0 0.44 ° 1 ; 8 s 6,q T 10 ° s a a� ass ,a BM 10 4.5 Roat Dwks ty slope Slaepn � 100 — 42Q e ISO F Root Density 100 — G Slope 35 o a S n 4 qZq IS aR 5.5 # ry 2 4 8 6 s �} �1 10 T BEHI $Eiil Surface Pratedon. Bank Material Adjustment i H Surface Bedrock (Overall Very Low BEHI) N/A _— Protection Boulders (Overall Low BEHI) 10 Cobble (-10 pts; No adjustment if sand / 40 _ gravel matrix > 50% of bank) Gravel (+5-10 pts depending on % sand) b 9 Sand (+10 points) 0 Silt/Clay (No adjustment) F Stratification Adjustment BeNi Add 5-10 points, depending on position of N/A unstable lavers in relation to bankfull staae VERY LOW1 LOW IMODERAT HIGH VERY HIGH EXTREME ADJECTIVE RATING and 39 5 - 9.5 10 -19.5 20 - 29.5 0 - 39.5 40 - 45 46 - 50 TOTAL SCORE Bank Sketch m v C <C <.i Horizontal Distance (ft) i 1,140 �Fh���*�✓� l ��ras� r rGI� 5 BEHI Variable Worksheet Stream: UT- TFC - 10 Reach: UT TO THIRD FORK CREEK Cross Section: XS # 10 Observers: BMD, EMD Photos: Date: 06.03.2020 A Bank Ht D Root Depth Bank HeighkEanktulr Kei4qht 7.5 Rooting OepttVE�mnk Height 3.0 3.5 8 Bankfull Ht A Bank Ht x a.6 125 2.4 m U.$ s --- - — C (A/B) p.s E (D/A) 3.1 I 0 0.4 Jq IBM 9.5 Rnat GannJty Sioprg Slaepnra�s e ISO F Root Density i+k7 - G Slope +40 - - - x 20 o a 4.5 b 9 a ry 2 4 K 6= 8<sr 1.1 Q s' 2 4 $ 6 X al 9 -to P h T BENI @EHI Surface P vted# on. 1Q¢ ' 40 44 c 20 0 a 2 5 4 9 6 6 9 14 BENI o' y H Surface Protection b 10 Bank Material Adjustment N/A Bedrock (Overall Very Low BEHI) Boulders (Overall Low BEHI) Cobble (-10 pts; No adjustment if sand / gravel matrix > 50% of bank) Gravel (+5-10 pts depending on % sand) Sand (+10 points) Silt/Clay (No adjustment) Stratification Adjustment N/A Add 5-10 points, depending on position of unstable lavers in relation to bankfull staae VERY LOW1 LOW IMODERAT HIGH VERY HIGH1 EXTREME I ADJECTIVE RATING[ ----- and 5 - 9.5 1 10 -19.5 1 20 - 29.5 KO - 39.5 40 - 45 1 46 - 50 TOTAL SCORE Bank Sketch m c cv <.i Horizontal Distance (ft) IN I `0fry7 Y, 5 BEHI Variable Worksheet Stream: UT- LLC - 12 Reach: UT TO LITTLE LICK CREEK Cross Section: XS # 12 Observers: BMD, EMD Photos: Date: 06.03.2020 A Bank Ht D Root Depth Bank HerghuBanktulr Kei4qht 6.2 Rooting OepttVE�mnk Height 6.2 3.5 B Bankfull Ht A Bank Ht x 013 2.5 a.$ - -- 6.2 s --- - C (A/B) U.E (D/A) 0.2 "38 10 BL�iI & $F�111. b 10 Rnat DannJty slope Sbn1}pn�s 101)e ISO - F Root Density 100 — - - G Slope go eo — - � 30 40 2d a b 6 11 � _ * r @EHI BENT Surface Pratoc#�on Bank Material Adjustment i H Surface Bedrock (Overall Very Low BEHI) N/A _— Protection Boulders (Overall Low BEHI) Cobble (-10 pts; No adjustment if sand / 20 40 — gravel matrix > 50% of bank) Gravel (+5-10 pts depending on % sand) 20 b Sand (+10 points) 0 Silt/Clay (No adjustment) a 9J z 4 9 6� 6 0W10 F - Stratification Adjustment e+l Add 5-10 points, depending on position of N/A unstable layers in relation to bankfull stage VERY LOW1 LOW ODERAT HIGH IVERY HIGH1 EXTREME I ADJECTIVE RATING ----29 ----- and 5 - 9.5 1 10 -19.5 20 - 29.V 30 - 39.5 1 40 - 45 1 46 - 50 TOTAL SCORE Bank Sketch m v C <C <.i Horizontal Distance (ft) �n�J, r�fiM i 1,140 �Fh���*�✓� l ��ras� r rGI� 5 BEHI Variable Worksheet Stream: UT- SC - 12 Reach: UT TO SANDY CREEK Cross Section: XS # 13 Observers: BMD, EMD Photos: Date: 06.03.2020 A Bank Ht D Root Depth 3.5 Bank HalghlMank#ull HNght 4.8 Rooting OepttVE3ank Height 4.8 -- —_ B Bankfull Ht A Bank Ht x 0.6 2.5 . 1.7 m U.$ s --- C (A/B) o.s E (D/A) 0.2q) 2 E� 4 6 10 0 2 4 a 10 E-1 _...- 2.8 o Root DwItafty slope Steepness 101)e ISO — F Root Density 100 — — — - G Slope 60 — 55 2[a o a b b �n 4 8 6x a �0 4 2 S' a a a sh ,I 5 T r @EHI BENT Surface Pratedon. Bank Material Adjustment i H Surface Bedrock (Overall Very Low BEHI) N/A _-- Protection Boulders (Overall Low BEHI) Cobble (-10 pts; No adjustment if sand / 40 40 _ gravel matrix > 50% of bank) Gravel (+5-10 pts depending on % sand) 70 b Sand (+10 points) 0 Silt/Clay (No adjustment) a 2 4 s 6 ;F 0 a 10 f Stratification Adjustment BEHI Add 5-10 points, depending on position of N/A unstable layers in relation to bankfull stage VERY LOW1 LOW /MODERATK HIGH IVERY HIGH1 EXTREME I ADJECTIVE RATING ----23 ----- and 5 - 9.5 1 10 -19.5 20 - 29.V 30 - 39.5 1 40 - 45 1 46 - 50 TOTAL SCORE Bank Sketch m v C <C <.i Horizontal Distance (ft) IN u i 140 �Fh���*�✓� l ��ras� r rGI� 5 APPENDIX A-3 Prepared Root Samples and Location Information DESCRIPTION AND OBSERVATIONS Sample Name: 4U0370 — V7 - CC — 07- —A Date: COLLECTED' 0U-0B.20Z0 Location: UT Ta EZLERgEE rpEEic BANK CITE #fix Spp: Bank geometry or buried depth: Diameter: Z3 mm Age: General Notes/Observations: Sketch of growth rings from microsections: DZ G au °3 41 fffl�illl 1f� fiClj�ii�fff(Il>if�fIilIi111jiial�iffi�f�il�ll111iiiljliil�ilTf�iiil�ill1jN11P cm !!2 ll3 4 5 IB 7 !!8 II9 j II llll lilt 4� oL s J s �I�I�Irld�lifililjldi��I�I�i�I ! I! 11 I I l I l I i I I I l I l DESCRIPTION AND OBSERVATIONS 01,0$20 -- V7 - ,EC - p2-- A OU-0S.20za UT ro 6UCIZ66C Cj2EEJt 8ANK 61TE #Z Bank geometry or buried depth; Diameter: 25 mm General Notes/Observations: Sketch of growth rings from microsections: DESCRIPTION AND OBSERVATIONS Sample Name: Q{►0370 - Vr- EC-e2-$ Date: COCLUTCD: OL. 43 . ZDZo Location: UT To f LLF R8FE aerie SA n IC ME # 2. 5pp: Bank geometry or buried depth: Diameter; qZ MM Age: General Notes/Observations: Sketch of growth rings from microsections: 0 (,u3 jo — UT, EC V 7- —8 Ill 111 Ill11{iilfJif Iljilf I`i111111111111fITHT11111HIIJfmIR111117f71mill -MUL,00— V I-11000a* ZII L lilllEf���f�llllll�III�I`dIIi�I��ll�l111lll�lllklIlillEllll�ill�ll��!Illlll�111�lII�IIEN111�11lllli�lllll�Ijlllllli�fl�il�I�I�if�li�lli�fll� , I I 11 I Ol D5SCRIPTION AND OBSERVATIONS Sample Name: oI! o3 ZO - Vr- EC - 02 - $ Date: C01A. C'l frb: 011. d$ .20i❑ Location- VT Trp C1,(-FP-8FC C ,e Y BAN9 SITE # Z. Spp: Bank geometry or buried depth: Diameter: y2 Vh►►7 Age: General Notes/Observations: Sketch of growth rings from microsections: 0 " f� zB z • - �i DESCRIPTION AND OBSERVATIONS Sample Name: 0UCS20 - UT - EC -02-C Date-. C0CLECTFD ft46" 0[►• 0$. 2020 Location: VT io .GL Ie$6E creer eANe crm # Z spp: Bank geometry or buried depth: Diameter: 50 mm Age: General Notes/Observatians: _,w Sketch of grc 0 too 320 - V T- E G- P 2- 0 ..Hoamw ZG L1 Ol 6 8 L DESCRIPTION AND OBSERVATIONS Sample Name. 0U0370 - LJ7-FC -OZ-C Date: C6L-tFCTCD' *44W* 0U, pg, 2pzp Location: VT To Ett ep gge CFf�fr- BRNe CITE # Z. Spp: Bank geometry or buried depth: Diameter: 50 mm Age: General Notes/Observations: Sketch of growth rings from microsections: DESCRIPTION AND OBSERVATIONS Sample Name: 0110? 7 0 - (I T - T F C - 10 _ A Date: COUEGTED ' CG• d3 . ZOZO Location: IJT To rMIZO F09-Tii CA"Ia BAND SITE V 10 Spp: Bank geometry or buried depth Diameter: 35 TM„rr, Age: General Notes/Observations: Sketch of growth rings from microsections: 5 f frf fl�l III III II�� lfit lIli [1{i ��i lflf ilil fli �1111�f1 I1fi I{Il f 7 8 9 1 o 11 12 13 14 1t 19 DESCRIPTION AND OBSERVATIONS Sample Name: 611p? Z p . UT - 7F C _ 10 - A Date: COL-LECTED, DU. 03 .20U) Location: Ur To 'rMIZD FGRTH CR-EE-IG 8ANk- SITE V 10 Spp: Bank geometry or buried depth: Diameter: 35 mrn Age. - General Notes/Observations: Sketch of growth rings from microsections: 10A i 10A4 , DESCRIPTION AND OBSERVATIONS Sample Name: OUG$20-UT-TFC - l�'8 Date: COLLECIrcO: 0(/.03.Z0ZG Location: Vf TO TMr_V FbW'H GkIGEE RNr SME # 14 Spp: Bank geometry or burred depth: Diameter; 20 mm Age: General Notes/observations: Sketch of growth rings from microsar": )r�: wW.0 W �T- IVC - 10- ��iflijl�iljfllf�r'�ff�Ifl��filf�fllf�rll1�11fI�f1fI�1111f11ll�IIIIjIIII�lllljllll��lllf IIlI�III��IIfI�fIIfIf11I�f11i�lllf+lllljl"";"""'"'! 1cm 2 3 4 5 6 7 8 S 10 11 12 13 14 [I�I�IEI�IfIIdI�dl�ill�Illilil����lll��Il�f�lilll�lll�lil�Ill�lil�l�f�lil�Illllll�i�llltlf fllllflll�l+ll DESCRIPTION AND OBSERVATIONS Sample Name: OU0SZQ' VT- '(Fe - 10-8 Date: C4LLFCrco: OU-05.2o2G Location: VT 7G 7MpV Frp-rH CP-E7Ej� BANr SITE # !4 Spp: Bank geometry or buried depth Diameter: 20 mm Age: General Notes/Observations: Sketch of growth rings from microsections: 106 � 1°B� DESCRIPTION AND OBSERVATIONS Sample Name: 4(103ZG- Ur-TFC- jG-C Date: eatECTEd . ou.03. Z0Z0 Location: Mlep FdaTN CXFPV- BANK SITE IT!0 5pp: Bank geometry or buried depth: Diameter: 21 mm Age: General Notes/0bservations : r Sketch of growth rings from microsections: v c v r 0 � iRf�llif lifljff�lff 111IT111111117 l11�i1filllil�I �,i1i111111 Q ll cm J2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17,. 18 19 2 Zk Mu GE W 6 +9 1 s I�If1IlIIIIIIIhIIlIIdIIIl,I�IIIIlIlllllllllllllll�lll�llllllllll>lIIIlIlll�llllllll}IIIIfIIIl�IIIIIlI111�lIl�lllllll � �111�.11l�!�. DESCRIPTION AND OBSERVATIONS Sample Name: 0 (j (I G " ur - -rFc - I G - C Date: COL cc(rED= btU.03• 7070 Location: U7 r0 rftep R9,TH CKEE1it- BANK SITE 1110 5pp: Bank geometry or buried depth: Diameter: 21 mm Age: General Notes/Observations7 Sketch of growth rings from microsections: DESCRIPTION AND OJESERVAQIONS Sample Name. 0Vo3 ZLI- Ur- TFD - 10- 60 Date: COCCCZTiE D : ec, , D . Zola Location: VT To TW tE D t+o izr C e 155- Spp: Bank geometry or buried depth: Diameter: 25 Mrrl Age: General Notes/Observations: Sketch of growth rings from microsections: Q 1cm 2 3 4 5 B J „I.1OWSI& zE !L N EFL i�i�� BA N+c 5 c rEJ it 10 7 8 9 10 11 12 s r vJ 1 11111it 1111117 18 19 2 DESCRIPTION AND OBSERVATIONS Sample Name: QG 03 Z - vT . TFC - 10 - D Date: CU . 03. 20Za Location: V-r To 'rKIIzp FcfzTW [12- FIFjt BANV SITE # IO Spp: Bank geometry or buried depth: Diameter: Zy Mry) Age: General Notes/Observations: Sketch of growth rings from microsections: loot 10D� �" 1GD3 DESCRIPTION AND OBSERVATIONS Sample Name: 0 (103 ZG - V7 - ZLC - 1Z -A Date: ca('t"FCTED: 0(Y-03• Z070 i*(km Location: Vr TO LIT -ME 1,1C K C B0,-V r P ANrc S116 -11r 1 Spp: Bank geometry or buried depth. Diameter. 315 rhm Age: General Notes/Observations: oft Sketch of growth rings from microsections: .. rr. ,ri rrr`rirr�rrri;rri'rr,rIf rrl lcm 2 3 4 5 6 7 8 9 10 11 12 13 :� i 0L 6 s L 16 17 18 19 DESCRIPTION AND OBSERVATIONS Sample Name: 0 Li03 ZG - Vr- L L C - 12 -A Date: coLf,rcTEp: ❑u-oz- Zp40 Location: VT -ra (AT -Me LICIC GBH1C F311"K SiTr_ 017- Spp: Bank geometry or buried depth: Diameter: 35 mm Age: General Notes/Observations: Sketch of growth rings from microsections: 12A, 12R� i 12A$ DESCRIPTION AND OBSERVATIONS Sample Name. Gt► 03 70 - UT - L.1. C - 17 - 8 Date: C 0Gt FCT E v: ou .0,3 . zozo Location: VT TC LITTGE [.ICiC Ci- IGEiI_ $ANIG 5pp. Bank geometry or buried depth. Diameter: 35 mrn Age: General Notes/Observations: Sketch of growth rings from microsections: �I114111 Y`I II Y�I Yll�l II I� I li I}I Y I I �I II I kl li I{ I II I� I I I 1tm 2 3 4 5 .LL0 s y Irr r i 3,gQl L au L L Q. L 6 7 8 9 0 4 15 16 17 18 19 DESCRIPTION AND OBSERVATIONS Sample Name: GU0370 - UT- Lt C - 1Z $ Date: C0[.GEC7Ep: 0to. 03. ZOZo Location: VT TC LITTLE LA C iC C2 elE:C 13AN K Sf'I-E # ! Z Spp: Bank geometry or buried depth- Diameter: 35 chrh Age: General Notes/Observations: Sketch of growth rings from microsections: DESCRIPTION AND OBSERVATIONS Sample Name: dG4370 - V T - LL C - jZ - C Date: COU15CTED = 0Le-03•207,0 Location: v"i -re, l l TTt E L l C k- C R-E-F- iG b hN IC S r7E # Spp: Bank geometry or buried depth: Diameter: 3 d mro Age: General Notes/Observations: Sketch of growth rings from microsections: IIIIfIInI I HylaI i yllfjfllf+flffjf! lI) 1cm 2 3 4 5 l Jr II !+ l+ I 10 +i1,f.�,li.I���1.�,Lf•1.1.1•+ r I I I I f i� i 1 � f,1 , f. i MUL DESCRIPTION AND OBSERVATIONS Sample Name: 0 U 03 2 0 - l/T - S C - I-3 -A Date: Ca Lt r c-r rp = a U • 03 . 7020 Location: UT ro SANDY G9,F-PX 6ANK SITE 013 Spp: Bank geometry or buried depth: Diameter: ZGj MM. Age. - General Notes/Observations.- Sketch of growth rings from microsections: .+ ►7rL 1�m 2 3 4 5 ' LLoauv* 0L 8 7 8 r 1'0 1r1 15 16 17 18 119 DESCRIPTION AND OBSERVATIONS Sample Name: a U O 3 2 p- V7 — S C 13 -- 13 Date: COLL EC-r E Ia : 00 • CS • 2a-Z G Location: LIT 'rO SANDY CRIFEIC BAN le srTIF � 13 Spp: Bank geometry or buried depth Diameter: lavv1 'Y1 Age: General Notes/observations: 1 Sketch of growth rings from microsections: I;i 1382 L 1353 1cm 2 3 4 5 6 7 S ..1,I.oais3�* zL i ! 0L 6 4 15 16 17 18 19 S APPENDIX A-4 Root Dendrogeomorphology Quality Assurance Project Plan (QAPP) ,ram - r�.� � x�•- -+ r T � • : '� �, .,yam .'+�.'` �!. �`� �. r 'ti >{� � � ' l�F At OP 1 ✓r I� � ... F `••'� `+ice A=COM / rnAlICHOLS Root Dendrogeomorphology Quality Assurance Project Plan City of Durham Stormwater & GIS Services Division Public Works Department 101 City Hall Plaza, Third Floor CITY OF DURHAM Durham, North Carolina 27701 AECOM / Freese and Nichols, Inc. Table of Contents 1 Introduction..................................................................................................................................................1-1 1.1 Project Description and Objectives.....................................................................................................................................1-1 2 Project Management and Quality Assurance (QA)/Quality Control(QC)................................................2-1 2.1 Quality Assurance Project Plan(QAPP)..............................................................................................................................2-1 2.2 Documents and Records..........................................................................................................................................................2-1 3 Root Dendrogeomorphology Field Data Collection.................................................................................3-1 3.1 Sampling Methodology..........................................................................................................................................................3-1 3.2 BEHI Methodology....................................................................................................................................................................3-2 3.3 Sampling Method Requirements.........................................................................................................................................3-3 3.4 Sample Handling Requirements...........................................................................................................................................3-5 3.5 Quality Control Requirements...............................................................................................................................................3-6 4 Sample Analysis and Data Interpretation...................................................................................................4-1 4.1 Preparation of Sample for Analysis.....................................................................................................................................4-1 4.2 Data Interpretation.....................................................................................................................................................................4-2 5 Root Dendrogeomorphology Training Session for City............................................................................ 5-1 5.1 Training...........................................................................................................................................................................................5-1 6 Final Report...................................................................................................................................................6-1 6.1 Technical Memorandum..........................................................................................................................................................6-1 7 References.....................................................................................................................................................7-1 Root Dendrogeomorphology QAPP List of Figure Figure 3-1 Roots marked gravity up before cutting...........................................................................................................................3-2 Figure 3-2 BEHI variables illustrated on a section of stream bank (adapted from Rosgen, 2006)...................................3-3 Figure 3-3 Root sample distribution along bank.................................................................................................................................3-4 Figure 3-4 Roots marked for sampling with flagging tape..............................................................................................................3-5 Figure 3-5 Vented Dish with Example Label..........................................................................................................................................3-6 Figure4-1 Example of Root Dissection....................................................................................................................................................4-1 Figure 4-2 Slide sandwiched between PVC and magnets for drying (Schweingruber, 2007)............................................4-2 Figure 4-3 Illustration of Annual Erosion Measurement (Dick et al. 2014)................................................................................4-3 List of Tables Table 1-1 Root Dendrogeomorphology Sample Collection Site List, City of Durham..........................................................1-2 Table 3-1 Proposed Root Dendrogeomorphology Site and Corresponding City of Durham Stream Bank Erosion Long -Term Monitoring Site...................................................................................................................................3-1 Table 3-2 BEHI Scores associated with the Qualitative Rating, as determined by the bank assessment procedure detailed in the BEHI forms located in Appendix B.................................................................................3-3 List of Appendices A-1 BEHI Form A-2 Sample Observation and Description Form A-3 Sample Envelop Label Template A-4 Sample ID Template A-5 Full -Size Overview Map of Root Dendrogeomorphology Sample Locations Root Dendrogeomorphology QAPP AECOM / Freese and Nichols, Inc. Acronyms and Abbreviations BEHI...............Bank Erosion Hazard Index City .................. City of Durham GIS................... Geographic Information Systems FNI................ Freese and Nichols, Inc. NBS................ Near Bank Stress PDF ................. Portable Document Format Root Dendrogeomorphology QAPP QA................... Quality Assurance QAPP.............. Quality Assurance Project Plan QC ................... Quality Control WIP................. Watershed Improvement Plan 1 Introduction City of Durham has contracted with AECOM and Freese and Nichols to assist with applying root dendrogeomorphology methods for estimating erosion rates. The scope of work consists of the following tasks: Task 1 Project Management and Quality Assurance (QA)/Quality Control (QC) — December 2020 Task 2 Root Dendrogeomorphology Field Data Collection — June 2020 Task 3 Root Dendrogeomorphology Training Session for City Staff — February 2020 Task 4 Final Report — December 2020 The purpose of this document is to present the Quality Assurance Project Plan (QAPP) for managing the collection and use of data under Task 9.2 (Root Dendrogeomorphology) of the New Hope Creek and Little Creek Watershed Improvement (WIP) Plan contract. It is anticipated that the QAPP will continue to evolve throughout the duration of the project as additional information and data are collected. Under this task, root dendrogeomorphology methods will be used in conjunction with bank pin data to develop erosion rate curves. This document outlines the project description, objectives, quality assurance project plan, documents and records, sampling methodology, sampling handling requirements, quality control requirements, preparation of sampling for analysis, data interpretation, training, and the technical memorandum requirements specific to Task 9.2. The project team consists of Freese and Nichols, Inc (FNI) staff with support from AECOM and the City of Durham (City). This document will be used by the project team when planning site selection, collecting, preparing, and analyzing field samples of roots. 1.1 Project Description and Objectives Root dendrogeomorphology is a method implemented to determine erosion within a fluvial environment using exposed tree roots along eroding stream banks. Tree ring anatomy of the exposed roots change in response to the duration of exposure and these changes are identified within cross -sectional samples of the root. The growth rings of the cross-section are then counted back to the exposure indicator to determine the number of years since the root was exposed. Using the date since exposure and a horizontally measured distance from the bank to the root sample, an average yearly rate of erosion is determined. This rate can then be used for several applications, the most prevalent being to determine the severity of erosion within a system or the urgency for stabilizing the banks to protect nearby infrastructure. Secondary purposes of determining erosion rates include long term planning such as TMDLs analysis, evaluation of measurable benefits for restoration projects, time -trend analysis of land use change and channel process responses and forecasting stability of systems facing land use change (Dick & Jewell, 2017). The primary objective of the Root Dendrogeomorphology task is to provide the City of Durham with erosion rate curves based on analysis from data collected from the four sites listed in Table 1-1, which the City can then use to quantify nutrient loading and sediment loss throughout the various watersheds. Erosion rates measured through root dendrogeomorphology methods will be collected from four locations within select City watersheds and will be compared to the erosion rates provided from established bank pins from a study conducted by City of Durham (2018). Additional information about previous root dendrogeomorphology studies and research are included in the references section of this QAPP. This project will also provide an opportunity for hands-on training and Root Dendrogeomorphology QAPP 1-1 collaboration with the FNI field team for development of Durham staff capability with root derived erosion rates. Ultimately, this project will establish a baseline of erosion information on which the City can build, by using root dendrogeomorphology or other methods for additional data collection at any site within the City. Bank Site #2 Bank Site #10 Bank Site #12 Bank Site #13 Table 1-1 Root Dendrogeomorphology Sample Collection Site List, City of Durham. Unnamed UT-EC-2 Ellerbe Creek 36.0307 -78.9032 Museum of Life and Science tributary (UT) to Ellerbe Creek Third Fork Creek UT-TFC-10 Third Fork 35.9664 -78.9130 Weaver St. Creek UT to Little Lick UT-LLC-12 Little Lick 35.9836 -78.8521 West of S. Woodcrest St. Creek Creek Downstream UT to Sandy Creek UT-SC-13 Sandy Creek 35.9770 -78.9521 West of Wade Rd. Upstream 1-2 Root Dendrogeomorphology QAPP 2 Project Management and Quality Assurance (QA)/Quality Control (QC) 2.1 Quality Assurance Project Plan (QAPP) As part of Task 9.2, a QAPP on the procedure to conduct root dendrogeomorphology methods is developed to assist in future efforts. The QAPP will be adjusted throughout the project as needed to provide City staff the needed guidance to conduct root dendrogeomorphology methods for future reference. 2.2 Documents and Records The following documents have been included in the appendix of this QAPP to aid in the collection, storage, and organization of data samples: BEHI Form The BEHI Form is to be used during the field data collection to document existing bank conditions. Streambank height, bankfull height, vegetative root depth within the bank profile, vegetative root density of the observed bank area, streambank slope, bank surface protection, and any bank material observations should be noted and scored in accordance with the form. A BEHI form should be completed for every bank location, and photo documentation should be captured and noted on the form as well. Individuals completing the BEHI assessment should have prior experience with BEHI measures or be trained in the field with someone who is knowledgeable on the subject. Once documented in the field, BEHI forms should be scanned and saved electronically within the project folder. Hard copies should be kept with the appropriate collected samples. ii. Sample Envelope Labels Template The Sample Envelope Labels Template is included to be used as a template for envelop labels. These labels are to be placed on large manila folders for sample storage after processing. iii. Sample ID Template The Sample ID Template is to be used as a template and printed on adhesive labels and applied to the brown paper sample collection bags prior to going to the field. Project name can be populated at the time of printing. Specific information relating to the root should be noted at the time of sample collection, such as sample id, species, buried or exposed, sample location, distance from bank, type of sample collections, and any notes or observations. These labels are included to maintain consistency and organization with the collected samples. iv. Sample Observations and Description Form The final form included in the appendix is the Sample Observation and Description Form to be populated and stored electronically and documents specific information about the root sample itself. Sample name, collection date, sample location, species, bank geometry, buried depth (as applicable), root diameter, and age of the sample are to be recorded. General notes and observations made during pre - Root Dendrogeomorphology QAPP 2-1 processing and analysis should also be noted. A rough sketch of the sample or microsection should be included for documentation purposes. All information should be stored in an organized manner which clearly indicates the stream name, site location, collection date and sample ID. Results from sample analysis should be documented and stored electronically in a similarly organized manner. It is recommended that results be stored within a program such as Microsoft Excel or equivalent. Measurements with appropriate units should be recorded and organized by project. Stream name, site location, collection date, and sample ID should be included with each data entry. Any unique or identifying notes should be included with the corresponding data. Titles and appropriate texts should be included to indicate specific steps taken during data analysis. Final results should be indicated in a manner that makes them stand out and the overall spreadsheet should be organized in a clear, concise manner to avoid future confusion. 2-2 Root Dendrogeomorphology QAPP 3 Root Dendrogeomorphology Field Data Collection 3.1 Sampling Methodology Erosion rates measured through root dendrogeomorphology methods will be used to analyze four of the City's Long -Term Stream Bank Erosion Monitoring sites (Table 3-1). A site map illustrating the proposed sites is included in the Appendix (A-5). Annual erosion rates obtained from root dendrogeomorphology methods will be compared to the annual erosion rates provided from the established bank pins as noted in a previous study (City of Durham, 2018), and expected to be updated in 2020. These bank pins were established by the City in 2014 and provide a means for comparison. Table 3-1 Proposed Root Dendrogeomorphology Site and Corresponding City of Durham Stream Bank Erosion Long -Term Monitoring Site Bank Site UT to Ellerbe Ellerbe Creek Museum of Life 36.0307 -78.9032 High Very High #2 Creek and Science Bank Site Third Fork Third Fork Weaver St. 35.9664 -78.9130 Extreme Very High #10 Creek Creek Bank Site UT to Little Little Lick West of S. 35.9836 -78.8521 High High #12 Lick Creek Creek Woodcrest St. Downstream Bank Site UT to Sandy Sandy Creek West of Wade Rd. 35.9770 -78.9521 Moderate Moderate #13 Creek Upstream Root samples shall be collected within 90 feet (-30 meters) of the established bank pins where possible, with the stipulation that the sampled bank exhibits the same bank erodibility conditions. Once a bank location is identified for root collection, the root samples intended to be cut are to be flagged with a labeled piece of high -visibility flagging tape approximately three feet long. An additional photo will be taken of the entire streambank, with a grade rod shown in the image for scale and will capture the flagged roots and their relative position to one another. A bank erosion hazard index (BEHI) streambank stability assessment shall be conducted on the bank being sampled and will include all necessary photo documentation and measurements associated with method, as discussed below. Bank height, bankfull height, root density, surface protection, and bank angle will all be measured and recorded. Sample forms for the BEHI assessment and the sample data collection are included in the Appendix. Paper bags for each sample are to be prepared with the corresponding label written on the bag with a permanent marker. The cut, flagged, root samples will be stored in these paper bags until they arrive in the lab. Once the bags are prepped, the first root sample is ready to be Root Dendrogeomorphology QAPP 3-1 measured and collected. Prior to cutting the root, measurements will be taken from the toe of bank slope to the centroid location of the root to be cut (y-measurement), and from the centroid of the root horizontally to the face of the bank slope (x-measurement). These measurements will be labeled to match the flagging for the sample and will include a photo of root with a pocket rod indicating the distance to the bank. Using the permanent marker, an arrow will be drawn on the root, indicating gravity up (Figure 3-1). Once all measurements and documentation are completed, a minimum six-inch sample (including the flagging) will be cut with a hand saw or equivalent and stored in the paper bag. The location of each root sample shall be recorded using a Global Position System with an accuracy of less than one meter. Figure 3-1 Roots marked gravity up before cutting 3.2 BEHI Methodology The BEHI method is a process that evaluates a stream bank's susceptibility to erosion from erosional processes. This method integrates multiple variables that relate to combined erosional processes leading to annual erosion rates. For an assessed bank on a given stream, each variable is evaluated and recorded. The first five variables (bank height divided by bankfull height, root density, surface protection, rooting depth ratio, and slope steepness) are converted to a BEHI score using previously developed relationships (Rosgen, 2006). BEHI relationships are shown in the forms included in Appendix A-1. A visual representation of the variables constituting a BEHI score are shown in Figure 3- 2. 3-2 Root Dendrogeomorphology QAPP " Root Depth _ (D) a a� Bank m Angle ( ' Bankfull Ln =1 �)� ❑ J m LL 5 N o Y � z— a` Start of Bank Figure 3-2 BEHI variables illustrated on a section of stream bank (adapted from Rosgen, 2006) The BEHI scores for each variable have values ranging between 0 and 10. The scores for each variable are totaled and the total score is adjusted based on the type of bank material (i.e., sand, gravel, cobble) and stratification of the bank materials to obtain an overall BEHI risk score (Total Score) that could potentially vary from 5 to 50. The BEHI Total Score is converted to a qualitative rating which is descriptive of the bank erosion risk. Table 3-2 provides a summary of the BEHI scores and ratings. For more information on BEHI procedure, please reference 'A Practical Method of Computing Streambank Erosion Rate' by Rosgen, 2001. Table 3-2 BEHI Scores associated with the Qualitative Rating, as determined by the bank assessment procedure detailed in the BEHI forms located in Appendix B BEHI Total 5 — Score 9.5 BEHI Rating Very Low 10 — 19.5 Low 20 — 29.5 Moderate 30 — 39.5 High 40 — 45 Very High 46 - 50 Extreme 3.3 Sampling Method Requirements The BEHI rating of the streambank and the bank characteristics at the location of the root samples should match the BEHI rating of the streambank and the bank characteristics where the bank pins are located and should have similar near bank stress (NBS) ratings (Table 3-1). A minimum of two roots with a minimum size of one -inch diameter will be cut for any one bank location at least one meter from the tree trunk, with no more than four root samples needed per bank (Dick, 2019). The distance from the bank should be noted, understanding that these samples may need additional analysis to determine the rate if the root has been exposed less than two years. Samples that are still in contact with the bank are acceptable but may have only one or two years of exposure in locations of higher Root Dendrogeomorphology QAPP 3-3 erosion rate. Some of these samples could have been exposed for over a decade, thus obtaining samples that are close to the bank and exposed for several years is ideal. Root bark that is well developed is an indicator of several years of exposure or more and should be used as a determining criterion when selecting roots. Typically, the roots used for comparison to erosion pins will be 0.5 m or less from the existing streambank surface, but this must be determined using judgment and experience. If multiple roots are available, uncertainty in the best samples can be resolved by collecting additional samples at varying distance from the bank and data filtered by years of exposure during the post -processing analysis. The ideal root will have been exposed for a period of time similar to the duration of erosion pin studies, in this case, 6 years of exposure or more is ideal. Thus, data may be filtered for 10 years or less of exposure, and even further refined to 7 years if data is sufficient in sample size at that exposure. Collected root samples should be vertically distributed along the same portion of bank to capture the variability of erosion that is typical from the toe of slope to the top of bank, as illustrated in (Dick, 2019). If multiple roots are not readily available, samples should capture an upper and lower bank location. It is recognized that when comparing to erosion pin data, the scientist must work with what is available in that near vicinity to the erosion pin location. Roots should be collected on the same side of the stream where the bank pins are located and that has a similar BEHI to the erosion pin bank. Figure 3-3 Root sample distribution along bank When determining where to cut the root, avoid cutting near branches or nodes and field verify the root is usable prior to leaving the field. Slower growing hardwood, ring porous tree species such as slippery elm, American elm, hackberry, oak species, hickory species and slower growing softwood species such as red maple, boxelder, and birch with known responses are ideal for collection (Dick, Peszlen, & Peralta, 2014). Likewise, fast growing species such as willow and cottonwood have less obvious responses and should be avoided if possible. Shrub species such as ironwood and privet can be difficult to use, and the response of many species is still being established. American beech has proven to be problematic due to rapid development of fungal growth that renders samples indeterminate and many samples are missing the pith of the root. If intact samples of beech are obtained, they must be samples within a day or two and kept in a freezer anytime they are not being analyzed. Any species can be used and may be cut if there are no other samples available yet prepare to conduct a detailed analysis of those samples (using a 3-4 Root Dendrogeomorphology QAPP microtome and prepared slides) If the tree species is known, the species name will be noted on the paper bag where the root is to be stored and recorded on field notes. The sampled root will be wrapped with flagging multiple times to a tight fit prior to cutting, as the root may experience shrinkage while in the bag and lose the label. 3.4 Sample Handling Requirements During sample collection, it is important to appropriately document, label and store all collected samples. The label shall correspond with the associated bank pins, the stream where the sample was collected, the date which it was sampled, and a unique identifier for that specific bank. The unique identifier should include an abbreviation of the stream name (i.e. Ellerbe Creek would be EC), the date of collection, and the sample number. If more than one sample is collected at a location, the sample should be further identified with a letter. An example of a unique identifier for the first sample collected on January 8th, 2020 along Ellerbe Creek would like the following: EC- 01082020-01-A and the second sample collected in the same bank area will be EC-01082020-01-B. Figure 3-4 illustrates a root sample with the described flagging. Figure 3-4 Roots marked for sampling with flagging tape The bank (right or left looking downstream) and the relative location the sample was collected on the bank (height from toe of slope, distance from the bank, etc.) should be recorded with the notes. Once a bank location is identified for root collection, the roots intended to be cut are to be flagged with a labeled piece of high -visibility flagging tape. When flagging the root, the label shall correspond with the associated bank pins, the stream where the sample was collected, the date which it was sampled, and a unique identifier for that specific bank. Paper bags for each sample are to be prepared with the corresponding label written on the bag in a permanent marker. Paper bags are important for short term storage of samples to avoid fungal development. If analysis of the sample is scheduled 10 or more days after field collection, the sample will be placed in Ziplock bags and stored in a freezer. Once collection is finished at a specific site, all equipment will be cleaned with soap and distilled water to avoid any water quality contamination. Root Dendrogeomorphology QAPP 3-5 3.5 Quality Control Requirements Once returned to the lab, all samples will be stored in labeled bags or boxes corresponding to the sample bank location and section of the root. During analysis, only one sample will be removed from the bag/box at a time to avoid mixing up samples. Wood shavings or microtome samples shall be stored in ventilated, labeled Petri dishes. All notes, observations, and measurements for a sample will include the appropriate label. Figure 3-5 Vented Dish with Example Label 3-6 Root Dendrogeomorphology QAPP 4 Sample Analysis and Data Interpretation 4.1 Preparation of Sample for Analysis Root samples will initially be cleaned with a sharpened, wood chisel. The end of the root will be made flush using the chisel, and then a knife with a fine blade (such as a Havalon-brand Piranta® knife) will be used to clean the root of cut marks. A one -centimeter width disk will be cut from the sample, using a toothless hand saw, for observation under a digital stereoscope (Schweingruber, 2007). If the sample is indiscernible under the stereoscope, a microtome sample (thin slice of material) will be cut using a sliding microtome and mounted on a slide to be viewed under a compound microscope. Root samples needing more detailed analysis will be prepared for microscopic analysis by cutting a one -centimeter disk with a band saw and then dividing the disk into smaller sections along two perpendicular axes in order to provide a complete cross-section of the root (Figure 4-1). This division is accomplished with a chisel to obtain —1cm by —1cm sections. Very thin slices of 10-60 µm width are recommended by Schweingruber (2007) to be cut using the sliding microtome, stained with safranin, grouped together to reconstruct the root section and then permanently mounted on slides. The best procedure for permanent mounting is to place a drop of Canada balsam turpentine on the center of the section, press a cover slip on the top, sandwich the slide between PVC and magnets to prevent buckling, and finally dry in a 60' C oven for 12 hours (Schweingruber, 2007) as seen in Figure 4-2. Figure 4-1 Example of Root Dissection Root Dendrogeomorphology QAPP 4-1 ANA Figure 4-2 Slide sandwiched between PVC and magnets for drying (Schweingruber, 2007) 4.2 Data Interpretation Prepared microscopic sections cut using a sliding microtome, stained with safranin, grouped together to reconstruct the root section, and permanently mounted on slides for archiving are then photographed. Digital images of each microscopic section should be taken using a Nikon SMZ800 stereo microscope, a Nikon Eclipse E200 light microscope, and a Sony DXC-390 CCD camera or equivalent. Using the Inside Wood Database for Stem -Wood Anatomy developed by the College of Natural Resources at North Carolina State University (Inside Wood), a comparison can be made between the documented known cellular structure of an unexposed sample available in the database to that of the exposed sample collected in the field Descriptive wood anatomy identified reliable indicators of exposure including; increases in growth ring width, changes to more pronounced growth ring boundary, ray widening, ray bending, vessel arrangement and frequency, and the occurrence of tension wood in hardwoods. Quantitative wood anatomy results demonstrate that exposed roots presented significant changes in the size and frequency of vessel, fiber lumen area, fiber lumen diameter and double cell wall thickness. The total years of exposure is determined by counting the number of growth rings from the first growth ring demarcating exposure to the bark. From this, the average annual erosion is calculated by dividing the recorded distance from the root to the bank by the total years of exposure for each root (Figure 4-3). 4-2 Root Dendrogeomorphology QAPP CO C in. C -C Annual Growth ring ,--�Exposed Figure 4-3 Illustration of Annual Erosion Measurement (Dick et al. 2014) Root Dendrogeomorphology QAPP 4-3 5 Root Dendrogeomorphology Training Session for City 5.1 Training FNI will provide a short training session for City staff on root dendrogeomorphology field and lab analysis method. The training will include a workshop session/presentation to provide an overview of the methodology, in -field training during sample collection, and lab training during sample analysis. Images of known species responses will be provided and methods for analyzing new species will be discussed. Field methods/ sample selection, handling, preparation, and analysis will be covered. Root Dendrogeomorphology QAPP 5-1 6 Final Report 6.1 Technical Memorandum FNI will provide a final technical memorandum for City staff describing the methodology and findings. The memorandum is anticipated to include a photo log from the field collection, photo documentation of the analyzed root samples, and the analysis and associated finds observed throughout Task 9.2. Root Dendrogeomorphology QAPP 6-1 7 References City of Durham, 2018. Summary of 3-Year Stream Bank Erosion Monitoring Results and Development of Bank Erosion Rate Curves. Durham, NO US. Dick, B.M., Hey, R., Peralta, P., Jewell, I., Simon, P. and Peszlen, I., 2014. Estimating annual riverbank erosion rates — a dendrogeomorphic method. River research and applications, 30(7), pp.845-856. Dick, B. M., Peszlen I., and Peralta, P., 2014. Changes in the Anatomy of Exposed Roots of Some Hardwood Species [PowerPoint slides]. Retrieved from https://www.swst.org/wp/meetings/AM 14/pdfs/presentations/dick%20pdf.pdf Dick, B. M., and Jewell I., 2017. Living Erosion Pins — Streambank and Hillslope Erosion Rate Assessments using Exposed Tree Roots [PowerPoint slides]. Retrieved from http://northcarolina.apwa.net/Content/Chapters/northcarolina.apwa.net/Documents/3%20Living%20Erosi on%20Pins Bryan%20Dick.pdf Dick, B.M., 2019. Getting to the Root of Erosion: Dendrogeomorphology as a Streambank Erosion Assessment Tool [PowerPoint slides]. Retrieved from https://www.freese.com/sites/default/files/OCLWA- 2019 Getting%20to%20the%20Root%20of%20Erosion. pdf Rosgen, D.L., 2001. A practical method of computing streambank erosion rate. In Proceedings of the Seventh Federal Interagency Sedimentation Conference (Vol. 1). Rosgen, D.L., 2006. Watershed assessment of river stability and sediment supply (WARSSS). Wildland Hydrology. Schweingruber, F.H., 2007. Preparation of wood and herb samples for microscopic analysis. Wood Structure and Environment, pp.3-5. The Inside Wood Database n.d.,. Retrieved from https://insidewood.lib.ncsu.edu/search?l1 Root Dendrogeomorphology QAPP 7-1 APPENDIX A-1 BEHI FORM BEHI Variable Worksheet Stream: Reach: Cross Section: Observers: Photos: Date: A Bank Ht D Root Depth Bank HalghuSank#ull Height Rooting OeptWEWnk Height — B Bankfull Ht A Bank Ht x a.s 1 2.5 — — Y � op m 0.6 - -- y 2.I -- C (A/B) E (D/A) 1.5 1 0.2 1 T3 D 5 6,2 9A 10 ° 2 4 a B 9 10 S BEHI & BE HI Root Dona ty srope-Stselpnes& 100 F Root Density 10d G Slope 8 a b b 2 4 $ 6 al 9 to a '; 2 r 4 X 6 S 9W 1Q 9Ew1 BENI Surface Pratectlan Bank Material Adjustment 100 H Surface Bedrock (Overall Very Low BEHI) pi Protection Boulders (Overall Low BEHI) Cobble (-10 pts; No adjustment if sand __ _ gravel matrix > 50% of bank) Gravel (+5-10 pts depending on % sand) zb Sand (+10 points) 0 - Silt/Clay (No adjustment) 0 2, 4 9 6 T. 6 0W10 : 8 T. Stratification Adjustment BENT Add 5-10 points, depending on position of unstable lavers in relation to bankfull staae VERY LOW1 LOW IMODERATO HIGH IVERY HIGH1 EXTREME I ADJECTIVE RATING and 5 - 9.5 1 10 -19.5 1 20 - 29.5 1 30 - 39.5 1 40 - 45 1 46 - 50 TOTAL SCORE A-2 SAMPLE OBSERVATION AND DESCRIPTION FORM DESCRIPTION AND OBSERVATIONS Sample Name: Date: Location: Spp: Bank geometry or buried depth: Diameter: Age: General Notes/Observations: Sketch of growth rings from microsections: A-3 SAMPLE ENVELOPE LABEL TEMPLATE Sample ID: Project: Species: Buried/Exposed: Sample Location: Distance from Bank: Root Sample Inside: ❑ Root Sample ❑ Disk If Neither, Location: Notes: Sample ID: Project: Species: Buried/Exposed: Sample Location: Distance from Bank: Root Sample Inside: ❑ Root Sample ❑ Disk If Neither, Location: Sample ID: Project: Species: Buried/Exposed: Sample Location: Distance from Bank: Root Sample Inside: ❑ Root Sample ❑ Disk If Neither, Location: Notes: Sample ID: Project: Species: Buried/Exposed: Sample Location: Distance from Bank: Root Sample Inside: ❑ Root Sample ❑ Disk If Neither, Location: Notes: Notes: A-4 SAMPLE ID TEMPLATE Sample ID: Species: Buried/Exposed: Partial/Both Sample Location: Distance from Bank: nccu Root Sample Inside: ❑ Yes ❑ No If No, Location: Notes: A-5 Full -Size Overview Map of Root Dendrogeomorphology Sample Locations Lf s�r� Ra I I I I Butner ,,to cR ' tR are Mva y Creednoor rr Eo L Hillshororl9h RP.*rState I v� , r ark �T ------ --- -� -�'' i pF d o Ps Q�rnelr k, A"R prSlr�R,r T S Dwham / r u s. nurna„ R 41 R0 4� o 15 9Jr A4 Rd Nurri Chapel E Hi" CarrhaG I � tTl �� o- ❑Lra+r n f1 6 C fiGNlgryy .LPL a Rn qa ir j d r o- to - i F Lynq An 1; rr pty -------- r3 «! " � o - -9• a E rn u t Lytcn•+4v / a v t�i 4 9 V .21 4 W Cult] Blvd n r`l7r C th _ 0,11 4' yrr a a ❑,rr. a En gi ct4 God Ayc Rry _ d g'L Lawndale Ave - `a n ., tivlia IIAnT Fri�JJ6r a a T W K n ux St r. 8- ❑ CreslSt^ I dq ,ty ° G o r v - n r / � Green St t J Location Overview Map AcOM CITY OF DURHAM DENDROGEOMORPHOLOGY STUDY LEGEND Site Locations Durham City Limits WATERSHED = Crooked Creek Ellerbe Creek = Eno River - Flat River ' Lick Creek = Little Creek = Little Lick Creek Little River Mud Creek New Hope Creek iNortheast Creek ' Panther Creek Sandy Creek Stirrup Iron Creek Third Fork Creek 3 bt 4ry u Green St ,m Or in ��a Sltirle aSr " a _ a } .-•i m C a � plats St a St Ponds and Lakes t-a pus Waik Ave X c der St a to � rn W Markham Ave rcr �� C '� p _ z:---. I f r = Parks tner ouis Eltl� �r r p� Erwin. Rd w c m c 07ic m m urb a i ry avw L �. x � i— — -� County Boundary N :? nlewetF SI 6 zt a Perry St 3 r❑,1 PF Oauan Avr - 0 2,000 D ❑ i? Shelwo fo c M Monw,i 'I ^ . 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Jos a QUri1.7 z _� Ln 3 c apt+l' BJS� ti 4a Ir f .ar _ Carl Ave rn s °err ,.. ....._ 6k Or - �� C a ,tee}. Yancey St -� 5 4crrys a` Grace Ev. Sty yprrnlIAv: Parker :: .y. 4� w s v hlurrllead Avr�..,il, �ri� ` 2 rl Lrperty S! `- rlarlpwdi' R455 Rd M.-.,.. ..,., .. F , '.I.... rnktopkrns $s4 j st n Joyland S¢tt MVu7.0 Avrrinv• W 41 Gci�'rner° r a o �{� t ..I c S v n .I " t, ` # , ,AhDaa- _ _ + r'� ar sr r -i[ 2 r. ,6e, y is r GS s y plkc sr � F _ v51 �podst - D ' W rsGuingat�c S1 y i¢ � N r Rachell,lS U G to Ll F n I c� BiUrvn o Ne'`� °rlry � Q GpttAVe� �ry R.w - - 4 o n r Sr rrya Cr 4 Et V �: n. 4 ds nrJ ti' ; y m a 011oy1 Aye Ava z Mozelfe :'. L D w❑vd 4va� l } trle tyt aRa +• r •aV A - o Long Si x rn c 8rvrrrs I,tts`•,SriLt y A"Ir .Y O n E Main St r 7 rri' 7edale Ave L a r c V r pr+nccSf e• � rtim °plsr ❑ _ Ng '� Hart SS w c r,- F!Irdrnon{ Avu 61d •¢ - p V �yt" �' 'bra Cr esso" A r `araeh ~ a Sr C ❑ } LS O w tl wr v y y arc3 qrP� �„ m U - n P 1 n n obr' m 5 `:rl3uns Sr v - �a Arcr�rr m 'm pr v .' �' 4 y � r_ 11 3 4 � ubGr R d i a C L „�(t S pr' i C W a 1'Ira arq ,� :i d Rd Ar Ka1e ${ a F . Site N o . 1 2 . °"are, u o° � o 'r r� a 00 dRtl a as SWIM A osyPrr r er S x o tvhy ui _"16 � S q c r ' UT to Little Ga •.s r 6 m a v'f ynrl R a r Lick Creek � sb a z Orr i7r A56R a L' n Site N o. Pineview Rd �at'd4 r t S - S C1* �e J Hayes 13 : UT to dp Sandy Creek a� • • � 7s act Dt ,� P"d ty NrJv Brookwood ❑r iP Bexley At - ace ` Prerrr, rd° ndto ° $ LlRay o chester br pr o �R❑� rV l ..,.G'� �+ ewottord Rd Cisco St par9+rersr �i J S a�* Yun r Site No. e � 10 : Third 00 RUr '� ? swrrari • ��Ld s D ❑va Fork Creek f Brooks SprIngdrle L•, v The O o p` �,pihy AveAvc _ _ Bllttlt.l fl s6Ur a °R a° n -- r� WlhOfO&� C _ y �p WIII p{yad! rasofrs ay a CSr .4 r or d q Buxt❑n 5 t A Buxton Or a h. � • r, : �. 4 N -I � r �, • 0 ❑ - ILI e c Larchwvvd Or - '' tyard Lks = ra H a y t7akrrtc -- � O L c / C0 wab .13 o sts att0sd �akg. ,.. t • •rPktwy T I: flu Brown GenturY Os' T °s U n I., icrock Ur a ° e �C 't o Allie t a: �v 1 c 55 nway ❑r m Leed4ri a' 4A, � V N p Q � $ n oral Dr 2 ` 6q psi •or a a1, c Qi 4d a a U o L~ �41rclle Ai CXk Way o ��r R t u` H 76 t�cLo <4 a Langford tL a IJrlrted ❑r 114 "Oa ❑r td 9ty� pc�7r �,.r? rp❑ � � 'l a11e R i d ` 7 °� pP m ypy c'1 �M'drfhrnur•. y �0❑ ❑ `� wi/ ac -fi `7Avr _ on W' 7 yor4s lei a� r04 J h R(! k'Y� . r ;Jyntrssddr r ti 4�+� S`4 r�r, a�s�� c 4 a O Few oati er�4 m c c c9slde Dr Tarr 1 11) # } o t❑0 ' a c C 't]` C't ;-'.ne-aline I_ e s a, gtlxtdn Ln a 0 p� y} o Sh-a a sQ ❑ �c i a Far Df i n t ¢ V p� r U ❑ a ¢ E n❑to d� r h. .Q x R a .. �o* �pn ,`y 'rhd .. . 4 ., G ' 4op c`' J fSan o „ r4 c Q Qs Y q '•' �. r ~� Br ss}3eld %r f ssey [tl _ n 4d Z pr yu G A Q b G n s q A yl� O r Q TWAlckarrder,' If n U 0 7 m U) --i / V 501 / 501 •,,+.,1Vn and A: e Site No. a • 2 : UT to x I, � EI lerbe Creek t , o - 3 to Englewood Ave Everett pl [Julaa Psrh .i l � R Y ❑ [1 l t~J a - g Knax � cedar u Ga 1s, N!r nao Array�� IS G L LT�'a9 Pt� "Sin� S � v r OSph tR Ort6" c 1 �,. ,.,•.. gyp❑ �3 Q �' ' ;,. 7 ern p �esdhall � • 9] a....•. �,tr ... �� �'` .; r❑ a Re0 Werivewoo .i L0 1% R Vol nyu7r[lpl b cir r/p am A rV 71 e,. SI` �l• n cat A +rrS c Rd � a°n rkfr'' r- E Wo crott Pkwy Men rc' - " Rnay Y4Y� QQ n Carpent Flcicher Rd F'arlrHath�p 1 �pssdlary akvey n A440fn V1Arig°� 2 Wlndcrest Rd a A r Ab rj F ' fi Lis° C It ° a trrpCrechking' 1 y .ram, ,kwy quo yL ? b - o Forge Rd 1-� Excha7� �c9 E*`t Mtrrldlan pkv r a �± pt ^vplollian \ . John RfpNc •' ... y Morehe an 1!1 ,s 3 v- a - Lowes Gr 1 t _ - L ti + fl a n a i _ r v - x a M❑�i pl• �_ APPENDIX A-5 Root Sample Photos (Electronic Submission)