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HomeMy WebLinkAbout20210806 Ver 1_Pre-Filing Meeting Request_20210420DWR Pre -Filing Meeting Request Form ID#* Regional Office* Reviewer List* 20210806 Version* 1 Asheville Regional Office - (828) 296-4500 Amy Annino Pre -Filing Meeting Request submitted 4/20/2021 Contact Name * Contact Email Address* Project Name* Project Owner* Project County* Heather Cotton hcotton@marionnc.org Marion Catawba River Greenway Bank Restoration (Zeta) City of Marion McDowell Owner Address: Street Address PO Drawer 700 Address Line 2 City State / Province / Region Marion NC Fbstal / Zip Code Country 28752 United States Is this a transportation project?* r Yes (' No Type(s) of approval sought from the DWR: f7 401 Water Quality Certification - I— 401 Water Quality Certification - Regular Express I— Individual Permit I— Modification F Shoreline Stabilization Does this project have an existing project ID#?* r Yes (' No Do you know the name of the staff member you would like to request a meeting with? No Please give a brief project description below and include location information. * The Catawba River in Marion, North Carolina has experienced significant riverbank erosion after significant rain events and tropical storms. A study was performed by Jennings Environmental PLLC in December 2020 to determine areas in need of bank stabilization and restoration. A copy of the report is attached to this pre -filing request form. The Catawba River Bank Stabilization Plan assessed approximately 6,000 linear feet of riverbank. The upstream extent of the study is located where the Catawba River becomes proximate to the Joseph McDowell Catawba Greenway at Latitude 35.701558, Longitude - 82.049985. The downstream extent is on the eastern side of the US Highway 221 bridge located at Latitude 35.707224, Longitude - 82.036504. Portions of the right (southern) river bank are actively eroding and threatening the integrity of the greenway trail and landscape nursery. Link to more information: https://storymaps. a rcg is. com/stories/b5c7b38e 169449af977a96fa0f3 b25b7 By digitally signing below, I certify that I have read and understood that per the Federal Clean Water Act Section 401 Certification Rule the following statements: • This form completes the requirement of the Pre -Filing Meeting Request in the Clean Water Act Section 401 Certification Rule. • I understand by signing this form that I cannot submit my application until 30 calendar days after this pre -filing meeting request. • I also understand that DWR is not required to respond or grant the meeting request. Your project's thirty -day clock started upon receipt of this application. You will receive notification regarding meeting location and time if a meeting is necessary. You will receive notification when the thirty -day clock has expired, and you can submit an application. Signature Submittal Date 4/20/2021 CATAWBA RIVER BANK STABILIZATION PLAN Joseph McDowell/Catawba River Greenway, Marion, North Carolina Submitted to McDowell Trails Association and City of Marion, North Carolina Jennings Environmental PLLC December 2020 MTA c�9Kc@ Trade 7).ss)-58�`0 fl Jennings Environmental 1. Introduction This report provides the results of a study regarding river bank erosion along the Catawba River in the vicinity of the Joseph McDowell/Catawba River Greenway in Marion, North Carolina. The study includes an assessment of existing conditions and development of a plan for addressing restoration/stabilization of eroding river banks. This report can be used for grant applications and funding allocations to implement an environmental enhancement project. Specifically, the study includes the following tasks: • Analyze existing bank conditions along the Catawba River to identify and map areas of concern for river bank erosion. • Develop conceptual plans and estimated costs for recommended river bank stabilization for each area of concern. • Prioritize implementation of stabilization projects. • Report findings with recommended implementation steps for addressing areas of concern. Overall project objectives are to stabilize river banks and adjacent trails through the application of natural river restoration/stabilization techniques. Long-term benefits to the community would include stable recreational trails, environmental education opportunities, improved environmental quality, and native riparian vegetation. Approximately 6,000 linear feet of river bank are included in this study. The upstream extent is at the location where the Catawba River becomes proximate to the greenway (Latitude 35.701558, Longitude - 82.049985). The downstream extent is on the eastern side of the US Highway 221 bridge (Latitude 35.707224, Longitude -82.036504). Portions of the right (southern) river bank are actively eroding and threatening the integrity of the greenway trail (Figures 1 and 2). Catawba River Bank Stabilization Plan Jennings Environmental PLLC 2 Figure 1. Representative view of river bank erosion adjacent to the greenway (Site 3). Figure 2. Representative view of river bank erosion adjacent to the greenway (Site 6). Catawba River Bank Stabilization Plan Jennings Environmental PLLC 3 2. River Bank Condition Assessment Banks within the study reach of the Catawba River were assessed to document existing morphological conditions, as well as opportunities and constraints that may affect potential management actions. Seven discrete locations of bank erosion were identified and are summarized in Table 1. The attached Appendix includes the following: • Sheet 1: Location map • Sheet 2: Aerial photography and site locations • Sheets 3-9: Conceptual designs and summaries of existing conditions with photos and measured river bank profiles for each site • Sheets 10-13: Typical design details for recommended bank stabilization approaches Table 1. Potential river bank stabilization sites. Site Length (feet) Latitude Longitude Relative Priority 1 220 35.703373 -82.049127 Moderate 2 80 35.703804 -82.049065 Moderate 3 130 35.707009 -82.047038 High 4 240 35.707003 -82.045010 High 5 170 35.706666 -82.043958 Moderate 6 380 35.706811 -82.042919 High 7 20 35.707168 -82.039858 Low Bank profile survey data were collected at the 7 sites. These profiles provide graphical representations of the shapes of the river banks, which allow for visualization of bank heights and bank angles. Figure 3 shows an example of existing and design bank profiles that represents grading of a near -vertical, eroding bank in order to achieve a narrow floodplain bench and stable bank slope. Catawba River Bank Stabilization Plan Jennings Environmental PLLC 4 Site 4 96 95 94 43 Existing — —Conceptual Design / 92 / / 91 90 89 ! 88 87 1 86 85 84 0 5 10 15 20 25 30 35 40 45 50 55 Figure 3. Example bank profiles (Site 4) showing existing and conceptual design conditions. Bank erosion rates and sediment loads were estimated using the BANCS approach (Rosgen, 2001). This approach applies a field estimation of bank erosion hazard based on the Bank Erosion Hazard Index (BEHI) and Near Bank Stress (NBS) at eroding bank locations. Table 2 lists the dominant BEHI and NBS observations, along with estimated erosion rates, for each site. Factors included in this analysis that contribute to river bank erosion and downstream sedimentation include the following: • Channel incision, which prevents flood flows from accessing a floodplain for energy dissipation. Degree of incision is measured using Bank Height Ratio (BHR). • Soil composition (cohesiveness) in the river banks, which determines the ability of the soil to resist erosion scour forces during high flows. • Vegetation root composition (depth and density), which determines the effectiveness of plant roots in enhancing soil resistance to erosive energy. • Bank angle, which determines the susceptibility of banks to slumping and mass wasting during high flows. • Near bank stress (NBS), which relates to accelerated bank erosion where the depth, slope, and velocity of flow increases in channel segments with tight meander bends, deep pools, and transverse bars. NBS is evaluated using radius of curvature ratio and other geomorphic parameters that indicate potential stressful conditions. Catawba River Bank Stabilization Plan Jennings Environmental PLLC 5 Table 2. Estimated river bank erosion rates. Site Dominant BEHI Dominant NBS Erosion Rate (cubic feet/year) Erosion Rate (tons/year) Average Erosion Rate (tons/ year/linear foot) 1 High Moderate 176 7.2 0.03 2 Very High Low 331 13.4 0.17 3 Very High Low 749 30.4 0.23 4 Very High Moderate 746 30.3 0.13 5 High Moderate 155 6.3 0.04 6 Very High Moderate 1982 80.4 0.21 7 High Low 17 0.7 0.03 Sites 1-7 Total 4157 168.6 0.14 At the 7 sites, banks are highly erodible, with BEHI ranging from High to Very High. The NBS ranges from Low to Moderate, as a result of the relative straightness of the river at these locations. The BANCS analysis estimates an average annual sediment contribution of 169 tons from the 1,240 linear feet of river bank that compose these sites. These results should be considered to be general estimates but can be helpful in understanding the relative sediment contribution from each site. These relative observations among the sites can be helpful with prioritization of reaches for potential restoration/stabilization projects. Sites 3, 4, and 6 stand out as the largest contributors to sedimentation within the study area. As a result of this, and proximity of these eroding areas to the greenway, Sites 3, 4, and 6 were assigned a relative priority of 'High'. Sites 1, 2, and 5 were assigned a relative priority of 'Moderate', with Site 7 being 'Low'. 3. River Bank Stabilization Approaches River bank stabilization at these 7 sites along the Catawba River will reduce the volume of sediment eroded from river banks. Additionally, such projects will improve water quality, habitat, and stability of the river and greenway through applying natural river restoration/ stabilization techniques. Long-term benefits to the community would include stable recreational trails, environmental education opportunities, improved environmental quality, and native riparian vegetation. Catawba River Bank Stabilization Plan Jennings Environmental PLLC 6 Suggested stabilization approaches for each of the 7 sites are described below and on Sheets 3 through 9 of the Appendix. Typical design details for bank stabilization components are shown on Sheets 10 through 13 of the Appendix. Although not specifically mentioned in the narratives below, vegetated geolifts are a stabilization approach that could be used at any of the sites, especially in areas where constraints prevent grading river banks to a 3:1 slope. The typical design details in this report conceptual in nature and are NOT FOR CONSTRUCTION. These conceptual plans should be evaluated for further design and permitting efforts. Decisions related to the design approaches and prioritization should be made after a full evaluation of project goals and resources, with input from stakeholders. Site 1 (220 feet): The river bank at Site 1 has eroded to the extent that it could be rebuilt with the toe of slope extending approximately 10 feet further into the river to match upstream and downstream conditions. This additional width for the river bank would allow the trail to remain in its existing location. At the toe of this bank, stacked boulders could be used to armor the bank for approximately 3 vertical feet above and below the water line. Above the boulder toe, the bank should be graded to a stable (3:1 or flatter) slope and lined with biodegradable erosion control matting. As part of the grading, the existing berm at the top of the river bank should be removed. A riparian buffer of native trees, shrubs, and grasses should be planted along the rebuilt river bank. Site 2 (80 feet): At the toe of the existing river bank, stacked boulders could be used to armor the bank for approximately 3 vertical feet above and below the water line. Above the boulder toe, the bank should be graded to a stable (3:1 or flatter) slope and lined with biodegradable erosion control matting. This approach would allow the trail and fence to remain in their existing locations with approximately 8 feet between the trail and rebuilt river bank. A riparian buffer of native trees, shrubs, and grasses should be planted along the river bank. Site 3 (130 feet): At the toe of the existing river bank, stacked boulders could be used to armor the bank for approximately 3 vertical feet above and below the water line. Above the boulder toe, the bank should be graded to a stable (3:1 or flatter) slope and lined with biodegradable erosion control matting. Due to the proximity between the existing trail and eroding bank, approximately 300 feet of the trail would need to be re -aligned at least 10-20 feet away from the river. A riparian buffer of native trees, shrubs, and grasses should be planted along the river bank. Site 4 (240 feet): In addition to eroding river banks, the area of instability at Site 4 includes areas of sediment and debris deposition in places where the bank has retreated. Unlike the other sites, sufficient width is available at Site 4 to include a floodplain bench along the river bank. The stabilization approach could include the construction of a wood toe revetment along the edge of the water. Above this revetment, a floodplain bench of up to 30 feet in width could be graded at the appropriate (i.e., bankfull) elevation. The bank could then be graded to a stable (3:1 or flatter) slope between the bench Catawba River Bank Stabilization Plan Jennings Environmental PLLC 7 and existing ground at the top of bank, then lined with biodegradable erosion control matting. The trail could remain in its existing location. A riparian buffer of native trees, shrubs, and grasses should be planted along the rebuilt river bank. Site 5 (170 feet): Like Site 1, the river bank at Site 5 has eroded to the extent that it could be rebuilt to protrude approximately 10 feet further into the river. This additional width for the river bank would allow the trail to remain in its existing location and provide additional protection for the fishing pier within this reach. At the toe of the bank, stacked boulders could be used to armor the bank for approximately 3 vertical feet above and below the water line. Above the boulder toe, the bank should be graded to a stable (3:1 or flatter) slope and lined with biodegradable erosion control matting. A riparian buffer of native trees, shrubs, and grasses should be planted along the rebuilt river bank. Site 6 (380 feet): At the toe of the existing river bank, stacked boulders could be used to armor the bank for approximately 3 vertical feet above and below the water line. Above the boulder toe, the bank should be graded to a stable (3:1 or flatter) slope and lined with biodegradable erosion control matting. Due to the proximity between the existing trail and eroding bank, approximately 500 feet of the trail would need to be re -aligned at least 30-40 feet away from the river. A riparian buffer of native trees, shrubs, and grasses should be planted along the river bank. Site 7 (20 feet): Site 7 represents a minor area of bank erosion, as compared to the other sites. This area of erosion could be repaired with minor grading, installation of biodegradable erosion control matting, and planting of a riparian buffer of native trees, shrubs, and grasses. Alternately, this area could be repaired using stacked boulders in a way that could also provide a hardened public access point to the river. The trail could remain in its existing location. Non -specified preps (approximately4,800 feet): While these areas did not contain significant river bank erosion, there are still actions that can be taken to promote a healthy riparian buffer and reduce the likelihood of future erosion. As needed, the riparian vegetation in these areas should be enhanced through additional planting of native trees, shrubs, and grasses, as well as removal of any invasive/exotic species. Additionally, the riparian buffer should be allowed to be as wide as possible, given the constraints of the trail location. Catawba River Bank Stabilization Plan Jennings Environmental PLLC 8 4. Cost Estimates, Funding Opportunities, and Permitting Cost Estimates Following are estimated ranges of costs for project implementation, including design, permitting, construction, and planting to achieve river bank stabilization and ecological enhancement objectives: Site 1 (Moderate priority): $35,000 to $60,000 Site 2 (Moderate priority): $15,000 to $35,000 Site 3 (High priority): $20,000 to $40,000 Site 4 (High priority): $30,000 to $55,000 Site 5 (Moderate priority): $25,000 to $45,000 Site 6 (High priority): $45,000 to $90,000 Site 7 (Low priority): $1,000 to $3,000 Cost estimates are based on typical fees for recent projects in western North Carolina. These are broad ranges of costs to be used only for general planning purposes. Cost savings can be incurred by grouping projects together or utilizing City forces and volunteers. Funding Opportunities Potential funding sources for river restoration in North Carolina include the following grant programs, all of which require local matching funds: NC DEQ Water Resources Development Grant Program https://deq.nc.gov/about/divisions/water-resources/water-resources-grants/financial-assistance North Carolina Land and Water Fund https://nclwf.nc.gov/ NC Department of Agriculture and Consumer Services Community Conservation Assistance Program (CCAP) http://www.ncagr.gov/SWC/costshareprograms/CCAP/index.html Other grants available for watershed restoration are described on the NC DEQ web site: https://deq.nc.gov/about/divisions/water-resources/planning/basin-planning/use-restoration- watershed-programs/funding Catawba River Bank Stabilization Plan Jennings Environmental PLLC 9 Permitting River restoration and stabilization projects require permitting at the federal, state, and local levels for environmental and floodplain impacts. Environmental permitting is coordinated by the NC Division of Water Resources and US Army Corps of Engineers using the web -based Pre -Construction Notification (PCN) Form for Nationwide Permits along with corresponding Water Quality Certifications: https://edocs.deq.nc.gov/Forms/Pre-Construction Notification Form Once the application is complete, the Corps will process it within 45 days for a Nationwide or General Permit, and the NC DWR will process the 401 Certification within 60 days. Other permit approvals may be required by NC Wildlife Resources Commission, US Fish & Wildlife Service, and the State Historic Preservation Office. If a Floodplain Development Permit is required, the restoration /stabilization project may require coordination with NC Department of Public Safety Floodplain Management Branch to obtain a "No -Rise" Certification or a Letter of Map Revision (LOMR). Project managers should work closely with permitting agencies to determine specific requirements for implementation. APPENDIX: Sheet 1: Location Map Sheet 2: Aerial Photography and Site Locations Sheet 3: Site 1 Conceptual Designs Sheet 4: Site 2 Conceptual Designs Sheet 5: Site 3 Conceptual Designs Sheet 6: Site 4 Conceptual Designs Sheet 7: Site 5 Conceptual Designs Sheet 8: Site 6 Conceptual Designs Sheet 9: Site 7 Conceptual Designs Sheet 10: Boulder Toe Protection Typical Details Sheet 11: Toe Wood Typical Details Sheet 12: Erosion Control Matting Typical Details Sheet 13: Vegetation Typical Details Catawba River Bank Stabilization Plan Jennings Environmental PLLC 10 Upstream Extent of Study Area Jennings Environmental Location Map 0 200 400 800 1,200 1,600 Feet Downstream Extent of Study Area Catawba River Bank Stabilization Conceptual Planning Marion, North Carolina Sheet 1 Catawba River Bank Stabilization Plan 11 Jennings Environmental PLLC Jennings Environmental Aerial Photography and Site Locations 0 200 400 800 1,200 1,600 Feet Catawba River Bank Stabilization Conceptual Planning Marion, North Carolina Sheet 2 Catawba River Bank Stabilization Plan 12 Jennings Environmental PLLC Site 1 98 97 96 95 — _ _ 9/ / 93 92 / 91 / / / 90 89 / —Existing ee — —Conceptual Design 98 85 -10 -5 0 5 10 15 20 25 ott On streambanks throughout the reach, plant a native riparian buffer of trees and shrubs Rebuild strearnba nk by constructing stacked boulder toe (at 1:1 slope) approximately 10 feet beyond the water line; then fill and grade to top of bank at 3:1 slope Remove existing berm along top of streambank Leave trail in existing location Upstream Extent Downstream Extent (220 linear feet) • Jennings Environmental Site 1 Conceptual Design 0 25 50 100 150 200 Peet Catawba River Bank Stabilization Conceptual Planning Marion, North Carolina Sheet 3 Catawba River Bank Stabilization Plan 13 Jennings Environmental PLLC Site 1 96 97 96 95 94 �� 93 92 i 91 e 90 58 r 1---ixisiing .-� 87 i — -Conceptual Dergn / 56 35 -10 -5 0 5 10 15 20 25 Jennings Environmental On streambanks throughout the reach, plant a native riparian buffer of trees and shrubs Rebuild streambank by constructing stacked boulder toe Cat 1:1 slope) approximately 10 feet beyond the water line; then fill and grade to top of bank at 3:1 slope Remove existing berm along top of streambank Leave trail in existing location Site 1 Conceptual Design 9 25 50 100 150 200 Feet Downstream Etitent (220 4uear leer.) Catawba River Bank Stabilization Conceptual Planning Marion, North Carolina Sheet 3 Catawba River Bank Stabilization Plan 14 Jennings Environmental PLLC Site 2 95 94 83 i 92 ' 91 e 89 44 91 —busting - — -Conceptual DePP•86 es 84 0 5 10 15 20 25 3C On stxe:unbaoks throughout the reach, plant a native rip ari:m hnffer of rrePS and shruhc Rebuild strearnhank by constructing stacked boulder toe (at 1:1 slope) at the water line; then grade to existing ground at 3:1 slope Upstream Extent • +a Dora :mined en Extent 100 linear feet} Leave trail and fence in existing locations Jennings Environmental Site 2 Conceptual Design 0 25 50 100 150 200 Feet Catawba River Bank Stabilization Conceptual Planning Marion, North Carolina Sheet 4 Catawba River Bank Stabilization Plan 15 Jennings Environmental PLLC Jennings Environmental On streambanks throughout the reach, plant a native riparian buffer of trees and shrubs Rebuild streambank by constructing stacked boulder toe (at 1:1 slope) at the water line; then grade to existing ground at 3:1 slope Realign approximately 300 feet of the trail at least 16-20 feet away from srreanibank Site 3 Conceptual Design 0 25 50 100 150 200 Feet Catawba River Bank Stabilization Conceptual Planning Marion, North Carolina Sheet 5 Catawba River Bank Stabilization Plan 16 Jennings Environmental PLLC Site 4 95 ■■MMM ■■■■■■ 94 ■' —Existing ' Fa 3 ■■ niCancePtual Desifln ■ /II. 9 ■■■■■■■■■ IE 91 MOM ■■■■CIE ■■ 3a 89 NI It mu, mar Allia5 VA ■■■■■■►■85 ■■■ 84 0 5 10 15 20 25 30 35 40 45 50 55 Jennings Environmental On streambanks throughout the reach, plant a Native riparian bntfel of trees and shrubs Rebuild streambank by constructing wood toe revetment at the water line; backfill to create bankhall bench up to 30 feet wide; grade from bench to existing ground at 3:1 slope t"psireani Extent Leave trail in existing location 4 llonvt:stcearn Extent �?.{0 Ltic,:r feel) Site 4 Conceptual Design o _ 50 100 150 zoo Feet .fit,.!poor .-, Catawba River Bank Stabilization Conceptual Planning Marion, North Carolina Sheet 6 Catawba River Bank Stabilization Plan 17 Jennings Environmental PLLC Site 5 ■■■I IMEMEM sa 33 ■■■Ifi■■■■ 32 ■■■■■■■Ell ■■31.■■■■■ 91 ■ISi11■■■■■■ ■WI■■■■■■ 88 Fa 36 y■Ia■rmmmm • im■■�-Conceptual�a fin � —Existing 25 -IC 5 10 13 20 25 30 35 Upstream Extent Existing fishing pier Leave trail in existing location On streambanks throughout the reach, plant a native riparian buffer of trees and shrubs Rebuild streauubank by constructing stacked boulder toe (at 1;1 slope) approximately 10 feet beyond the water line; then fill and grade to top of bank at 3:1 slope l Downstream Extent (170 linear feet) •. N... i.- AN. • •- • e -41r nrrtr . Jennings Environmental Site 5 Conceptual Design 0 25 50 100 l50 200 Feet Catawba River Bank Stabilization Conceptual Planning Marion, North Carolina Sheet 7 Catawba River Bank Stabilization Plan 18 Jennings Environmental PLLC 96 35 83 92 91 90 53 47 4g 99 54 43 82 Site 6 r [misting .Conceptual Design 5 10 15 20 25 30 is =� ;4 SI. �.�1s'1tiS1, On streandaanks throughout the reach, plant a native riparian buffer of trees and shrubs Rebuild streambank by constructing stacked boulder toe (at hi slope) at the water line; then grade to existing ground at 3:1 slope Realign approxunately 500 feet of the trail at least 30-40 feet away from streambank 41-424,7454040. Jennings Environmental Site 6 Conceptual Design 0 25 50 100 150 200 Fect Catawba River Bank Stabilization Conceptual Planning Marion, North Carolina Sheet 8 Catawba River Bank Stabilization Plan 19 Jennings Environmental PLLC Jennings Environmental On streatnbanks throughout the reach, plant a native riparian buffer of trees and shrubs Stabilize streambank in place using boulders, possibly stacked to allow for river access Downstrea[n Extent (20 linear feet) Site 7 Conceptual Design 0 25 50 100 150 200 Feet Catawba River Bank Stabilization Conceptual Planning Marion, North Carolina Sheet 9 Catawba River Bank Stabilization Plan 20 Jennings Environmental PLLC SOIL GEOLI1TS TO BANKFULL STAGE #0.,* #704;14. �pp1 oripp**110 lower' A 4001410010111.11111001, ` LIVE CUTTINGS INSTALLED BETWEEN UFTS 20' o.0 D(CAVATI N LIMITS---_� WOOD STAKE -__ 2'x2'xt8'-T6' ---- COMPACTED CARTE BACKFILL FINER GRAVEL AND- { COBBLE BA.061LL _ri�_� 'L APPRO)(IMAIE LOW FLOW WSE OR NC DOT CLASS 1 - RACE BOULDERS =1. DOTING0'1, BED ROCKAPRO)C ELV =1 030' - I M131' ALTER FABRIC BOUT DFRS BOULDER TOE PRO! EL. IIL/ N 7. DETAILED PLAN NOT TO SCALE BOULDER TOE NOTES 1_ ALL 6OULDFRS SHALL BE STRUCTURAL STONE, CUBICAL OR RECTANGULAR IN SHAPE BOULDERS AVAILABLE ONS10E MAY BE USW IF APPROVED BY THE ENGINEER. BOULDERS SHALL BE 3.0' X 5.0' X 25' IOU X L X FB -H5. 0.5'. THE NYNIMUM ACCEPTABLE BOULDER 11-LCKNESS 1M 15 2_0'- BOULDERS LONGER (LI THAN 55' WILL BE ACCEPTED, 2. A BEDDING COURSE CONSISUTIG OF 70% NCOOT 51 Ass 6 AND 3V0 NWOT CLASS A SHALL BE INSTALLED BELOW THE FIRST ROW OF BOULDER'' IF BEDROCK IS ENCOUNTERED ON511E, THE FIRST LIFT OF BOULDERS SHALL BE PLACED DIRECTLY ON THE BEDROCK_ ALL BOULDER'. SHALL FIT TIGHTLY TOGETHER. INSTALL EACH LIFT OF BOULOEFS WITH A 0.5' SETBACK FROM THE FRONT FUDGE OF THE 0*0(0 5 UFTOF BOULDERS. 3. UNCONSOLIDATED GRAVEL AND TOPSOIL SHALL BE INSTALLED AS A IEVEUNG COURSE THE ABOVE BOULDERS BEFORE THE LIVE CUTTINGS ANC SOLE LIFTS 400INSTALLED_ 4. PLACE LAYER OF LIVE CUTTINGS (MIN- 4' LENGTH) A 20. 0G ON THE GRAVEL AND TOPSOIL SUCH THAT APPROXIMATELY 6INCHES TO I FOOT OF EACH LIVE BRANCH WILL BE EIEOSED AND THE REMAINDER Ix TO 4) OF EACH LIVE BRANCH YN LL BE COVERED BY THE SOIL LIFT. LNE BRANCHES SHALL BE OF THE SPECIES SPECIFIED FOR NHE STAKES OR APPROVED BYTHE ENGINEER. 5. INSTALL SOIL UETS FROM THE LIVE CUTTINGS UP TO Tif BANKFULL STAGE. UETS SHALL NOT EXCEED 1,0' THICKNESS. UFTS SHALL INCLUDE ALL SOL PREPARATION, TEMPORARY AND PERMANENT SEEDING AND MULCH. SOIL LIFTS SHALL USE 2 LAYERS OF MATTING: 260Z. / YD' COIL MATTING (OUTER) AND 11.2 OZ/YER COCONUT FIBER BLANKET (INNER). EROSION CONTROL MATTING USED FOR SOIL LIFTS SHALL BE MADE OF 101% NATURAL FIBERS AND MATERIALS AND BE BIODEGRADABLE UNDER NORMAL CUMA.TE CONDITIONS EROSION CONTROL MATTING CONTAINING PLASTICS OR PLASTIC BASED MATERIALS SHALL NOT BE U50 6. PLACE SOIL BACKRLL UP TO 11-E UFT HEIGHT SPEGRED OF NO GREATER THAN 1.0 FT BEING CAREFUL NOT TO PONT BARON INSIDE BEND PUSH/PULL OR TEAR THE FABRIC PREVIOI BLY PLACED_ BNNKRULL NVESTAKIE.S AND BARE ROOT PLANTINGS INSTALL SOIL UFTS UP TO BANKFULL STAGE ay.. 1p16S' SOIL LIFTS SHALL USE 2 LAYERS OF MATTING_ 2602/YD' CCU MATTING (OUTER) AND 11.2 O2Y31 COCONUT FIBER BLANKET (INNER. LNE CUTTINGS BETWEEN LIFTS UNCON5C%1DATED GRAVEL AND TOPSOIL TOP OF BOULDERS ELV - 1,033.5' DETAILED SECTION A - A NOT TO SCALE 7_ REPEAT STETS 04, Y5 AND Y6 AS NEEDED TO INSTALL SOIL LIFTS UP TO THE BANKF ULL STAGE B. THE SU00ACE OF THIS STRUCTURE SHALL BE FIMSFED TO A SMOOTH AND COMPACT SURFACE IN ACCORDANCE WIN THE LINES. GRADES. AND CB056SECTEON5 OR ELEVATIONS SHOWN ON THE DRAWINGS. THE DEGREE OF FINISH FOR ELEVATIONS SHALL BE WITHIN 0.1 FT OF THE GRADES AMU ELEVATIONS INDICATED OR APPROVE? BY THE ENGINEER. 9. REDRESSING OF CHANNEL AND BAER:FULL BENC500100014154 WILL UKELY BE REQUIRED FOLLOWING INSTALLATION OF IN -STREAM STRUCTURES APT SHAM BE CONSIDERED INCIDENTAL TO CONSTIUCNON_ 00 c C E c C 5 5Y CATAWBA RIVER BANK STABILIZATION PLAN DETAIL: BOULDER TOE PROTECTION PRELIMINARY DRAWING ME 1 MOWN tin 10 Catawba River Bank Stabilization Plan 21 Jennings Environmental PLLC SOIL GEOLIFTS TO BANKROLL STAGE f 1 EXCAVATION LIMn1 . _ WOOD STATE 2-X2'X1W-36' - COMPACTED MITE 1 BAO(FILL • • WOODY MATDBAL INSTALLED N 1.0' LIFTS ABOVE LOGS 4 DETAILED PLAN NOT TO SCALE LNECUTTNGI INSTALLED BETWEEN LIFTS 20' 0.0 POINT BARON INSIDE BEND RANKFULL USIE STAKES AND BARE ROOT FIANTINGS INSTALL SOIL UR'S UP TO BANKROLL STAGE ELV = 1,036.0 SOR LIFTS SHALL USE 2 LAYEIS OF MATTING: 260Z ! LLD' COR MATTING IA I.u, ()UTERI) AND 112ODYD' COCONUT METER BLANKET 0NKER)_ �1 uVECUTTINGS BETWEEN LIFTS UNCONSOLIDATED GRAVEL AND TOPSOIL DETAILED SECTION A - A NOT TO SCALE TOP OF TOE WOOD ELV - 1,0315' APPROXIMATE LOW FLOW WSE LOGS WITH ROOTWADS IN1TALUXD AT BASE OF WOODY DEBRIS BASE OF TOE WDOD APPROX. ELV = 1 0280' - 1,0290' TOE WOOD NOTES 1 WOODY MATRON USED IN THE TOE WOOD STRUCTURE SHALL CONSIST OF LOGS, LARGE BRANCHES AND WOOLY DEBRIS RANGING IN DIAMETER FROM 1 • TO 12'_ LARGE VOIDS SHALL BE RUED VHTH FINE \VDDDY MATERIAL AND DEERS. ALL MATERIALS ARE TO BE APPROVED BY TFE ENGINEER A LAYER OF LOGS WRH ROOD WADS INTACT STALL BE INSTALLED ALONG THE BASE OF THE STRUCTURE WOODY MATERIAL SHALL BE INSTALLED IN 1.0' LIFTS. EACH LIFT SHALL BE COMPACTED WITH THE EXCAVATOR BUCKET AND COVERED WTH A LAYER OF A1.LSJ'ALM OR MIXED SOIL AND GRAVEL TO FORM A DENSE LAYER OF WOODY MATERIAL AND ALLUVIAL TO LINES, ELEVATIONS AND GRADES N THE DRAWINGS, 2, UNCGNSOUDATED GRAVEL AND TOPSOIL SHALL BE INSTALLED ABOVE WOODY MATERWL BEFORE THE NNE CUTTINGS AND SOIL LIFTS ARE INSTALLED_ 3_ PUKE LAYER OF LIVE CUTTINGS (MAN_ 4' LENGTH) A 2 U 0 C ON THE GRAVEL AND TOPSOIL SUCH THAT APPROXIMATELY 6 INCHES TO I FOOT OF EACH LIVE BRAN51.1 WILL RE EXPOSED AND THE REMAINDER (2' TO 45 OF EACH LINE BRANCH WILL BE COVERED BY THE SOIL LIFT LIVE BRANCHES SHALL BE OF THE SPECIES SPECIFIED FOR LNE STAKES OR APPROVID BY ILE ENGINEER. 4 INSTALL SOIL LIFTS FROM THE LIVE CUTTINGS UP TO THE BANK/FULL STAGE LIFTS SHALL NOT EXCEED 1 0' THICKNESS. LIFTS SHALL INCLUDE ALL 5OL PREPARATION, TEMPORARY AND PERMANENT SEEDING AND MULCH SOIL LIFTS SHALL USE 2 LAYERS OF MATTING- 2607_ / VD' COIR MATTING (OUTER) AND 11.2 07MD' COCONUT FIBER BLANKET ANNER). EROSION CONTROL MATTING u5ED FOR SOIL UFEB SNAIL BE MADE OF 100% NATURAL FIBERS AND MATERIALS AND BE BIODEGRADABLE UNDER NORMAL CLIMATE CONDTIONS EROSION CONTROL MATTING CONTAINING PLASTICS OR PLASTIC BASED MATFAAL55HALL NOT BE USED. 5. PLACE SOIL BACKFILL UP TO THE LIFT HEIGHT SPECIFIED OF NO GREATER THAN 1.0 FT BEING CAREFIJL NOT TO PUSH/PULL OR TEAR THE FABRIC PREVIOUSLY RACED. 6. REPEAT STEI5R3,e4 AND 45 AS NEEDED TO INSTALL SOIL LIFTS UP TO THE SANIKEUU. STAGE. 7, THE SURFACE OF THIS STRUCTURE SHALL RE FINISHED TO A SMOOTH AND COMPACT SURFACE IN ACCORDANCE WFIH TEE LANES, GRADES, AND CROSS -SECTIONS OR ELEVATIONS SHOWN ON THE DRAWINGS_ THE DEGREE OF FINISH FOR ELEVATIONS SHALL BE WITHIN 0.1 FT OF THE GRADES AND ELEVATIONS INDICATED OR APPROVED SY THE ENGINEER. 8, RE -DRESSING OE CHANNEL AND BANKFULL BENCHYFLOODPLAIN WILL LIKELY BE REQUIRED FOLLOWING INSTALLATION OF IN -STREAM STRUCTURE' AND SHALL BE CONSIDERED INGDENTALTO CONSTRUCTION. CATAWBA RIVER BANK STABILIZATION PLAN DETAIL TOE WOOD PROTECTION PRELIMINARY DRAWING NIS nriala 11 Catawba River Bank Stabilization Plan 22 Jennings Environmental PLLC 4' MIN. HORIZONTAL — OVERLAP BANKFULL TOE OF SLOPE 10001 I;74 :r110f EROSION CONTROL MATTING FROM TOE OF CHANNEL TO 3.0' BEYOND BANKFULL STAGE DETAILED PLAN NOT TO SCALE VERTICAL OVERLAP MIN, 12' WITH DOUBLE ECO-STAKES 2' 11 B 1 ■ B B 1 ■ EDGE OVERLAP MIN. 4' WITH DOUBLE ECO-STAKES AT 2' QC. ■= EROSION CONTROL MATTING k • DETAILED STAKING PLAN BANKFULL STAGE SINGLE 12' ECO-STAKES OFFSET ROWS AT 2'-3'OC. EROSION CONTROL MATTING NOTES 1_ EROSION CONTROL MATTING IS UY-D TO PROTECT RECENTLY CONSTRUCTTD STREAMBANKS FROM EROSION THE MATTING WILL REMAN INTACT WHILE TFE BANK AND RIPARIAN VEGETATION MATURES. PROPIDING CRITICAL BANK PROTECTION_ 2. BEFORE INSTALLING EROSION CONTROL MATTING, RAKE SOIL LEVEL, ADD TEMPORARY AND PERMANENT SEED, SOIL PREPARATION AND MULCH 3, EROSION CONTROL MATTING SHALL BE PLACED ALONG THE LENGTH OF TEE NEW CHANNEL FROM TFE TOE OF SLOPE OJT TO A MINIMUM OF 4.5' BEYOND THE BANKFULL STAGE. 4. SECURE MATTING IN PLACE BY STAKING AND OVERLAPPING AT THE SEEMS WITH A SHINGLE -TYPE METHOD SUCH THAT THE OVERLAPPING PIECE IS IN TIE SAME DIRECTION AND AS THE STREAM FLOW AS SHOWN IN THE DETAIL ADDITIONAL STAKING SHALL BE APPLIED BY THE CONTRACTOR AT NO ALUTTIONAL COST IF THE MATTING SEPARATES FROM THE SOIL MORE THAN ONE INCH UNDER A REASONABLE PULL 5. EROSION CONTROL MATTING SHALL BE MADE OF 1CO% NATURAL FIBERS AND MATERIALS AND BE BIODEGRADABLE UNDER NORMAL CL MATE CONDITIONS . EROSION CONTROL MATTING CONTAINING PLASTICS OR PLASTIC BASED MATERIALS SNAIL NOT BE US®. EROSION CONTROL MATTING 4.5' BANKFULL III `SECURE MATTING WITH ECO-STAKE 4' OVERLAP AND MIN 12' LENGTH DOUBLED ECO-STAKES BURY 6' BELOW STREAMBED DETAILED SECTION A - A' NOT TO SCALE NOT TO SCALE CATAWBA RIVER BANK STABIUZATION PLAN DETAIL: EROSION CONTROL MATTING PRELIMINARY DRAWING 11.1.17,12/09.171. Mr, MIMI 12 Catawba River Bank Stabilization Plan 23 Jennings Environmental PLLC SPAONG PER PlANUNG PLAN 0 INSERT THE DIBBLE STRAIGHT D0VN INFO THE SOIL TO TFE FULL DEPTH OF THE BLADE AND PULL BACK ON THE HANDLE TO OPENT THE PLANTING HOLE. DO NOT ROCK THE SHOVEL BACK ASO FORTH AS THIS CAUSES THE SOIL IN THE RANTING HOLE TO BE COMPACTED, INHIBFIING ROOT GROWTH. BANKFULL TOE OF SLOPE BARE ROOT SEEDLING BANKFULL LJ VE STAKE JUNCUS PLUG BARE ROOT PLANTINGS 3.0' FROM BANK( ULL REMOVE THE DIBBLE INSERT THE CREOLE AND PUSH THE SEVERAL INCHES IN SEEDLING ROOTS DEEP FRONT OF THE INTO TEE PLANTING SEEDLING AND PUSH HOLE PULL THE THE BLADE HALFWAY SFFOIING BACK UP TO INTO THE SOIL TWIST THE CORRECT AND PUSH THE HANDLE PUNTING DEPTH_ THE FORWARD TO CLOSE ROOT COLLAR SHOULD THE TOP OF THE BE 1' - 3' BELOW THE PLANTING HOLE TO SOIL SURFACE GENTLY HOLD THE SEEDLING IN SHAKE THE SEEDLING PLACE TO ALLOW THE ROOTS TO STRAIGHTEN OUT DO NOT TWIST OR SPIV DE SEEDLING OR LEAVE THE ROOTS J-ROOTED_ DIBBLE BAR PLANTING BAR SHALL HAVE A BLADE WITH A TRIANGULAR CROSS-SECTION, AND SHALL BE 12' LONG, 4' WIDE AM) I' 11-INK AT THE GENTS_ ROOT PRIMING ALL ROOTS SHALL BE PRUNED TO AN APPROPRIATE LENGTH FOR PLANTING TO PREVENT .4ROOTIING. PUSH THE DIBBLE 0DWN TO THE FILL DEPTHOF THE BLADE. BARE ROOT DETAILS 3' O.C. LIVE STAKE AND PLUG SPACING / 3' ROW SPACING 0 NOTES 1_ ALL SOILS WITHIN THE BUFFER PLANTING AREA SHALL BE DISKED, AS REQUIRED, PRIOR TO PLANTING. 2_ ALL RANTS SHALL BE HANDLED PROPERLY PRIOR TO INSTALLATION TO ENSURE SURVIVAL Alp PULLBACK ON THE HANDLE TO CLOSE THE BOTTOM OF THE PLANTING HOLE THEN PUSH FORWARD TO CLOSE THE TOP EDMNATING AIR POCKETS AROUND THE ROOT. PLANT LIVE STAKES AND PLUGS IN RRT15 FROM TOE OF SLOPE TO 3' BEYOND THE BAMESILLSTAGE 0 REMOVE ME DIBBLE_ CLILBP AND HRM UP TFE OPENING WITH YOIAF HFEL RE CARERL TO AVOID DAMAGING THE SEEDING. LIVE STAKES AND BAREROOT PLANTINGS IN OFFSET ROWS PER PLANTING PLAN NOTES CONTAINER WIDTH NOTES 1. PLANTS SHALL HAVE BEEN GROWN IN A CONTAINER LONG ENOUGH FOR THE ROOT SYSTEM TO HAVE DEVELOPED SUFFICIENTLY TO HOLD ITS SOIL TOGETHER ONCE REMOVED FROM THE CONTAINER. 2. RANTS WILL NEED TO BE WATERED REGULARLY AND PLACED IN SHADY CONDITIONS UNTIL PLANTING OCCURS 3 THE DIAMETER OF THE PLANTING PITS FOR EACH PLANT S!-OND BE AT LEAST TWO TIMES THE DIAMETER OF THE ROOT MASS SCARIFY THE PLANTING PR PRIOR TO EACH PLANT INSTALLATION_ 4. SET PLANTS UPRIGHT IN THE CENTER OF THE PT THE BOTTOM OF THE ROOT MASS SHOULD BE RESTING ON UNDISTURBED SOIL 5. PLACE BACKHLL AROUND LASE AND SIDES OF ROOT MASS, AND WORK FpGI LAYER TO SETTLE BACXHLL AND TO RUMINATE VOIDS AND AIR POCKETS_ WHEN PIT 5 APPROXIMATELY FULL, WATER THOROUGHLY BEFORE PLACING REMAINDER OF THE BAC-KELL WATER AGAIN AFTER PLACING FINAL LAYER OF B4CKHLL SECTION A - A' CONTAINER PLANT DETAILS 1 30 2DIAMR 2'TO BLNESTAKE TAPERED AT BOTTOM LNE STAKE 1. WE STAKE MUST BE DORMANT WHEN CUT. KEEP LIVE STaSES MOIST UNTIL RANTING. THE STAKE SHOULD BE PREPARED WTH THE BIAS POINTED UP, AND THE BOTTOM SHOULD BE CUT AT AN ANGLE FOR INSERTION INTO THE GROUND. AN IRON BAR CAN BE USED TO MAKE A PLOT HOLE TO PREVENT BARK FROM BEING DAMAGED DURING INSTALLATION. 2 LIVE STAKES SHALL BE 0.5'- 2` IN DIAMETER AND 2'-3' IN LENGTH. 3, IJVE STAKES SHOULD BE PLACED WITH TO OF E-E LENGTH OF TEE STAKE BELOW GROUND AND ANGLED DOWNSTREAM ENSURE THE BASE OF THE LNE STAKE WILL REACH TFE WATER TABLE AFTER INSTALLATION THE TOP OF TFE LIVE STAKE SHALL BE PRUNED VHTH A SQUARE OJT LEASING NO LESS THAN 3' AND NO LESS THAN 6' ABOVE THE GROUND. 4. PLANTUVE STAKES AND JUNCUS PLUGS IN OFFSET ROWS AND SPACINGS PER RANTING PLAN, LIVE STAKING DETAILS �¢8 CATAWBA RIVER BANK STABILIZATION PLAN VEGETATION DETAILS PRELIMINARY DRAWING Drat emwaw wRw 13 Catawba River Bank Stabilization Plan 24 Jennings Environmental PLLC