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HomeMy WebLinkAbout20160804 Ver 1_Revised Consistency Determination_20170125Burdette, Jennifer a From: Hughes, Emily B CIV USARMY CESAW (US) < Emily.B.Hughes@usace.army.mil > Sent: Wednesday, January 25, 2017 8:37 AM To: Govoni, Daniel Cc: Burdette, Jennifer a Subject: Eagle Is Dike Raise revised consistency determination_23Jan2017FINAL.docx Attachments: SIGNED_Eagle Island Dike Raise -Revised Consistency Determination_Jan2017.pdf Daniel, Please see attached revised consistency determination for the Eagle Island Improvement Project. A hard copy will go out I the mail today. The 401 application is pending an analysis of temporary impacts, and will be submitted to the State as soon as this is complete. Thank you for your time and consideration. Sincerely, Emily Environmental Resources Specialist Planning Section, Wilmington District US Army Corps of Engineers 69 Darlington Ave. Wilmington, NC 28403 (910) 251-4635 Emily.b.hughes@usace.army.mil 1 O Gyrrf STAPES OF �Mp,`P Environmental Resources Section Mr. Daniel Govoni DEPARTMENT OF THE ARMY WILMINGTON DISTRICT, CORPS OF ENGINEERS 69 DARLINGTON AVENUE WILMINGTON, NORTH CAROLINA 28403-1343 January 24, 2017 North Carolina Department of Environment and Natural Resources Division of Coastal Management 400 Commerce Avenue Morehead City, North Carolina 28557 Dear Mr. Govoni: As you are aware, the U.S. Army Corps of Engineers (Corps), Wilmington District, proposes the construction of dike raises to elevation 50 feet NAVD88 for Cells 1-3 on Eagle Island in the Cape Fear River, New Hanover and Brunswick Counties, North Carolina. The project location is shown on Figure 1 and the project area is shown on Figure 2. The Corps initially submitted a consistency determination to your office on July 28, 2016, in tandem with the release of the project's draft Environmental Assessment (EA). Our office received comments from the North Carolina Division of Coastal Management (NCDCM) requesting information on the impacts to coastal wetlands and the location of mean high water (MHW). In response to this, the Corps coordinated with Ms. Heather Coats, NCDCM permit coordinator, to conduct a site visit to specifically identify the areas of concern. Maps classifying vegetation types within the impact areas were provided which also identified the MHW line (2 -foot elevation contour). On September 16, 2016, the Corps and NCDCM met onsite and utilized the maps to ascertain coastal wetland impacts, which were also supported with 2015 ground photography of these locations. The initial mitigation plan that accompanied the draft EA proposed purchasing 3.04 acres of coastal wetland credits from the North Carolina Division of Mitigation Services to offset impacts to approximately 39 acres of tidal wetlands. Impacts have since been recalculated and final impacts associated with the toe berm construction are 35.45 acres of Phragmites-dominated tidal freshwater marsh, of which 2.85 acres are located below the MHW line. Impact areas are shown on Figure 3. The mitigation plan has been revised to include the purchase of 35.5 credits of riparian/tidal freshwater marsh from the Lower Cape Fear Umbrella Mitigation Bank, Sneeden Tract, located in the same Hydrologic Unit Code as the project. In accordance with Section 307 (c)(1) of the Federal Coastal Zone Management Act of 1972, as amended, the Corps has determined that the proposed construction of the dike raises and toe berm is consistent, to the maximum extent practicable, with North Carolina's Coastal -2 - Management Program. This determination is based on the review of the proposed project against the enforceable policies of the State's coastal management program, which are principally found in Chapter 7 of Title 15A of North Carolina's Administrative Code. Enclosed are the details of the revised consistency determination, which contains project plans and a supportive narrative. We request that the NCDCM concur with this revised consistency determination. Should you have any questions or require additional information, please contact Ms. Emily Hughes, Environmental Resources Section, at telephone (910) 251-4635 or by email at emily.b.hughes@usace.anny.mil. Sincerely, Jennifer L. Owens Chief, Environmental Resources Section Enclosure CONSISTENCY DETERMINATION FOR WILMINGTON DISTRICT U.S. ARMY CORPS OF ENGINEERS Eagle Island Improvements, Dike Raise to Elevation 50 Feet Cape Fear River, New Hanover and Brunswick Counties, North Carolina L Proposed Project Description The U.S. Army Corps of Engineers (USACE) proposes the construction of dike raises to elevation 50 feet NAVD88 for Cells 1-3 on Eagle Island in the Cape Fear River, New Hanover and Brunswick Counties, North Carolina. To ensure dike stability, the 50 -foot dike raise will require a supportive outer toe berm. This toe berm is projected to impact 35.45 acres of Phragmites-dominated tidal freshwater marsh. The proposed dike raise will increase disposal capacity approximately 16 years. The project area is shown on Figure 2. IL Background Wilmington Harbor, located on North Carolina's southeast coast, is one of the state's two deep- water ports and a major contributor to its economy. The Wilmington Harbor project connects deep water of the Atlantic Ocean with port facilities at Wilmington by way of a 38 -mile -long channel along the Cape Fear River. The USACE, Wilmington District, is responsible for maintaining the federally -authorized Wilmington Harbor navigation project. The primary disposal facility for dredged material from the Upper Harbor reaches of the Wilmington Harbor is the Eagle Island Confined Disposal Facility (CDF), which is located on the peninsula between the Cape Fear and Brunswick Rivers, south of U.S. Highway 74/76 (Figure 2). Improvements at the Eagle Island CDF are required to provide adequate dredged material disposal capacity for continued maintenance dredging of the Wilmington Harbor navigation project. III. Existing Conditions The Eagle Island CDF, which has been the primary disposal site for this dredged material, is rapidly filling up. Phase I of the Eagle Island Dike Improvement Project is currently underway. Phase I includes the increase of the dike heights at each of the 3 cells. The existing dikes on Cell 1 have been raised to elevation 40 feet (NAVD 88), and Cells 2 and 3 are being raised to 42 feet (NAVD 88). Cell 1 is complete and Cells 2 and 3 will be under construction through the summer of 2018. These dike raises will not increase the footprint of Eagle Island, rather, they will be done with dike step-ins and raises to the interior of the existing dikes. Although these improvements will increase disposal capacity, the increased capacity will only last approximately 5-6 years (allowing for at most another 6 dredging and disposal cycles). Therefore, the need remains for additional dredged material disposal capacity for the Upper Harbor reaches, beyond the dike raises currently underway. IV. Alternatives Analysis As documented in the EA, the only other potentially feasible alternative to the proposed project (constructing of dike raises and toe berms) is the no action alternative. All alternatives considered are described in the EA and the no action alternative is discussed below. The No Action Alternative: The No Action alternative would be the continuance of currently utilized disposal practices at Eagle Island and completion of the current dike raises at Cells 2 and 3 to elevation 42 feet NAVD 88. The Cell 1 dike cannot be raised above 40 feet without the construction of toe berms. Dike raises at Cells 2 and 3 to 42 feet NAVD 88 are being done with step-ins to the interior of the dike. Since toe berms are not required for this raise, the overall footprint would not change. These improvements will add approximately one year of capacity for a total of six years of volume life at Eagle Island. Beyond that time, Eagle Island will no longer have the capacity to accept dredged material. Therefore, dredging projects that previously disposed of dredged material at Eagle Island will require transport to another approved disposal location. Currently, the only disposal area suitable for this fine-grained dredged material is the Wilmington Ocean Dredged Material Disposal Site (ODMDS). The ODMDS is located in the Atlantic Ocean, offshore of the mouth of the Cape Fear River, approximately 38 miles from the upper reaches of the Wilmington Harbor navigation proj ect. V. Resource Agency Coordination The USACE informally coordinated the proposal with local and state agencies early in the design process. A scoping meeting and site visit were held on March 4, 2015, with the North Carolina Division of Coastal Management (DCM), the North Carolina Division of Water Resources (DWR), the U.S. Fish and Wildlife Service (USFWS), the National Marine Fisheries Service (NMFS), the North Carolina Division of Marine Fisheries (DMF), and the North Carolina Wildlife Resources Commission (WRC). The purpose was to discuss the proposed project and to assess the potential impact areas for mitigation. A scoping letter was sent on April 17, 2015, to representatives of the agencies above, as well as, the North Carolina Division of Cultural Resources. This allowed for a 30 -day comment period on the project to solicit comments on the proposed project and the mitigation proposal. In addition, a teleconference was held on April 20, 2015, between the North Carolina Division of Mitigation Services (NCDMS) and the USACE. No comments were received on the proposed project design or mitigation proposal during the scoping process. A draft EA was prepared and the Public Notice was issued July 29, 2016. The draft EA has been reviewed by all state, federal and local resource agencies and all comments received are being addressed in the final EA. 2 VI. Mitigation _ The USACE has conducted several coordination meetings with state and federal resource agencies regarding appropriate mitigation to offset the impacts of the proposed fill. The 35.45 acres of impact are to Phragmites-dominated tidal freshwater marsh. Phragmites are a non- native aggressive wetland plant that outcompetes native spartina alterniflora and patens, typha and juncus. As a monoculture, Phragmites provide little habitat and food source for native species. Because of the lessened adverse environmental impact of filling Phragmites-dominated marsh, the USACE has determined that a set ratio of 1:1 wetland mitigation is sufficient to offset the impacts of the proposed project. The USACE has coordinated with the Lower Cape Fear Umbrella Mitigation Bank (LCFUMB) to determine the availability of 35.5 credits of riverine/freshwater tidal marsh at their Sneeden Tract, which is located 5 miles upstream of the project site. Through this process, the USACE would purchase these credits to offset the loss of wetland function and value of the 35.45 acres of impacts. This mitigation proposal, revised from the original proposal to purchase 3.04 credits of coastal marsh through the NCDMS In -Lieu Fee Program, has been coordinated with the USFWS, NMFS and the WRC, and it was determined that this would mitigate for the loss of Phragmites wetlands associated with the toe berm construction. VII. Areas of Environmental Concern The project area is located in the Cape Fear River and is an area of environmental concern (AEC) as defined by Section 113A-113 of the North Carolina Coastal Area Management Act (CAMA). Specifically, the proposed project will be occurring in the estuarine waters and public trust waters AECs. The DWR classifies the Cape Fear River at the project site as SA, HQW and the Brunswick River as SC. The classification definitions are: • Class SA = Tidal salt waters that are used for commercial shellfishing or marketing purposes. All SA waters are also HQW by supplemental classification. • Class SC = All tidal salt waters protected for secondary recreation such as fishing, boating, and other activities involving minimal skin contact, fish and noncommercial shellfish consumption, aquatic life propagation and survival, and wildlife. • High Quality Waters (HQW) = Supplemental classification intended to protect waters, which are rated excellent based on biological and physical/chemical characteristics, through Division monitoring or special studies, primary and other functional nursery areas designated by the Marine Fisheries Commission. The DMF has classified the project area as a Primary Nursery Area (PNA) (15A NCAC 07H .0208(a)(4)) and secondary nursery areas defined by rule 15 NCAC 3N .0102(c). The PNA within the project area has been identified by the Mean High Water (MHW) line, which is also the 2 -foot elevation contour. The construction of toe berms would impact approximately 2.85 acres of PNA tidal area waterward of MHW surrounding Eagle Island; the majority being on the west side adjacent to the Brunswick River (Figure 3). To avoid impacts to fisheries within the 3 PNA areas, every effort will be made to construct the toe berms outside of the April 1- July 31 anadromous fish window proposed by NMFS in their email dated November 22, 2016. This should protect species from turbidity and acoustic effects of construction during their upriver migration. If construction cannot be limited to this timeframe, coordination with environmental agencies will occur prior to work within these areas. There is no submerged aquatic vegetation (SAV) adjacent to the proposed toe berms or any adjacent areas in the Cape Fear or Brunswick Rivers. Shellfish beds are present in the Cape Fear Estuary; however, they are primarily south of Snows Cut (Woodward -Clyde Consultants 1980), which is several miles south of the area of potential effect for the proposed Eagle Island CDF improvements. Therefore, the proposed action is not expected to impact shellfish beds (15A NCAC .0208(a)(2)). The project site is not designated as a "Natural and Cultural Resources Area" (15A NCAC 07H.0501). There are no known cultural resources within the project's area of effect; therefore, the project is not likely to impact cultural resources. Any cultural resources encountered during construction would be protected and upon discovery; rapid coordination with the USACE and the North Carolina Department of Cultural Resources, Underwater Archaeology Unit would occur. VIII. Project Conformance with New Hanover and Brunswick Counties and Local Land Use Plans The North Carolina Coastal Area Management Act of 1974 was passed in accordance with the Federal Coastal Zone Management Act. It requires each of the 20 coastal counties to have a local land use plan in accordance with guidelines established by the North Carolina Coastal Resources Commission. Each land use plan includes local policies that address growth issues such as: the protection of productive resources (i.e., farmland, forest resources, and fisheries), desired types of economic development, natural resource protection, and the reduction of storm hazards. The proposal complies with the Brunswick and New Hanover County Land Use Plans (LUPs) and their goals for developing in accordance with the requirements of CAMA. Both counties are experiencing rapidly increasing development and economic growth, yet are committed to protecting water quality, including all coastal wetlands, rivers, streams, and estuaries. IX. Analysis of the Project in Relation to North Carolina's Coastal Management Program 15A NCAC 07H .0203 identifies the Management Objective of the Estuarine and Ocean System: It is the objective of the Coastal Resources Commission to conserve and manage estuarine waters, coastal wetlands, public trust areas, and estuarine and public trust shorelines, as an interrelated group ofAECs, so as to safeguard and perpetuate their biological, social, economic, and aesthetic values and to ensure that development occurring within these AECs is compatible with natural characteristics so as to minimize the likelihood of significant loss of private M property and public resources. Furthermore, it is the objective of the Coastal Resources Commission to protect present common-law and statutory public rights of access to the lands and waters of the coastal area. The project will not result in the loss of coastal uses. Construction of this project will not result in significant impacts to coastal resources or prohibit access to coastal resources by the public. Completion of the dike raise and associated toe berms will allow future maintenance of the upper Wilmington Harbor to be more feasible, keeping these areas accessible. 15A NCAC 07H.0206 identifies the Management Objective of Estuarine Waters: To conserve and manage the important features of estuarine waters so as to safeguard and perpetuate their biological, social, aesthetic, and economic values; to coordinate and establish a management system capable of conserving and utilizing estuarine waters so as to maximize their benefits to man and the estuarine and ocean system. This section also identifies the Use Standards for Estuarine Waters: Suitable land/water uses shall be those consistent with the management objectives in this Rule. Highest priority of use shall be allocated to the conservation of estuarine waters and their vital components. Second priority of estuarine waters use shall be given to those types of development activities that require water access and use which cannot function elsewhere such as simple access channels; structures to prevent erosion; navigation channels; boat docks, marinas, piers, wharfs, and mooring pilings. The project does not violate the management objective and use standards for estuarine waters in that it involves construction of toe berms to support the improvements of the CDF. Construction of this project will not have a long-term adverse impact on the estuarine waters. Completion of the toe berms will permanently impact 35.45 acres of Phragmites-dominated tidal freshwater marsh, which will be mitigated through the purchase of 35.5 acres of credits from the LCFUMB, Sneeden Tract. 15A NCAC 07H.0207 identifies the Management Objective of Public Trust Waters: To protect public rights for navigation and recreation and to conserve and manage the public trust areas so as to safeguard and perpetuate their biological, economic and aesthetic value. The project will not result in the loss of coastal uses. Construction of this project will not result in significant impacts to coastal resources or prohibit access to coastal resources by the public. Completion of the project will allow for prolonged disposal in the CDF so maintenance of the federal navigation channel can continue in the most feasible way. 15A NCAC 07H .0209 (c)(2) identifies the Management Objectives for Coastal Shorelines: The management objective is to ensure that shoreline development is compatible with the dynamic nature of coastal shorelines as well as the values and the management objectives of the estuarine and ocean system. Other objectives are to conserve and manage the important natural features of the estuarine and ocean system so as to safeguard and perpetuate their biological, social, aesthetic, and economic values; to coordinate and establish a management system capable of k' conserving and utilizing these shorelines so as to maximize their benefits to the estuarine and ocean system and the people of North Carolina. The proposed project meets the listed management objectives. The project has been designed to minimize/avoid adverse environmental impacts, as addressed above. X. Other Required Approvals No permits, authorizations, or approvals other than NCDCM concurrence with this consistency determination are necessary at this time. A Section 401 General Certificate (GC) under the Clean Water Act of 1977 (P.L. 95-217), as amended, is required for the proposed action, and will be obtained from the North Carolina Department of Environmental Quality (DEQ) before construction begins. XI. Conclusions The proposed project conforms to the management objectives of 15A NCAC 07H .0203, 15A NCAC 07H .0206, and 15A NCAC 07H .0209; it will not adversely impact Estuarine Waters and Public Trust Areas. The proposed project will not affect any wildlife recognized by the State as species of concern, will not adversely impact water quality, and will result in minimal, temporary, and short-lived impacts to fisheries and the aquatic habitat. The proposed project will be undertaken in compliance with all conditions of DCM recommendations based on concurrence with this consistency determination. Adherence to these conditions and recommendations will further minimize adverse biological and environmental impacts to the maximum extent practicable. 0 Figure 1. Project Location t z lit Cell 3 •' - : L' 4 Vii: _ �agie Asiana- ..t J, _ � 3 •Ii�TJ• .i'., y�-1 V ro 'ham r' T City of WilrrliQgton y Brunswick County i New Hahoyer'County,, _ �. s Cell 1 t: Perimeter r + Containment ,�~ z Dike , ��' r •a 1 , 14 0 • � +• � �r .. '-. UlarkS ISland _ *e Tour Gvilt 7893 Imagery nate: lON874 34°13'I0.58' Hr77�59'5fi.82''W gl2g,ReKe aR 19412 R Q Figure 3. Footprint of the 50' Toe Berms Showing Impacts to Vegetation Type and Areas Below Mean High Water