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HomeMy WebLinkAbout20040561 Ver 4_Other Agency Correspondence_20200609Strickland, Bev From: Deaton, Anne Sent: Tuesday, June 9, 2020 10:52 AM To: Mairs, Robb L Subject: RE: Bald Head Island Major Mod Nourishment w Frying Pan Shoals Attachments: USACE_BHI Frying Pan Shoals _NCWRC 2017.pdf, VBHI JBS Renourishment Comments Signed CW2017.pdf, VBHI-Frying PanShoals_2012-00040_3aLetter_FINAL_09 NMFS Mar20l7.pdf Here they are. Also NMFSs. From: Mairs, Robb L Sent: Tuesday, June 9, 2020 10:39 AM To: Deaton, Anne <anne.deaton@ncdenr.gov> Subject: RE: Bald Head Island Major Mod Nourishment w Frying Pan Shoals Yeah, I'm not sure on all that, but he indicated it was elevated to headquarters. Do you have the 2017 DMF or WRC comments as well? From: Deaton, Anne Sent: Tuesday, June 9, 2020 10:13 AM To: Mairs, Robb L <robb.mairs@ncdenr.gov> Subject: RE: Bald Head Island Major Mod Nourishment w Frying Pan Shoals Hmm. I think Twyla told me the Corps wasn't passing along to them. Anne From: Mairs, Robb L Sent: Tuesday, June 9, 2020 9:28 AM To: Deaton, Anne <anne.deaton@ncdenr.gov> Subject: RE: Bald Head Island Major Mod Nourishment w Frying Pan Shoals I'm just getting up to speed on the project, and eventually found out who's handling the project with the Corps. I heard from Ronnie Smith that this was elevated up to headquarters, and NMFS was involved. From: Deaton, Anne Sent: Tuesday, June 9, 2020 9:13 AM To: Mairs, Robb L <robb.mairs@ncdenr.gov> Subject: RE: Bald Head Island Major Mod Nourishment w Frying Pan Shoals NMFS isn't commenting! From: Mairs, Robb L Sent: Tuesday, June 9, 2020 9:12 AM To: Deaton, Anne <anne.deaton@ncdenr.gov> Subject: RE: Bald Head Island Major Mod Nourishment w Frying Pan Shoals Thanks Anne. From: Deaton, Anne Sent: Tuesday, June 9, 2020 9:11 AM To: Mairs, Robb L <robb.mairs@ncdenr.gov> Subject: FW: Bald Head Island Major Mod Nourishment w Frying Pan Shoals From: Deaton, Anne Sent: Friday, June 5, 2020 2:31 PM To: Coats, Heather <heather.coats@ncdenr.gov> Cc: Murphey, Steve <steve.murphev@ncdenr.gov>; Lupton, Dee <dee.lupton@ncdenr.gov>; Davis, Braxton C <Braxton. Davis@ WIDEN R.Gov> Subject: Bald Head Island Major Mod Nourishment w Frying Pan Shoals Comments from NCDMF are attached. Anne Anne Deaton rlakitat anc F nkancement,-jection NC Division of urine Fisheries anne.cleaton@ncJenr.i�!ov 910-796-751 1 4D Email correspondence to and from this address is subject to the North Carolina Public Records Law and may be disclosed to third parties. Cf North Carolina Wildlife Resources Commission 9 Gordon Myers, Executive Director MEMORANDUM TO: Ronnie Smith US Army Corps of Engineers, Wilmington District And Karen Higgins NC Division of Water Resources FROM: Maria T. Dunn, Coastal Coordinator Habitat Conservation Division DATE: March 9, 2017 SUBJECT: Public Notice for Village of Bald Head Island, Frying Pan Shoals Project, Brunswick County, North Carolina. SAW-2012-00040 Biologists with the North Carolina Wildlife Resources Commission (NCWRC) reviewed the public notice with regard to impacts on fish and wildlife resources. Our comments are provided in accordance with provisions of the Coastal Area Management Act (G.S. I I3A-100 through I I3A-128), as amended, Sections 401 and 404 of the Clean Water Act, as amended, and the Fish and Wildlife Coordination Act (48 Stat. 401, as amended; 16 U.S.C. 661 et seq.). The Village of Bald Head Island is proposing to perform groin fillet maintenance and beach nourishment along the shoreline of Bald Head Island, including West Beach and South Beach, with material dredged from Frying Pan Shoals. This site proposal would be for the current request as well as future nourishment events. An approximate 460-acre source site has been identified on the western side of Frying Pan Shoals, approximately 1 mile offshore of Bald Head Island. Sediment identified would be excavated by cutter head dredge and pumped to shore, providing an overall site capacity of 5.2 million cubic yards. Within this borrow area is a 9.73 exclusion zone to address historic properties / cultural resources. Physical monitoring of the dredge borrow site would be monitored immediately after construction, annually for three years, and biennially afterward. The footprint of each monitoring survey would include the entire permitted site as well as the area of excavation within and any changes in morphology to the Frying Pan Shoals formation. This current proposal is stated to be phase two of the terminal groin installation project. Although we understand that the initial proposal included nourishment to accompany the groin, information should be Mailing Address: Habitat Conservation • 1721 Mail Service Center • Raleigh, NC 27699-1721 Telephone: (919) 707-0220 • Fax: (919) 707-0028 Bald Head Island, Frying Pan Shoals Page 2 March 9, 2017 provided to show the need for the nourishment after structure construction. It may be that the structure has not been in place long enough to accurately model sediment transport and need for nourishment. This is of importance due to environmental impacts to the sediment borrow source and oceanfront beaches during nourishment activities. Frying Pan Shoals provides important marine fishery habitat. Removal of material from this area may alter these habitat areas significantly. Although the NCWRC generally voices concern with impacts to more anadromous, estuarine, and inland fish species, we strongly encourage the applicant and permitting agencies to coordinate with and incorporate concerns and management practices recommended by state and federal marine resource agencies. Independent of source material location and sediment compatibility, projects that affect oceanfront beaches and natural inlet processes such as beach nourishment, inlet dredging, inlet relocation and the construction of hardened structures on or along beaches may adversely affect nesting sea turtles and shorebird foraging and nesting areas. Due to the scope of this project and the documented use of the beaches by sea turtles and shorebirds, the NCWRC has the following comments and recommendations: — The NCWRC has an established sea turtle nesting moratorium that reduces the potential for unintended impacts to nesting sea turtle species that frequent the coast of North Carolina. To avoid impacts to these species, all work on the oceanfront shoreline, including mobilization and demobilization for all beach nourishment events should be conducted outside of the sea turtle nesting season which runs from May 1 until November 15, or until the last known sea turtle nest has hatched. — Oceanfront beaches on Bald Head Island provide suitable nesting, foraging and roosting areas for multiple shorebird species. Nesting birds are sensitive to increased human activity and other disturbances around their nesting areas. To limit unintended impacts to nesting bird species in and near the project area, all work should adhere to the shorebird nesting period from April 1 until August 31. — Survey and monitoring reports should be provided to the appropriate parties in a timely manner and consultation should be done with regulatory and resources agencies prior to ceasing or changing any survey or monitoring activity. — As stated in our comments provided during the review of the terminal groin application, regular nourishment events could potentially impact benthic invertebrate populations Benthic invertebrates are an important food source for foraging birds, both resident and migratory, during both the breeding and nonbreeding seasons. Regular beach nourishment events, such as every five years, can reduce benthic populations when populations are not given appropriate time for recovery. Thank you for the opportunity to review and comment on this public notice. Please feel free to contact me at (252) 948-3916 or at maria.dunn(kncwildlife.org if there are any questions or comments pertaining to this project. ROY COOPER Governor It MICHAEL S. REGAN Secretary " BRAXTON DAVIS coastat anagoment Director ENWROFl MENTAL QUALITY MEMORANDUM: TO: Heather Coats, DCM Assistant Major Permit Coordinator THROUGH: Doug Huggett, DCM Major Permits Coordinator FROM: Curt Weychert, DCM Fisheries Resource Specialist SUBJECT: Village of Bald Head Island/Frying Pan Shoals DATE: July 6, 2017 A North Carolina Division of Coastal Management (DCM) Fisheries Resource Specialist has reviewed the subject permit application for proposed actions that impact fish and fish habitats. The applicant has identified a 472-acre sand borrow site located on Frying Pan Shoals to discharge the dredged material along the shoreline of Bald Head Island, including West Beach and South Beach, for groin fillet maintenance and beach nourishment. The applicant currently has a permit that authorizes the use of Jay Bird Shoals for groin fillet maintenance and beach nourishment in cases where the applicant could demonstrate the dredging fill material from the federal channel to the Cape Fear was not practicable. The applicant has identified an approximately 472-acre area along the western edge of Frying Pan Shoals approximately 1 mile off the southeast shoreline of Bald Head Island. Material would be excavated by a cutter suction dredge and pumped by submerge pipeline to the South Beach shoreline. The sand volume to -20' NAVD 88 would yield 5.2 million yards and the sand volume to -25' NAVD88 is 8.5 million yards. The applicant also proposes to cut a fairway into the western side of the proposed borrow site from the -20' contour. The width of this fairway would not exceed 400' and would affect approximately 22.5 acres. Impacts to Fisheries Resources There are significant concerns over the potential negative impacts to fisheries resources that could arise from the dredging of Frying Pan Shoals. North Carolina's cape -associated shoals represent a significant and unique habitat. The cape -associated shoal complex is designated as Essential Fish Habitat (EFH) by the National Marine Fisheries Service (NMFS) as well as the South Atlantic Fishery Management Council for several different fish species such as tuna, swordfish, billfish, coastal and pelagic sharks, cobia, mackerel species and invertebrates such as sea scallop, Atlantic surfclam, ocean quahog, stone crab, and brown, pink, royal red, and white shrimp) (NMFS 2013). Additionally, The SAFMC designates these areas as Habitat Areas of Particular Concern (HAPC), meaning that these areas are rare, sensitive to disturbance and stress, and important to the ecosystem function of shrimp, snapper/grouper complex, and coastal migratory pelagic species. NMFS further State of North Carolina I Environmental Quality I Coastal Management 400 Commerce Avenue I Morehead City, NC 28557 252-808-2808 1252-247-3330 (fax) designates several species which inhabit the project area of the cape shoal features as Aquatic Resources of National Importance (ARNI) (i.e., bluefish (Pomatomus saltatrix), spotted seatrout (Cynoscion nebulosus), croaker (Micropogonias undulatus), southern flounder (Paralichthys lethostignia), blue crab (Callinectes sapidus), Spanish mackerel (Scomberomorus maculates), pompano (Trachinotais carolinus), and penaeid shrimp). Along the Cape Fear River, smaller blue crab (Callinectes sapidus) (juvenile and sub adult) are common just outside the inlet as well as in structural habitats and shallow areas of the estuary (Posey et al. 2005). Shoals extending perpendicular from shore account for an average 22% of shrimp landed in North Carolina (NCDMF Shrimp Fishery Management Plan Draft Amendment 1, 2015). Dredging sand from Frying Pan Shoals will result in the physical removal of benthic invertebrate communities. These epifauna and infauna species provide a food source for benthic and pelagic fish and invertebrates as a source of food. By removing this foraging habitat, benthic -pelagic coupling may be interrupted until recruitment and recolonization occurs. The shallow nature of shoaling features offer physical and chemical advantages as well. Shoal crests are more shallow than the sea floor and can provide a refuge from hypoxia (Dubois et al. 2009) as well as allow more light penetration to increase benthic diatoms (Grippo et al. 2009) providing productive foraging areas. These shoal features act as current baffles which create barriers to nutrient inputs (Brooks et al. 2006). Schooling planktivores (e.g. menhaden (Brevoortia tyrannus), anchovies, herring and scad) collect in these areas and often attract pelagic predators such as mackerel, cobia, and sharks. Removal of sand from Frying Pan Shoal could fragment the habitat and negatively affect these fish populations. The physical characteristics of sand placed on beaches is critically important for nesting sea turtles. Sea turtles can be affected by the sands placed on nourished beaches. Temperature fluctuations as minimal as 1-2°C are enough to change the sex of a developing embryo (Milton et al. 1997). The U.S. Fish and Wildlife Service Programmatic Biological Opinion (BO) for the state specifically mentions Bald Head Island as nesting areas for loggerhead turtles (Caretta caretta), green turtles (Chelonia mydas), and leatherback turtles (Dermochelys coriacea) because there are nest records for these species since 2000. Additionally, Bald Head Island is listed as critical habitat for loggerhead turtles. For these reasons, it is strongly suggested that any sand placed on the beach be evaluated by appropriate resource agencies to ensure that all sand is appropriate to prevent any adverse effects to existing turtle habitat. Recommendations Based on the above discussion, the DMF recommends denial of the permit application for this project as proposed because it will have significant adverse impacts on marine and estuarine fisheries, fish habitat, and fishing activity at the project site based on the information included in the application. The DMF may revise its recommendation if the following specific information is provided: 1. An Environmental Impact Statement (EIS) through the USACE State of North Carolina I Environmental Quality I Coastal Management 1367 US Hwy 17 South I Elizabeth City, NC 27909 252-264-3901 2. Impacts to Larval Transport - Dredging in Frying Pan Shoals can potentially interfere with the passage of larvae and early juveniles from offshore spawning grounds into estuarine nursery areas. Successful transport of larvae through the inlet occurs within a narrow zone parallel to the shoreline and is highly dependent on along -shore transport processes. DMF requests a detailed scientific field investigation, analysis, and modelling of larval transport dynamics that exist around Frying Pan Shoals currently and how that will change based on the proposed dredging activity. This information should be used to model estimated impacts of the dredging to larval ingress and egress through the inlet. 3. Sediment Transport - The proposal to dredge a hole, nearly 20 feet deep in some locations, in the shoal connected to adjacent water depths via a fairway could negatively and potentially permanently alter the habitat on the shoal. Frying Pan Shoal is classified as a relict shoal receiving much of its sand deposits from the Holocene and Pleistocene periods (Rutecki et al. 2014). These relict shoals take long periods of time to form and may not recover at rates necessary to sustain recurring borrow activities. The applicant states that the site of Frying Pan Shoals is intended to be a source for the next several decades, however, it is unknown how currents, wind, and storm events will respond spatially and temporally to removal of sand from the shoal. In addition, no studies have been performed to investigate the type of material that is expected to be deposited within the footprint of the excavated area. The concern to fisheries resources is that if incompatible materials fill the dredged footprint, new borrow sources will be sited on the shoal resulting in cumulative impacts to the habitat. DMF requests that a sediment transport model be used to investigate the previously mentioned concerns. 4. DMF would also like to see the applicant explore alternative sand sources that may have less significant impacts to critical fisheries habitats; this would include previously permitted alternative borrow sources described below. Bald Head Creek Bald Head Creek Shoal has been previously permitted as a borrow source for West Beach and Row Boat Row. The applicant has identified the remains of 250,000 cubic yards of existing beach compatible sand resource which has already been biologically and physically evaluated though monitoring and vibracores, respectively. The applicant states that this source of sand is not viable because it is designated for "offsetting any future adverse effects of the terminal groin." The purpose of this application is to place excavated sand on the areas in and around the footprint of the terminal groin fillet, and would further protect the shoreline impacted by the terminal groin. It is preferable to use an existing permitted and biologically monitored borrow source be utilized en lieu of a new borrow source with unexamined and undetermined effects. Jay Bird Shoals Jay Bird Shoals has been identified by the applicant as an alternative sand source for the West Beach and South Beach maintenance areas. The applicant states that suitable sediment has been identified to -22ft NGVD and had previously used 1.58 million cubic yards of material on a previous project in 2009/2010. The applicant states that the last date of physical monitoring completed by LMG was in State of North Carolina I Environmental Quality I Coastal Management 1367 US Hwy 17 South I Elizabeth City, NC 27909 252-264-3901 2013 and identified 1 million cubic yards of sand existing on the borrow source. The applicant incorrectly states that "permits issued for the recently constructed terminal groin, however, have conditions which operationally restrict near term excavation of the Jay Bird Shoals borrow area to 250/000 cy." CAMA Permit #91-14 condition 22a states that if the permittee receives modification to dredge more than 250,000 cubic yards from Jay Bird Shoals, it may be permissible under the requirements stipulated in condition 22 and 23. I would strongly suggest that this source be further investigated to see if site characteristics have changed since 2013, and prioritize this previously permitted and successfully utilized sand source be used to perform maintenance on West and South Beach before the utilization of Frying Pan Shoals. Brooks, R.A, C.N. Purdy, S.S. Bell, and K.J. Sulak. 2006. The benthic community of the eastern US continental shelf. A literature synopsis of benthic faunal resources. Continental Shelf Research 26:804-818. Dubois, S., C. Gelpi, R. Condrey, M. Grippo, and J. Fleeger. 2009. Diversity and composition of macrobenthic community associated with sandy shoals of the Louisiana continental shelf. Biodiversity and Conservation, 18: 3759-3784. Grippo, M.A., J.W. Flegger, R. Condrey, and K.R. Carman. 2009. High benthic microalgal biomass found on Ship Shoal, north -central Gulf of Mexico. Bulletin of Marine Science 84: 237-256. Milton, S. L., Schulman, A. A., & Lutz, P. L. (1997). The effect of beach nourishment with aragonite versus silicate sand on beach temperature and loggerhead sea turtle nesting success. Journal of Coastal Research, 904-915. NCDMF (North Carolina Division of Marine Fisheries). 2015. North Carolina Fishery Management Plan for Shrimp. North Carolina Department of Environment and Natural Resources, Divison of Marine Fisheries. NMFS (National Marine Fisheries Service). 2013. Summary of Essential Fish Habitat (EFH) and General Habitat Parameters for Federally Managed Species. Available at http://www.nero.noaa.gov/hcd/list.htm. Accessed on June 25, 2013. Posey, M.H., T.D. Alphin, H. Harwell, and B, Allen. 2005. Importance of low salinity areas for juvenile blue crabs, Callinectes sapidus Rathbun, in river -dominated estuaries in southeastern United States. Journal of Experimental Marine Biology and Ecology. 319: 8 1 - 100. Rutecki, D., T. Dellapenna, E. Nestler, F. Scharf, J. Rooker, C. Glass, and A. Pembroke. 2014. Understanding the Habitat Value and Function of Shoals and Shoal Complexes to Fish and Fisheries on the Atlantic and Gulf of Mexico Outer Continental Shelf. Literature Synthesis and Gap Analysis. Prepared for the U.S. Dept. of the Interior, Bureau of Ocean Energy Management. Contract # M12PS00009. BOEM 2015-012. 176 pp. State of North Carolina I Environmental Quality I Coastal Management 1367 US Hwy 17 South I Elizabeth City, NC 27909 252-264-3901 Contact Curt Weychert at (252) 808-2808 ext. 213 or Curt.Weychertkncdenr.gov with further questions or concerns. State of North Carolina I Environmental Quality I Coastal Management 1367 US Hwy 17 South I Elizabeth City, NC 27909 252-264-3901 ENT OF "'ArES Of UNITED STATES DEPARTMENT OF COMMERCE National Oceanic and Atmospheric Administration NATIONAL MARINE FISHERIES SERVICE Southeast Regional Office 26313th Avenue South St. Petersburg, Florida 33701-5505 hftp://sero.nmfs.noaa.gov March 9, 2017 F/SER47:KR/pw Colonel Kevin P. Landers Sr., Commander U.S. Army Corps of Engineers Wilmington District 69 Darlington Avenue Wilmington, North Carolina 28403-1398 Attention: Ronnie Smith Dear Colonel Landers: NOAA's National Marine Fisheries Service (NMFS) reviewed public notice SAW-2012-00040, dated February 8, 2017. The Village of Bald Head Island (Village) requests authorization from the Department of the Army to modify a permit for groin fillet maintenance and beach nourishment. Specifically, the Village seeks authorization to dredge a portion of Frying Pan Shoals and place the dredged material along the shoreline of Bald Head Island, including West Beach and South Beach. The Wilmington District's initial determination is the proposed project may adversely affect essential fish habitat (EFH) or associated fisheries managed by the South Atlantic Fishery Management Council (SAFMC), the Mid -Atlantic Fishery Management Council, or NMFS. For reasons detailed below, the NMFS agrees with this determination and concludes borrowing sand from Frying Pan Shoals may have long-term impacts to a substantial amount of shoal habitat the SAFMC designates EFH for cobia, Spanish mackerel, and king mackerel and the NMFS designates for Atlantic highly migratory species (tuna, swordfish, billfish, small and large coastal sharks, and pelagic sharks). In accordance with Part IV, Section 3(a) of the Memorandum of Agreement (MOA) between the Department of Commerce and the Department of the Army, dated August 11, 1992, the NMFS has also determined the mining of Frying Pan Shoals may lead to substantial and unacceptable impacts to aquatic resources of national importance (ARNI). As the nation's federal trustee for the conservation and management of marine, estuarine, and diadromous fishery resources, the NMFS provides the following comments pursuant to authorities of the Fish and Wildlife Coordination Act and the Magnuson -Stevens Fishery Conservation and Management Act (Magnuson -Stevens Act). Description of the Proposed Project The Village has relied on a variety of shoreline management actions to address chronic erosion on the western end of South Beach, The Point, and West Beach over the past 18 years. The most recent project, completed in December 2015, included construction of a 1,300-linear-foot terminal groin concurrent with a federal beach disposal operation on Bald Head Island. Recent physical monitoring reports the average annualized loss is 371,700 cubic yards of sand from West Beach and South Beach. Previous groin fillet maintenance and beach nourishment projects used material sourced from the Wilmington Harbor Federal Navigation Project and Jay Bird Shoals. Since 2001, Bald Head Island has received 250,000 to 366,000 cubic yards of sand per year from the Wilmington Harbor Federal Navigation Project. The Wilmington District has committed to continue contributing beach compatible sand from the Wilmington Harbor Federal Navigation Project to the Village for beach nourishment activities. Other sources of material approved in the current permit for beach disposal are located on Jay Bird Shoal and Bald Head Creek Shoal. The Village wants to secure an additional long-term source of material for groin fillet maintenance and beach nourishment. The Village has identified a borrow source located within a 460-acre site on the western portion of the Frying Pan Shoals formation, approximately one mile off the southeast shoreline of Bald Head Island. Sediment would be excavated to a depth up to -25 feet by cutter suction dredge and pumped by submerged pipeline to the shoreline of Bald Head Island. The identified borrow site could yield up to 8.5 million cubic yards of sand material meeting North Carolina's standards for beach compatibility. Because of draft restrictions to access the borrow source, the Village also seeks authorization for the dredge plant to excavate a fairway (channel) to access the borrow location. The effective width of the fairway would not exceed 400 feet and the affected area would be approximately 22.5 acres. The public notice does not discuss the fate of the material dredged for the fairway, and it is not clear if the material is suitable for beach disposal. Hence, impacts from dredging the fairway may exceed the amount stated. The Village proposes to conduct physical monitoring of the borrow site immediately after dredging, annually for three years, and biennially thereafter until the permit expires in November 2024. The footprint of each monitoring survey would include the entire permitted nourishment site as well as the area of excavation within Frying Pan Shoals. The results of the monitoring would be incorporated into the Village's existing Shoreline Monitoring Program annual report. The Village does not propose any environmental surveys or ecological studies of affected fisheries or fish habitat. Consultation History The NMFS participated in a scoping meeting with the Village, North Carolina Division of Coastal Management, North Carolina Wildlife Resources Commission, U.S. Fish and Wildlife Service, and the Wilmington District on November 4, 2016. The NMFS expressed concerns that a project of this scope may affect EFH associated with an important cape -associated shoal complex. The NMFS recommended a more thorough alternatives analysis be completed and recommended the analysis include additional sources of material from the Wilmington Harbor Federal Navigation Project (e.g., Outer Ocean Bar and Mid -River) and the Wilmington Harbor Ocean Dredged Material Disposal Site. The NMFS also recommended the Village investigate other offshore sand sources not affiliated with the Cape Fear inlet and shoal complex (e.g., Outer Continental Shelf). The NMFS commented extensively in review of the Environmental Impact Statement (EIS) entitled, Village of Bald Head Island Shoreline Protection Project, dated August 2014, and its EFH Assessment, dated January 2014. The NMFS comments noted significant errors and omissions in these documents. The NMFS provided guidance on interpretations of impacts to fisheries. The NMFS provided an EFH conservation recommendation requesting the permit authorizing the terminal groin and beach nourishment not include dredging of sand from Frying Pan Shoals without further EFH consultation and in-depth review of environmental impacts. The 2 Wilmington District agreed, and the permit it issued did not authorize dredging in Frying Pan Shoals. Essential Fish Habitat and Aquatic Resources of National Importance Pursuant to the Magnuson -Stevens Act, the SAFMC and NMFS designate EFH within the study area to include tidal inlets and cape -associated shoal complexes because these areas provide feeding, resting, and staging habitat for a variety of commercially, recreationally, and ecologically important fish species. The SAFMC also designates these areas as an HAPC under the fishery management plans for shrimp, snapper/grouper complex, and coastal migratory pelagic species because these areas are rare, sensitive to stress and disturbance, and important to ecosystem function. Understanding how tidal inlets and shoals function to provide habitat is the product of a complex mix of connections between biological processes and physical factors. The cape -associated shoal complexes of North Carolina are known "hot -spot" environments where dense aggregations of fish are supported by local primary production. The SAMFC provides additional information on the species it manages and their EFH in Fishery Ecosystem Plan of the South Atlantic Region (available at www.safmc.net), and the NMFS provides additional information on the EFH of highly migratory species in Amendment 10 to the 2006 Consolidated HMS Fishery Management Plan: Essential Fish Habitat (available at www. nmfs. noaa. gov/sfa/hmsl) Several fish and invertebrates inhabiting the project area are ARNI in accordance with Section 906(e)(1) of the Water Resources Development Act of 1986 (PL 99-602), including bluefish (Pomatomus saltatrix), spotted seatrout (Cynoscion nebulosus), croaker (Micropogonias undulatus), southern flounder (Paralichthys lethostigma), blue crab (Callinectes sapidus), Spanish mackerel (Scomberomorus maculates), pompano (Trachinotus carolinus), and penaeid shrimp. Impacts to Essential Fish Habitat The Wilmington District and NMFS evaluated EFH impacts from dredging sand at Jay Bird Shoals, Bald Head Creek Shoal, and the Wilmington Harbor federal channel during the original EFH consultation for this project. Consequently, this additional review focuses on the EFH impacts from dredging sand at Frying Pan Shoals. The North Carolina coast consists of a series of cuspate bays or coastal compartments, each with different spatial orientations and a geologic character reflecting the adjacent continental shelf (McNinch and Luettich 2000; Riggs and Ames 2009). Frying Pan Shoals, like the other cape - associated shoal complexes in North Carolina, is a prominent feature extending to the continental shelf break. Among the three cape -associated shoal complexes, Frying Pan Shoals extends the farthest, approximately 30 miles. Each of the cape -associated shoal complexes appears to have large volumes of high quality, beach compatible sand (Riggs et al. 2011). Cape -associated shoal complexes are constantly changing. They shift under normal current regimes, but storm events are largely responsible for sediment transport, sand distribution, and shoal migration. Wind - driven currents and storm -induced waves suspend sediment causing frequent erosion and deposition on the seabed. A significant knowledge gap exists in understanding the role of cape - associated shoal complexes in the function and maintenance of North Carolina's barrier island system (Kalo and Schiavinato 2009). It is entirely unknown how barrier islands and longshore 3 coastal currents will respond to dredging and removal of large volumes of sand from Frying Pan Shoals. There is potential for significant short-term and long-term physical and biological impacts from dredging shoal habitat. Frying Pan Shoals is characterized by a high fish production, a high benthic faunal density, and species diversity. The Shoals are critically important for fisheries as it demarcates the boundary where the Labrador Current flowing south collides with the Gulf Stream Current flowing north. This biogeographical boundary plays a key role in supporting shrimp, the snapper -grouper complex, coastal migratory pelagic species, and highly migratory species by generating localized areas of high productivity. Upwelling in frontal eddies and summer bottom intrusions driven by the Gulf Stream contribute to this productivity by providing nutrient rich waters and a succession of biological responses (Lee et al. 1991). Shoal habitat is defined by such factors as exposure, sediment texture, depth, and rugosity. The NMFS is primarily concerned about the impacts of dredging on prey resources and foraging habitat provided by the Frying Pan Shoal complex. Benthic invertebrate communities consisting of crustaceans, worms, and mollusks are diverse and productive despite the high-energy disturbance regime affecting the Shoal complex. Infaunal species provide important trophic linkages coupling benthic-pelagic ecosystems. Many of the organisms utilizing these habitats also provide trophic linkages between inshore and offshore populations. Succession and recovery of benthic communities established in shallow high-energy environments may reflect the adaptation of communities that occur in these habitats to frequent disturbance from episodic storm events (Normandeau Associates 2014). Potential impacts caused by dredging include physical removal of benthic faunal communities and disturbance of foraging habitat for fish and invertebrates. Dredging can also affect benthic communities by altering sediment transport characteristics of a shoal favoring sedimentation instead of resuspension. Benthic impacts are expected to be reflected in measures of abundance, biomass, and taxa richness. Several practices have been suggested to reduce recovery times for benthic communities following dredging events. Most important is ensuring dredging activities do not create a depression in which fine sediments deposit and collect. This may change the sediment composition and associated infaunal assemblages, which is essential for recovery and recolonization (Byrnes et al. 2004; Crowe et al. 2016). Also, timing of dredging prior to the peak recruitment period of spring and summer, along with the preservation of local refuge patches to maximize the rate and success of benthic recolonization have also been suggested to improve recovery times (Byrnes et al. 2004; Brooks et al. 2006). The NMFS believes dredging and alterations of habitat on Frying Pan Shoals could affect spatiotemporal longshore movements of migratory fish species by disrupting feeding behavior (i.e., movement based on patchy food availability) and by disrupting a significant orientation cue for migration. Frying Pan Shoals serve as a migratory corridor for many species that traverse the coastal waters of the Southeast. Data on fish migration through North Carolina's cape -associated shoal complexes are sparse (Schwartz 1989). Anadromous species are the most common and well known fish to exhibit longshore migratory behavior. Anadromous species have complex lifecycles where individuals migrate great distances along the continental shelf and then return to their natal rivers to spawn. In the Southeast, Atlantic sturgeon, shortnose sturgeon, striped bass, American shad, and blueback herring move along and across the shoal habitat multiple times 4 throughout their life cycle. Sexually mature adults move across the shoals to aggregate and stage at river mouths and inlets prior to spawning migration in rivers. Similarly, young -of -year emerge from estuaries and migrate across the shoals en route to the waters of the North Atlantic for growing. Inlets and nearshore shallow areas with predominantly sandy substrate are particularly important refuge and foraging habitat for sturgeon and other anadromous species (Laney et al. 2007; Taylor et al. 2016). A number of marine species seasonally migrate across the shoals. Cobia is a popular recreational and commercial species distributed worldwide in tropical, subtropical, and warm -temperate waters. Cobia are abundant in the warm waters off the coast of the U.S. from Virginia south throughout the Gulf of Mexico. The SAFMC manages cobia as part of the Coastal Migratory Pelagics Fishery Management Plan because the species is highly migratory. In late spring, schools of fish begin to migrate north from Florida. Migration and movement correlate with water temperature. Schools of migrating fish occur throughout coastal waters moving along beaches and the nearshore environment. Cobia form large spawning aggregations off North Carolina in May and June. There are numerous other examples of spatial movement patterns of fish across Frying Pan Shoals at various temporal scales. Atlantic menhaden form large schools that migrate between inshore and offshore waters foraging on plankton. During fall and early winter, menhaden migrate south around the North Carolina capes to spawn (ASMFC 2015). The accumulation of menhaden and other schooling planktivores (e.g., anchovies, sardines, herring, and scad) on the shoals attract pelagic predators such as Spanish mackerel, king mackerel, and coastal sharks. The NMFS is concerned the systematic dredging of cape -associated shoal complexes, such as the proposed project and subsequently other projects, may result in cumulative and unanticipated changes in habitat quality. Although opportunistic invertebrate communities may repopulate these areas after dredging, benthic populations may not recover to pre -project levels. Dredging will also suspend any fine material in the borrow area which may clog the gills in young, less mobile fish and invertebrates and thereby increase their mortality rates within assemblages. The extent of negative effect is dependent on the life history stages of the species present and the duration of the event. Frying Pan Shoals are a long-established seascape feature unique to North Carolina that provides valuable habitat for fishery resources utilizing estuaries and offshore waters as a part of their life cycle. Avoiding dredging of sand from this shoal complex would ensure that these important areas would not be altered to the point they no longer provide valuable habitat. Monitoring Needed for the Dredging Impacts To fully evaluate the proposed mining of Frying Pan Shoals for sand, the NMFS requires additional information regarding the rates at which borrow areas are expected to fill and measures the Wilmington District may require the Village to take to limit dredging to portions of the Shoal expected to fill in most rapidly. The NMFS also requires information on the biological monitoring the District may require quantifying whether the actual impacts to EFH are within acceptable limits. To characterize distribution, abundance, biomass, and diversity of fish and invertebrates on the Shoal complex, the NMFS recommends using fishery -independent surveys 5 that include a combination of active sampling (e.g., trawling) and passive sampling (e.g., acoustic surveillance technology). Dredging Best Management Practices The NMFS requests the District develop best management practices (BMPs) to minimize the adverse effects from dredging the shoal -complex and provide these for review before the District makes its final decision on the proposed permit modification. For example, limiting the dredging to the prevailing downdrift flanks of the shoals and limiting the depth of the dredge cuts to ten feet may be good practices. Dredging within the shoal -complex should be limited to the portions of the shoal expected to fill in most quickly once dredging has stopped. Environmental windows (seasonal restrictions) should be used to limit the timing of dredge and disposal activities to protect fish during sensitive life stages. Impacts to Aquatic Resources of National Importance Several fish and invertebrates known to inhabit the project area are ARNI in accordance with Section 906(e)(1) of the Water Resources Development Act of 1986 (PL 99-602), including bluefish, spotted seatrout, croaker, southern flounder, blue crab, Spanish mackerel, pompano, and penaeid shrimp. These species utilize sandy shoals for spawning, refuge, foraging, or nursery areas. As proposed, the work could directly and permanently eliminate a substantial amount of sandy shoal habitat. Indirect impacts to this habitat and the ARNI that depend upon the Shoals also may result from the altered wave climate caused by removing a substantial portion of the Shoal. These indirect and cumulative impacts from the proposed action include increased turbidity and sedimentation from placement of fill in the aquatic environment and loss of food production functions performed by sandy shoals. EFH Conservation Recommendations Section 305(b)(4)(A) of the Magnuson -Stevens Act requires the NMFS to provide EFH Conservation Recommendations for any federal action or permit which may result in adverse impacts to EFH. Therefore, the NMFS recommends the following to ensure the conservation of EFH and associated fishery resources: 1. The excavation of Frying Pan Shoals for terminal groin maintenance and beach nourishment should be eliminated from the project design. The NMFS would reconsider this recommendation based on receipt of additional environmental analysis performed including an EFH Assessment addressing the proposed permit modifications. 2. An alternatives analysis should be done to identify whether Frying Pan Shoals is the least environmentally damaging practicable alternative sand source the Village could use during the remainder of the permit period. This analysis should include examination of additional offshore sources, including those in the Outer Continental Shelf, capable of providing beach compatible sand. 3. A physical and biological monitoring plan for the offshore borrow areas should be developed to more accurately determine impacts to shoal habitat. The objectives of the monitoring should include documenting the extent and grain -size distribution of the material filling the excavation sites. Environmental monitoring should also document biological components of the ecosystem, including fish, invertebrates, and infauna, to quantify recovery and whether the actual impacts to EFH are within acceptable limits. 6 4. BMPs should be developed to minimize the adverse impacts associated with dredging Frying Pan Shoals and integrated into the project design. For example, limiting the dredging to the prevailing downdrift region of the shoal and limiting the depths of the dredge cuts to ten (10) feet may be good practices. Similarly, restricting the time of year for construction activities including dredging, groin maintenance, and beach nourishment, should be included to reduce impacts to EFH and vulnerable life stages of federally managed fishery species. Please provide a list of BMPs to NMFS for review before the District makes its final decision on the proposed permit modification. Section 305(b)(4)(B) of the Magnuson -Stevens Act and implementing regulation at 50 CFR Section 600.920(k) require the Wilmington District to provide a written response to this letter within 30 days of its receipt. If it is not possible to provide a substantive response within 30 days, in accordance with the "findings" with the Wilmington District, an interim response should be provided to the NMFS. A detailed response then must be provided prior to final approval of the action. The detailed response must include a description of measures proposed by the Wilmington District to avoid, mitigate, or offset the adverse impacts of the activity. If the response is inconsistent with the EFH conservation recommendations, the Wilmington District must provide a substantive discussion justifying the reasons for not following the recommendations. Closing Thank you for the opportunity to provide these comments. Please direct related questions or correspondence to the attention of Dr. Ken Riley at our Beaufort Field Office, 101 Pivers Island Road, Beaufort, North Carolina 28516-9722. He may be reached by telephone at (252) 728- 8750 or by e-mail at Ken.Riley@noaa.gov. cc: COE, Ronnie.D.Smith@usace.army.mil USFWS, Pete_Benjamin@usfws.gov NCDCM, Doug.Huggett@ncdenr.gov NCDCM, Shane. Staples@ncdenr.gov EPA, Bowers.Todd@epa.gov SAFMC, Roger.Pugliese@safmc.net ASMFC, LHavel@asmfc.org F/SER4, David.Dale@noaa.gov F/SER47, Ken.Riley@noaa.gov Sincerely, Virginia M. Fay Assistant Regional Administrator Habitat Conservation Division 7 References ASMFC. 2015. Southeast Data, Assessment, and Review (SEDAR 40): Atlantic Menhaden Stock Assessment Report. Atlantic States Marine Fisheries Commission, North Charleston, South Carolina. 643 pp. Brooks, R.A, C.N. Purdy, S.S. Bell, and K.J. Sulak. 2006. The benthic community of the eastern U.S. continental shelf. A literature synopsis of benthic faunal resources. Continental Shelf Research 26:804-818. Byrnes, M.R., R.M. Hammer, J.L. Kelley, D.B. Baker, T.D. Thibaut, S.A. Zichichi, L.M. Lagera, S.T. Viada, B.A. Vittor, J.S. Ramsey, and J.D. Germano. 2004. Environmental surveys of potential borrow areas offshore northern New Jersey and southern New York and the environmental implications of sand removal for coastal and beach restoration. U.S. Department of the Interior, Minerals Management Service, Leasing Division, Marine Minerals Branch, Herndon, VA. OCS Report MMS 2004-044. 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Chapel Hill: University of North Carolina Press. 142 pp. Schwartz, F.J. 1989. Zoogeography and ecology of fishes inhabiting North Carolina's marine waters to depths of 600 meters. Pages 335-374 in R.Y. George and A.W. Hulbert, editors. North Carolina Coastal Oceanography Symposium. U.S. Department of Commerce, NOAA-NURP Rep. 89-2. Taylor, A. D., K. Ohashi, J. Sheng, and M. K. Litvak. 2016. Oceanic distribution, behaviour, and a winter aggregation area of adult Atlantic sturgeon, Acipenser oxyrinchus oxyrinchus, in the Bay of Fundy, Canada. P1OS One 11:1-16. 9