Takes of Marine Mammals Incidental to Specified Activities; Taking Marine Mammals Incidental to the Maryland Offshore Wind Project, Offshore of Maryland

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Federal RegisterOct 23, 2024
89 Fed. Reg. 84674 (Oct. 23, 2024)
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    Department of Commerce National Oceanic and Atmospheric Administration
  • 50 CFR Part 217
  • [Docket No. 240917-0242]
  • RIN 0648-BM32
  • AGENCY:

    National Marine Fisheries Service (NMFS), National Oceanic and Atmospheric Administration (NOAA), Commerce.

    ACTION:

    Final rule.

    SUMMARY:

    In accordance with the regulations implementing the Marine Mammal Protection Act (MMPA), as amended, notification is hereby given that NMFS promulgates regulations to govern the incidental taking of marine mammals incidental to US Wind, Inc. (US Wind) during the construction of an offshore wind energy project (the Project) in Federal and State waters off of Maryland, specifically within the Bureau of Ocean Energy Management (BOEM) Commercial Lease of Submerged Lands for Renewable Energy Development on the Outer Continental Shelf (OCS) Lease Area (OCS-A-0490) (referred to as the Lease Area) and along associated export cable routes to sea-to-shore transition points (collectively, the project area), over the course of 5 years (January 1, 2025 through December 31, 2029). These regulations, which allow for the issuance of a Letter of Authorization (LOA) for the incidental take of marine mammals during specific construction related activities within the project area during the effective dates of the regulations, prescribe the permissible methods of taking and other means of effecting the least practicable adverse impact on marine mammal species or stocks and their habitat, as well as requirements pertaining to the monitoring and reporting of such taking.

    DATES:

    This rule is effective from January 1, 2025, through December 31, 2029.

    FOR FURTHER INFORMATION CONTACT:

    Jessica Taylor, Office of Protected Resources, NMFS, (301) 427-8401.

    SUPPLEMENTARY INFORMATION:

    Availability

    A copy of US Wind's application and supporting documents, as well as a list of the references cited in this document, may be obtained online at: https://www.fisheries.noaa.gov/national/marine-mammal-protection/incidental-take-authorizations-other-energy-activities-renewable. In case of problems accessing these documents, please call the contact listed above (see FOR FURTHER INFORMATION CONTACT ).

    Purpose and Need for Regulatory Action

    This final rule, as promulgated, provides a framework under the authority of the MMPA (16 U.S.C. 1361 et seq.) to authorize the take of marine mammals incidental to construction of the Project within the project area. NMFS received a request from US Wind to incidentally take a small number of marine mammals from 19 species of marine mammals, comprising 20 stocks (5 stocks by Level A harassment and Level B harassment; 15 stocks by Level B harassment only), incidental to US Wind's construction activities. US Wind did not request and NMFS neither anticipates nor allows take by serious injury or mortality incidental to the specified activities in this final rulemaking.

    Legal Authority for the Final Action

    The MMPA prohibits the “take” of marine mammals, with certain exceptions. Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.) direct the Secretary of Commerce (as delegated to NMFS) to allow, upon request, the incidental, but not intentional, taking of small numbers of marine mammals by U.S. citizens who engage in a specified activity (other than commercial fishing) within a specified geographical region if certain findings are made, regulations are promulgated (when applicable), and public notice and an opportunity for public comment are provided.

    Authorization for incidental takings shall be granted if NMFS finds that the taking will have a negligible impact on the species or stock(s) and will not have an unmitigable adverse impact on the availability of the species or stock(s) for taking for subsistence uses (where relevant). Further, NMFS must prescribe the permissible methods of taking and other “means of effecting the least practicable adverse impact” on the affected species or stocks and their habitat, paying particular attention to rookeries, mating grounds, and areas of similar significance, and on the availability of the species or stocks for taking for certain subsistence uses (referred to as “mitigation”); and requirements pertaining to the mitigation, monitoring and reporting of the takings are set forth.

    As noted above, US Wind did not request and NMFS neither anticipates nor allows take by serious injury or mortality incidental to the specified activities in this final rulemaking. Relevant definitions of MMPA statutory and regulatory terms are included below:

    • U.S. Citizens —individual U.S. citizens or any corporation or similar entity if it is organized under the laws of the United States or any governmental unit defined in 16 U.S.C. 1362(13) (50 CFR 216.103);
    • Take —to harass, hunt, capture, or kill, or attempt to harass, hunt, capture, or kill any marine mammal (16 U.S.C. 1362; 50 CFR 216.3);
    • Incidental Harassment, Incidental Taking and Incidental, but not Intentional, Taking —an accidental taking. This does not mean that the taking is unexpected, but rather it includes those takings that are infrequent, unavoidable or accidental (see 50 CFR 216.103);
    • Serious Injury —any injury that will likely result in mortality (50 CFR 216.3);
    • Level A harassment —any act of pursuit, torment, or annoyance which has the potential to injure a marine mammal or marine mammal stock in the wild (16 U.S.C. 1362; 50 CFR 216.3); and
    • Level B harassment —any act of pursuit, torment, or annoyance which has the potential to disturb a marine mammal or marine mammal stock in the wild by causing disruption of behavioral patterns, including, but not limited to, migration, breathing, nursing, breeding, feeding, or sheltering (16 U.S.C. 1362; 50 CFR 216.3).

    Section 101(a)(5)(A) of the MMPA and the implementing regulations at 50 CFR part 216, subpart I provide the legal basis for proposing and, if appropriate, issuing this rule containing 5-year regulations and associated LOA. This final rule also establishes required mitigation, monitoring, and reporting requirements for US Wind's construction activities.

    Summary of Major Provisions Within the Final Rule

    The major provisions within this final rule include:

    • Allowing NMFS to authorize, under a LOA, the take of small numbers of marine mammals by Level A harassment and/or Level B harassment (50 CFR 217.312) incidental to the Project and prohibiting take of such species or stocks in any manner not permitted (50 CFR 217.313) ( e.g., mortality or serious injury);
    • Establishing a seasonal moratorium on foundation impact pile driving during December 1-April 30, annually, as well as avoiding foundation impact pile driving in November to the maximum extent practicable to minimize impacts to North Atlantic right whales ( Eubalaena glacialis);
    • Conducting both visual and passive acoustic monitoring (PAM) by trained, NMFS-approved Protected Species Observers (PSO) and PAM operators before, during, and after select in-water construction activities;
    • Requiring training for all Project personnel to ensure marine mammal protocols and procedures are clearly understood;
    • Establishing clearance and shutdown zones for all in-water construction activities and high-resolution geophysical (HRG) marine site characterization surveys to prevent or reduce the risk of Level A harassment and to minimize the risk of Level B harassment, including a delay or shutdown of foundation impact pile driving if a North Atlantic right whale is observed at any distance by PSOs or acoustically detected within certain distances;
    • Establishing minimum visibility and PAM monitoring zones during foundation impact pile driving;
    • Requiring use of at least two sound attenuation devices during all foundation impact pile driving installation activities to reduce noise levels to those modeled assuming a broadband 10 decibel (dB) attenuation;
    • Requiring sound field verification (SFV) monitoring during impact pile driving of foundation piles to measurein situ noise levels for comparison against the modeled results and ensure noise levels assuming 10 dB attenuation are not exceeded;
    • Requiring SFV during the operational phase of the Project;
    • Implementing soft-starts during impact pile driving and ramp-up during the use of HRG marine site characterization survey equipment;
    • Requiring various vessel strike avoidance measures;
    • Requiring various measures during fisheries monitoring surveys, such as removing gear from the water if marine mammals are considered at-risk or are interacting with gear;
    • Requiring regular and situational reporting including, but not limited to, information regarding activities occurring, marine mammal observations and acoustic detections, and SFV monitoring results; and
    • Requiring monitoring of the North Atlantic right whale sighting networks, Channel 16, and PAM data, as well as reporting any sightings to the NMFS.

    Through adaptive management ( see50 CFR 217.347(c)(1)) NMFS Office of Protected Resources may modify ( e.g., remove, revise, or add to) the existing mitigation, monitoring, or reporting measures summarized above and required by the LOA.

    NMFS must withdraw or suspend an LOA issued under these regulations, after notice and opportunity for public comment, if it finds the methods of taking or the mitigation, monitoring, or reporting measures are not being substantially complied with (16 U.S.C. 1371(a)(5)(B); 50 CFR 216.106(e)). Additionally, failure to comply with the requirements of the LOA may result in civil monetary penalties and knowing violations may result in criminal penalties (16 U.S.C. 1375; 50 CFR 216.106(g)).

    Fixing America's Surface Transportation Act (FAST-41)

    This Project is covered under title 41 of the Fixing America's Surface Transportation Act, or “FAST-41.” A “covered project” under FAST-41 is defined generally as “any activity in the United States that requires authorization or environmental review by a Federal agency involving construction of infrastructure for renewable or conventional energy production” 42 U.S.C. 4370m-(6)(A). The Project, which involves construction of renewable wind energy infrastructure off of Maryland, will provide 300 megawatts (MW) of energy and, upon completion, advance the State of Maryland's renewable energy goals. As such, the Project falls under FAST-41's definition of “covered project.”

    FAST-41 includes a suite of provisions designed to expedite the environmental review for covered infrastructure projects, including enhanced interagency coordination as well as milestone tracking on the public-facing Permitting Dashboard. FAST-41 also places a 2-year limitations period on any judicial claim that challenges the validity of a Federal agency decision to issue or deny an authorization for a FAST-41 covered project 42 U.S.C. 4370m-6(a)(1)(A).

    The Project is listed on the Permitting Dashboard, where milestones and schedules related to the environmental review and permitting for the Project can be found at https://www.permits.performance.gov/permitting-project/fast-41-covered-projects/maryland-offshore-wind-project.

    Summary of Request

    On August 31, 2022, US Wind submitted a request for the promulgation of regulations and issuance of an associated 5-year LOA to take marine mammals incidental to construction activities associated with implementation of the Project offshore of Maryland in the BOEM Lease Area OCS-A 0490 and associated export cable routes. US Wind's request is for the incidental, but not intentional, taking of a small number of 19 marine mammal species (comprising 20 stocks) by Level B harassment (for all 20 stocks) and by Level A harassment (for 5 of the 20 stocks). US Wind did not request, and NMFS does not anticipate, take by serious injury or mortality to occur for any marine mammal species or stock incidental to the specified activities.

    In response to our questions and comments and following extensive information exchanges between US Wind and NMFS, US Wind submitted a final, revised application on March 31, 2023 that NMFS deemed adequate and complete on April 3, 2023. This application is available on NMFS' website at: https://www.fisheries.noaa.gov/action/incidental-take-authorization-us-wind-inc-construction-and-operation-maryland-offshore-wind.

    On May 2, 2023, NMFS published a notice of receipt (NOR) of US Wind's adequate and complete application in the Federal Register (88 FR 27463), requesting comments and soliciting information related to US Wind's request during a 30-day public comment period. During the NOR public comment period, NMFS received comment letters from 77 private citizens, 6 non-governmental organizations, and 1 State government organization (Delaware Department of Natural Resources and Environmental Control). NMFS reviewed all submitted material and took these into consideration during the drafting of the proposed rule.

    On September 6, 2023 and September 11, 2023, US Wind submitted supplemental information related to its pilot whale and seal take analyses. The corresponding memos, entitled “US Wind NMFS Request for Information (RFI) Response Memo and Maryland Offshore Wind Project Revised Requested Take Tables” are available on our website at https://www.fisheries.noaa.gov/action/incidental-take-authorization-us-wind-inc-construction-and-operation-maryland-offshore-wind.

    On January 4, 2024, NMFS published the proposed rule for the Project in the Federal Register (89 FR 504). In the proposed rule, NMFS synthesized all of the information provided by US Wind, all best available scientific information and literature relevant to the Project, outlined, in detail, proposed mitigation designed to effect the least practicable adverse impacts on marine mammal species and stocks as well as proposed monitoring and reporting measures, and made preliminary negligible impact and small numbers determinations. The public comment period on the proposed rule was open for 30 days from January 4, 2024 through February 5, 2024 on https://Regulations.gov. A summary of public comments received during this 30-day period are described in the Comments and Responses section; full public comments may be viewed on https://Regulations.gov.

    On August 1, 2022, NMFS announced proposed changes to the existing North Atlantic right whale vessel speed regulations (87 FR 46921) to further reduce the likelihood of mortalities and serious injuries to endangered right whales from vessel collisions, which are a leading cause of the species' decline and a primary factor in an ongoing Unusual Mortality Event (UME). Should a final vessel speed rule be issued and become effective during the effective period of this incidental take authorization (or any other MMPA incidental take authorization), the authorization holder would be required to comply with any and all applicable requirements contained within the final rule. Specifically, where measures in any final vessel speed rule are more protective or restrictive than those in this or any other MMPA authorization, authorization holders would be required to comply with the requirements of the rule. Alternatively, where measures in this or any other MMPA authorization are more restrictive or protective than those in any final vessel speed rule, the measures in the MMPA authorization would remain in place. The responsibility to comply with the applicable requirements of any vessel speed rule would become effective immediately upon the effective date of any final vessel speed rule and when notice is published on the effective date, NMFS would also notify US Wind if the measures in the speed rule were to supersede any of the measures in the MMPA authorization such that they were no longer required.

    Description of Specified Activity

    Overview

    US Wind plans to construct and operate a wind energy facility, the Project, in the Atlantic Ocean in lease area OCS-A 0490, offshore Maryland. The Project consists of 3 construction campaigns including MarWin, located in the southeastern portion of the Lease Area with the potential to generate approximately 300 megawatts (MW) of energy, Momentum Wind, located immediately west of MarWin with the potential to generate approximately 808 MW of energy, and Future Development, which encompasses buildout of the remainder of the Lease Area and for which generation capacity has yet to be determined (table 1). Once operational, MarWin and Momentum Wind would advance the State of Maryland's renewable energy goals, providing 50 percent of the State's goal by the year 2030, with the full buildout of the Lease Area further achieving renewable energy targets. US Wind also anticipates completing the Future Development campaign within the effective period of the rule.

    The Project will consist of several different types of permanent offshore infrastructure, including up to 114 WTGs ( e.g., 18-MW model with a 250-meter (m) rotor diameter platform), four OSSs, a MET tower, and inter-array and export cables. MarWin will occupy approximately 46.6 square kilometers (km2 ) (11,515 acres), which will include approximately 21 WTGs and 1 OSS. The MarWin campaign, as well as subsequent Momentum Wind and Future Development, includes monopiles as the only potential WTG foundation type. For each campaign, the OSS would be supported by monopiles or jacket foundations with skirt piles. Skirt piles are post-piled pin piles. Jacket foundations are placed on the seabed and pin piles are driven into jacket pile guides, which are known as skirts. Table 1 provides a summary of each construction campaign.

    Table 1—US Wind's Anticipated Construction Campaign Schedule

    Campaigns Construction year Number of 11-m monopiles for WTGs Number 3-m pin piles for OSS jacket foundations Number of 1.8-m pin piles for Met tower Onshore export cables Offshore substations
    MarWin 1 (2025) 21 4 (1 jacket) 0 4 1
    Momentum 2 (2026) 55 8 (2 jackets) 3 0 2
    Future Development 3 (2027) 38 4 (1 jacket) 0 0 1
    Potential OSS foundations could also include monopile and suction bucket jacket foundations.

    Table 2—US Wind's Anticipated Construction and Operations Schedule During the Effective Period of the LOA

    Project activity Construction campaign Expected timing Expected duration (approximate)
    Scour Protection Pre-Installation MarWin Year 1: Q2 through Q3 of 2025 21 days.
    Momentum Wind Year 2: Q2 through Q3 of 2026 55 days.
    Future Development Year 3: Q2 through Q3 of 2027 38 days.
    WTG Foundation Installation MarWin Year 1: June through September of 2025 21 days.
    Momentum Wind Year 2: May through August of 2026 55 days.
    Future Development Year 3: June through August of 2027 38 days.
    Scour protection post-installation MarWin Year 1: Q2 through Q3 of 2025 42 days.
    Momentum Wind Year 2: Q2 through Q3 of 2026 110 days.
    Future Development Year 3: Q2 through Q3 of 2027 76 days.
    OSS Foundation installation MarWin Year 1: July of 2025 1 day.
    Momentum Wind Year 2: July of 2026 2 days.
    Future Development Year 3: July of 2027 1 day.
    Met Tower installation Momentum Wind Year 2: June of 2026 1 day.
    HRG surveys Momentum Wind Year 2: Q2 through Q3 of 2026 14 days.
    Future Development Year 3: Q2 through Q3 of 2027 14 days.
    Site preparation n/a Not anticipated n/a.
    Inter-array cable installation MarWin Year 1: Q2 through Q4 of 2025 42 days.
    Momentum Wind Year 2: Q2 through Q4 of 2026 110 days.
    Future Development Year 3: Q2 through Q4 of 2027 76 days.
    Export cable installation MarWin Year 1: Q1 through Q4 of 2025 60 days.
    Momentum Wind Year 2: Q1 through Q4 of 2026 120 days (2 cables).
    Future Development Year 3: Q1 through Q4 of 2027 60 days.
    Fishery monitoring surveys MarWin Momentum Wind Future Development Q1 through Q4 Years 1-5 16 days/year for commercial pot surveys. 12 days/year for recreational surveys.
    Currently, US Wind is not planning to conduct activities that have the potential to result in take in 2028 and 2029. However, while table 2 represents US Wind's current schedule, NMFS recognizes the potential for activity schedules to shift such that they could occur during different timeframes within the five year effective period of this rule.
    Installation timing will depend on vessel availability, contractor selection, weather, and more. Year 1 is anticipated to be 2025, year 2 to be 2026, and year 3 to be 2027, although these are subject to change per the factors identified. Note: “Q1, Q2, Q3, and Q4” each refer to a quarter of the year, starting in January and comprising 3 months each. Therefore, Q1 represents January through March, Q2 represents April through June, Q3 represents July through September, and Q4 represents October through December.
    The months identified here represent US Wind's planned schedule; however, in case of unanticipated delays, foundation installation may occur between May 1 and November 30 annually.
    US Wind anticipates that all WTGs, OSS, and Met tower foundations will be installed by November 30, 2027; however, unanticipated delays may require some foundation pile driving to occur in years 4 (2028) or 5 (2029).
    Represents HRG surveys that may result in take of marine mammals. US Wind plans to conduct HRG surveys that are not expected to result in take of marine mammals during Q2 through Q3 of year 1 given those surveys would utilize equipment all operating over 180kHz or have no acoustic output.

    Table 3—Marine Mammal Species That May Occur in the Project Area and Be Taken, by Harassment

    Common name Scientific name Stock ESA/ MMPA status; strategic (Y/N) Stock abundance ( CV, N min , most recent abundance survey) PBR Annual M/SI
    Order Artiodactyla—Cetacea—Mysticeti (baleen whales)
    Family Balaenidae:
    North Atlantic right whale Eubalaena glacialis Western Atlantic E, D, Y 340 (0; 337; 2021) 0.7 27.2
    Family Balaenopteridae (rorquals):
    Fin whale Balaenoptera physalus Western North Atlantic E, D, Y 6,802 (0.24, 5,573, 2021) 11 2.05
    Sei whale Balaenoptera borealis Nova Scotia E, D, Y 6,292 (1.02, 3098, 2021) 6.2 0.6
    Minke whale Balaenoptera acutorostrata Canadian Eastern Coastal -, -, N 21,968 (0.31, 17,002, 2021) 170 9.4
    Humpback whale Megaptera novaeangliae Gulf of Maine -, -, Y 1,396 (0, 1,380, 2016) 22 12.15
    Superfamily Odontoceti (toothed whales, dolphins, and porpoises)
    Family Delphinidae:
    Killer whale Orcinus orca Western North Atlantic -, -, N UNK (UNK, UNK, 2016) UNK 0
    Long-finned pilot whale Globicephala melas Western North Atlantic -, -, N 39,215 (0.3, 30,627, 2021) 306 5.7
    Short-finned pilot whale Globicephala macrorhynchus Western North Atlantic -, -, Y 18,726 (0.33, 14,292, 2021) 143 218
    Bottlenose dolphin Tursiops truncatus Western North Atlantic Offshore -, -, N 64,587 (0.24, 52,801, 2021) 507 28
    Bottlenose dolphin Tursiops truncatus Northern Migratory Coastal -, -, Y 6,639 (0.41, 4,759, 2016) 48 12.2-21.5
    Common dolphin Delphinus delphis Western North Atlantic -, -, N 93,100 (0.56, 59,897, 2021) 1,452 414
    Atlantic spotted dolphin Stenella frontalis Western North Atlantic -, -, N 31,506 (0.28, 25,042, 2021) 250 0
    Pantropical spotted dolphin Stenella attenuata Western North Atlantic -, D, N 2,757 (0.50, 1,56, 2021) 19 0
    Risso's dolphin Grampus griseus Western North Atlantic -, -, N 44,067 (0.19, 30,662, 2021) 307 18
    Rough-toothed dolphin Steno bredanensis Western North Atlantic -, -, N unk (unk, unk, 2021) undet 0
    Striped dolphin Stenella coeruleoalba Western North Atlantic -, -, N 48,274 (0.29, 38,040, 2021) 529 0
    Family Phocoenidae (porpoises):
    Harbor porpoise Phocoena phocoena Gulf of Maine/Bay of Fundy -, -, N 85,765 (0.53, 56,420, 2021) 649 145
    Order Carnivora—Pinnipedia
    Family Phocidae (earless seals):
    Harbor seal Phoca vitulina Western North Atlantic -, -, N 61,336 (0.08, 57,637, 2018) 1,729 339
    Gray seal Halichoerus grypus Western North Atlantic -, -, N 27,911 (0.20, 23,624, 2021) 1,512 4,570
    Harp seal Pagophilus groenlandicus Western North Atlantic -, -, N 7.6M (UNK, 7.1M, 2019) 426,000 178,573
    Information on the classification of marine mammal species can be found on the web page for The Society for Marine Mammalogy's Committee on Taxonomy ( https://www.marinemammalscience.org/science-and-publications/list-marine-mammal-species-subspecies/; Committee on Taxonomy (2022)).
    ESA status: Endangered (E), Threatened (T)/MMPA status: Depleted (D). A dash (-) indicates that the species is not listed under the ESA or designated as depleted under the MMPA. Under the MMPA, a strategic stock is one for which the level of direct human-caused mortality exceeds PBR, or which is determined to be declining and likely to be listed under the ESA within the foreseeable future. Any species or stock listed under the ESA is automatically designated under the MMPA as depleted and as a strategic stock.
    NMFS marine mammal stock assessment reports online at: https://www.fisheries.noaa.gov/national/marine-mammal-protection/marine-mammal-stock-assessments. CV is the coefficient of variation; N min is the minimum estimate of stock abundance.
    These values, found in NMFS's SARs, represent annual levels of human-caused mortality plus serious injury from all sources combined ( e.g., commercial fisheries, ship strike).
    In the proposed rule (89 FR 504, January 4, 2023), a population estimate of 368 was used which represented the best available science at the time of publication. However, since the publication of the proposed rule, a new estimate (n=340) was released in NMFS' draft 2023 SARs and has been incorporated into this final rule. The current draft SAR includes an estimated population (N best 340) based on sighting history through December 2021 (89 FR 5495, January 29, 2024). In October 2023, NMFS released a technical report identifying that the North Atlantic right whale population size based on sighting history through 2022 was 356 whales, with a 95 percent credible interval ranging from 346 to 363 (Linden, 2023); Total annual average observed North Atlantic right whale mortality during the period 2017-2021 was 7.1 animals and annual average observed fishery mortality was 4.6 animals. Numbers presented in this table (27.2 total mortality and 17.6 fishery mortality) are 2016-2020 estimated annual means, accounting for undetected mortality and serious injury.
    As noted in the draft 2023 SAR (89 FR 5495, January 29, 2024), abundance estimates may include sightings of the coastal form.
    There are two morphologically and genetically distinct forms of common bottlenose dolphin (Duffield et al., 1983; Mead and Potter, 1995; Rosel et al., 2009) described as the coastal and offshore forms in the western North Atlantic (Hersh and Duffield, 1990; Mead and Potter, 1995; Curry and Smith, 1997; Rosel et al., 2009). The two morphotypes are genetically distinct based upon both mitochondrial and nuclear markers (Hoelzel et al., 1998; Rosel et al., 2009). The genetic and morphological differences recently led to the coastal form being described as a new species, Tursiops erebennus (Costa et al., 2022; 89 FR 5495, January 29, 2024). Population estimates are based upon recent surveys in 2021.
    US Wind did not request take of these species; however, their exposure analysis demonstrates there is potential for harassment. Although these species are rare in the project area, NMFS would authorize a small amount of Level B harassment in the case of potential presence during pile driving.
    NMFS' stock abundance estimate (and associated PBR value) applies to the U.S. population only. Total stock abundance (including animals in Canada) is approximately 451,431. The annual M/SI value given is for the total stock.

    Table 4—Marine Mammal Hearing Groups

    [NMFS, 2018]

    Hearing group Generalized hearing range *
    Low-frequency (LF) cetaceans (baleen whales) 7 Hz to 35 kHz.
    Mid-frequency (MF) cetaceans (dolphins, toothed whales, beaked whales, bottlenose whales) 150 Hz to 160 kHz.
    High-frequency (HF) cetaceans (true porpoises, Kogia, river dolphins, cephalorhynchid, Lagenorhynchus cruciger & L. australis) 275 Hz to 160 kHz.
    Phocid pinnipeds (PW) (underwater) (true seals) 50 Hz to 86 kHz.
    * Represents the generalized hearing range for the entire group as a composite ( i.e., all species within the group), where individual species' hearing ranges are typically not as broad. Generalized hearing range chosen based on ~65-dB threshold from normalized composite audiogram, with the exception for lower limits for LF cetaceans (Southall et al., 2007) and PW pinniped (approximation).

    Table 5—Onset of PTS

    [NMFS, 2018]

    Hearing group PTS onset thresholds * (received level)
    Impulsive Non-impulsive
    Low-frequency (LF) cetaceans Cell 1: Lp ,0-pk,flat : 219 dB; L E, p ,LF,24h : 183 dB Cell 2: L E, p ,LF,24h : 199 dB.
    Mid-frequency (MF) cetaceans Cell 3: Lp ,0-pk,flat : 230 dB; L E, p ,MF,24h : 185 dB Cell 4: L E, p ,MF,24h : 198 dB.
    High-frequency (HF) cetaceans Cell 5: Lp ,0-pk,flat : 202 dB; L E, p ,HF,24h : 155 dB Cell 6: L E, p ,HF,24h : 173 dB.
    Phocid pinnipeds (PW) (Underwater) Cell 7: Lp ,0-pk.flat : 218 dB; L E, p ,PW,24h : 185 dB Cell 8: L E, p ,PW,24h : 201 dB.
    Otariid pinnipeds (OW) (Underwater) Cell 9: Lp ,0-pk,flat : 232 dB; L E, p ,OW,24h : 203 dB Cell 10: L E, p ,OW,24h : 219 dB.
    * Dual metric thresholds for impulsive sounds: Use whichever results in the largest isopleth for calculating PTS onset. If a non-impulsive sound has the potential of exceeding the peak sound pressure level thresholds associated with impulsive sounds, these thresholds are recommended for consideration.
    Note: Peak sound pressure level ( Lp ,0-pk ) has a reference value of 1 µPa, and weighted cumulative sound exposure level ( L E, p ) has a reference value of 1μPa s. In this table, thresholds are abbreviated to be more reflective of International Organization for Standardization standards (ISO, 2017). The subscript “flat” is being included to indicate peak sound pressure are flat weighted or unweighted within the generalized hearing range of marine mammals ( i.e., 7 Hz to 160 kHz). The subscript associated with cumulative sound exposure level thresholds indicates the designated marine mammal auditory weighting function (LF, MF, and HF cetaceans, and PW and OW pinnipeds) and that the recommended accumulation period is 24 hours. The weighted cumulative sound exposure level thresholds could be exceeded in a multitude of ways ( i.e., varying exposure levels and durations, duty cycle). When possible, it is valuable for action proponents to indicate the conditions under which these thresholds will be exceeded.

    Table 6—Maximum Level A Harassment and Level B Harassment Takes for All Activities That May Be Authorized During the Construction of the Project and Over the Course of the Five Years Covered by the Rule

    Marine mammal species Total take by Level A harassment that may be authorized Total take by Level B harassment that may be authorized
    North Atlantic right whale 0 10
    Fin whale 6 35
    Humpback whale 6 30
    Minke whale 9 58
    Sei whale 3 3
    Killer whale 0 9
    Atlantic spotted dolphin 0 168
    Coastal bottlenose dolphin 0 2,165
    Offshore bottlenose dolphin 0 2,755
    Bottlenose dolphin 0 258
    Common dolphin 0 488
    Long-finned pilot whale 0 48
    Short-finned pilot whale 0 33
    Pantropical spotted dolphin 0 15
    Risso's dolphin 0 70
    Rough-toothed dolphin 0 18
    Striped dolphin 0 138
    Harbor porpoise 6 68
    Gray seal 0 496
    Harbor seal
    Harp seal
    The final rule and LOA would be effective from January 1, 2025 through December 31, 2029, however, US Wind has not planned activities to occur in 2028 or 2029. As described in table 2, NMFS recognizes the potential for activity schedules to shift such that they occur during different timeframes within the five year effective period of the rule, including the potential for activities to occur in 2028 and 2029.
    Listed as Endangered under the ESA.
    The total take over 5 years represented here accounts for HRG surveys wherein the take may occur to either the Northern migratory coastal stock and/or the offshore stock of bottlenose dolphins.
    Take that may be authorized includes harbor seals, gray seals, and harp seals.

    Table 7—Maximum Number of Takes by Level A Harassment and Level B Harassment That May Be Authorized in Any One Year of the Project Relative to Stock Population Size

    Marine mammal species NMFS stock abundance Maximum annual Level A harassment Maximum annual Level B harassment Maximum annual take Maximum take (instances) as a percentage of stock abundance)
    North Atlantic right whale 338 0 4 4 1.18
    Fin whale 6,802 2 18 20 0.29
    Humpback whale 1,396 2 16 18 1.29
    Minke whale 21,968 6 41 47 0.21
    Sei whale 6,292 1 1 2 0.03
    Killer whale UNK 0 3 3 UNK
    Atlantic spotted dolphin 39,921 0 69 69 0.17
    Coastal bottlenose dolphin 6,639 0 1,591 1,591 24.0
    Offshore bottlenose dolphin 62,851 0 1,768 1,768 2.81
    Common dolphin 172,974 0 298 298 0.17
    Long-finned pilot whale 39,215 0 16 16 0.04
    Short-finned pilot whale 28,924 0 11 11 0.04
    Pantropical spotted dolphin 6,593 0 5 5 0.08
    Risso's dolphin 35,215 0 26 26 0.07
    Rough-toothed dolphin 136 0 6 6 4.41
    Striped dolphin 67,036 0 46 46 0.07
    Harbor porpoise 95,543 3 39 42 0.04
    Gray seal 27,300 0 341 341 1.25
    Harbor seal 61,336 0.56
    Harp seal 7.6M 0.004
    Year 2 (2026) represents the most overall impactful year.
    The values in this column represent the assumption that each take that may be authorized would occur to a unique individual. Given the scope of planned work, this is highly unlikely for species common to the project area ( e.g., North Atlantic right whales, humpback whales) such that the actual percentage of the population taken is less than the percentages identified here.
    Listed as Endangered under the ESA.
    Take that may be authorized is based on average group size.
    The amount of take identified includes the maximum amount of take that could occur from impact pile driving in any given year plus the maximum amount of take from HRG surveys in any given year, assuming all take from HRG surveys is allocated to both bottlenose dolphin stocks.
    Assumes 100 percent of the take by Level B harassment is from either the gray seal stock, harbor seal stock, or harp seal stock.

    Table 8—Vessel Strike Avoidance Separation Zones

    Marine mammal species Vessel separation zone (m)
    North Atlantic right whale 500
    Other ESA-listed species and large whales 100
    Other marine mammals 50
    With the exception of seals and delphinid(s) from the genera Delphinus, Lagenorhynchus, Stenella or Tursiops, as described below.

    Table 9—Minimum Visibility, Clearance, Shutdown, and Level B Harassment Zones During Impact Pile Driving, Assuming 10 d B of Attenuation

    Monitoring zone North Atlantic right whales Other large whales Delphinids and pilot whales Harbor porpoises Seals
    Minimum visibility zone Monopiles: 2,900 m.
    3-m pin piles: 1,400 m.
    1.8-m pin piles: 200 m.
    Clearance zone Any distance (visual) from the pile driving location or within PAM Monitoring Zone Monopiles: 5,250 m 3-m pin piles: 1,400 m. Monopiles: 500 m.
    1.8-m pin piles: 200 m. 3-m pin piles, 1.8-m pin piles: 200 m.
    Shutdown zone Any distance (visual) from the pile driving location or within PAM Monitoring Zone Monopiles: 2,900 3-m pin piles: 1,400 m. Monopiles: 250 m.
    1.8-m Pin piles: 100 m. 3-m pin piles, 1.8-m pin piles: 100 m.
    PAM monitoring zone 10,000 m.
    Level B Harassment (Acoustic Monopiles: 5,250 m.
    Range, R 95% ) 3-m pin piles: 500 m.
    1.8-m pin piles: 100 m.
    The minimum visibility zone is equal to the modeled maximum R 95 percent distances to the Level A harassment threshold for low-frequency cetaceans for monopiles and 3-m pin piles. The minimum visibility zone for 1.8-m pin piles is equal to the clearance zone which is double the modeled maximum R 95 percent distance to the Level B harassment threshold (100 m) and four times the modeled maximum R 95 percent distance to the Level A harassment threshold (50 m) for low frequency cetaceans. NMFS increased the 1.8 m pile minimum visibility zone given the very small zone sizes from this short (3 piles total) activity.
    The clearance zone for other large whales from monopile installation is equal to the modeled maximum R 95 percent distance to the Level B harassment threshold (5,250 m). The clearance zone for other large whales from 3-m pin pile installation is equal to the modeled maximum R 95 percent distance to the Level A harassment threshold (1,400 m) given the Level B harassment zone is less than this distance (500 m). The clearance zone for other large whales from 1.8-m pin pile installation is equal to twice the modeled maximum R 95 percent distance to the Level B harassment threshold given the very small Level B harassment zone (100 m) which could be encompassed by the bubble curtains.
    The clearance zone for non-large whales ( i.e., delphinids and pilot whales, harbor porpoises, and seals) from monopile and 3-m pin pile installation is equal to double the modeled maximum R 95 percent distance to the Level A harassment threshold for harbor porpoise (the most sensitive species). The clearance zone for 1.8-m pin pile installation is equal to double the modeled maximum R 95 percent distance to the Level B harassment threshold given Level A harassment thresholds were not exceeded for this activity ( i.e., 0 m). US Wind requested the clearance zone for non-large whales be identical for PSO implementation ease.
    The shutdown zones for other large whales from monopiles and 3-m pin pile installation are equal to the modeled maximum R 95 percent distances to the Level A harassment threshold for low-frequency cetaceans. The shutdown zone for other large whales from 1.8-m pin piles is equal to two times the modeled maximum R 95 percent distance to the Level A harassment threshold for low-frequency cetaceans.
    The shutdown zones for non large whales from monopile and 3-m pin pile installation are equal to the modeled maximum R 95 percent distance to the Level A harassment threshold for harbor porpoise (the most sensitive species). The shutdown zone for non large whales from 1.8-m pin pile installation is equal to the modeled maximum R 95 percent distance to the Level B harassment threshold, given the Level A harassment thresholds were not exceeded for this activity ( i.e., 0 m). US Wind requested the shutdown zone for non large whales be identical for PSO implementation ease.
    The PAM system must be capable of detecting baleen whales at 10,000 m during pile driving. The system should also be designed to detect other marine mammals; however, it is not required these other species be detected out to 10,000 m given higher frequency calls and echolocation clicks are not typically detectable at large distances.

    Table 10—HRG Survey Clearance and Shutdown Zones

    Marine mammal species Clearance zone (m) Shutdown zone (m)
    North Atlantic right whale 500 500
    Other ESA-listed species ( i.e., fin, sei, sperm whale) 500 100
    Other marine mammals 200 100
    With the exception of seals and delphinid(s) from the genera Delphinus, Lagenorhynchus, Stenella or Tursiops, as described below.

    Table 1 to Paragraph (d)

    Marine mammal species Scientific name Stock
    North Atlantic right whale Eubalaena glacialis Western Atlantic.
    Fin whale Balaenoptera physalus Western North Atlantic.
    Humpback whale Megaptera novaeangliae Gulf of Maine.
    Minke whale Balaenoptera acutorostrata Canadian Eastern Coastal.
    Sei whale Balaenoptera borealis Nova Scotia.
    Killer whale Orcinus orca Western North Atlantic.
    Atlantic spotted dolphin Stenella frontalis Western North Atlantic.
    Pantropical spotted dolphin Stenella attenuata Western North Atlantic.
    Bottlenose dolphin Tursiops truncatus Western North Atlantic—Offshore. Northern Migratory Coastal.
    Common dolphin Delphinus delphis Western North Atlantic.
    Long-finned pilot whale Globicephala melas Western North Atlantic.
    Short-finned pilot whale Globicephala macrorhynchus Western North Atlantic.
    Risso's dolphin Grampus griseus Western North Atlantic.
    Rough-toothed dolphin Steno bredanensis Western North Atlantic.
    Striped dolphin Stenella coeruleoalba Western North Atlantic.
    Harbor porpoise Phocoena phocoena Gulf of Maine/Bay of Fundy.
    Gray seal Halichoerus grypus Western North Atlantic.
    Harbor seal Phoca vitulina Western North Atlantic.
    Harp seal Pagophilus groenlandicus Western North Atlantic.