Takes of Marine Mammals Incidental to Specified Activities; Taking Marine Mammals Incidental to a Marine Geophysical Survey of the Chain Transform Fault in the Equatorial Atlantic Ocean

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Federal RegisterOct 2, 2024
89 Fed. Reg. 80214 (Oct. 2, 2024)
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    Department of Commerce National Oceanic and Atmospheric Administration
  • [RTID 0648-XE190]
  • AGENCY:

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

    ACTION:

    Notice; issuance of an incidental harassment authorization.

    SUMMARY:

    In accordance with the regulations implementing the Marine Mammal Protection Act (MMPA) as amended, notification is hereby given that NMFS has issued an incidental harassment authorization (IHA) to the Lamont-Doherty Earth Observatory of Columbia University (L-DEO) to incidentally harass marine mammals during survey activities associated with a marine geophysical survey at the Chain Transform Fault in the equatorial Atlantic Ocean.

    DATES:

    The authorization is effective from September 27, 2024 through September 26, 2025.

    ADDRESSES:

    Electronic copies of the 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-research-and-other-activities. In case of problems accessing these documents, please call the contact listed below.

    FOR FURTHER INFORMATION CONTACT:

    Jenna Harlacher, Office of Protected Resources, NMFS, (301) 427-8401.

    SUPPLEMENTARY INFORMATION:

    Background

    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 and either regulations are proposed or, if the taking is limited to harassment, a notice of a proposed IHA is provided to the public for review.

    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 in shorthand as “mitigation”); and requirements pertaining to the monitoring and reporting of the takings. The definitions of all applicable MMPA statutory terms cited above are included in the relevant sections below.

    Summary of Request

    On April 15, 2024, NMFS received a request from L-DEO for an IHA to take marine mammals incidental to conducting a marine geophysical survey of the Chain Transform Fault in the equatorial Atlantic Ocean. Following NMFS review of the application and additional clarifying information from L-DEO, NMFS deemed the application adequate and complete on May 22, 2024. L-DEO's request is for take of 28 marine mammal species by Level B harassment, and for take of a subset of 5 of these species, by Level A harassment. Neither L-DEO nor NMFS expect serious injury or mortality to result from this activity and, therefore, an IHA is appropriate. There are no changes from the proposed IHA to the final IHA.

    Description of Activity

    Researchers from the Woods Hole Oceanographic Institution, University of Delaware, University of New Hampshire, Boise State University and Boston College, with funding from the National Science Foundation, plan to conduct a high-energy seismic survey using airguns as the acoustic source from the research vessel (R/V) Marcus G. Langseth (Langseth), which is owned and operated by L-DEO. The survey would occur at the Chain Transform Fault, off the coast of Africa, in the equatorial Atlantic Ocean during austral summer 2024 in the Southern Hemisphere ( i.e., between October 2024 and February 2025). The survey would occur within International Waters more than 600 kilometers (km) in the Gulf of Guinea, Africa, in water depths ranging from approximately 2,000 to 5,500 meters (m). To complete this survey, the R/V Langseth would tow a 36-airgun array with a total discharge volume of approximately (~) 6,600 cubic inches (in3 ) at a depth of 9 to 12 m. The airgun array receiving system would consist of a 15 km long solid-state hydrophone streamer and 20 Ocean Bottom Seismometers (OBS). The airguns would fire at a shot interval of 37.5 m (~18 seconds (s)) during seismic acquisition. Approximately 2,058 km of total survey trackline are planned. Airgun arrays would introduce underwater sounds that may result in take, by Level A and Level B harassment, of marine mammals.

    A detailed description of the planned geophysical survey was provided in the Federal Register notice of the proposed IHA (89 FR 56158, July 8, 2024). Since that time, no changes have been made to the planned survey activities. Therefore, a detailed description is not provided here. Please refer to that Federal Register notice for the description of the specified activity.

    Comments and Responses

    A notice of NMFS' proposal to issue an IHA to L-DEO was published in the Federal Register on July 8, 2024 (89 FR 56158). That notice described, in detail, L-DEO's activity, the marine mammal species that may be affected by the activity, and the anticipated effects on marine mammals. In that notice, we requested public input on the request for authorization described therein, our analyses, the proposed authorization, and any other aspect of the notice of proposed IHA, and requested that interested persons submit relevant information, suggestions, and comments. The proposed notice was available for a 30-day public comment period. NMFS received no public comments.

    Description of Marine Mammals in the Area of Specified Activities

    Sections 3 and 4 of the application summarize available information regarding status and trends, distribution and habitat preferences, and behavior and life history of the potentially affected species. NMFS fully considered all of this information, and we refer the reader to these descriptions, instead of reprinting the information. Additional information regarding population trends and threats may be found in NMFS' Stock Assessment Reports (SARs; https://www.fisheries.noaa.gov/national/marine-mammal-protection/marine-mammal-stock-assessments ) and more general information about these species ( e.g., physical and behavioral descriptions) may be found on NMFS' website ( https://www.fisheries.noaa.gov/find-species). NMFS refers the reader to the aforementioned source for general information regarding the species listed in table 1.

    The populations of marine mammals found in the survey area do not occur within the U.S. exclusive economic zone (EEZ) and therefore, are not assessed in NMFS' SARs. For most species, there are no stocks defined for management purposes in the survey area, and NMFS is evaluating impacts at the species level. As such, information on potential biological removal level (PBR; defined by the MMPA as the maximum number of animals, not including natural mortalities, that may be removed from a marine mammal stock while allowing that stock to reach or maintain its optimum sustainable population) and annual levels of serious injury and mortality from anthropogenic sources are not available for these marine mammal populations. Abundance estimates for marine mammals in the survey location are lacking; therefore, the modeled abundances presented here are based on a variety of proxy sources, including the U.S Navy Atlantic Fleet Training and Testing Area Marine Mammal Density (AFTT) model (Roberts et al., 2023) and the International Whaling Commission (IWC) Population (Abundance) Estimates (IWC 2024). The modeled abundance is considered the best scientific information available on the abundance of marine mammal populations in the area.

    Table 1 lists all species that occur in the survey area that may be taken as a result of the planned survey and summarizes information related to the population, including regulatory status under the MMPA and Endangered Species Act (ESA).

    Table 1—Species Likely Impacted by the Specified Activities

    Common name Scientific name Stock ESA/MMPA status; strategic (Y/N) Modeled abundance
    Order Artiodactyla—Cetacea—Mysticeti (baleen whales)
    Family Balaenopteridae (rorquals):
    Blue Whale Balaenoptera musculus NA E, D, Y 191/2, 300
    Fin Whale Balaenoptera physalus NA E, D, Y 11,672
    Humpback Whale Megaptera novaeangliae NA -, -, N 4,990/ 42,000
    Common Minke Whale Balaenoptera acutorostrata NA -, -, N 13,784
    Antarctic Minke Whale Balaenoptera bonaerensis NA -, -, N 515,000
    Sei Whale Balaenoptera borealis NA E, D, Y 19,530
    Bryde's Whale Balaenoptera edeni NA -, -, N 536
    Odontoceti (toothed whales, dolphins, and porpoises)
    Family Physeteridae:
    Sperm Whale Physeter macrocephalus NA E, D, Y 64,015
    Family Kogiidae:
    Pygmy Sperm Whale Kogia breviceps NA -, -, N 26,043
    Dwarf Sperm Whale Kogia sima NA -, -, N
    Family Ziphiidae (beaked whales):
    Blainville's Beaked Whale Mesoplodon densirostris NA -, -, N 65,069
    Cuvier's Beaked Whale Ziphius cavirostris NA -, -, N
    Gervais' Beaked Whale Mesoplodon europaeus NA -, -, N
    Family Delphinidae:
    Killer Whale Orcinus orca NA -, -, N 972
    Short-Finned Pilot Whale Globicephala melas NA -, -, N 264,907
    Rough-toothed Dolphin Steno bredanensis NA -, -, N 32,848
    Bottlenose Dolphin Tursiops truncatus NA -, -, N 418,151
    Risso's Dolphin Grampus griseus NA -, -, N 78,205
    Common Dolphin Delphinus delphis NA -, -, N 473,260
    Striped Dolphin Stenella coeruleoalba NA -, -, N 412,729
    Pantropical Spotted Dolphin Stenella attenuata NA -, -, N 321,740
    Atlantic Spotted Dolphin Stenella frontalis NA -, -, N 259,519
    Spinner Dolphin Stenella longirostris NA -, -, N 152,511
    Clymene Dolphin Stenella clymene NA -, -, N 181,209
    Fraser's Dolphin Lagenodelphis hosei NA -, -, N 19,585
    Melon-headed Whale Peponocephala electra NA -, -, N 64,114
    Pygmy Killer Whale Feresa attenuata NA -, -, N 9,001
    False Killer Whale Pseudorca crassidens NA -, -, N 12,682
    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.
    Modeled abundance value from U.S Navy Atlantic Fleet Training and Testing Area Marine Mammal Density (AFTT) (Roberts et al., 2023) unless otherwise noted.
    Abundance of minke whales (species unspecified) for the Southern Hemisphere (IWC 2024)
    Abundance of blue whales (excluding pygmy blue whales) for Southern Hemisphere (IWC 2024)
    Abundance of humpback whales on Antarctic feeding grounds (IWC 2024)
    Pilot whale guild.
    Estimate includes dwarf and pygmy sperm whales.
    Beaked whale guild.

    Table 2—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.
    Otariid pinnipeds (OW) (underwater) (sea lions and fur seals) 60 Hz to 39 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 3—Predicted Radial Distances From the R/V Langseth Seismic Source to Isopleth Corresponding to Level B Harassment Threshold

    Airgun configuration Tow depth (m) Water depth (m) Predicted distances (in m) to the Level B harassment threshold
    4 strings, 36 airguns, 6,600 in 12 >1,000 6,733
    Maximum tow depth was used for conservative distances.
    Distance is based on L-DEO model results.

    Table 4—Modeled Radial Distance to Isopleths Corresponding to Level A Harassment Thresholds

    Low frequency cetaceans Mid frequency cetaceans High frequency cetaceans
    PTS SEL cum 426.9 0 1.3
    PTS Peak 38.9 13.6 268.3
    The largest distance (in bold ) of the dual criteria (cumulative sound exposure level (SEL cum ) or Peak) was used to estimate threshold distances and potential takes by Level A harassment.

    Table 5—Authorized Take

    Species Estimated take Authorized take Modeled abundance Percent of abundance
    Level B Level A Level B Level A
    Humpback whale 39 2 39 2 4,990 0.82
    Bryde's whale 4 0 4 0 536 0.75
    Minke whale 23 1 23 1 13,784 0.17
    Fin whale 0 0 1 0 11,672 0.01
    Sei whale 11 1 11 1 19,530 0.06
    Blue whale 1 0 1 0 191 0.52
    Sperm whale 110 0 110 0 64,015 0.17
    Beaked whales 106 0 106 0 65,069 0.16
    Risso's dolphin 88 0 88 0 78,205 0.11
    Rough-toothed dolphin 166 0 166 0 32,848 0.51
    Bottlenose dolphin 1,229 2 1,231 0 418,151 0.30
    Pantropical spotted dolphin 46 0 76 0 321,740 0.02
    Atlantic spotted dolphin 435 1 436 0 259,519 0.17
    Spinner dolphin 898 2 900 0 152,511 0.59
    Striped dolphin 55 0 73 0 412,729 0.02
    Clymene dolphin 1,038 2 1,040 0 181,209 0.57
    Fraser's dolphin 110 0 110 0 19,585 0.56
    Common dolphin 27 0 92 0 473,206 0.02
    Short-finned pilot whale 1,301 2 1,303 0 264,907 0.49
    Melon-headed whale 502 1 503 0 64,114 0.78
    False killer whale 99 0 99 0 12,682 0.78
    Pygmy killer whale 71 0 71 0 9,001 0.79
    Killer whale 1 0 5 0 972 0.51
    Kogia spp 122 5 122 5 26,043 0.49
    Modeled abundance (Roberts et al. 2023) or North Atlantic abundance (NAMMCO 2023), where applicable.
    Requested take authorization is expressed as percent of population for the AFTT Area only (Roberts et al. 2023).
    Takes assigned equally between Common minke whales (11 Level B takes and 1 Level A take) and Antarctic minke whales (12 Level B takes).
    Beaked whale guild. Includes Cuvier's beaked whale, Blaineville's beaked whale, and Gervais' beaked whale.
    Takes based on density for Globicephala sp. All takes are assumed to be for short-finned pilot whales.
    Kogia spp. Includes Pygmy sperm whale and Dwarf sperm whale.
    Takes rounded to a mean group size (Weir 2011).