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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 Petrogas Pacific, LLC (Petrogas) to incidentally harass marine mammals during construction activities associated with Ferndale Pier Maintenance Activities in Ferndale, Washington.
DATES:
The authorization is effective from August 1, 2025 to July 31, 2026.
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/action/incidental-take-authorization-petrogas-pacific-llcs-ferndale-pier-maintenance-activities. In case of problems accessing these documents, please call the contact listed below.
FOR FURTHER INFORMATION CONTACT:
Robert Pauline, 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 January 3, 2024 we received a request from Petrogas for an IHA to take marine mammals incidental to Ferndale Pier Maintenance Activities in Ferndale, Washington. Following NMFS' review of the application, Petrogas submitted a revised version on March 26, 2024. The application was deemed adequate and complete on April 25, 2024. The notice of proposed IHA published for public comment on June 4, 2024 (89 FR 47903). Petrogas requested authorization of take of harbor seal, California sea lion, Steller sea lion and harbor porpoise by Level B harassment and, for harbor seal and harbor porpoise only, take by Level A harassment. Neither Petrogas nor NMFS expect serious injury or mortality to result from this activity and, therefore, an IHA is appropriate.
Description of the Specified Activity
Petrogas is planning to remove the existing timber Pier that has served as a loading facility since 1965 and replace it with a new structure that meets current industry best practices. The activity includes vibratory removal of existing timber piles and installation of steel piles by both vibratory and impact driving. Due to in-water work timing restrictions to protect Endangered Species Act (ESA)-listed salmonids, all planned in-water construction in this area is limited to a work window beginning August 1 and ending February 1. However, since the Strait of Georgia is a very large water body with a long fetch, calm in-water work conditions are typically only available from August to the end of October. In-water construction will occur for 17 days intermittently between August 1, 2025 and October 31, 2026. Take of marine mammals is anticipated to occur due to vibratory pile removal as well as impact and vibratory pile installation.
A detailed description of the planned project is provided in the Federal Register notice for the proposed IHA (89 FR 47903, June 4, 2024). A detailed description is not provided here. Please refer to that Federal Register notice for the description of the specific activity.
Comments and Responses
A notice of NMFS' proposal to issue an IHA to Petrogas was published in the Federal Register on June 4, 2024 (89 FR 47903). That notice described, in detail, Petrogas' 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. During the 30-day public comment period, NMFS did not receive any public comments.
Changes From the Proposed IHA to Final IHA
The notice of proposed IHA (89 FR 47903, June 4, 2024) indicated that the IHA would be effective from August 1, 2024 to July 31, 2025. Petrogas has decided to delay the start of the project by 1 year. The new effective dates are from August 1, 2025 to July 31, 2026.
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 ).
Table 1 lists all species or stocks for which exposure is expected for this activity and summarizes information related to the population or stock, including regulatory status under the MMPA and ESA and potential biological removal (PBR), where known. PBR is 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 (as described in NMFS' SARs). While no serious injury or mortality is anticipated or authorized here, PBR and annual serious injury and mortality from anthropogenic sources are included here as gross indicators of the status of the species or stocks and other threats.
Marine mammal abundance estimates presented in this document represent the total number of individuals that make up a given stock or the total number estimated within a particular study or survey area. NMFS' stock abundance estimates for most species represent the total estimate of individuals within the geographic area, if known, that comprises that stock. For some species, this geographic area may extend beyond U.S. waters. All managed stocks in this region are assessed in NMFS' Alaska and Pacific SARs. All values presented in table 1 are the most recent available at the time of publication (including from the draft 2023 SARs) and are available online at: ( https://www.fisheries.noaa.gov/national/marine-mammal-protection/marine-mammal-stock-assessment-reports ). All species that could potentially occur in the planned project area are included in table 2 of the IHA application. While the gray whale, minke whale, Dall's porpoise, and the Eastern North Pacific Northern Resident stock of killer whale have been reported in the area, the temporal and/or spatial occurrence of these species is such that take is not expected to occur, and they are not discussed further beyond the explanation provided in the Federal Register notice for the proposed IHA (89 FR 47903, June 4, 2024).
Table 1—Species for Which Take Could Occur in the Project Area
Common name | Scientific name | Stock | ESA/MMPA status; strategic (Y/N) | Stock abundance (CV, N min , most recent abundance survey) | PBR | Annual M/SI3 |
---|---|---|---|---|---|---|
Order Artiodactyla—Cetacea—Mysticeti (baleen whales) | ||||||
Family Balaenopteridae (rorquals) | ||||||
Humpback Whale | Megaptera novaeangliae | Central America/Southern Mexico—CA/OR/WA | E, D, Y | 1,494 (0.171, 1,284, 2021) | 3.5 | 14.9 |
Humpback Whale | Megaptera novaeangliae | Mainland Mexico—CA/OR/WA | T, D, Y | 3,477 (0.101, 3,185, 2018) | 43 | 22 |
Humpback Whale | Megaptera novaeangliae | Hawaii | -, -, N | 11,278 (0.56, 7,265, 2020) | 127 | 27.09 |
Odontoceti (toothed whales, dolphins, and porpoises) | ||||||
Family Delphinidae | ||||||
Killer Whale | Orcinus orca | Eastern North Pacific Southern Resident | E, D, Y | 73 (N/A, 73, 2022) | 0.13 | 0 |
Killer Whale | Orcinus orca | West Coast Transient | -, -, N | 349 (N/A, 349, 2018) | 3.5 | 0.4 |
Family Phocoenidae (porpoises) | ||||||
Harbor porpoise | Phocoena phocoena | Washington Inland Waters | -, -, N | 11,233 (0.37, 8,308, 2015) | 66 | ≥7.2 |
Order Carnivora—Pinnipedia | ||||||
Family Otariidae (eared seals and sea lions) | ||||||
California Sea Lion | Zalophus californianus | U.S. | -, -; N | 257,606 (N/A, 233,515, 2014) | 14,011 | >321 |
Steller Sea Lion | Eumetopias jubatus | Eastern | -, -; N | 36,308 (N/A, 36,308, 2022) | 2,178 | 93.2 |
Family Phocidae (earless seals) | ||||||
Harbor Seal | Phoca vitulina | Washington Northern Inland Waters | -, -, N | 16,451 (0.07, 15,462, 2019) | 928 | 40 |
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/). 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 coefficient of variation; N min is the minimum estimate of stock abundance. In some cases, CV is not applicable. | ||||||
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, vessel strike). Annual M/SI often cannot be determined precisely and is in some cases presented as a minimum value or range. |
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—Proxy Sound Source Levels for Pile Sizes and Driving Methods
Table 4—User Spreadsheet Inputs for Level A Harassment Isopleths
Inputs | 30-in steel impact installation | 30-in steel vibratory installation | 16-in timber vibratory removal |
---|---|---|---|
Spreadsheet Tab Used | (E.1) Impact Pile Driving (STATIONARY SOURCE: Impulsive, Intermittent) | (A.1) Vibratory Pile Driving (STATIONARY: Non-impulsive, Continuous) | |
Source Level (Single Strike/shot SEL) | 177 | ||
Peak | 210 | ||
RMS | 190 | 159 | 162 |
Weighting Factor Adjustment (kHz) | 2 | 2.5 | 2.5 |
Strikes per pile | 2000 | ||
Piles Per day | 1.5 | 1.5 | 20 |
Propagation (xLogR) | 15 | 15 | 15 |
Duration | 20 | 2 | |
Distance of source level measurement (meters) | 10 | 10 | 10 |
Table 5—Calculated Level A and Level B Harassment Isopleths (m) and Ensonified Areas
Pile size/type | Level A pinnipeds | Level A cetaceans | Level B | |||
---|---|---|---|---|---|---|
Harbor seal | Sea lions | LF | MF | HF | ||
Impact Installation | 160 dB threshold | |||||
30-in steel | 205.4 (0.139) | 15 (0.001) | 383.2 (0.463) | 13.7 (0.001) | 457.2 (0.665) | 464.2 (0.679) |
Vibratory Installation/Removal * | 120 dB threshold | |||||
16-in Timber Piles | 3.7 | 0.3 | 6.1 | 0.5 | 9.0 | 6,309.6 (62.5) |
30-in steel | 1.9 | 0.1 | 3.2 | 0.3 | 4.7 | 3,981 (24.9) |
* The Level A harassment isopleths associated with vibratory installation/removal are all below the minimum shutdown zone and result in very small ensonified areas. Therefore they are not provided in this table but will be included in the following calculated take tables. |
Table 6—Marine Mammal Species Densities Used for Exposure Calculations
Table 7—Calculated Take by Level A and Level B Harassment
Total days | 7 days | 7 days | 10 days | Requested level A take | |
---|---|---|---|---|---|
30-in steel impact driving | 30-in steel vibratory driving | 16-in timber vibratory removal | |||
Level A | Level A | Level A | Totals | Total | |
Humpback Whale | 0.009 | 0.000 | 0.000 | 0.009 | 0 |
Southern Resident Killer Whales | 0.000 | 0.000 | 0.000 | 0.000 | 0 |
Transient Killer whales | 0.000 | 0.000 | 0.000 | 0.000 | 0 |
Harbor Porpoise | 10.1 | 0.005 | 0.007 | 10.063 | 10 |
Steller Sea Lion | 0.000 | 0.000 | 0.000 | 0.000 | 0 |
Cali Sea Lion | 0.000 | 0.000 | 0.000 | 0.000 | 0 |
Harbor Seal | 0.737 | 0.002 | 0.002 | 0.741 | 1 |
Level B Calculated Take | Total Level B Calculated Take | Requested Level B Take | |||
Level B | Level B | Level B | Totals | ||
Humpback Whale | 0.013 | 0.471 | 1.689 | 2.172 | 0 |
Southern Resident Killer Whale | 0.037 | 1.359 | 4.878 | 6.275 | 0 |
Transient Killer Whale | 0.015 | 0.533 | 1.914 | 2.462 | 0 |
Harbor Porpoise | 10.271 | 376.405 | 1,350.927 | 1,738 | 1,738 |
Steller Sea Lion | 0.013 | 0.471 | 1.689 | 2.172 | 17 |
California Sea Lion | 0.085 | 3.119 | 11.195 | 14.400 | 51 |
Harbor Seal | 3.614 | 132.439 | 475.326 | 611.379 | 611 |
Table 8—Authorized Take of Marine Mammals by Level A and Level B Harassment by Species and Stock and Percent of Take by Stock
Common name | Stock | Stock abundance | Level A | Level B | Total authorized take | Authorized take as percentage of stock |
---|---|---|---|---|---|---|
Harbor porpoise | Washington Inland Waters | 11,233 | 10 | 1,738 | 1,748 | 15.56.4 |
Steller sea lion | Eastern U.S | 36,308 | 17 | 17 | 0.05 | |
California sea lion | U.S | 257,606 | 51 | 51 | 0.02 | |
Harbor seal | Washington Northern Inland | 16,451 | 1 | 611 | 612 | 3.7 |
Table 9—Shutdown Zones during Pile Installation and Removal ( m )
Pile size/type | Shutdown zone | Level B harassment monitoring zone | ||
---|---|---|---|---|
HF | Phocid | Otariid | ||
16-in timber Vibratory | 10 | 10 | 10 | 6,310 |
30-in steel Vibratory | 10 | 10 | 10 | 3,990 |
30-in steel Impact | 460 | 210 | 20 | 465 |