Takes of Marine Mammals Incidental to Specified Activities; Taking Marine Mammals Incidental to Pier 58 Reconstruction and Pier 63 Removal Projects in Seattle, Washington, 12089-12114 [2022-04499]

Agencies

• DEPARTMENT OF COMMERCE
• National Oceanic and Atmospheric Administration

[Federal Register Volume 87, Number 42 (Thursday, March 3, 2022)]
[Notices]
[Pages 12089-12114]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2022-04499]


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DEPARTMENT OF COMMERCE

National Oceanic and Atmospheric Administration

[RTID 0648-XB627]


Takes of Marine Mammals Incidental to Specified Activities; 
Taking Marine Mammals Incidental to Pier 58 Reconstruction and Pier 63 
Removal Projects in Seattle, Washington

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

ACTION: Notice; proposed incidental harassment authorizations; request 
for comments on proposed authorizations and possible renewals.

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SUMMARY: NMFS has received a request from the City of Seattle (City) 
for authorization to take marine mammals incidental to the Pier 58 
Reconstruction Project and Pier 63 Removal Project in Seattle, 
Washington. Pursuant to the Marine Mammal Protection Act (MMPA), NMFS 
is requesting comments on its proposal to issue two incidental 
harassment authorizations (IHAs) to the City to incidentally take, by 
Level A and Level B harassment only, marine mammals during the 
specified activities. NMFS is also requesting comments on possible one-
time, one-year renewals of each IHA that could be issued under certain 
circumstances and if all requirements are met, as described in Request 
for Public Comments at the end of this notice. NMFS will consider 
public comments prior to making any final decision on the issuance of 
the requested MMPA authorizations and agency responses will be 
summarized in the final notice of our decision.

DATES: Comments and information must be received no later than April 4, 
2022.

ADDRESSES: Comments should be addressed to Jolie Harrison, Chief, 
Permits and Conservation Division, Office of Protected Resources, 
National Marine Fisheries Service. Written comments should be submitted 
via email to [email protected].
    Instructions: NMFS is not responsible for comments sent by any 
other method, to any other address or individual, or received after the 
end of the comment period. Comments, including all attachments, must 
not exceed a 25-megabyte file size. All comments received are a part of 
the public record and will generally be posted online at 
www.fisheries.noaa.gov/permit/incidental-take-authorizations-under-marine-mammal-protection-act without change. All personal identifying

[[Page 12090]]

information (e.g., name, address) voluntarily submitted by the 
commenter may be publicly accessible. Do not submit confidential 
business information or otherwise sensitive or protected information.

FOR FURTHER INFORMATION CONTACT: Amy Fowler, Office of Protected 
Resources, NMFS, (301) 427-8401. 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/permit/incidental-take-authorizations-under-
marine-mammal-protection-act. In case of problems accessing these 
documents, please call the contact listed above.

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 incidental harassment authorization 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 mitigation, 
monitoring and reporting of the takings are set forth. The definitions 
of all applicable MMPA statutory terms cited above are included in the 
relevant sections below.

National Environmental Policy Act

    To comply with the National Environmental Policy Act of 1969 (NEPA; 
42 U.S.C. 4321 et seq.) and NOAA Administrative Order (NAO) 216-6A, 
NMFS must review our proposed action (i.e., the issuance of an IHA) 
with respect to potential impacts on the human environment.
    This action is consistent with categories of activities identified 
in Categorical Exclusion B4 (IHAs with no anticipated serious injury or 
mortality) of the Companion Manual for NOAA Administrative Order 216-
6A, which do not individually or cumulatively have the potential for 
significant impacts on the quality of the human environment and for 
which we have not identified any extraordinary circumstances that would 
preclude this categorical exclusion. Accordingly, NMFS has 
preliminarily determined that the issuance of the proposed IHAs 
qualifies to be categorically excluded from further NEPA review.
    We will review all comments submitted in response to this notice 
prior to concluding our NEPA process or making a final decision on the 
IHA requests.

Summary of Request

    On July 21, 2021, NMFS received two requests from the City for an 
IHA to take marine mammals incidental to the Pier 63 Removal Project 
and, separately, the Pier 58 Reconstruction Project on the waterfront 
in downtown Seattle, Washington. The City submitted revised 
applications for each project on September 29, 2021 and January 3, 
2022. Both applications were deemed adequate and complete on January 
26, 2022. The City's request is for take of a small number of 12 
species of marine mammals, by Level B harassment only for the Pier 63 
Removal Project, and by Level A and Level B harassment for the Pier 58 
Reconstruction Project. Neither the City nor NMFS expects serious 
injury or mortality to result from these activities and, therefore, 
IHAs are appropriate.

Description of Proposed Activities

Overview

    The City is proposing to reconstruct Waterfront Park along the 
Elliott Bay shoreline in Seattle, Washington. When replaced, Waterfront 
Park will be renamed Pier 58 in reference to the original structure and 
to avoid confusion with the larger waterfront park promenade that will 
be reconstructed along Alaskan Way. The City intends to repair 
structural and safety deficiencies and optimize public access and 
recreational uses of the piers, including reconfiguring Waterfront Park 
to better accommodate programming while providing views of Elliott Bay 
toward the Olympic Mountain Range. The Pier 58 reconstruction project 
includes vibratory removal of existing in-water piles and vibratory and 
impact installation of new piles to support the expanded overwater 
structure.
    The City also plans to remove Pier 63 from the downtown Seattle 
waterfront. The structural integrity of the pier has deteriorated and 
the pier has been closed to the public for safety. Removing Pier 63 
will leave the nearshore environment open for improved ecosystem 
function and salmonid migration. The project includes vibratory removal 
of existing in-water piles; no plans have been made to reconstruct Pier 
63, therefore no new piles will be installed.
    The City submitted an individual IHA application for each project. 
However, given the City applied for both projects concurrently, the 
projects' close proximity to each other, and similarities in the 
proposed activities and potential impacts on marine mammals, NMFS is 
using this single Federal Register notice to solicit public comments on 
the issuance of the two similar, but separate, IHAs.

Dates and Duration

    In-water work at both piers will occur during the in-water work 
window designated by NMFS, the U.S. Army Corps of Engineers, and the 
Washington State Department of Fish and Wildlife, which is imposed to 
avoid in-water construction when Endangered Species Act (ESA)-listed 
juvenile salmonids are most likely to be present. For the Seattle 
waterfront, this window is anticipated to be September 1 through 
February 15. The City expects Pier 58 reconstruction (including above-
water construction that does not have the potential to take marine 
mammals) to take a little over a year to complete, from August 2022 to 
December 2023, with a total of 70 days of in-water work expected during 
the designated window. Funding for this project has been secured. Pier 
63 will be removed during one in-water work season, with a total of 47 
days of in-water work expected. Pier 63 may be removed during the 
September 2022 to February 2023 or September 2023 to February 2024 work 
window, depending on when funding is made available. Both IHAs would be 
valid from August 1, 2022 through July 31, 2023. If funding for Pier 63 
removal is not authorized during that period, the City will request the 
IHA be reissued for the following year. Due to this possibility, the 
analysis that follows for the Pier 63 Removal Project considers 
possible effects on marine mammals during either the August 2022 
through July 2023 period or the August 2023

[[Page 12091]]

through July 2024 period, based on the current best available science.

Specific Geographic Region

    Both piers are located along the Seattle waterfront on Elliott Bay, 
which is an 8 square mile (mi\2\) (21 square kilometer (km\2\)) urban 
embayment in central Puget Sound. Pier 58 is approximately \1/4\ mile 
(0.4 km) north of Pier 63, with several occupied piers in between. The 
Seattle waterfront includes land and piers used for businesses, 
residences, transportation facilities (e.g., ferries, cargo ships, 
cruise ships), public services (e.g., fire station, utilities), city 
parks, and other recreational elements. West Point and Alki Point are 
considered the northern and southern entrances of Elliott Bay, 
respectively, with downtown Seattle serving as the eastern boundary of 
the bay. Bainbridge Island is located approximately 7 miles (11.3 km) 
to the west of downtown Seattle. The inner bay receives fresh water 
from the Duwamish River and most of the stormwater runoff from 
approximately 26 mi\2\ (67 km\2\) of highly developed land in 
metropolitan Seattle. Elliott Bay is an important industrial region and 
home to the Port of Seattle, which, coupled with the Port of Tacoma 
located approximately 22 miles (35 km) to the south, ranked as the 
nation's fifth busiest U.S. seaport in 2020 (Northwest Seaport 
Alliance, 2021). Water depths in the area range from less than 10 feet 
(ft; 3.05 meters (m)) along the seawall to nearly 600 ft (183 m) at the 
outer extent of the bay.

Detailed Description of Specific Activities

    Waterfront Park (hereafter referred to as Pier 58) was a public 
pier with substantial structural deficiencies. The pier pulled away 
from the waterfront in August 2020 and was closed to public access. 
Based on the known structural deficiencies, the City determined that 
emergency demolition was required for public safety. During initial 
demolition work in September 2020, a substantial portion of the pier 
collapsed into the water, thus necessitating an additional in-water 
activity of concrete demolition. The City conducted marine mammal 
monitoring during the emergency demolition work to avoid take of 
Southern Resident killer whales (Orcinus orca) and document occurrence 
and take of other marine mammals. The City removed the minimum number 
of piles and over-water structures necessary to protect the integrity 
of the seawall and maintain a safe environment. The remainder of the 
existing piles will be removed and replaced under the proposed IHA.
    Pier 58 will be reconstructed to maintain public park space and 
improve access, safety, and flexibility in use, while offering 
expansive views of Elliott Bay and the Olympic Mountains. The 
reconstructed pier will be 47,280 square feet and will include the 
installation of 120 permanent 30-inch steel piles. The decking will 
consist of both pre-cast concrete panels and a cast-in-place concrete 
deck slab. There will also be a 770 square foot area of grating to 
provide additional lighting to the existing intertidal salmon migratory 
corridor. The new park will feature a new public plaza, maintain the 
Fitzgerald fountain, and create a new children's play area, seating 
areas, and a large lawn and trees in planters to provide shade.
    The reconstructed Pier 58 is also designed with an approximately 
4,962-square-foot open water habitat area to provide natural lighting 
of the shallow water habitat near the shore (located at depths less 
than -10 feet mean lower-low water (MLLW)) that will enhance nearshore 
habitat for a variety of species, such as juvenile salmon that use the 
nearshore area during migratory periods and comprise part of the prey 
base for many marine mammal species. An expanded intertidal habitat 
bench with the top surface at MLLW, sloping to a foundation rock sill 
would be installed in this new open water area to facilitate 
recruitment of native invertebrate and algal species. Due to the new 
configuration, the replacement pier will cover up an existing habitat 
substrate patch that was created as part of the Elliot Bay Seawall 
Project. To address loss of function of this habitat feature, the City 
will install an equal area of new habitat substrate enhancement to 
replicate the existing feature adjacent to Pier 58, further north 
between the Seattle Aquarium (Pier 59) and Pier 62. The new substrate 
enhancement will improve benthic habitat for juvenile crabs and other 
invertebrates and will generally improve productivity and support food 
web processes. The substrate enhancement will consist of an 
approximately 2,000 square foot, 2-foot thick layer of 1.5-inch 
subtidal habitat gravel and will be located at elevations between 
approximately -10 to -20 feet MLLW. This habitat work will not result 
in the take of marine mammals.
    A total of 31 existing steel H-piles and timber piles will be 
removed in whole, wherever possible, by pulling the piles using a 
vibratory extraction method or clamshell bucket. If a timber pile 
breaks above the mudline during removal, the City will attempt to pull 
the remainder of the pile in a way that minimizes disturbance of 
sediment; otherwise, it will be cut below the mudline. All creosote-
treated wood and steel that is removed will be disposed of in 
accordance with appropriate regulations.
    Once all existing piles have been removed, the City will begin the 
reconstruction by using a vibratory hammer to install 100 24-inch steel 
pipe template piles, which will all subsequently be removed using the 
same vibratory hammer. The City anticipates the contractor will use 
approximately 6 template piles at a time, for every 4 permanent piles, 
so that the template piles can be re-used. The City will then install a 
total of 120 permanent 30-inch steel pipe piles using a vibratory 
hammer, followed by an impact hammer to ``proof'' the pilings to their 
maximum depth and load-bearing capacity. All impact pile driving will 
be conducted using a bubble curtain surrounding the pile (see Proposed 
Mitigation). The City does not plan to conduct pile driving with 
multiple hammers concurrently.

                                            Table 1--Summary of Piles To Be Installed and Removed at Pier 58
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                                                                                                                                           Maximum days
          Pile type and size                            Method                    Number of     Maximum piles   Duration or strikes per       of pile
                                                                                    piles          per day                pile                driving
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Steel H-pile, 14-inch timber pile.....  Vibratory removal....................              31              20  20 minutes...............              10
24-inch steel pipe pile...............  Vibratory installation...............         \a\ 100              10  15 minutes...............              10
24-inch steel pipe pile...............  Vibratory removal....................         \a\ 100              10  5 minutes................              10
30-inch steel pipe pile...............  Vibratory installation...............         \b\ 120               4  45 minutes...............          \c\ 40
30-inch steel pipe pile...............  Impact installation..................         \b\ 120               3  400 strikes..............          \c\ 40
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[[Page 12092]]

 
    Total.............................  Vibratory and impact.................             251  ..............  .........................              70
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\a\ These same 100 piles will be installed and later removed.
\b\ These same 120 piles will be installed first using a vibratory hammer, than finished with an impact hammer.
\c\ Vibratory and impact installation of 30-inch piles will occur on the same 40 days.

    Pier 63 was previously used as a public open space where concerts 
and special events were hosted, but the pier has deteriorated and can 
no longer support heavy loads and is no longer in use. The City plans 
to demolish and remove the existing pier (with a total over-water area 
of 35,108 square feet), including removal of 900 14-inch timber piles 
and 8 30-inch steel pipe piles. During demolition, broken piles and 
debris from previous pier configurations will also be removed, as 
feasible, to comply with Washington State Department of Natural 
Resources lease terms. The number of broken piles to be removed is 
unknown but would be removed with a clamshell bucket and pulled or cut 
below the mudline. Broken piles and debris removed without the use of a 
vibratory hammer is not expected to result in take of marine mammals.
    During pile removal for Pier 63, decking and framing will be 
removed using heavy equipment or by workers on the deck. Timber piles 
will be removed in whole, wherever possible, by pulling the piles using 
a vibratory extraction method or clamshell bucket. If a pile breaks 
above the mudline during removal, then an attempt will be made to pull 
the remainder of the pile in a way that minimizes disturbance of 
sediments; otherwise, it will be cut below the mudline. All creosote-
treated wood that is removed will be disposed of in accordance with 
appropriate regulations. Steel piles will be removed using vibratory 
extraction. The vibratory hammer will be positioned on a barge adjacent 
to the pier.

                               Table 2--Summary of Piles To Be Removed at Pier 63
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                                                                   Maximum piles   Duration  per   Maximum days
                    Pile type                        Number of     removed  per        pile           of pile
                                                       piles            day          (minutes)        removal
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14-inch timber pile.............................             900              20              20              45
30-inch steel pipe pile.........................               8               4              45               2
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    Proposed mitigation, monitoring, and reporting measures are 
described in detail later in this document (please see Proposed 
Mitigation and Proposed Monitoring and Reporting).

Description of Marine Mammals in the Area of Specified Activities

    Sections 3 and 4 of the applications summarize available 
information regarding status and trends, distribution and habitat 
preferences, and behavior and life history, of the potentially affected 
species, and can be found at https://www.fisheries.noaa.gov/permit/
incidental-take-authorizations-under-marine-mammal-protection-act. All 
of this information was fully considered and we refer the reader to 
these descriptions, incorporated here by reference, instead of 
reprinting the information. Additional information regarding population 
trends and threats may be found in NMFS's 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's website (https://www.fisheries.noaa .gov/find-species).
    Table 3 lists all species or stocks for which take is expected and 
proposed to be authorized for both proposed IHAs, and summarizes 
information related to the population or stock, including regulatory 
status under the MMPA and ESA and potential biological removal (PBR), 
where known. For taxonomy, we follow Committee on Taxonomy (2021). 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's 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's 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 values for each managed stock presented in 
Table 3 are the most recent available at the time of publication and 
are available in the 2020 SARs (Carretta et al., 2021, Muto et al., 
2021) and draft 2021 SARs (available online at: https://www.fisheries.noaa.gov/national/marine-mammal-protection/draft-marine-
mammal-stock-assessment-reports).

[[Page 12093]]



                                               Table 3--Marine Mammals That Could Occur in the Survey Area
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                                                                                         ESA/MMPA status;    Stock abundance  (CV,
             Common name                  Scientific name               Stock             strategic (Y/N)      Nmin, most recent       PBR     Annual  M/
                                                                                                \1\          abundance survey) \2\               SI \3\
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                                          Order Cetartiodactyla--Cetacea--Superfamily Mysticeti (baleen whales)
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Family Eschrichtiidae:
    Gray whale......................  Eschrichtius robustus..  Eastern N Pacific......  -, -, N             26,960 (0.05, 25,849,         801        131
                                                                                                             2016).
Family Balaenopteridae (rorquals):
    Humpback whale..................  Megaptera novaeangliae.  California/Oregon/       E, D, Y             4,973 (0.05, 4,776,          28.7     >=48.6
                                                                Washington.                                  2018).
    Minke whale.....................  Balaenoptera             California/Oregon/       -, -, N             915 (0.792, 509, 2018)        4.1     >=0.59
                                       acutorostrata.           Washington.
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                                            Superfamily Odontoceti (toothed whales, dolphins, and porpoises)
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Family Delphinidae:
    Long Beaked Common Dolphin......  Delphinus capensis.....  California.............  -, -, N             83,379 (0.216, 69,636,        668     >=29.7
                                                                                                             2018).
    Bottlenose Dolphin..............  Tursiops truncatus.....  California Coastal.....  -, -, N             453 (0.06, 346, 2011).        2.7      >=2.0
    Killer Whale....................  Orcinus orca...........  Southern Resident......  E, D, Y             72 (N/A, 72, 2020)....       0.13      >=0.4
                                                               West Coast Transient...  -, -, N             349 \4\ (N/A, 349,            3.5        0.4
                                                                                                             2018).
Family Phocoenidae (porpoises):
    Harbor Porpoise.................  Phocoena phocoena......  Washington Inland        -, -, N             11,233 (0.37, 8,308,           66      >=7.2
                                                                Waters.                                      2015).
    Dall's Porpoise.................  Phocoenoides dalli.....  California/Oregon/       -, -, N             16,498 (0.61, 10,286,          99     >=0.66
                                                                Washington.                                  2019).
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                                                         Order Carnivora--Superfamily Pinnipedia
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Family Otariidae (eared seals and
 sea lions):
    California Sea Lion.............  Zalophus californianus.  U.S....................  -, -, N             257,606 (N/A,233,515,      14,011       >320
                                                                                                             2014).
    Steller Sea Lion................  Eumetopias jubatus.....  Eastern................  -, -, N             43,201 \5\ (see SAR,        2,592        112
                                                                                                             43,201, 2017).
Family Phocidae (earless seals):
    Harbor Seal.....................  Phoca vitulina.........  Washington Northern      -, -, N             11,036 \6\ (UNK, UNK,         UND        9.8
                                                                Inland Waters.                               1999).
    Northern Elephant Seal..........  Mirounga angustirostris  California Breeding....  -, -, N             187,386 (N/A, 85,369,       5,122       13.7
                                                                                                             2013).
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\1\ 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.
\2\ NMFS marine mammal stock assessment reports online at: https://www.fisheries.noaa.gov/national/marine-mammal-protection/marine-mammal-stock-
  assessment-reports-region. CV is coefficient of variation; Nmin is the minimum estimate of stock abundance.
\3\ 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). Annual mortality/serious injury (M/SI) often cannot be determined precisely and is in some cases presented as a
  minimum value or range.
\4\ Based on counts of individual animals identified from photo-identification catalogues. Surveys for abundance estimates of these stocks are conducted
  infrequently.
\5\ Best estimate of pup and non-pup counts, which have not been corrected to account for animals at sea during abundance surveys.
\6\ The abundance estimate for this stock is greater than eight years old and is therefore not considered current. PBR is considered undetermined for
  this stock, as there is no current minimum abundance estimate for use in calculation. We nevertheless present the most recent abundance estimates, as
  these represent the best available information for use in this document.

    As indicated above, all 12 species (with 13 managed stocks) in 
Table 3 temporally and spatially co-occur with the activities to the 
degree that take is reasonably likely to occur, and we propose 
authorizing it. The Pacific white-sided dolphin (Lagenorhynchus 
obliquidens) is a rare visitor to the inland waters of Puget Sound 
(Orca Network, 2021). However, they have not been observed during 
recent marine mammal monitoring for projects in Elliott Bay (e.g., 
WSDOT 2021; Anchor QEA 2019) and are considered unlikely to occur in 
the area during the City's proposed activities. The City has not 
requested take of Pacific white-sided dolphins for either project and 
NMFS does not anticipate or propose to authorize take of this species. 
Therefore, Pacific white-sided dolphins are not discussed further in 
this document.

Humpback Whale

    Humpback whales are found in coastal waters of Washington as they 
migrate from feeding grounds in Alaska to California to winter breeding 
grounds in Mexico. Humpbacks used to be considered only rare visitors 
to Puget Sound. In 1976 and 1978, two sightings were reported in Puget 
Sound and one sighting was reported in 1986 (Osborne et al., 1988; 
Calambokidis and Steiger 1990; Calambokidis and Baird 1994). Humpback 
whale occurrence in Puget Sound has been steadily increasing since 
2000, with some individuals remaining in the area through the winter 
(Calambokidis et al., 2018). Prior to 2016, humpback whales were listed 
under the ESA as an endangered species worldwide. Following a 2015 
global status review (Bettridge et al., 2015), NMFS delineated 14 
distinct population segments (DPSs) with different listing statuses (81 
FR 62259; September 8, 2016) pursuant to the ESA. The DPSs that occur 
in U.S. waters do not necessarily equate to the existing stocks 
designated under the MMPA and shown in Table 1. Because MMPA stocks 
cannot be portioned, i.e., parts managed as ESA-listed while other 
parts managed as not ESA-listed, until such time as the MMPA stock 
delineations are reviewed in light of the DPS designations, NMFS 
considers the existing humpback whale stocks under the MMPA that 
overlap with endangered or threatened DPSs to be depleted for MMPA 
management purposes (e.g., selection of a recovery factor, stock 
status). All humpback whales in the project areas would be from the 
California/Oregon/Washington stock. Within Puget Sound, three DPSs may 
occur and be taken incidental to the City's activities: The Hawai'i DPS 
(not listed), Mexico DPS (threatened),

[[Page 12094]]

and Central America DPS (endangered). According to Wade et al. (2021), 
the probability that humpback whales encountered in Washington and 
Southern British Columbia waters are as follows: Hawai'i DPS, 69 
percent; Mexico DPS, 25 percent; and Central America DPS, 6 percent. We 
therefore assume that the numbers of humpback whales taken incidental 
to the City's proposed activities would fall under the same relative 
proportions. Critical habitat for Mexico and Central America DPS 
humpback whales has been established on the outer coast of Washington 
(86 FR 21082; April 21, 2021) but none has been designated within Puget 
Sound.
    Entanglement in fishing gear and marine debris is considered a 
primary threat to humpback whales in the northeast Pacific. 
Entanglements are the most commonly identified cause of death and 
injury among humpback whales along California, Oregon, and Washington 
(Carretta et al. 2013, 2019), and probably cause a modest reduction in 
the size or growth rate of the Central America and Mexico DPSs 
(Bettridge et al., 2015). Humpbacks were the second most frequently 
entangled whale species (after gray whales) in this region from 1982 to 
2013, averaging 2.1 reports per year (Sato and Wiley, 2021). However, 
actual numbers of entanglements were likely much higher, as indicated 
by photographic data showing scarring from past incidents on half or 
more of the humpback whales occurring off these states (Robbins et al., 
2007). Most humpback entanglements in Washington involve trap/pot gear, 
especially from commercial Dungeness crab fisheries (Saez et al., 2013; 
NMFS 2017).
    Humpback whales are one of the most commonly vessel-struck whale 
species in some areas of the world (Jensen and Silber 2004; Neilson et 
al., 2012; Hill et al., 2017). For example, in Alaskan and Hawaiian 
waters, members of the Hawaii DPS experienced an average of at least 
4.0 deaths and serious injuries per year because of collisions from 
2012 to 2016 (Muto et al., 2019). In Washington, just two humpback 
whales were reported killed by vessel strikes from 1980 to 2017 
(Douglas et al., 2008; Carretta et al., 2013, 2019). The state has 
several areas where heavy vessel traffic poses a higher collision risk 
for humpback whales. These include the mouths of the Strait of Juan de 
Fuca and Columbia River, the north-south shipping lane that parallels 
the outer coast, and the Strait of Juan de Fuca and other parts of the 
Salish Sea (Williams and O'Hara 2010; Nichol et al., 2017; Rockwood et 
al., 2017).

Gray Whale

    Gray whales generally spend the summer and fall in Arctic feeding 
grounds and winter to early spring in Mexican breeding areas. Between 
October and February, the species migrates south along the U.S. West 
Coast, returning north between February and July (Carretta et al., 
2021). A subpopulation of the Eastern North Pacific stock, referred to 
as the Pacific Coast Feeding Group (PCFG), remains along the Washington 
and Oregon coast to feed for extended periods while the rest of the 
stock continues along their migratory path (Calambokidis et al., 2018). 
Like humpback whales, occurrence of gray whales in Puget Sound has been 
steadily increasing in recent years. Occurrence of gray whales in Puget 
Sound is generally highest between February and May. Most gray whales 
remain further north in Puget Sound, concentrating in the waters around 
Whidbey Island, but some venture south, including into Elliott Bay near 
the proposed activities (Orca Network, 2021).
    Biologically Important Areas (BIAs) for feeding gray whales along 
the coasts of Washington, Oregon, and California have been identified, 
including northern Puget Sound, Northwestern Washington, and Grays 
Harbor in Washington, Depoe Bay and Cape Blanco and Orford Reef in 
Oregon, and Point St. George in California; most of these areas are of 
importance from late spring through early fall (Calambokidis et al., 
2015). BIAs have also been identified for migrating gray whales along 
the entire coasts of Washington (including the inland waters of Puget 
Sound), Oregon, and California; although most whales travel within 10 
km from shore, the BIAs were extended out to 47 km from the coastline 
(Calambokidis et al., 2015).
    On May 30, 2019, NMFS declared an unusual mortality event (UME) for 
gray whales after elevated numbers of strandings occurred along the 
U.S. west coast. As of January 7, 2022, a total of 502 stranded gray 
whales have been reported, including 256 in the United States (117 in 
Alaska, 56 in Washington, 12 in Oregon, and 71 in California), 225 in 
Mexico, and 21 in Canada. Full or partial necropsy examinations were 
conducted on a subset of the whales. Preliminary findings in several of 
the whales have shown evidence of emaciation. These findings are not 
consistent across all of the whales examined, so more research is 
needed. The UME is ongoing, and NMFS continues to investigate the 
cause(s). Additional information about the UME is available at https://www.fisheries.noaa.gov/national/marine-life-distress/2019-2020-gray-
whale-unusual-mortality-event-along-west-coast.

Minke Whale

    The International Whaling Commission (IWC) recognizes three stocks 
of minke whales in the North Pacific: The Sea of Japan/East China Sea, 
the rest of the western Pacific west of 180[deg] N, and the remainder 
of the Pacific (Donovan 1991). Minke whales are relatively common in 
the Bering and Chukchi seas and in the Gulf of Alaska, but are not 
considered abundant in any other part of the eastern Pacific 
(Brueggeman et al., 1990). In the far north, minke whales are thought 
to be migratory, but they are believed to be year-round residents in 
coastal waters off the west coast of the United States (Dorsey et al., 
1990).
    Minke whales are reported in Washington inland waters year-round, 
although few are reported in the winter (i.e., during the anticipated 
in-water work window for these projects; Calambokidis and Baird 1994). 
They are relatively common in the San Juan Islands and Strait of Juan 
de Fuca (especially around several of the banks in both the central and 
eastern Strait), but are relatively rare in Puget Sound and the Orca 
Network has no sighting records of minke whales in the project areas.

Killer Whale

    There are three distinct ecotypes, or forms, of killer whales 
recognized in the north Pacific: Resident, transient, and offshore. The 
three ecotypes differ morphologically, ecologically, behaviorally, and 
genetically. Resident killer whales exclusively prey upon fish, with a 
clear preference for salmon (Ford and Ellis 2006; Hanson et al., 2010; 
Ford et al., 2016), while transient killer whales exclusively prey upon 
marine mammals (Caretta et al., 2019). Less is known about offshore 
killer whales, but they are believed to consume primarily fish, 
including several species of shark (Dahlheim et al., 2008). Currently, 
there are eight killer whale stocks recognized in the U.S. Pacific 
(Carretta et al., 2021; Muto et al., 2021). Of those, individuals from 
the Southern Resident stock and West Coast Transient stock may occur in 
the Seattle area and be taken incidental to the City's proposed 
activities.
    The Southern Resident killer whale (SRKW) population is comprised 
of three pods, J, K, and L pods, which typically travel independent of 
each other. The stock occurs for part of the

[[Page 12095]]

year in the inland waterways of the Salish Sea, including Puget Sound, 
the Strait of Juan de Fuca, and the southern Strait of Georgia mostly 
during the spring, summer, and fall. Their movement patterns appear 
related to the seasonal availability of prey, especially Chinook salmon 
(Oncorhynchus tshawytscha). They also move to coastal waters, primarily 
off Washington and British Columbia, in search of suitable prey, and 
have been observed as far as central California and southeast Alaska 
(NMFS 2019). During the fall, SRKW, especially J pod, expand their 
movements into Puget Sound, likely taking advantage of chum 
(Oncorhynchus keta) and Chinook salmon runs (Hanson et al., 2021).
    The SRKW DPS was listed as endangered under the ESA in 2005 after a 
nearly 20 percent decline in abundance between 1996 and 2001 (70 FR 
69903; November 18, 2005). As compared to stable or growing 
populations, the DPS reflects lower fecundity and has demonstrated 
little to no growth in recent decades, and in fact has declined further 
since the date of listing (NMFS 2019). The population abundance listed 
in the draft 2021 SARs is 72 individuals, from the July 1, 2020 annual 
census conducted by the Center for Whale Research (Carretta et al., 
2021); since that date, two adult SRKW have died or are presumed dead, 
and three calves were born, bringing the current abundance to 73 whales 
(Orca Network, 2021).
    Designated ESA critical habitat for SRKW includes the inland waters 
of Washington relative to a contiguous shoreline delimited by the line 
at a depth of 6.1 m relative to extreme high water (71 FR 69054; 
November 29, 2006). The Seattle waterfront is in the Puget Sound 
segment of the designated critical habitat, which is defined as the 
area south of the Deception Pass Bridge, west of the entrance to 
Admiralty Inlet, and north of the Hood Canal Bridge. SRKW have been 
observed in this area in all seasons but most occurrence in this area 
typically correlates with fall salmon runs, which occur during the 
anticipated in-water work window for these projects (NMFS 2006).
    In contrast to SRKW, which exclusively prey on fish, the main diet 
of transient killer whales consists of marine mammals. Within Puget 
Sound, transient killer whales primarily hunt pinnipeds and porpoises, 
though some groups will occasionally target larger whales. The West 
Coast Transient stock of killer whales occurs from California through 
southeast Alaska (Muto et al., 2021). The seasonal movements of 
transients are largely unpredictable, although there is a tendency to 
investigate harbor seal haulouts off Vancouver Island more frequently 
during the pupping season in August and September (Baird 1994; Ford 
2014). Transient killer whales have been observed in central Puget 
Sound in all months (Orca Network 2021).

Bottlenose Dolphin

    Bottlenose dolphins are distributed worldwide from approximately 
45[deg] N to 45[deg] S. Bottlenose dolphins inhabiting west coast U.S. 
waters are considered to be in either the California coastal stock, 
which ranges from Mexico to the San Francisco area within approximately 
1 kilometer of shore, or the California/Oregon/Washington offshore 
stock, which is most commonly found along the California coast, 
northward to about the Oregon border. NMFS offshore surveys from 1991 
to 2014 resulted in no sightings during study transects off the Oregon 
or Washington coasts (Carretta et al., 2019). In September 2017, 
however, multiple sightings of a bottlenose dolphin throughout the 
Puget Sound and in Elliott Bay were reported to Cascadia Research 
Collective and Orca Network. One of the individuals was identified as 
belonging to the California coastal stock (Cascadia Research 
Collective, 2017). Bottlenose dolphins are considered rare in Puget 
Sound but occasional sightings have continued since the initial reports 
in 2017 (Orca Network, 2021).

Long-Beaked Common Dolphin

    Long-beaked common dolphins are commonly found along the U.S. West 
Coast, from Baja, California (including the Gulf of California), 
northward to about central California (Carretta et al., 2020). The 
Salish Sea is not considered part of their typical range (Carretta et 
al., 2020), but there have been reports of long-beaked common dolphins 
in inland waters. Two individual common dolphins were observed in 
August and September of 2011 (Whale Museum, 2015). The first record of 
a pod of long-beaked common dolphins in this area came in the summer of 
2016. Beginning on June 16, 2016 long-beaked common dolphins were 
observed near Victoria, B.C. Over the following weeks, a pod of 15 to 
20 (including a calf) was observed in central and southern Puget Sound. 
They were positively identified as long-beaked common dolphins (Orca 
Network 2016). Two long-beaked common dolphins were observed by 
Washington State Department of Transportation (WSDOT) marine mammal 
monitors during construction at Colman Dock (Pier 52) during the 2017-
18 construction window (WSDOT 2019).

Harbor Porpoise

    In the eastern North Pacific Ocean, harbor porpoise are found in 
coastal and inland waters from Point Barrow, along the Alaskan coast, 
and down the west coast of North America to Point Conception, 
California (Gaskin 1984). Harbor porpoise are known to occur year-round 
in the inland trans-boundary waters of Washington and British Columbia, 
Canada (Osborne et al., 1988), and along the Oregon/Washington coast 
(Barlow 1988, Barlow et al., 1988, Green et al., 1992). There was a 
significant decline in harbor porpoise sightings within southern Puget 
Sound between the 1940s and 1990s but sightings have increased 
seasonally in the last 10 years (Carretta et al., 2019). Annual winter 
aerial surveys conducted by the Washington Department of Fish and 
Wildlife from 1995 to 2015 revealed an increasing trend in harbor 
porpoise in Washington inland waters, including the return of harbor 
porpoise to Puget Sound. The data suggest that harbor porpoise were 
already present in Juan de Fuca, Georgia Straits, and the San Juan 
Islands from the mid-1990s to mid-2000s, and then expanded into Puget 
Sound and Hood Canal from the mid-2000s to 2015, areas they had used 
historically but abandoned. Changes in fishery-related entanglement was 
suspected as the cause of their previous decline and more recent 
recovery, including a return to Puget Sound (Evenson et al., 2016). 
Seasonal surveys conducted in spring, summer, and fall 2013-2015 in 
Puget Sound and Hood Canal documented substantial numbers of harbor 
porpoise in Puget Sound. Observed porpoise numbers were twice as high 
in spring as in fall or summer, indicating a seasonal shift in 
distribution of harbor porpoise (Smultea 2015). The reasons for the 
seasonal shift and for the increase in sightings is unknown. Marine 
mammal monitors have reported few sightings of harbor porpoises in 
Elliott Bay during recent construction projects at the Seattle 
waterfront (e.g., WSDOT 2019).

Dall's Porpoise

    Dall's porpoises are endemic to temperate waters of the North 
Pacific Ocean. Off the U.S. west coast, they are commonly seen in 
shelf, slope, and offshore waters (Morejohn 1979). Sighting patterns 
from aerial and shipboard surveys conducted in California, Oregon, and 
Washington (Green et al., 1992, 1993; Forney and Barlow 1998; Barlow 
2016) suggest that north-south movement between these

[[Page 12096]]

states occurs as oceanographic conditions change, both on seasonal and 
inter-annual time scales. Dall's porpoise are considered rare in Puget 
Sound; no observations of Dall's porpoises have been reported during 
recent construction projects at the Seattle waterfront (e.g., WSDOT 
2019).

California Sea Lion

    The California sea lion is the most frequently sighted pinniped 
found in Washington waters and uses haul-out sites along the outer 
coast, Strait of Juan de Fuca, and in Puget Sound. Haul-out sites are 
located on jetties, offshore rocks and islands, log booms, marina 
docks, and navigation buoys. This species also may be frequently seen 
resting in the water, rafted together in groups in Puget Sound. Only 
male California sea lions migrate into Pacific Northwest waters, with 
females remaining in waters near their breeding rookeries off the coast 
of California and Mexico. The California sea lion was considered rare 
in Washington waters prior to the 1950s. More recently, peak numbers of 
3,000 to 5,000 animals move into the Salish Sea during the fall and 
remain until late spring, when most return to breeding rookeries in 
California and Mexico (Jeffries et al., 2000).
    California sea lions are often observed in the area of potential 
effects and are known to be comfortable and seemingly curious around 
human activities. There are four documented haul-out areas near 
Bainbridge Island, approximately 6 miles (9.6 km) from Pier 63, and two 
documented haul-out areas between Bainbridge Island and Magnolia. The 
haul-outs consist of buoys and floats, and some are within the area of 
potential effects, but at the outer extent, and some are just outside 
the area of potential effects (Jefferies et al., 2000). California sea 
lions are regularly observed in Elliott Bay, especially around two 
navigational buoys near Alki Point, at the southwest edge of Elliott 
Bay. During construction at Pier 62 in 2018 and 2019, between 0 and 31 
California sea lions were observed in the project area per day, with an 
average of 6 per day. More than half of the reported takes of 
California sea lions during this project were animals near Alki Point 
(Anchor QEA 2018, 2019).

Steller Sea Lion

    Steller sea lions range along the North Pacific Rim from northern 
Japan to California (Loughlin et al., 1984). There are two separate 
stocks of Steller sea lions, the Eastern U.S. stock, which occurs east 
of Cape Suckling, Alaska (144[deg] W), and the Western U.S. stock, 
which occurs west of that point. Only the Western stock of Steller sea 
lions, which is designated as the Western DPS of Steller sea lions, is 
listed as endangered under the ESA (78 FR 66139; November 4, 2013). 
Unlike the Western U.S. stock of Steller sea lions, there has been a 
sustained and robust increase in abundance of the Eastern U.S. stock 
throughout its breeding range. The eastern stock of Steller sea lions 
has historically bred on rookeries located in Southeast Alaska, British 
Columbia, Oregon, and California. However, within the last several 
years a new rookery has become established on the outer Washington 
coast (at the Carroll Island and Sea Lion Rock complex), with more than 
100 pups born there in 2015 (Muto et al., 2020).
    Steller sea lions use haul-out locations in Puget Sound, and may 
occur at the same haul-outs as California sea lions, but are considered 
rare visitors to Elliott Bay and the Seattle waterfront area. Few 
Steller sea lions have been observed during monitoring of recent 
construction projects in the area; typically fewer than 5 total 
observations per year (e.g., Anchor QEA 2018, 2019). However, a total 
of 54 Steller sea lions were observed over 99 days of monitoring during 
the 2017-2018 work season at Colman Dock (Pier 52; WSDOT 2019).

Northern Elephant Seal

    Northern elephant seals breed and give birth in California (U.S.) 
and Baja California (Mexico), primarily on offshore islands (Stewart et 
al. 1994), from December to March (NOAA 2015). Males migrate to the 
Gulf of Alaska and western Aleutian Islands along the continental shelf 
to feed on benthic prey, while females migrate to pelagic areas in the 
Gulf of Alaska and the central North Pacific Ocean to feed on pelagic 
prey (Le Boeuf et al., 2000). Adults return to land between March and 
August to molt, with males returning later than females. Adults return 
to their feeding areas again between their spring/summer molting and 
their winter breeding seasons (Carretta et al., 2015).
    Individual elephant seals have been reported in Elliott Bay and 
central Puget Sound (e.g., WSDOT 2019) but are generally considered 
rare in Puget Sound. However, a female elephant seal has been reported 
hauled-out in Mutiny Bay on Whidbey Island periodically since 2010. She 
was observed alone for her first three visits to the area, but in March 
2015, she was seen with a pup. Since then, she has produced two more 
pups, born in 2018 and 2020. Northern elephant seals generally give 
birth in January but this individual has repeatedly given birth in 
March. She typically returns to Mutiny Bay in April and May to molt. 
Her pups have also repeatedly returned to haul-out on nearby beaches 
(Orca Network 2020).

Harbor Seal

    Harbor seals inhabit coastal and estuarine waters off Baja 
California, north along the western coasts of the continental U.S., 
British Columbia, and Southeast Alaska, west through the Gulf of Alaska 
and Aleutian Islands, and in the Bering Sea north to Cape Newenham and 
the Pribilof Islands (Carretta et al., 2014). They haul out on rocks, 
reefs, beaches, and drifting glacial ice and feed in marine, estuarine, 
and occasionally fresh waters. Harbor seals generally are non-
migratory, with local movements associated with such factors as tides, 
weather, season, food availability, and reproduction (Scheffer and 
Slipp 1944; Fisher 1952; Bigg 1969, 1981). Within U.S. west coast 
waters, five stocks of harbor seals are recognized: (1) Southern Puget 
Sound (south of the Tacoma Narrows Bridge); (2) Washington Northern 
Inland Waters (including Puget Sound north of the Tacoma Narrows 
Bridge, the San Juan Islands, and the Strait of Juan de Fuca); (3) Hood 
Canal; (4) Oregon/Washington Coast; and (5) California. Harbor seals in 
the project areas would be from the Washington Northern Inland Waters 
stock.
    Harbor seals are the only pinniped species that occurs year-round 
and breeds in Washington waters (Jeffries et al., 2000). Pupping 
seasons vary by geographic region, with pups born in coastal estuaries 
(Columbia River, Willapa Bay, and Grays Harbor) from mid-April through 
June; Olympic Peninsula coast from May through July; San Juan Islands 
and eastern bays of Puget Sound from June through August; southern 
Puget Sound from mid-July through September; and Hood Canal from August 
through January (Jeffries et al., 2000). The most recent estimate for 
the Washington Northern Inland Waters Stock is 11,036 based on surveys 
conducted in 1999. There are no current estimates of abundance for this 
stock but the population is thought to be stable (Carretta et al., 
2014).
    There is one documented harbor seal haulout area near Bainbridge 
Island, approximately 6 miles west of Piers 58 and 63. The haulout, 
which is estimated at less than 100 animals, consists of intertidal 
rocks and reef areas around Blakely Rocks and is within the area of 
potential effects but at the outer extent near Bainbridge Island 
(Jefferies et al., 2000). Harbor seals are a commonly

[[Page 12097]]

observed marine mammal in the area of potential effects and are known 
to be comfortable and seemingly curious around human activities. 
Observations of harbor seals were reported during many recent 
construction projects along the Seattle waterfront. During two seasons 
of construction at Pier 62, up to 54 harbor seals were observed per 
day, with an average of 5 individuals per day (Anchor QEA 2019).

Marine Mammal Hearing

    Hearing is the most important sensory modality for marine mammals 
underwater, and exposure to anthropogenic sound can have deleterious 
effects. To appropriately assess the potential effects of exposure to 
sound, it is necessary to understand the frequency ranges marine 
mammals are able to hear. Current data indicate that not all marine 
mammal species have equal hearing capabilities (e.g., Richardson et 
al., 1995; Wartzok and Ketten, 1999; Au and Hastings, 2008). To reflect 
this, Southall et al. (2007) recommended that marine mammals be divided 
into functional hearing groups based on directly measured or estimated 
hearing ranges on the basis of available behavioral response data, 
audiograms derived using auditory evoked potential techniques, 
anatomical modeling, and other data. Note that no direct measurements 
of hearing ability have been successfully completed for mysticetes 
(i.e., low-frequency cetaceans). Subsequently, NMFS (2018) described 
generalized hearing ranges for these marine mammal hearing groups. 
Generalized hearing ranges were chosen based on the approximately 65 
decibel (dB) threshold from the normalized composite audiograms, with 
the exception for lower limits for low-frequency cetaceans where the 
lower bound was deemed to be biologically implausible and the lower 
bound from Southall et al. (2007) retained. Marine mammal hearing 
groups and their associated hearing ranges are provided in Table 4.

                  Table 4--Marine Mammal Hearing Groups
                              [NMFS, 2018]
------------------------------------------------------------------------
            Hearing group                 Generalized hearing range *
------------------------------------------------------------------------
Low-frequency (LF) cetaceans (baleen   7 Hz to 35 kHz.
 whales).
Mid-frequency (MF) cetaceans           150 Hz to 160 kHz.
 (dolphins, toothed whales, beaked
 whales, bottlenose whales).
High-frequency (HF) cetaceans (true    275 Hz to 160 kHz.
 porpoises, Kogia, river dolphins,
 cephalorhynchids, Lagenorhynchus
 cruciger & L. australis).
Phocid pinnipeds (PW) (underwater)     50 Hz to 86 kHz.
 (true seals).
Otariid pinnipeds (OW) (underwater)    60 Hz to 39 kHz.
 (sea lions and fur seals).
------------------------------------------------------------------------
* 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 pinnipeds (approximation).

    The pinniped functional hearing group was modified from Southall et 
al. (2007) on the basis of data indicating that phocid species have 
consistently demonstrated an extended frequency range of hearing 
compared to otariids, especially in the higher frequency range 
(Hemil[auml] et al., 2006; Kastelein et al., 2009; Reichmuth and Holt, 
2013).
    For more detail concerning these groups and associated frequency 
ranges, please see NMFS (2018) for a review of available information. 
Twelve marine mammal species (8 cetacean and 4 pinniped (2 otariid and 
2 phocid) species) have the reasonable potential to co-occur with the 
proposed survey activities. Please refer to Table 3. Of the cetacean 
species that may be present, 3 are classified as low-frequency 
cetaceans (i.e., all mysticete species), 3 are classified as mid-
frequency cetaceans (i.e., all delphinid species), and 2 are classified 
as high-frequency cetaceans (i.e., all porpoise species).

Potential Effects of Specified Activities on Marine Mammals and Their 
Habitat

    This section includes a discussion of the ways that components of 
the specified activities may impact marine mammals and their habitat. 
The Estimated Take section later in this document includes a 
quantitative analysis of the number of individuals that are expected to 
be taken by these activities. The Negligible Impact Analysis and 
Determination section considers the content of this section, the 
Estimated Take section, and the Proposed Mitigation section, to draw 
conclusions regarding the likely impacts of these activities on the 
reproductive success or survivorship of individuals and how those 
impacts on individuals are likely to impact marine mammal species or 
stocks.
    Acoustic effects on marine mammals during the specified activities 
can occur from impact pile driving and vibratory driving and removal. 
The effects of underwater noise from the City's proposed activities 
have the potential to result in Level A or Level B harassment of marine 
mammals in the action areas.

Description of Sound Sources

    The marine soundscape is comprised of both ambient and 
anthropogenic sounds. Ambient sound is defined as the all-encompassing 
sound in a given place and is usually a composite of sound from many 
sources both near and far (ANSI 1995). The sound level of an area is 
defined by the total acoustical energy being generated by known and 
unknown sources. These sources may include physical (e.g., waves, wind, 
precipitation, earthquakes, ice, atmospheric sound), biological (e.g., 
sounds produced by marine mammals, fish, and invertebrates), and 
anthropogenic sound (e.g., vessels, dredging, aircraft, construction).
    The sum of the various natural and anthropogenic sound sources at 
any given location and time--which comprise ``ambient'' or 
``background'' sound--depends not only on the source levels (as 
determined by current weather conditions and levels of biological and 
shipping activity) but also on the ability of sound to propagate 
through the environment. In turn, sound propagation is dependent on the 
spatially and temporally varying properties of the water column and sea 
floor, and is frequency-dependent. As a result of the dependence on a 
large number of varying factors, ambient sound levels can be expected 
to vary widely over both coarse and fine spatial and temporal scales. 
Sound levels at a given frequency and location can vary by 10-20 
decibels (dB) from day to day (Richardson et al., 1995). The result is 
that, depending on the source type and its intensity, sound from the 
specified activities may be a negligible addition to the local 
environment or could form a

[[Page 12098]]

distinctive signal that may affect marine mammals.
    In-water construction activities associated with the project would 
include impact and vibratory pile driving and removal. The sounds 
produced by these activities fall into one of two general sound types: 
Impulsive and non-impulsive. Impulsive sounds (e.g., explosions, sonic 
booms, impact pile driving) are typically transient, brief (less than 1 
second), broadband, and consist of high peak sound pressure with rapid 
rise time and rapid decay (ANSI, 1986; NIOSH, 1998; NMFS, 2018). Non-
impulsive sounds (e.g., machinery operations such as drilling or 
dredging, vibratory pile driving, underwater chainsaws, and active 
sonar systems) can be broadband, narrowband or tonal, brief or 
prolonged (continuous or intermittent), and typically do not have the 
high peak sound pressure with raid rise/decay time that impulsive 
sounds do (ANSI 1995; NIOSH 1998; NMFS 2018). The distinction between 
these two sound types is important because they have differing 
potential to cause physical effects, particularly with regard to 
hearing (e.g., Ward 1997 in Southall et al., 2007).
    Two types of hammers would be used on this project, impact and 
vibratory. Impact hammers operate by repeatedly dropping and/or pushing 
a heavy piston onto a pile to drive the pile into the substrate. Sound 
generated by impact hammers is considered impulsive. Vibratory hammers 
install piles by vibrating them and allowing the weight of the hammer 
to push them into the sediment. Vibratory hammers produce non-
impulsive, continuous sounds. Vibratory hammering generally produces 
SPLs 10 to 20 dB lower than impact pile driving of the same-sized pile 
(Oestman et al., 2009). Rise time is slower, reducing the probability 
and severity of injury, and sound energy is distributed over a greater 
amount of time (Nedwell and Edwards, 2002; Carlson et al., 2005).
    The likely or possible impacts of the City's proposed activities on 
marine mammals could be generated from both non-acoustic and acoustic 
stressors. Potential non-acoustic stressors include the physical 
presence of the equipment, vessels, and personnel; however, we expect 
that any animals that approach the project site(s) close enough to be 
harassed due to the presence of equipment or personnel would be within 
the Level B harassment zones from pile driving and would already be 
subject to harassment from the in-water activities. Therefore, any 
impacts to marine mammals are expected to primarily be acoustic in 
nature. Acoustic stressors are generated by heavy equipment operation 
during pile installation and removal (i.e., impact and vibratory pile 
driving and removal).

Acoustic Impacts

    The introduction of anthropogenic noise into the aquatic 
environment from pile driving equipment is the primary means by which 
marine mammals may be harassed from the City's specified activities. In 
general, animals exposed to natural or anthropogenic sound may 
experience physical and psychological effects, ranging in magnitude 
from none to severe (Southall et al., 2007). Generally, exposure to 
pile driving and removal and other construction noise has the potential 
to result in auditory threshold shifts and behavioral reactions (e.g., 
avoidance, temporary cessation of foraging and vocalizing, changes in 
dive behavior). Exposure to anthropogenic noise can also lead to non-
observable physiological responses such as an increase in stress 
hormones. Additional noise in a marine mammal's habitat can mask 
acoustic cues used by marine mammals to carry out daily functions such 
as communication and predator and prey detection. The effects of pile 
driving and demolition noise on marine mammals are dependent on several 
factors, including, but not limited to, sound type (e.g., impulsive vs. 
non-impulsive), the species, age and sex class (e.g., adult male vs. 
mother with calf), duration of exposure, the distance between the pile 
and the animal, received levels, behavior at time of exposure, and 
previous history with exposure (Wartzok et al., 2004; Southall et al., 
2007). Here we discuss physical auditory effects (threshold shifts) 
followed by behavioral effects and potential impacts on habitat. No 
physiological effects other than PTS are anticipated or proposed to be 
authorized, and therefore are not discussed further.
    NMFS defines a noise-induced threshold shift (TS) as a change, 
usually an increase, in the threshold of audibility at a specified 
frequency or portion of an individual's hearing range above a 
previously established reference level (NMFS, 2018). The amount of 
threshold shift is customarily expressed in dB. A TS can be permanent 
or temporary. As described in NMFS (2018), there are numerous factors 
to consider when examining the consequence of TS, including, but not 
limited to, the signal temporal pattern (e.g., impulsive or non-
impulsive), likelihood an individual would be exposed for a long enough 
duration or to a high enough level to induce a TS, the magnitude of the 
TS, time to recovery (seconds to minutes or hours to days), the 
frequency range of the exposure (i.e., spectral content), the hearing 
and vocalization frequency range of the exposed species relative to the 
signal's frequency spectrum (i.e., how animal uses sound within the 
frequency band of the signal; e.g., Kastelein et al., 2014), and the 
overlap between the animal and the source (e.g., spatial, temporal, and 
spectral).
    Permanent Threshold Shift (PTS)--NMFS defines PTS as a permanent, 
irreversible increase in the threshold of audibility at a specified 
frequency or portion of an individual's hearing range above a 
previously established reference level (NMFS 2018). Available data from 
humans and other terrestrial mammals indicate that a 40 dB threshold 
shift approximates PTS onset (see Ward et al., 1958, 1959; Ward, 1960; 
Kryter et al., 1966; Miller, 1974; Ahroon et al., 1996; Henderson et 
al., 2008). PTS levels for marine mammals are estimates, because there 
are limited empirical data measuring PTS in marine mammals (e.g., 
Kastak et al., 2008), largely due to the fact that, for various ethical 
reasons, experiments involving anthropogenic noise exposure at levels 
inducing PTS are not typically pursued or authorized (NMFS, 2018).
    Temporary Threshold Shift (TTS)--TTS is a temporary, reversible 
increase in the threshold of audibility at a specified frequency or 
portion of an individual's hearing range above a previously established 
reference level (NMFS, 2018). Based on data from cetacean TTS 
measurements (see Southall et al., 2007), a TTS of 6 dB is considered 
the minimum threshold shift clearly larger than any day-to-day or 
session-to-session variation in a subject's normal hearing ability 
(Schlundt et al., 2000; Finneran et al., 2000, 2002). As described in 
Finneran (2016), marine mammal studies have shown the amount of TTS 
increases with cumulative sound exposure level (SELcum) in 
an accelerating fashion: At low exposures with lower SELcum, 
the amount of TTS is typically small and the growth curves have shallow 
slopes. At exposures with higher SELcum, the growth curves 
become steeper and approach linear relationships with the noise SEL.
    Depending on the degree (elevation of threshold in dB), duration 
(i.e., recovery time), and frequency range of TTS, and the context in 
which it is experienced, TTS can have effects on marine mammals ranging 
from discountable to serious (similar to those discussed in auditory 
masking, below). For example, a marine mammal may be able to readily

[[Page 12099]]

compensate for a brief, relatively small amount of TTS in a non-
critical frequency range that takes place during a time when the animal 
is traveling through the open ocean, where ambient noise is lower and 
there are not as many competing sounds present. Alternatively, a larger 
amount and longer duration of TTS sustained during time when 
communication is critical for successful mother/calf interactions could 
have more serious impacts. We note that reduced hearing sensitivity as 
a simple function of aging has been observed in marine mammals, as well 
as humans and other taxa (Southall et al., 2007), so we can infer that 
strategies exist for coping with this condition to some degree, though 
likely not without cost.
    Currently, TTS data only exist for four species of cetaceans 
(bottlenose dolphin, beluga whale (Delphinapterus leucas), harbor 
porpoise, and Yangtze finless porpoise (Neophocoena asiaeorientalis)) 
and five species of pinnipeds exposed to a limited number of sound 
sources (i.e., mostly tones and octave-band noise) in laboratory 
settings (Finneran, 2015). TTS was not observed in trained spotted 
(Phoca largha) and ringed (Pusa hispida) seals exposed to impulsive 
noise at levels matching previous predictions of TTS onset (Reichmuth 
et al., 2016). In general, harbor seals and harbor porpoises have a 
lower TTS onset than other measured pinniped or cetacean species 
(Finneran, 2015). The potential for TTS from impact pile driving 
exists. After exposure to playbacks of impact pile driving sounds (rate 
2,760 strikes/hour) in captivity, mean TTS increased from 0 dB after 15 
minute exposure to 5 dB after 360 minute exposure; recovery occurred 
within 60 minutes (Kastelein et al., 2016). Additionally, the existing 
marine mammal TTS data come from a limited number of individuals within 
these species. No data are available on noise-induced hearing loss for 
mysticetes. Nonetheless, what we considered is the best available 
science. For summaries of data on TTS in marine mammals or for further 
discussion of TTS onset thresholds, please see Southall et al. (2007), 
Finneran and Jenkins (2012), Finneran (2015), and Table 5 in NMFS 
(2018).
    Installing piles for these projects requires impact pile driving. 
There would likely be pauses in activities producing the sound during 
each day. Given these pauses and the fact that many marine mammals are 
likely moving through the project areas and not remaining for extended 
periods of time, the potential for TS declines.
    Behavioral Harassment--Exposure to noise from pile driving and 
removal also has the potential to behaviorally disturb marine mammals. 
Available studies show wide variation in response to underwater sound; 
therefore, it is difficult to predict specifically how any given sound 
in a particular instance might affect marine mammals perceiving the 
signal. If a marine mammal does react briefly to an underwater sound by 
changing its behavior or moving a small distance, the impacts of the 
change are unlikely to be significant to the individual, let alone the 
stock or population. However, if a sound source displaces marine 
mammals from an important feeding or breeding area for a prolonged 
period, impacts on individuals and populations could be significant 
(e.g., Lusseau and Bejder, 2007; Weilgart, 2007; NRC, 2005).
    Disturbance may result in changing durations of surfacing and 
dives, number of blows per surfacing, or moving direction and/or speed; 
reduced/increased vocal activities; changing/cessation of certain 
behavioral activities (such as socializing or feeding); visible startle 
response or aggressive behavior (such as tail/fluke slapping or jaw 
clapping); or avoidance of areas where sound sources are located. 
Pinnipeds may increase their haul-out time, possibly to avoid in-water 
disturbance (Thorson and Reyff, 2006). Behavioral responses to sound 
are highly variable and context-specific and any reactions depend on 
numerous intrinsic and extrinsic factors (e.g., species, state of 
maturity, experience, current activity, reproductive state, auditory 
sensitivity, time of day), as well as the interplay between factors 
(e.g., Richardson et al., 1995; Wartzok et al., 2004; Southall et al., 
2007; Weilgart, 2007; Archer et al., 2010). Behavioral reactions can 
vary not only among individuals but also within an individual, 
depending on previous experience with a sound source, context, and 
numerous other factors (Ellison et al., 2012), and can vary depending 
on characteristics associated with the sound source (e.g., whether it 
is moving or stationary, number of sources, distance from the source). 
In general, pinnipeds seem more tolerant of, or at least habituate more 
quickly to, potentially disturbing underwater sound than do cetaceans, 
and generally seem to be less responsive to exposure to industrial 
sound than most cetaceans. Please see Appendices B and C of Southall et 
al. (2007) for a review of studies involving marine mammal behavioral 
responses to sound.
    Disruption of feeding behavior can be difficult to correlate with 
anthropogenic sound exposure, so it is usually inferred by observed 
displacement from known foraging areas, the appearance of secondary 
indicators (e.g., bubble nets or sediment plumes), or changes in dive 
behavior. As for other types of behavioral response, the frequency, 
duration, and temporal pattern of signal presentation, as well as 
differences in species sensitivity, are likely contributing factors to 
differences in response in any given circumstance (e.g., Croll et al., 
2001; Nowacek et al., 2004; Madsen et al., 2006; Yazvenko et al., 
2007). A determination of whether foraging disruptions incur fitness 
consequences would require information on or estimates of the energetic 
requirements of the affected individuals and the relationship between 
prey availability, foraging effort and success, and the life history 
stage of the animal.
    In 2016, the Alaska Department of Transportation and Public 
Facilities (ADOT&PF) documented observations of marine mammals during 
construction activities (i.e., pile driving) at the Kodiak Ferry Dock 
(see 80 FR 60636, October 7, 2015). In the marine mammal monitoring 
report for that project (ABR 2016), 1,281 Steller sea lions were 
observed within the Level B disturbance zone during pile driving or 
drilling (i.e., documented as Level B harassment take). Of these, 19 
individuals demonstrated an alert behavior, 7 were fleeing, and 19 swam 
away from the project site. All other animals (98 percent) were engaged 
in activities such as milling, foraging, or fighting and did not change 
their behavior. In addition, two sea lions approached within 20 m of 
active vibratory pile driving activities. Three harbor seals were 
observed within the disturbance zone during pile driving activities; 
none of them displayed disturbance behaviors. Fifteen killer whales and 
three harbor porpoise were also observed within the Level B harassment 
zone during pile driving. The killer whales were travelling or milling 
while all harbor porpoises were travelling. No signs of disturbance 
were noted for either of these species. Given the similarities in 
species, activities, and habitat (e.g., cool-temperate waters, 
industrialized area), we expect similar behavioral responses from the 
same and similar species affected by the City's specified activities. 
That is, disturbance, if any, is likely to be temporary and localized 
(e.g., small area movements).
    Stress responses--An animal's perception of a threat may be 
sufficient to trigger stress responses consisting of

[[Page 12100]]

some combination of behavioral responses, autonomic nervous system 
responses, neuroendocrine responses, or immune responses (e.g., Seyle 
1950; Moberg 2000). In many cases, an animal's first and sometimes most 
economical (in terms of energetic costs) response is behavioral 
avoidance of the potential stressor. Autonomic nervous system responses 
to stress typically involve changes in heart rate, blood pressure, and 
gastrointestinal activity. These responses have a relatively short 
duration and may or may not have a significant long-term effect on an 
animal's fitness.
    Neuroendocrine stress responses often involve the hypothalamus-
pituitary-adrenal system. Virtually all neuroendocrine functions that 
are affected by stress--including immune competence, reproduction, 
metabolism, and behavior--are regulated by pituitary hormones. Stress-
induced changes in the secretion of pituitary hormones have been 
implicated in failed reproduction, altered metabolism, reduced immune 
competence, and behavioral disturbance (e.g., Moberg 1987; Blecha 
2000). Increases in the circulation of glucocorticoids are also equated 
with stress (Romano et al., 2004).
    The primary distinction between stress (which is adaptive and does 
not normally place an animal at risk) and ``distress'' is the cost of 
the response. During a stress response, an animal uses glycogen stores 
that can be quickly replenished once the stress is alleviated. In such 
circumstances, the cost of the stress response would not pose serious 
fitness consequences. However, when an animal does not have sufficient 
energy reserves to satisfy the energetic costs of a stress response, 
energy resources must be diverted from other functions. This state of 
distress will last until the animal replenishes its energetic reserves 
sufficient to restore normal function.
    Relationships between these physiological mechanisms, animal 
behavior, and the costs of stress responses are well-studied through 
controlled experiments and for both laboratory and free-ranging animals 
(e.g., Holberton et al., 1996; Hood et al., 1998; Jessop et al., 2003; 
Krausman et al., 2004; Lankford et al., 2005). Stress responses due to 
exposure to anthropogenic sounds or other stressors and their effects 
on marine mammals have also been reviewed (Fair and Becker 2000; Romano 
et al., 2002b) and, more rarely, studied in wild populations (e.g., 
Romano et al., 2002a). For example, Rolland et al. (2012) found that 
noise reduction from reduced ship traffic in the Bay of Fundy was 
associated with decreased stress in North Atlantic right whales. These 
and other studies lead to a reasonable expectation that some marine 
mammals will experience physiological stress responses upon exposure to 
acoustic stressors and that it is possible that some of these would be 
classified as ``distress.'' In addition, any animal experiencing TTS 
would likely also experience stress responses (NRC, 2003), however 
distress is an unlikely result of these projects based on observations 
of marine mammals during previous, similar projects in the area.
    Masking--Sound can disrupt behavior through masking, or interfering 
with, an animal's ability to detect, recognize, or discriminate between 
acoustic signals of interest (e.g., those used for intraspecific 
communication and social interactions, prey detection, predator 
avoidance, navigation) (Richardson et al., 1995). Masking occurs when 
the receipt of a sound is interfered with by another coincident sound 
at similar frequencies and at similar or higher intensity, and may 
occur whether the sound is natural (e.g., snapping shrimp, wind, waves, 
precipitation) or anthropogenic (e.g., pile driving, shipping, sonar, 
seismic exploration) in origin. The ability of a noise source to mask 
biologically important sounds depends on the characteristics of both 
the noise source and the signal of interest (e.g., signal-to-noise 
ratio, temporal variability, direction), in relation to each other and 
to an animal's hearing abilities (e.g., sensitivity, frequency range, 
critical ratios, frequency discrimination, directional discrimination, 
age or TTS hearing loss), and existing ambient noise and propagation 
conditions. Masking of natural sounds can result when human activities 
produce high levels of background sound at frequencies important to 
marine mammals. Conversely, if the background level of underwater sound 
is high (e.g., on a day with strong wind and high waves), an 
anthropogenic sound source would not be detectable as far away as would 
be possible under quieter conditions and would itself be masked. The 
Seattle area contains active commercial shipping, ferry operations, and 
commercial fishing as well as numerous recreational and other 
commercial vessels, and background sound levels in the area are already 
elevated.
    Airborne Acoustic Effects--Pinnipeds that occur near the project 
site could be exposed to airborne sounds associated with pile driving 
and removal that have the potential to cause behavioral harassment, 
depending on their distance from pile driving activities. Cetaceans are 
not expected to be exposed to airborne sounds that would result in 
harassment as defined under the MMPA.
    Airborne noise would primarily be an issue for pinnipeds that are 
swimming or hauled out near the project site within the range of noise 
levels elevated above the acoustic criteria. We recognize that 
pinnipeds in the water could be exposed to airborne sound that may 
result in behavioral harassment when looking with their heads above 
water. Most likely, airborne sound would cause behavioral responses 
similar to those discussed above in relation to underwater sound. For 
instance, anthropogenic sound could cause hauled-out pinnipeds to 
exhibit changes in their normal behavior, such as reduction in 
vocalizations, or cause them to temporarily abandon the area and move 
further from the source. However, these animals would likely previously 
have been `taken' because of exposure to underwater sound above the 
behavioral harassment thresholds, which are generally larger than those 
associated with airborne sound. There are no haulouts near the project 
sites. Thus, the behavioral harassment of these animals is already 
accounted for in these estimates of potential take. Therefore, we do 
not believe that authorization of incidental take resulting from 
airborne sound for pinnipeds is warranted, and airborne sound is not 
discussed further here.

Marine Mammal Habitat Effects

    The City's construction activities could have localized, temporary 
impacts on marine mammal habitat, including prey, by increasing in-
water sound pressure levels and slightly decreasing water quality. 
Increased noise levels may affect acoustic habitat (see masking 
discussion above) and adversely affect marine mammal prey in the 
vicinity of the project areas (see discussion below). During impact and 
vibratory pile driving or removal, elevated levels of underwater noise 
would ensonify the project areas where both fishes and mammals occur 
and could affect foraging success. Additionally, marine mammals may 
avoid the area during construction, however, displacement due to noise 
is expected to be temporary and is not expected to result in long-term 
effects to the individuals or populations. Construction activities are 
of short duration and would likely have temporary impacts on marine 
mammal habitat through increases in underwater and airborne sound.
    A temporary and localized increase in turbidity near the seafloor 
would occur in the immediate area surrounding the

[[Page 12101]]

area where piles are installed or removed. In general, turbidity 
associated with pile installation is localized to about a 25-ft (7.6-m) 
radius around the pile (Everitt et al., 1980). The sediments of the 
project site will settle out rapidly when disturbed. Cetaceans are not 
expected to be close enough to the pile driving areas to experience 
effects of turbidity, and any pinnipeds could avoid localized areas of 
turbidity. Local currents are anticipated to disburse any additional 
suspended sediments produced by project activities at moderate to rapid 
rates depending on tidal stage. Therefore, we expect the impact from 
increased turbidity levels to be discountable to marine mammals and do 
not discuss it further.

In-Water Construction Effects on Potential Foraging Habitat

    The area likely impacted by the project is relatively small 
compared to the available habitat in Puget Sound. The area is highly 
influenced by anthropogenic activities. The total seafloor area 
affected by pile installation and removal is a small area compared to 
the vast foraging area available to marine mammals in the area. At 
best, the impact area provides marginal foraging habitat for marine 
mammals and fishes. Furthermore, pile driving and removal at the 
project site would not obstruct long-term movements or migration of 
marine mammals.
    Avoidance by potential prey (i.e., fish or, in the case of 
transient killer whales, other marine mammals) of the immediate area 
due to the temporary loss of this foraging habitat is also possible. 
The duration of fish and marine mammal avoidance of this area after 
pile driving stops is unknown, but a rapid return to normal 
recruitment, distribution, and behavior is anticipated. Any behavioral 
avoidance by fish or marine mammals of the disturbed area would still 
leave significantly large areas of fish and marine mammal foraging 
habitat in the nearby vicinity.
    In-Water Construction Effects on Potential Prey--Sound may affect 
marine mammals through impacts on the abundance, behavior, or 
distribution of prey species (e.g., crustaceans, cephalopods, fish, 
zooplankton, other marine mammals). Marine mammal prey varies by 
species, season, and location. Here, we describe studies regarding the 
effects of noise on known marine mammal prey other than other marine 
mammals (which have been discussed earlier).
    Fish utilize the soundscape and components of sound in their 
environment to perform important functions such as foraging, predator 
avoidance, mating, and spawning (e.g., Zelick and Mann, 1999; Fay, 
2009). Depending on their hearing anatomy and peripheral sensory 
structures, which vary among species, fishes hear sounds using pressure 
and particle motion sensitivity capabilities and detect the motion of 
surrounding water (Fay et al., 2008). The potential effects of noise on 
fishes depends on the overlapping frequency range, distance from the 
sound source, water depth of exposure, and species-specific hearing 
sensitivity, anatomy, and physiology. Key impacts to fishes may include 
behavioral responses, hearing damage, barotrauma (pressure-related 
injuries), and mortality.
    Fish react to sounds which are especially strong and/or 
intermittent low-frequency sounds, and behavioral responses such as 
flight or avoidance are the most likely effects. Short duration, sharp 
sounds can cause overt or subtle changes in fish behavior and local 
distribution. The reaction of fish to noise depends on the 
physiological state of the fish, past exposures, motivation (e.g., 
feeding, spawning, migration), and other environmental factors. 
Hastings and Popper (2005) identified several studies that suggest fish 
may relocate to avoid certain areas of sound energy. Additional studies 
have documented effects of pile driving on fish; several are based on 
studies in support of large, multiyear bridge construction projects 
(e.g., Scholik and Yan, 2001, 2002; Popper and Hastings, 2009). Several 
studies have demonstrated that impulse sounds might affect the 
distribution and behavior of some fishes, potentially impacting 
foraging opportunities or increasing energetic costs (e.g., Fewtrell 
and McCauley, 2012; Pearson et al., 1992; Skalski et al., 1992; 
Santulli et al., 1999; Paxton et al., 2017). However, some studies have 
shown no or slight reaction to impulse sounds (e.g., Pena et al., 2013; 
Wardle et al., 2001; Jorgenson and Gyselman, 2009; Popper et al., 
2015).
    SPLs of sufficient strength have been known to cause injury to fish 
and fish mortality. However, in most fish species, hair cells in the 
ear continuously regenerate and loss of auditory function likely is 
restored when damaged cells are replaced with new cells. Halvorsen et 
al. (2012a) showed that a TTS of 4-6 dB was recoverable within 24 hours 
for one species. Impacts would be most severe when the individual fish 
is close to the source and when the duration of exposure is long. 
Injury caused by barotrauma can range from slight to severe and can 
cause death, and is most likely for fish with swim bladders. Barotrauma 
injuries have been documented during controlled exposure to impact pile 
driving (Halvorsen et al., 2012b; Casper et al., 2013).
    The most likely impact to fishes from pile driving and removal and 
construction activities at the project areas would be temporary 
behavioral avoidance of the area. The duration of fish avoidance of 
this area after pile driving stops is unknown, but a rapid return to 
normal recruitment, distribution, and behavior is anticipated.
    Construction activities, in the form of increased turbidity, have 
the potential to adversely affect forage fish in the project areas. 
Forage fish form a significant prey base for many marine mammal species 
that occur in the project areas. Increased turbidity is expected to 
occur in the immediate vicinity (on the order of 10 ft (3 m) or less) 
of construction activities. However, suspended sediments and 
particulates are expected to dissipate quickly within a single tidal 
cycle. Given the limited area affected and high tidal dilution rates 
any effects on forage fish are expected to be minor or negligible. 
Finally, exposure to turbid waters from construction activities is not 
expected to be different from the current exposure; fish and marine 
mammals in Elliott Bay are routinely exposed to substantial levels of 
suspended sediment from natural and anthropogenic sources.
    In summary, given the short daily duration of sound associated with 
individual pile driving events and the relatively small areas being 
affected, pile driving activities associated with the proposed actions 
are not likely to have a permanent, adverse effect on any fish habitat, 
or populations of fish species. Any behavioral avoidance by fish of the 
disturbed area would still leave significantly large areas of fish and 
marine mammal foraging habitat in the nearby vicinity. Thus, we 
conclude that impacts of the specified activities are not likely to 
have more than short-term adverse effects on any prey habitat or 
populations of prey species. Further, any impacts to marine mammal 
habitat are not expected to result in significant or long-term 
consequences for individual marine mammals, or to contribute to adverse 
impacts on their populations.

Estimated Take

    This section provides an estimate of the number of incidental takes 
proposed for authorization through these IHAs, which will inform both 
NMFS' consideration of ``small numbers'' and the negligible impact 
determinations.

[[Page 12102]]

    Harassment is the only type of take expected to result from these 
activities. Except with respect to certain activities not pertinent 
here, section 3(18) of the MMPA defines ``harassment'' as any act of 
pursuit, torment, or annoyance, which (i) has the potential to injure a 
marine mammal or marine mammal stock in the wild (Level A harassment); 
or (ii) 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 (Level B harassment).
    Authorized takes would primarily be by Level B harassment (in the 
form of behavioral disturbance and TTS), as use of the acoustic sources 
(i.e., vibratory or impact pile driving and removal) have the potential 
to result in disruption of behavioral patterns and cause a temporary 
loss in hearing sensitivity for individual marine mammals. There is 
also some potential for auditory injury (Level A harassment) to result 
for porpoises and harbor seals because predicted auditory injury zones 
are larger. The proposed mitigation and monitoring measures are 
expected to minimize the severity of the taking to the extent 
practicable.
    As described previously, no serious injury or mortality is 
anticipated or proposed to be authorized for these activities. Below we 
describe how the take is estimated.
    Generally speaking, we estimate take by considering: (1) Acoustic 
thresholds above which NMFS believes the best available science 
indicates marine mammals will be behaviorally harassed or incur some 
degree of permanent hearing impairment; (2) the area or volume of water 
that will be ensonified above these levels in a day; (3) the density or 
occurrence of marine mammals within these ensonified areas; and, (4) 
the number of days of activities. We note that while these basic 
factors can contribute to a basic calculation to provide an initial 
prediction of takes, additional information that can qualitatively 
inform take estimates is also sometimes available (e.g., previous 
monitoring results or average group size). Below, we describe the 
factors considered here in more detail and present the proposed take 
estimate.

Acoustic Thresholds

    NMFS recommends the use of acoustic thresholds that identify the 
received level of underwater sound above which exposed marine mammals 
would be reasonably expected to be behaviorally harassed (equated to 
Level B harassment) or to incur PTS of some degree (equated to Level A 
harassment).
    Level B Harassment for non-explosive sources--Though significantly 
driven by received level, the onset of behavioral disturbance from 
anthropogenic noise exposure is also informed to varying degrees by 
other factors related to the source (e.g., frequency, predictability, 
duty cycle), the environment (e.g., bathymetry), and the receiving 
animals (hearing, motivation, experience, demography, behavioral 
context) and can be difficult to predict (Southall et al., 2007; 
Ellison et al., 2012). Based on what the available science indicates 
and the practical need to use a threshold based on a factor that is 
both predictable and measurable for most activities, NMFS uses a 
generalized acoustic threshold based on received level to estimate the 
onset of behavioral harassment. NMFS predicts that marine mammals are 
likely to be behaviorally harassed in a manner we consider Level B 
harassment when exposed to underwater anthropogenic noise above 
received levels of 120 dB re 1 microPascal ([mu]Pa) (root mean square 
(rms)) for continuous sources (e.g., vibratory pile-driving, drilling) 
and above 160 dB re 1 [mu]Pa (rms) for non-explosive impulsive (e.g., 
seismic airguns) or intermittent (e.g., scientific sonar) sources. This 
take estimation includes disruption of behavioral patterns resulting 
directly in response to noise exposure (e.g., avoidance), as well as 
that resulting indirectly from associated impacts such as TTS or 
masking.
    The City's proposed activities includes the use of continuous 
(vibratory hammer) and impulsive (impact hammer) sources, and therefore 
the 120 and 160 dB re 1 [mu]Pa (rms) thresholds are applicable.
    Level A harassment for non-explosive sources--NMFS' Technical 
Guidance for Assessing the Effects of Anthropogenic Sound on Marine 
Mammal Hearing (Version 2.0) (Technical Guidance, 2018) identifies dual 
criteria to assess auditory injury (Level A harassment) to five 
different marine mammal groups (based on hearing sensitivity) as a 
result of exposure to noise from two different types of sources 
(impulsive or non-impulsive). The City's activities include the use of 
impulsive (impact hammer) and non-impulsive (vibratory hammer) sources.
    These thresholds are provided in the table below. The references, 
analysis, and methodology used in the development of the thresholds are 
described in NMFS 2018 Technical Guidance, which may be accessed at 
https://www.fisheries.noaa.gov/national/marine-mammal-protection/
marine-mammal-acoustic-technical-guidance.

                     Table 5--Thresholds Identifying the Onset of Permanent Threshold Shift
----------------------------------------------------------------------------------------------------------------
                                                     PTS onset acoustic thresholds * (received level)
             Hearing group              ------------------------------------------------------------------------
                                                  Impulsive                         Non-impulsive
----------------------------------------------------------------------------------------------------------------
Low-Frequency (LF) Cetaceans...........  Cell 1: Lpk,flat: 219 dB;   Cell 2: LE,LF,24h: 199 dB.
                                          LE,LF,24h: 183 dB.
Mid-Frequency (MF) Cetaceans...........  Cell 3: Lpk,flat: 230 dB;   Cell 4: LE,MF,24h: 198 dB.
                                          LE,MF,24h: 185 dB.
High-Frequency (HF) Cetaceans..........  Cell 5: Lpk,flat: 202 dB;   Cell 6: LE,HF,24h: 173 dB.
                                          LE,HF,24h: 155 dB.
Phocid Pinnipeds (PW) (Underwater).....  Cell 7: Lpk,flat: 218 dB;   Cell 8: LE,PW,24h: 201 dB.
                                          LE,PW,24h: 185 dB.
Otariid Pinnipeds (OW) (Underwater)....  Cell 9: Lpk,flat: 232 dB;   Cell 10: LE,OW,24h: 219 dB.
                                          LE,OW,24h: 203 dB.
----------------------------------------------------------------------------------------------------------------
* Dual metric acoustic 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 should also be considered.
Note: Peak sound pressure (Lpk) has a reference value of 1 [mu]Pa, and cumulative sound exposure level (LE) has
  a reference value of 1[mu]Pa\2\s. In this Table, thresholds are abbreviated to reflect American National
  Standards Institute standards (ANSI 2013). However, peak sound pressure is defined by ANSI as incorporating
  frequency weighting, which is not the intent for this Technical Guidance. Hence, the subscript ``flat'' is
  being included to indicate peak sound pressure should be flat weighted or unweighted within the generalized
  hearing range. 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 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 acoustic thresholds will be
  exceeded.


[[Page 12103]]

Ensonified Area

    Here, we describe operational and environmental parameters of the 
activities that will feed into identifying the area ensonified above 
the acoustic thresholds, which include source levels and transmission 
loss coefficient.
    The sound field in the project areas is the existing background 
noise plus additional construction noise from the proposed project. 
Marine mammals are expected to be affected by sound generated by the 
primary components of the project (i.e., impact and vibratory pile 
driving).
    In order to calculate distances to the Level A harassment and Level 
B harassment thresholds for the methods and piles being used in this 
project, NMFS used acoustic monitoring data from other locations to 
develop source levels for the various pile types, sizes, and methods 
for the two piers (Tables 6 and 7).

                                  Table 6--Pier 58 Project Sound Source Levels
----------------------------------------------------------------------------------------------------------------
                                                                 Source level (dB re 1
       Pile type and size (in)                  Method                  [mu]Pa)                 Reference
----------------------------------------------------------------------------------------------------------------
14-in timber, steel H-piles..........  Vibratory removal......  152 dB rms.............  Greenbusch Group
                                                                                          (2018).
24-in steel pipe pile................  Vibratory removal and    163 dB rms.............  Greenbusch Group
                                        installation.                                     (2019).
30-in steel pipe pile................  Vibratory installation.  163 dB rms.............  Greenbusch Group
                                                                                          (2019).
30-in steel pipe pile................  Impact installation....  180 dB rms,\1\ 193 dB    Greenbusch Group
                                                                 peak.                    (2019).
----------------------------------------------------------------------------------------------------------------
\1\ Highest RMS sound level from bubble curtain attenuated impact driving of 30-in steel piles at Pier 62.


                                  Table 7--Pier 63 Project Sound Source Levels
----------------------------------------------------------------------------------------------------------------
                                                                 Source level (dB re 1
       Pile type and size (in)                  Method                  [mu]Pa)                 Reference
----------------------------------------------------------------------------------------------------------------
14-in timber.........................  Vibratory removal......  152 dB rms.............  Greenbusch Group
                                                                                          (2018).
30-in steel pipe pile................  Vibratory removal......  163 dB rms.............  Greenbusch Group
                                                                                          (2019).
----------------------------------------------------------------------------------------------------------------

Level B Harassment Zones

    Transmission loss (TL) is the decrease in acoustic intensity as an 
acoustic pressure wave propagates out from a source. TL parameters vary 
with frequency, temperature, sea conditions, current, source and 
receiver depth, water depth, water chemistry, and bottom composition 
and topography. The general formula for underwater TL is:

TL = B * Log10 (R1/R2)

Where:

TL = transmission loss in dB
B = transmission loss coefficient; for practical spreading equals 15
R1 = the distance of the modeled SPL from the driven pile, and
R2 = the distance from the driven pile of the initial measurement

    The recommended TL coefficient for most nearshore environments is 
the practical spreading value of 15. This value results in an expected 
propagation environment that would lie between spherical and 
cylindrical spreading loss conditions, which is the most appropriate 
assumption for the City's proposed activities in the absence of 
specific modelling. The Level B harassment zones for the City's 
proposed activities are shown in Tables 8 and 9.

Level A Harassment Zones

    The NMFS Technical Guidance (2018) recognizes that ensonified area/
volume can be more technically challenging to predict because of the 
duration component in the new thresholds, and therefore includes a User 
Spreadsheet that includes tools to help predict a simple isopleth that 
can be used in conjunction with marine mammal density or occurrence to 
help predict takes. We note that because of some of the assumptions 
included in the methods used for these tools, we anticipate that 
isopleths produced are typically going to be overestimates of some 
degree, which may result in some degree of overestimate of Level A 
harassment. However, these tools offer the best way to predict 
appropriate isopleths when more sophisticated 3D modeling methods are 
not available, and NMFS continues to develop ways to quantitatively 
refine these tools, and will qualitatively address the output where 
appropriate. For stationary sources such as pile installation and 
removal, the NMFS User Spreadsheet predicts the distance at which, if a 
marine mammal remained at that distance for the whole duration of the 
activity, it would incur PTS. The isopleths generated by the User 
Spreadsheet used the same TL coefficient as the Level B harassment zone 
calculations (i.e., the practical spreading value of 15). Inputs used 
in the User Spreadsheet (e.g., number of piles per day, duration and/or 
strikes per pile) are presented in Tables 1 and 2, and the resulting 
isopleths are reported below in Tables 8 and 9. The areas expected to 
be ensonified above the Level B harassment threshold(s) are also 
presented in Tables 8 and 9. Due to the bathymetry and geography of the 
project areas, sound will not reach the full distance of the harassment 
isopleths in all directions.

                                            Table 8--Pier 58 Level A Harassment and Level B Harassment Zones
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                          Level A harassment zone (m)                         Level B         Level B
                      Pile type                       -------------------------------------------------------------------   harassment      ensonified
                                                       LF cetacean   MF cetacean   HF cetacean    Phocids      Otariids      zone (m)      area (km\2\)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Timber and steel H-pile removal......................          6.1           0.5           9.0          3.7          0.3       \b\ 1,359            2.35
24-in steel vibratory install and removal, 30-in              19.3           1.7          28.6         11.7          0.8       \b\ 7,357           34.34
 steel vibratory install \a\.........................

[[Page 12104]]

 
30-in steel impact install...........................        153.3           5.5         182.6         82.0          6.0         \c\ 215            0.07
--------------------------------------------------------------------------------------------------------------------------------------------------------
\a\ Level A harassment zones for vibratory installation and removal of steel piles calculated using the highest total duration of driving (installation
  of 30-inch piles) and conservatively applied to all vibratory pile driving.
\b\ Distance to 120 dB rms threshold.
\c\ Distance to 160 dB rms threshold.


                                            Table 9--Pier 63 Level A Harassment and Level B Harassment Zones
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                          Level A harassment zone (m)                         Level B         Level B
                      Pile type                       -------------------------------------------------------------------   harassment      ensonified
                                                       LF cetacean   MF cetacean   HF cetacean    Phocids      Otariids    zone (m) \a\    area (km\2\)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Timber...............................................          6.1           0.5           9.0          3.7          0.3           1,359            2.35
Steel................................................         19.3           1.7          28.6         11.7          0.8           7,357           34.34
--------------------------------------------------------------------------------------------------------------------------------------------------------
\a\ Distance to 120 dB rms threshold.

Marine Mammal Occurrence and Take Calculation and Estimation

    In this section we provide the information about the presence, 
density, or group dynamics of marine mammals that will inform the 
proposed take incidental to the City's pile driving activities. Unless 
otherwise specified, the term ``pile driving'' in this section, and all 
following sections, may refer to either pile installation or removal. 
The City considered estimating take using the ensonified area and 
density estimates from the U.S. Navy's Marine Species Density Database 
for the Northwest Training and Testing Study Area (U.S. Navy, 2019) but 
did not consider the resulting take estimates to be realistic (i.e., 
either over- or underestimated take). Instead, the City compiled 
monitoring results from recent construction projects in Elliott Bay 
(e.g., WSDOT, 2019; Anchor QEA, 2021) to estimate the likely daily or 
monthly occurrence of each species in the project areas. Unless 
otherwise specified, the occurrence information described below is used 
to estimate take for both the Pier 58 and Pier 63 projects. NMFS has 
carefully reviewed the City's analysis and concludes that it represents 
an appropriate and accurate method for estimating incidental take 
caused by the City's activities.
Humpback Whale
    During previous work for the Pier 62 Project and the Elliott Bay 
Seawall Project, up to two humpback whales were observed during the 
approximately one month of work each year for both projects (Anchor QEA 
2014, 2015, 2016, 2017, 2018 and 2019). Therefore, the City assumes 
that two humpback whales may be present in the project areas and taken 
by Level B harassment per month. The City anticipates up to 6 months of 
activities at Pier 58 and 3 months at Pier 63, for a total of 12 takes 
of humpback whales by Level B harassment from Pier 58 reconstruction 
and 6 takes by Level B harassment from Pier 63 removal.
    Since the City would be required to comply with all mitigation and 
monitoring measures, including marine mammal monitoring and 
coordination with Orca Network (see Proposed Mitigation), these 
measures would likely be successful in detecting humpback whales given 
their size and visibility, the City would stop work before humpback 
whales could enter the small Level A harassment zones (up to 153.3 m), 
and humpback whales are infrequent visitors to the project areas, it is 
unlikely that any humpback whales would be taken by Level A harassment. 
No take of humpback whales by Level A harassment is requested or 
proposed to be authorized.
Gray Whale
    Gray whales are infrequent visitors to the project areas but are 
most commonly seen during the winter months. Although no observations 
of gray whales have been reported during recent pile driving projects 
along the Seattle waterfront (e.g., WSDOT 2021; Anchor QEA 2019), 
individual gray whales have been reported in Elliott Bay by WSDOT ferry 
operators in December 2018, January 2019, and November 2019. Therefore, 
the City estimates that one gray whale may be taken by Level B 
harassment in each winter month (November, December, January, and 
February) of the work window. Therefore, the City has requested 4 takes 
of gray whales by Level B harassment from Pier 58 reconstruction. Since 
Pier 63 removal is expected to take only 3 months total, the City has 
requested 3 takes of gray whales by Level B harassment from Pier 63 
removal.
    Since the City would be required to comply with all mitigation and 
monitoring measures, including marine mammal monitoring and 
coordination with Orca Network, these measures would likely be 
successful in detecting gray whales given their size and visibility, 
the City would stop work before gray whales could enter the small Level 
A harassment zones (up to 153.3 m), and gray whales are infrequent 
visitors to the project areas, it is unlikely that any gray whales 
would be taken by Level A harassment. No take of gray whales by Level A 
harassment is requested or proposed to be authorized.
Minke Whale
    Minke whales are rarely observed in the project areas and none have 
been reported during monitoring for recent pile driving activities in 
the area (e.g., WSDOT 2021; Anchor QEA 2019). The City estimates that 
no more than one minke whale per month may be taken by Level B 
harassment. Therefore, the City has requested 6 takes of minke whales 
by Level B harassment from Pier 58 reconstruction and 3 takes by Level 
B harassment from Pier 63 removal.
    Like humpback and gray whales, minke whales are considered 
infrequent visitors to the project areas. As with humpback and gray 
whales, the City would be required to coordinate with Orca Network and 
would likely be alerted to the presence of minke whales in the area, 
allowing them to shut down pile driving equipment before a minke whale 
could enter the Level A

[[Page 12105]]

harassment zones. Hence, in consideration of the expected effectiveness 
of mitigation and infrequent occurrence, no take of minke whales by 
Level A harassment is requested or proposed to be authorized.
Transient Killer Whale
    Transient killer whales are frequently seen in central Puget Sound 
and occasionally within Elliott Bay (Orca Network 2021). Transient 
killer whales typically travel in small groups. The City estimates that 
a group of 6 transient killer whales may enter the Level B harassment 
zone per month. Therefore, the City has requested take of 36 transient 
killer whales by Level B harassment from Pier 58 reconstruction and 18 
takes by Level B harassment from Pier 63 removal.
    The Level A harassment zones for mid-frequency cetaceans are all 
less than 10 m. The City would be required to coordinate with Orca 
Network and would likely be alerted to the presence of transient killer 
whales in the area, allowing them to detect the animals and cease pile 
driving well before killer whales could enter the Level A harassment 
zone. No take of transient killer whales by Level A harassment is 
requested or proposed to be authorized.
Southern Resident Killer Whale
    Although SRKW are generally infrequently observed in Puget Sound, 
they are known to venture past the project areas during the fall and 
winter months as they hunt fall runs of salmon (Hanson et al., 2021). 
Of the three pods within the SRKW population, J pod (which is comprised 
of 23 individuals; Orca Network, 2020) is the most likely to occur in 
the area.
    The City would coordinate with the Orca Network to obtain sightings 
reports of SRKW near the project areas and shut down pile driving 
equipment before any SRKW enters the Level B harassment zone to avoid 
take of this stock. Given the relatively large size and visibility of 
SRKW, and the use of marine mammal sightings network reports (i.e., 
Orca Network) for advanced notice of SRKW presence in Puget Sound, 
these mitigation measures would likely be successful in preventing any 
Level B harassment. However, the City acknowledges that due to the 
large Level B harassment zone during vibratory installation and removal 
of steel piles at Pier 58 (approximately 7.4 km), over the course of 40 
days of construction activities, it is possible that one pod of SRKW 
could enter the area undetected. That pod would most likely be J pod 
because it is the pod most likely to be near the project areas. In an 
abundance of caution, the City has requested take of 23 SRKW by Level B 
harassment from pile driving at Pier 58 in the event a pod were able to 
enter the Level B harassment zone prior to detection and shutdown.
    During vibratory removal of timber piles at Pier 63, the Level B 
harassment zone is less than 1.4 km, which is well within Elliott Bay. 
SRKW are unlikely to enter the Level B harassment zone during this 
activity and even if they did, would be readily detected and pile 
removal activities shut down. The Level B harassment zone for vibratory 
removal of steel piles at Pier 63 is approximately 7.4 km, which 
reaches the outer extent of Elliott Bay and into the central core Puget 
Sound between Seattle and Bainbridge Island where SRKW may occur. 
However, removal of steel piles at Pier 63 is only expected to occur on 
2 days, and given the mitigation measures that would be in place and 
the relatively large size and visibility of SRKW, the City considers it 
unlikely that SRKW would enter the Level B harassment zone undetected 
and be exposed to sound above the Level B harassment threshold before 
the City could cease pile driving activities. We concur with the City's 
conclusion.
    The Level A harassment zones for all activities for both Pier 58 
reconstruction and Pier 63 removal are less than 10 m for mid-frequency 
cetaceans. Given the size and visibility of killer whales, the City 
would be able to implement the proposed mitigation and monitoring 
measures and shut down pile driving equipment well before SRKW could 
approach within 10 m. Therefore no take of SRKW by Level A harassment 
is expected to occur, and no Level A harassment is requested or 
proposed to be authorized.
Bottlenose Dolphin
    In 2017 the Orca Network (2017) reported sightings of a bottlenose 
dolphin in Puget Sound and in Elliott Bay, and WSDOT observed two 
bottlenose dolphins in one week during monitoring for the Colman Dock 
Multimodal Project (WSDOT 2018). In addition, a group of 7 bottlenose 
dolphins were observed in 2017 and were positively identified as part 
of the California coastal stock (Cascadia Research Collective, 2017). 
Bottlenose dolphins typically travel in groups of 2 to 15 in coastal 
waters (Carretta et al., 2020). The City estimates that 7 bottlenose 
dolphins may be taken by Level B harassment per month. Therefore, the 
City has requested take of 42 bottlenose dolphins by Level B harassment 
from Pier 58 reconstruction and 21 takes by Level B harassment from 
Pier 63 removal.
    The Level A harassment zones for mid-frequency cetaceans are all 
less than 10 m. Given the visibility of bottlenose dolphins, the City 
would be able to cease pile driving before bottlenose dolphins could 
enter the Level A harassment zone. No take of bottlenose dolphins by 
Level A harassment is requested or proposed to be authorized.
Long-Beaked Common Dolphin
    In June 2011, two long-beaked common dolphins were sighted in South 
Puget Sound. Sightings continued in 2012, and in 2016-17 (Carretta et 
al., 2018). Sightings of 4 to 12 individuals were reported regularly, 
with confirmed sightings of up to 30 individuals. In 2016, the Orca 
Network (2016) reported a pod of up to 20 long-beaked common dolphins. 
During monitoring for the Colman Dock Project in 2017-2018, 2 long-
beaked common dolphins were observed in smaller Level B harassment 
zones than estimated for pile driving at Piers 58 and 63. The average 
reported group size of long-beaked common dolphins in Puget Sound is 7 
individuals. Therefore, the City estimates 7 long-beaked common 
dolphins may be taken by Level B harassment per month and has requested 
take of 42 long-beaked common dolphins by Level B harassment from Pier 
58 reconstruction and 21 takes by Level B harassment from Pier 63 
removal.
    The Level A harassment zones for mid-frequency cetaceans are all 
less than 10 m. Given the visibility of long-beaked common dolphins, 
the City would be able to cease pile driving before long-beaked common 
dolphins could enter the Level A harassment zone. No take of long-
beaked common dolphins by Level A harassment is requested or proposed 
to be authorized.
Harbor Porpoise
    Recent monitoring data from the Colman Dock Project (Pier 52) in 
2017 and 2018 (WSDOT 2019) included observations of 288 harbor 
porpoises over 99 days of monitoring activity. This equates to 
approximately 3 porpoises per day.
    To account for unobserved animals at the outer extent of the Level 
B harassment zones, the City estimates up to 6 harbor porpoises may 
enter the Level B harassment zone per day of pile driving at Pier 58 
(70 days) for a total of 420 harbor porpoises. For impact installation 
of steel piles at Pier 58, the Level A harassment zone for high-
frequency cetaceans is 183 m. Although

[[Page 12106]]

the City would be required to implement a shutdown zone of 185 m during 
this activity (see Proposed Mitigation), due to the cryptic nature and 
lower detectability of harbor porpoises at large distances, the City 
anticipates that up to 12 of the harbor porpoises (2 per month) that 
enter the Level B zone could approach the project site closer and 
potentially enter the Level A harassment zone undetected during impact 
installation at Pier 58, which could occur as one group in one day or 
single animals over two days. The Level A harassment zones for all 
vibratory pile driving at Pier 58 are all under 30 m. At that distance, 
the City would be able to detect harbor porpoises and cease pile 
driving activities before harbor porpoises could enter the Level A 
harassment zone. Therefore, no take of harbor porpoises by Level A 
harassment is anticipated from vibratory pile driving. In total, the 
City has requested take of 420 harbor porpoises, 408 takes by Level B 
harassment and 12 takes by Level A harassment from Pier 58 
reconstruction.
    On all but two days of work at Pier 63, the Level B harassment zone 
will be well within Elliott Bay. Since the extent of the Level B 
harassment zone for this project on most days is less than for Pier 58, 
the City estimates that up to 5 harbor porpoises may be taken by Level 
B harassment per day during 47 days of pile removal at Pier 63, for a 
total of 235 takes by Level B harassment. The largest Level A 
harassment zone from pile removal at Pier 63 is 29 m. At that close 
range, the City would be able to detect harbor porpoises and would be 
required to shut down pile driving activities before they approach 
within 29 m. Therefore, no take of harbor porpoises by Level A 
harassment from pile driving at Pier 63 is requested or proposed to be 
authorized.
Dall's Porpoise
    Dall's porpoises are rarely sighted in the project areas. The City 
conservatively estimates that up to 12 Dall's porpoises may enter the 
Level B harassment zone per month, for a total of 72 Dall's porpoises 
from Pier 58 reconstruction and 36 from Pier 63 removal.
    For impact installation of steel piles at Pier 58, the Level A 
harassment zone for high-frequency cetaceans is 183 m. Although the 
City would be required to comply with all mitigation and monitoring 
measures and would implement a shutdown zone of 185 m during this 
activity, the City anticipates that up to 12 of the Dall's porpoises (2 
per month) that enter the Level B harassment zone could approach the 
project site closer and potentially enter the Level A harassment zone 
undetected during impact installation at Pier 58, which could occur as 
one group in one day or a single animal over two days. The Level A 
harassment zones for all vibratory pile driving at Pier 58 are all 
under 30 m. At that distance, the City would be able to detect Dall's 
porpoises and cease pile driving activities before Dall's porpoises 
could enter the Level A harassment zone. Therefore, no take of Dall's 
porpoises by Level A harassment is anticipated from vibratory pile 
driving. In total, the City has requested take of 72 Dall's porpoise, 
60 takes by Level B harassment and 12 takes by Level A harassment from 
Pier 58 reconstruction.
    The largest Level A harassment zone from pile removal at Pier 63 is 
29 m. At that close range, the City would be able to detect Dall's 
porpoises and would be required to shut down pile driving activities 
before they approach within 29 m. Therefore, no take of Dall's 
porpoises by Level A harassment from pile driving at Pier 63 is 
requested or proposed to be authorized. The City has requested 36 takes 
of Dall's porpoise by Level B harassment only for activities at Pier 
63.
California Sea Lion
    During monitoring for the Pier 62 Project, a maximum of 31 
California sea lions were observed in one day, with an average of 6 
takes per day (Anchor QEA 2019). To account for unobserved animals at 
the outer extent of the Level B harassment zones, the City estimates up 
to 10 California sea lions may be taken by Level B harassment per day 
for a total of 700 takes by Level B harassment from Pier 58 
reconstruction and 470 takes by Level B harassment from Pier 63 
removal.
    The largest Level A harassment zone for otariid pinnipeds is 6 m. 
The City would be required to implement a minimum shutdown zone of 10 m 
for all activities. At that close range, the City would be able to 
detect California sea lions and implement the required shutdown 
measures before California sea lions could enter the Level A harassment 
zone. Therefore, no takes of California sea lions by Level A harassment 
are requested or proposed to be authorized.
Steller Sea Lion
    Recent monitoring data from the Colman Dock Project in 2017 and 
2018 (WSDOT 2019) reported observations of 54 Steller sea lions over 99 
days of monitoring activity, which is roughly equivalent to one Steller 
sea lion every other day. To account for unobserved animals at the 
outer extent of the Level B harassment zones, the City estimates two 
Steller sea lions may be taken by Level B harassment per day for a 
total of 140 takes by Level B harassment from Pier 58 reconstruction 
and 94 takes by Level B harassment from Pier 63 removal.
    The largest Level A harassment zone for otariid pinnipeds is 6 m. 
The City would be required to enforce a minimum shutdown zone of 10 m 
for all activities. At that close range, the City would be able to 
detect Steller sea lions and implement the required shutdown measures 
before Steller sea lions could enter the Level A harassment zone. 
Therefore, no takes of Steller sea lions by Level A harassment are 
requested or proposed to be authorized.
Northern Elephant Seal
    Individual elephant seals have occasionally been reported in 
central Puget Sound (e.g., Orca Network, 2020) but are considered rare 
in the project areas. WSDOT (2019) reported observations near Alki 
Point (at the outer extent of the Level B harassment zones) and Maury 
Island (just outside the Level B harassment zones) in 2017 and 2015, 
respectively. Based on these reports, the City estimates that one 
northern elephant seal may be taken by Level B harassment per month for 
a total of 6 takes by Level B harassment from Pier 58 reconstruction 
and 3 takes by Level B harassment from Pier 63 removal.
    The largest Level A harassment zone (82 m) occurs during impact 
installation of steel pipe piles at Pier 58. It is unlikely that 
northern elephant seals would be found within this zone, and even more 
unlikely that northern elephant seals would be found within the Level A 
harassment zones for vibratory pile driving at either pier (less than 
12 m for all pile types). However, even if northern elephant seals were 
encountered in the project areas, at that close range, the City would 
be able to detect them and implement the required shutdown measures 
before any northern elephant seals could enter the Level A harassment 
zones. Therefore, no take of northern elephant seals by Level A 
harassment is requested or proposed to be authorized.
Harbor Seal
    During monitoring for the Pier 62 Project, the maximum number of 
harbor seals documented as taken by Level B harassment in one day was 
54, but the average number documented per day was 5 (Anchor QEA 2019). 
To account for potentially unobserved animals at the outer extent of 
the Level B

[[Page 12107]]

harassment zone during the previous monitoring, the City estimates that 
10 harbor seals per day may enter the Level B harassment zone during 
pile driving work at Pier 58 for a total of 700 harbor seals. In 
addition, due to their apparent curious nature and previously reported 
close approaches to pile driving equipment (Anchor QEA 2019), the City 
estimates that of those 700 harbor seals that could enter the Level B 
harassment zone, one harbor seal may approach closer and enter the 82-m 
Level A harassment zone before the animal is detected and activities 
shut down, and thus be taken by Level A harassment on each day of 
impact pile installation at Pier 58 (40 days). The Level A harassment 
zones for phocids for all vibratory pile driving at Pier 58 are all 
under 12 m. At that distance, the City would be able to detect harbor 
seals and cease pile driving activities before harbor seals could enter 
the Level A harassment zone. Therefore, no take of harbor seals by 
Level A harassment is anticipated from vibratory pile driving at Pier 
58. In total, the City has requested 700 takes of harbor seals, 660 
takes by Level B harassment and 40 takes by Level A harassment from 
Pier 58 reconstruction.
    On all but two days of work at Pier 63, the Level B harassment zone 
will be well within Elliott Bay. Since the extent of the Level B 
harassment zone for this project on most days is less than for Pier 58, 
the City estimates that up to 6 harbor seals may be taken by Level B 
harassment per day during the 47 days of pile removal at Pier 63 for a 
total of 282 takes by Level B harassment.
    The largest Level A harassment zone for the City's proposed 
activities at Pier 63 is 12 m. The City would be required to implement 
a 15 m shutdown zone to prevent Level A take of phocids for this 
project (see Proposed Mitigation). At that close range, the City would 
be able to detect harbor seals and cease pile driving activities before 
harbor seals could enter the Level A harassment zone. Therefore, no 
take of harbor seals by Level A harassment is requested or proposed to 
be authorized for work at Pier 63.
    NMFS has carefully considered all information and analysis 
presented by the City as well as all other applicable information and, 
based on the best available science, concurs that the City's estimates 
of the types and amounts of take for each species and stock are 
complete and accurate.

   Table 10--Proposed Take of Marine Mammals by Level A and Level B Harassment From Pier 58 Reconstruction, by
                                 Species and Stock and Percent of Take by Stock
----------------------------------------------------------------------------------------------------------------
                                                   Proposed take   Proposed take
            Species                   Stock         by Level B      by Level A         Stock        Percent of
                                                    harassment      harassment       abundance         stock
----------------------------------------------------------------------------------------------------------------
Humpback whale................  California/               \a\ 12               0           4,973            0.24
                                 Oregon/
                                 Washington.
Gray whale....................  Eastern North                  4               0          26,960            0.01
                                 Pacific.
Minke whale...................  California/                    6               0             915            0.66
                                 Oregon/
                                 Washington.
Killer whale..................  West Coast                    36               0             349           10.32
                                 Transient.
Killer whale..................  Southern                      23               0              72           31.94
                                 Resident.
Bottlenose dolphin............  California                    42               0             453            9.27
                                 Coastal.
Long-beaked common dolphin....  California......              42               0          83,379            0.05
Harbor porpoise...............  Washington                   408              12          11,233            3.74
                                 Inland Waters.
Dall's porpoise...............  California/                   60              12          16,498            0.44
                                 Oregon/
                                 Washington.
California sea lion...........  U.S.............             700               0         257,606            0.27
Steller sea lion..............  Eastern.........             140               0          43,201            0.32
Northern elephant seal........  California                     6               0         187,386           0.003
                                 Breeding.
Harbor seal...................  Washington                   660              40          11,036            6.34
                                 Northern Inland
                                 Waters.
----------------------------------------------------------------------------------------------------------------
\a\ Based on proportional estimates of humpback DPS occurrence in the area from Wade et al. (2021), we estimate
  that of the 12 total takes, 25 percent (approximately 3) would be from the threatened Mexico DPS and 6 percent
  (approximately 1) from the endangered Central America DPS. The remaining 69 percent of humpback whales
  (approximately 8) would be from the unlisted Hawai'i DPS.


Table 11--Proposed Take of Marine Mammals by Level A and Level B Harassment From Pier 63 Removal, by Species and
                                       Stock and Percent of Take by Stock
----------------------------------------------------------------------------------------------------------------
                                                   Proposed take   Proposed take
            Species                   Stock         by Level B      by Level A         Stock        Percent of
                                                    harassment      harassment       abundance         stock
----------------------------------------------------------------------------------------------------------------
Humpback whale................  California/                \a\ 6               0           4,973            0.12
                                 Oregon/
                                 Washington.
Gray whale....................  Eastern North                  3               0          26,960            0.01
                                 Pacific.
Minke whale...................  California/                    3               0             915            0.33
                                 Oregon/
                                 Washington.
Killer whale..................  West Coast                    18               0             349            5.16
                                 Transient.
Killer whale..................  Southern                       0               0              72               0
                                 Resident.
Bottlenose dolphin............  California                    21               0             453            4.64
                                 Coastal.
Long-beaked common dolphin....  California......              21               0          83,379            0.02
Harbor porpoise...............  Washington                   235               0          11,233             2.1
                                 Inland Waters.
Dall's porpoise...............  California/                   36               0          16,498            0.22
                                 Oregon/
                                 Washington.
California sea lion...........  U.S.............             470               0         257,606            0.18
Steller sea lion..............  Eastern.........              94               0          43,201            0.22
Northern elephant seal........  California                     3               0         187,386           0.002
                                 Breeding.
Harbor seal...................  Washington                   282               0          11,036            2.56
                                 Northern Inland
                                 Waters.
----------------------------------------------------------------------------------------------------------------
\a\ Based on proportional estimates of humpback DPS occurrence in the area from Wade et al. (2021), we estimate
  that of the 6 total takes, 25 percent (approximately 1) would be from the Mexico DPS and 6 percent
  (approximately 1) from the Central America DPS. The remaining 69 percent of humpback whales (approximately 4)
  would be from the unlisted Hawai'i DPS.


[[Page 12108]]

Proposed Mitigation

    In order to issue an IHA under section 101(a)(5)(D) of the MMPA, 
NMFS must set forth the permissible methods of taking pursuant to the 
activity, and other means of effecting the least practicable impact on 
the species or stock and its habitat, paying particular attention to 
rookeries, mating grounds, and areas of similar significance, and on 
the availability of the species or stock for taking for certain 
subsistence uses (latter not applicable for these actions). NMFS 
regulations require applicants for incidental take authorizations to 
include information about the availability and feasibility (economic 
and technological) of equipment, methods, and manner of conducting the 
activity or other means of effecting the least practicable adverse 
impact upon the affected species or stocks and their habitat (50 CFR 
216.104(a)(11)).
    In evaluating how mitigation may or may not be appropriate to 
ensure the least practicable adverse impact on species or stocks and 
their habitat, as well as subsistence uses where applicable, we 
carefully consider two primary factors:
    (1) The manner in which, and the degree to which, the successful 
implementation of the measure(s) is expected to reduce impacts to 
marine mammals, marine mammal species or stocks, and their habitat. 
This considers the nature of the potential adverse impact being 
mitigated (likelihood, scope, range). It further considers the 
likelihood that the measure will be effective if implemented 
(probability of accomplishing the mitigating result if implemented as 
planned), the likelihood of effective implementation (probability 
implemented as planned), and;
    (2) The practicability of the measures for applicant 
implementation, which may consider such things as cost, impact on 
operations, and, in the case of a military readiness activity, 
personnel safety, practicality of implementation, and impact on the 
effectiveness of the military readiness activity.

Time Restrictions

    The City has provided in its description of the projects that pile 
driving would occur only during daylight hours, when visual monitoring 
of marine mammals can be conducted. In addition, all in-water 
construction would be limited to the period between September 1 and 
February 15.

Shutdown Zones

    Before the commencement of in-water construction activities, the 
City would establish shutdown zones for all activities. The purpose of 
a shutdown zone is generally to define an area within which shutdown of 
the activity would occur upon sighting of a marine mammal (or in 
anticipation of an animal entering the defined area). Pile driving 
would also not commence until all marine mammals are clear of their 
respective shutdown zones. Shutdown zones are meant to encompass the 
Level A harassment zones and therefore would vary based on the activity 
type and marine mammal hearing group (Tables 12 and 13). At minimum, 
the shutdown zone for all hearing groups and all activities is 10 m. 
For in-water heavy machinery work other than pile driving (e.g., 
standard barges, etc.), if a marine mammal comes within 10 m, 
operations would cease and vessels would reduce speed to the minimum 
level required to maintain steerage and safe working conditions. This 
type of work could include, for example, the movement of the barge to 
the pile location or positioning of the pile on the substrate via a 
crane.
    The City would also establish shutdown zones for all marine mammals 
for which take has not been authorized or for which incidental take has 
been authorized but the authorized number of takes has been met. These 
zones are equivalent to the Level B harassment zones for each activity 
(see Tables 12 and 13).
    The City would also implement shutdown measures for SRKW. If SRKW 
are sighted within the vicinity of the project areas and are 
approaching the Level B harassment zone, the City would shut down the 
pile driving equipment to avoid possible take of the stock. If a killer 
whale approaches the Level B harassment zone during pile driving, and 
it is unknown whether it is a SRKW or a transient killer whale, it 
would be assumed to be a SRKW and the City would implement the shutdown 
measure. If a SRKW or an unidentified killer whale enters the Level B 
harassment zone undetected, in-water pile driving would be suspended 
until the whale exits the Level B harassment zone, or 15 minutes have 
elapsed with no sighting of the animal, to avoid further Level B 
harassment.

                               Table 12--Shutdown Zones for Pier 58 Reconstruction
----------------------------------------------------------------------------------------------------------------
                                                               Shutdown zone (m)
                              ----------------------------------------------------------------------------------
                                                                                                    SRKW  (and
     Pile type and method                                                                              other
                               LF cetacean   MF cetacean   HF cetacean    Phocids      Otariids    unauthorized
                                                                                                     species)
----------------------------------------------------------------------------------------------------------------
Timber and steel H-pile                 10            10            10           10           10           1,359
 vibratory removal...........
24-in steel vibratory                   20            10            30           15           10           7,357
 installation and removal, 30-
 in steel vibratory
 installation................
30-in steel impact                     155            10           185           85           10             215
 installation................
----------------------------------------------------------------------------------------------------------------


                                  Table 13--Shutdown Zones for Pier 63 Removal
----------------------------------------------------------------------------------------------------------------
                                                               Shutdown zone (m)
                              ----------------------------------------------------------------------------------
                                                                                                    SRKW  (and
          Pile type                                                                                    other
                               LF cetacean   MF cetacean   HF cetacean    Phocids      Otariids    unauthorized
                                                                                                     species)
----------------------------------------------------------------------------------------------------------------
Timber pile vibratory removal           10            10            10           10           10           1,359
Steel pile vibratory removal.           20            10            30           15           10           7,357
----------------------------------------------------------------------------------------------------------------


[[Page 12109]]

Protected Species Observers

    The placement of protected species observers (PSOs) during all pile 
driving activities (described in the Proposed Monitoring and Reporting 
section) would ensure that the entire shutdown zone is visible. Should 
environmental conditions deteriorate such that the entire shutdown zone 
would not be visible (e.g., fog, heavy rain), pile driving would be 
delayed until the PSO is confident marine mammals within the shutdown 
zone could be detected.
Monitoring for Level A and Level B Harassment
    PSOs would monitor the Level B harassment zones to the extent 
practicable, and all of the Level A harassment zones. Monitoring zones 
provide utility for observing by establishing monitoring protocols for 
areas adjacent to the shutdown zones. Monitoring zones enable observers 
to be aware of and communicate the presence of marine mammals in the 
project areas outside the shutdown zones and thus prepare for a 
potential cessation of activity should the animal enter the shutdown 
zone.
Pre-Activity Monitoring
    Prior to the start of daily in-water construction activity, or 
whenever a break in pile driving of 30 minutes or longer occurs, PSOs 
would observe the shutdown and monitoring zones for a period of 30 
minutes. The shutdown zone would be considered cleared when a marine 
mammal has not been observed within the zone for that 30-minute period. 
If a marine mammal is observed within the shutdown zones listed in 
Tables 12 and 13, pile driving activity would be delayed or halted. If 
pile driving is delayed or halted due to the presence of a marine 
mammal, the activity would not commence or resume until either the 
animal has voluntarily exited and been visually confirmed beyond the 
shutdown zones or 15 minutes have passed without re-detection of the 
animal. When a marine mammal for which Level B harassment take is 
authorized is present in the Level B harassment zone, activities would 
begin and Level B harassment take would be recorded. If work ceases for 
more than 30 minutes, the pre-activity monitoring of the shutdown zones 
would commence. A determination that the shutdown zone is clear must be 
made during a period of good visibility (i.e., the entire shutdown zone 
and surrounding waters must be visible to the naked eye).
Coordination With Local Marine Mammal Research Network
    Prior to the start of pile driving for the day, and at the 
approximate mid-point of the pile driving work to be conducted each 
day, the PSOs would contact the Orca Network to find out the location 
of the nearest marine mammal sightings. The Local Marine Mammal 
Research Network consists of a list of over 600 (and growing) 
residents, scientists, and government agency personnel in the United 
States and Canada. Sightings are called or emailed into the Orca 
Network and immediately distributed to other sighting networks 
including: The NMFS Northwest Fisheries Science Center, the Center for 
Whale Research, Cascadia Research, the Whale Museum Hotline and the 
British Columbia Sightings Network.
    Sightings information collected by the Orca Network includes 
detection by hydrophone. The SeaSound Remote Sensing Network is a 
system of interconnected hydrophones installed in the marine 
environment of Haro Strait (west side of San Juan Island) to study orca 
communication, in-water noise, bottom fish ecology and local climatic 
conditions. A hydrophone at the Port Townsend Marine Science Center 
measures average in-water sound levels and automatically detects 
unusual sounds. These passive acoustic devices allow researchers to 
hear when different marine mammals come into the region. This acoustic 
network, combined with the volunteer (incidental) visual sighting 
network allows researchers to document presence and location of various 
marine mammal species.

Soft Start

    Soft-start procedures are used to provide additional protection to 
marine mammals by providing warning and/or giving marine mammals a 
chance to leave the area prior to the hammer operating at full 
capacity. For impact pile driving, contractors would be required to 
provide an initial set of three strikes from the hammer at reduced 
energy, followed by a 30-second waiting period, then two subsequent 
reduced-energy strike sets. Soft start would be implemented at the 
start of each day's impact pile driving and at any time following 
cessation of impact pile driving for a period of 30 minutes or longer.

Bubble Curtain

    A bubble curtain would be employed during impact installation or 
proofing of steel piles. A noise attenuation device would not be 
required during vibratory pile driving. If a bubble curtain or similar 
measure is used, it would distribute air bubbles around 100 percent of 
the piling perimeter for the full depth of the water column. Any other 
attenuation measure would be required to provide 100 percent coverage 
in the water column for the full depth of the pile. The lowest bubble 
ring would be in contact with the mudline for the full circumference of 
the ring. The weights attached to the bottom ring would ensure 100 
percent mudline contact. No parts of the ring or other objects would 
prevent full mudline contact.
    Based on our evaluation of the City's proposed measures, as well as 
other measures considered by NMFS, NMFS has preliminarily determined 
that the proposed mitigation measures provide the means of effecting 
the least practicable impact on the affected species or stocks and 
their habitat, paying particular attention to rookeries, mating 
grounds, and areas of similar significance for the Pier 58 
Reconstruction Project. NMFS also preliminarily finds that the proposed 
mitigation measures and other measures considered by NMFS provide the 
means of effecting the least practicable impact on the affected species 
or stocks and their habitat, paying particular attention to rookeries, 
mating grounds, and areas of similar significance for the Pier 63 
Removal Project.

Proposed Monitoring and Reporting

    In order to issue an IHA for an activity, section 101(a)(5)(D) of 
the MMPA states that NMFS must set forth requirements pertaining to the 
monitoring and reporting of such taking. The MMPA implementing 
regulations at 50 CFR 216.104(a)(13) indicate that requests for 
authorizations must include the suggested means of accomplishing the 
necessary monitoring and reporting that will result in increased 
knowledge of the species and of the level of taking or impacts on 
populations of marine mammals that are expected to be present while 
conducting the activities. Effective reporting is critical both to 
compliance as well as ensuring that the most value is obtained from the 
required monitoring.
    Monitoring and reporting requirements prescribed by NMFS should 
contribute to improved understanding of one or more of the following:
     Occurrence of marine mammal species or stocks in the area 
in which take is anticipated (e.g., presence, abundance, distribution, 
density).
     Nature, scope, or context of likely marine mammal exposure 
to potential

[[Page 12110]]

stressors/impacts (individual or cumulative, acute or chronic), through 
better understanding of: (1) Action or environment (e.g., source 
characterization, propagation, ambient noise); (2) affected species 
(e.g., life history, dive patterns); (3) co-occurrence of marine mammal 
species with the action; or (4) biological or behavioral context of 
exposure (e.g., age, calving or feeding areas).
     Individual marine mammal responses (behavioral or 
physiological) to acoustic stressors (acute, chronic, or cumulative), 
other stressors, or cumulative impacts from multiple stressors.
     How anticipated responses to stressors impact either: (1) 
Long-term fitness and survival of individual marine mammals; or (2) 
populations, species, or stocks.
     Effects on marine mammal habitat (e.g., marine mammal prey 
species, acoustic habitat, or other important physical components of 
marine mammal habitat).
     Mitigation and monitoring effectiveness.

Visual Monitoring

    Marine mammal monitoring during pile driving activities would be 
conducted by PSOs meeting NMFS' standards and in a manner consistent 
with the following:
     Independent PSOs (i.e., not construction personnel) who 
have no other assigned tasks during monitoring periods would be used;
     At least one PSO would have prior experience performing 
the duties of a PSO during construction activity pursuant to a NMFS-
issued incidental take authorization;
     Other PSOs may substitute education (degree in biological 
science or related field) or training for experience; and
     Where a team of three or more PSOs is required, a lead 
observer or monitoring coordinator would be designated. The lead 
observer would be required to have prior experience working as a marine 
mammal observer during construction.
    PSOs would have the following additional qualifications:
     Ability to conduct field observations and collect data 
according to assigned protocols;
     Experience or training in the field identification of 
marine mammals, including the identification of behaviors;
     Sufficient training, orientation, or experience with the 
construction operation to provide for personal safety during 
observations;
     Writing skills sufficient to prepare a report of 
observations including but not limited to the number and species of 
marine mammals observed; dates and times when in-water construction 
activities were conducted; dates, times, and reason for implementation 
of mitigation (or why mitigation was not implemented when required); 
and marine mammal behavior; and
     Ability to communicate orally, by radio or in person, with 
project personnel to provide real-time information on marine mammals 
observed in the area as necessary.
    The City would have PSOs stationed around Elliott Bay to monitor 
during all pile driving activities. During removal of timber and/or 
steel H-piles at Pier 58 and Pier 63, two PSOs would monitor the area, 
one at the construction site and one at Alki Point on the south side of 
Elliott Bay. During vibratory removal and/or installation of steel 
piles at Pier 58 and Pier 63, PSOs would be stationed at the same 
locations as above, with an additional PSO monitoring from Magnolia on 
the north side of Elliott Bay and one PSO monitoring from the Seattle-
Bainbridge ferry. Impact installation of 30-inch permanent steel piles 
at Pier 58 is expected to occur on the same day as vibratory 
installation of those piles. If all vibratory installation has 
concluded for the day, only the PSO stationed at the construction site 
would be required to continue monitoring during impact pile driving.
    Monitoring would be conducted 30 minutes before, during, and 30 
minutes after all in water construction activities. In addition, 
observers would record all incidents of marine mammal occurrence, 
regardless of distance from activity, and would document any behavioral 
reactions in concert with distance from piles being driven or removed. 
Pile driving activities include the time to install or remove a single 
pile or series of piles, as long as the time elapsed between uses of 
the pile driving equipment is no more than 30 minutes.

Reporting

    A draft marine mammal monitoring report would be submitted to NMFS 
within 90 days after the completion of pile driving activities, or 60 
days prior to a requested date of issuance of any future IHAs for the 
project, or other projects at the same location, whichever comes first. 
The marine mammal report would include an overall description of work 
completed, a narrative regarding marine mammal sightings, and 
associated PSO data sheets. Specifically, the report would include:
     Dates and times (begin and end) of all marine mammal 
monitoring;
     Construction activities occurring during each daily 
observation period, including: (a) How many and what type of piles were 
driven or removed and the method (i.e., impact or vibratory); and (b) 
the total duration of time for each pile (vibratory driving) number of 
strikes for each pile (impact driving);
     PSO locations during marine mammal monitoring; and
     Environmental conditions during monitoring periods (at 
beginning and end of PSO shift and whenever conditions change 
significantly), including Beaufort sea state and any other relevant 
weather conditions including cloud cover, fog, sun glare, and overall 
visibility to the horizon, and estimated observable distance.
    For each observation of a marine mammal, the following would be 
reported:
     Name of PSO who sighted the animal(s) and PSO location and 
activity at time of sighting;
     Time of sighting;
     Identification of the animal(s) (e.g., genus/species, 
lowest possible taxonomic level, or unidentified), PSO confidence in 
identification, and the composition of the group if there is a mix of 
species;
     Distance and location of each observed marine mammal 
relative to the pile being driven or hole being drilled for each 
sighting;
     Estimated number of animals (min/max/best estimate);
     Estimated number of animals by cohort (adults, juveniles, 
neonates, group composition, etc.);
     Description of any marine mammal behavioral observations 
(e.g., observed behaviors such as feeding or traveling), including an 
assessment of behavioral responses thought to have resulted from the 
activity (e.g., no response or changes in behavioral state such as 
ceasing feeding, changing direction, flushing, or breaching);
     Number of marine mammals detected within the harassment 
zones, by species; and
     Detailed information about implementation of any 
mitigation (e.g., shutdowns and delays), a description of specified 
actions that ensued, and resulting changes in behavior of the 
animal(s), if any.
    If no comments are received from NMFS within 30 days, the draft 
reports would constitute the final reports. If comments are received, a 
final report addressing NMFS' comments would be required to be 
submitted within 30 days after receipt of comments. All PSO datasheets 
and/or raw sighting data would be submitted with the draft marine 
mammal report.

[[Page 12111]]

    In the event that personnel involved in the construction activities 
discover an injured or dead marine mammal, the City would report the 
incident to the Office of Protected Resources (OPR) 
([email protected]), NMFS and to the West Coast Region 
(WCR) regional stranding coordinator as soon as feasible. If the death 
or injury was clearly caused by the specified activity, the City would 
immediately cease the specified activities until NMFS is able to review 
the circumstances of the incident and determine what, if any, 
additional measures are appropriate to ensure compliance with the terms 
of the IHAs. The City would not resume their activities until notified 
by NMFS.
    The report would include the following information:
    1. Time, date, and location (latitude/longitude) of the first 
discovery (and updated location information if known and applicable);
    2. Species identification (if known) or description of the 
animal(s) involved;
    3. Condition of the animal(s) (including carcass condition if the 
animal is dead);
    4. Observed behaviors of the animal(s), if alive;
    5. If available, photographs or video footage of the animal(s); and
    6. General circumstances under which the animal was discovered.

Negligible Impact Analysis and Determination

    NMFS has defined negligible impact as an impact resulting from the 
specified activity that cannot be reasonably expected to, and is not 
reasonably likely to, adversely affect the species or stock through 
effects on annual rates of recruitment or survival (50 CFR 216.103). A 
negligible impact finding is based on the lack of likely adverse 
effects on annual rates of recruitment or survival (i.e., population-
level effects). An estimate of the number of takes alone is not enough 
information on which to base an impact determination. In addition to 
considering estimates of the number of marine mammals that might be 
``taken'' through harassment, NMFS considers other factors, such as the 
likely nature of any responses (e.g., intensity, duration), the context 
of any responses (e.g., critical reproductive time or location, 
migration), as well as effects on habitat, and the likely effectiveness 
of the mitigation. We also assess the number, intensity, and context of 
estimated takes by evaluating this information relative to population 
status. Consistent with the 1989 preamble for NMFS's implementing 
regulations (54 FR 40338; September 29, 1989), the impacts from other 
past and ongoing anthropogenic activities are incorporated into this 
analysis via their impacts on the environmental baseline (e.g., as 
reflected in the regulatory status of the species, population size and 
growth rate where known, ongoing sources of human-caused mortality, or 
ambient noise levels).
    Pile driving activities from Pier 58 reconstruction and Pier 63 
removal have the potential to disturb or displace marine mammals. 
Specifically, the project activities may result in take, in the form of 
Level A and Level B harassment, from underwater sounds generated from 
pile driving. Potential takes could occur if individuals are present in 
the ensonified zone when these activities are underway.
    The takes from Level A and Level B harassment would be due to 
potential behavioral disturbance, TTS, and PTS. No serious injury or 
mortality is anticipated given the nature of the activities and 
measures designed to minimize the possibility of injury to marine 
mammals. The potential for harassment is minimized through the 
construction method and the implementation of the planned mitigation 
measures (see Proposed Mitigation section).
    To avoid repetition, the majority of our analyses apply to all the 
species listed in Table 3, and to both the Pier 58 and Pier 63 IHAs, 
given that the anticipated effects of the City's two projects on 
different marine mammal stocks are expected to be relatively similar in 
nature. Where there are meaningful differences between species or 
stocks--as is the case of the SRKW--they are included as separate 
subsections below. Similarly, where there are differences between the 
two IHAs, they are highlighted below.
    NMFS has identified key factors which may be employed to assess the 
level of analysis necessary to conclude whether potential impacts 
associated with a specified activity should be considered negligible. 
These include (but are not limited to) the type and magnitude of 
taking, the amount and importance of the available habitat for the 
species or stock that is affected, the duration of the anticipated 
effect to the species or stock, and the status of the species or stock. 
The following factors support negligible impact determinations for the 
affected stocks of humpback whales, gray whales, transient killer 
whales, bottlenose dolphins, long-beaked common dolphins, harbor 
porpoise, Dall's porpoise, California sea lions, Steller sea lions, 
northern elephant seals, and harbor seals. Some of these factors may 
also apply to SRKW; however, a more detailed analysis for SRKW is 
provided below.
    No take by Level A harassment is anticipated or proposed to be 
authorized incidental to the Pier 63 Removal Project. For the Pier 58 
Reconstruction Project, take by Level A harassment is proposed for 
three species (harbor seals, harbor porpoise, and Dall's porpoise) to 
account for the possibility that an animal could enter a Level A 
harassment zone prior to detection, and remain within that zone for a 
duration long enough to incur PTS before being observed and the City 
shutting down pile driving activity. Any take by Level A harassment is 
expected to arise from, at most, a small degree of PTS, i.e., minor 
degradation of hearing capabilities within regions of hearing that 
align most completely with the energy produced by impact pile driving 
(i.e. the low-frequency region below 2 kHz), not severe hearing 
impairment or impairment within the ranges of greatest hearing 
sensitivity. Animals would need to be exposed to higher levels and/or 
longer duration than are expected to occur here in order to incur any 
more than a small degree of PTS.
    Additionally, the amount of authorized take, by Level A harassment 
is very low for all marine mammal stocks and species. For the Pier 58 
Reconstruction Project, for 10 of 13 stocks, NMFS anticipates and 
proposes to authorize no Level A harassment take over the duration of 
the City's planned activities; for the other three stocks, NMFS 
authorizes no more than 40 takes by Level A harassment. If hearing 
impairment occurs, it is most likely that the affected animal would 
lose only a few decibels in its hearing sensitivity. These takes of 
individuals by Level A harassment (i.e., a small degree of PTS) are not 
expected to accrue in a manner that would affect the reproductive 
success or survival of any individuals, much less result in adverse 
impacts on the species or stock.
    As described above, NMFS expects that marine mammals would likely 
move away from an aversive stimulus, especially at levels that would be 
expected to result in PTS, given sufficient notice through use of soft 
start. The City would also shut down pile driving activities if marine 
mammals approach within hearing group-specific zones that encompass the 
Level A harassment zones (see Tables 12 and 13) further minimizing the 
likelihood and degree of PTS that would be incurred. Even absent 
mitigation, no serious injury or mortality from

[[Page 12112]]

construction activities is anticipated or authorized.
    Effects on individuals that are taken by Level B harassment in the 
form of behavioral disruption, on the basis of reports in the 
literature as well as monitoring from other similar activities, would 
likely be limited to reactions such as avoidance, increased swimming 
speeds, increased surfacing time, or decreased foraging (if such 
activity were occurring) (e.g., Thorson and Reyff 2006). Most likely, 
individuals would simply move away from the sound source and 
temporarily avoid the area where pile driving is occurring. If sound 
produced by project activities is sufficiently disturbing, animals are 
likely to simply avoid the area while the activities are occurring, 
particularly as the project is located on a busy waterfront with high 
amounts of vessel traffic. We expect that any avoidance of the project 
areas by marine mammals would be temporary in nature and that any 
marine mammals that avoid the project areas during construction would 
not be permanently displaced. Short-term avoidance of the project areas 
and energetic impacts of interrupted foraging or other important 
behaviors is unlikely to affect the reproduction or survival of 
individual marine mammals, and the effects of behavioral disturbance on 
individuals is not likely to accrue in a manner that would affect the 
rates of recruitment or survival of any affected stock.
    Additionally, and as noted previously, some subset of the 
individuals that are behaviorally harassed could also simultaneously 
incur some small degree of TTS for a short duration of time. However, 
since the hearing sensitivity of individuals that incur TTS is expected 
to recover completely within minutes to hours, it is unlikely that the 
brief hearing impairment would affect the individual's long-term 
ability to forage and communicate with conspecifics, and would 
therefore not likely impact reproduction or survival of any individual 
marine mammal, let alone adversely affect rates of recruitment or 
survival of the species or stock.
    The projects are also not expected to have significant adverse 
effects on affected marine mammals' habitats. The project activities 
will not modify existing marine mammal habitat for a significant amount 
of time. The activities may cause some fish to leave the area of 
disturbance, thus temporarily impacting marine mammals' foraging 
opportunities in a limited portion of the foraging range; but, because 
of the short duration of the activities and the relatively small area 
of the habitat that may be affected (with no known particular 
importance to marine mammals), the impacts to marine mammal habitat are 
not expected to cause significant or long-term negative consequences. 
Aside from the SRKW critical habitat and BIA for gray whales described 
below, there are no known important areas for other marine mammals, 
such as feeding or pupping areas.
    For all species and stocks, and both project areas (Pier 58 and 
63), take would occur within a limited, relatively confined area 
(Elliott Bay within central Puget Sound) of the stock's range. Given 
the availability of suitable habitat nearby, any displacement of marine 
mammals from the project areas is not expected to affect marine 
mammals' fitness, survival, and reproduction due to the limited 
geographic area that would be affected in comparison to the much larger 
habitat for marine mammals in Puget Sound. Level A harassment and Level 
B harassment would be reduced to the level of least practicable adverse 
impact to the marine mammal species or stocks and their habitat through 
use of mitigation measures described herein. Some individual marine 
mammals in the project areas may be present and be subject to repeated 
exposure to sound from pile driving on multiple days. However, these 
individuals would likely return to normal behavior during gaps in pile 
driving activity. Therefore, any behavioral effects of repeated or long 
duration exposures are not expected to negatively affect survival or 
reproductive success of any individuals. Thus, even repeated Level B 
harassment of some small subset of an overall stock is unlikely to 
result in any effects on rates of reproduction and survival of the 
stock.

Southern Resident Killer Whales

    No takes of any sort are proposed to be authorized or anticipated 
for SRKW at the Pier 63 project. For the Pier 58 project, no permanent 
hearing impairment (PTS), or any other Level A harassment, is 
anticipated or proposed to be authorized; authorized takes of SRKW at 
Pier 58 would be limited to Level B harassment in the form of 
behavioral disturbance.
    SRKW may be exposed to sound above the Level B harassment threshold 
during the Pier 58 reconstruction project. Although the City would be 
required to shut down any pile driving equipment before SRKW approach 
the Level B harassment zone, there is some potential that one or more 
SRKW could enter the area undetected and be taken before the City is 
able to shut down. If that were to occur, it is likely that the whales 
would be detected at the outer edges of the Level B harassment zone, 
which would lessen the degree of sound than would be experienced if 
they were to approach closer to the project site. Therefore, if SRKW 
were exposed to sound above the Level B harassment threshold, it would 
generally be of a lower level and very short duration (only the time to 
detect the animals and shut down), which is expected to lessen the 
degree and duration of potential disturbance.
    SRKW could be foraging while traveling past the Pier 58 
reconstruction area and cease foraging effort in response to sound from 
the project if they entered the Level B harassment zone undetected, as 
discussed above. Most studies on the effects of disturbance on SRKW 
foraging have focused on impacts of whale watch vessels operating in 
close proximity to SRKW, and commercial shipping traffic in the Salish 
Sea. Exposure to vessel noise and presence of whale watching boats can 
significantly affect the foraging behavior of SRKW (Williams et al., 
2006; Lusseau et al., 2009; Giles and Cendak 2010; Senigaglia et al., 
2016). Nutritional stress has also been identified as a primary cause 
of SRKW decline (Ayres et al., 2012; Wasser et al., 2017), suggesting 
that reduced foraging effort may have a greater impact than behavioral 
disturbance alone. However, given the typical frequency of killer whale 
foraging echolocation clicks (18 to 32 kHz), Lacy et al. (2017) note 
that high-frequency noise from small, outboard motors on many 
commercial whale watching and private vessels likely causes a greater 
reduction in killer whale foraging success than low-frequency (<1 kHz) 
noise from commercial shipping or pile driving (<2 kHz). While SRKW may 
experience elevated sound levels of lower frequencies from the City's 
proposed projects if they were to enter the Level B harassment zone 
during pile driving activities, the relatively small amount of time of 
altered behavior and minimal overlap of the predominant frequencies of 
pile driving and echolocation would not likely affect their overall 
foraging ability. Short-term impacts to foraging ability are not likely 
to have any effect on reproduction or survival of the individual SRKW, 
let alone effects on rates of recruitment or survival for the 
population as a whole (see Ayres et al., 2012). Given the extensive 
monitoring and mitigation measures for all marine mammals and SRKW in 
particular, it is unlikely that individual whales would be exposed on 
multiple occasions.

[[Page 12113]]

    ESA critical habitat for SRKW has been designated in Puget Sound, 
including the project areas (71 FR 69054; November 29, 2006). Critical 
habitat features were identified in consideration of physical and 
biological features essential to conservation of SRKW (essential 
features): (1) Water quality to support growth and development; (2) 
Prey species of sufficient quantity, quality, and availability to 
support individual growth, reproduction, and development, as well as 
overall population growth; and (3) Passage conditions to allow for 
migration, resting, and foraging. NMFS did not identify in-water sound 
levels as a separate essential feature of critical habitat, though 
anthropogenic sound is recognized as one of the primary threats to SRKW 
(NMFS 2019). The exposure of SRKW to sound from the proposed activities 
would be minimized by the required proposed mitigation measures (e.g., 
shutdown zones equivalent to the Level B harassment zones). The effects 
of the activities on SRKW habitat generally, such as sedimentation and 
impacts to availability of prey species, are expected to be limited 
both spatially and temporally, constrained to the immediate area around 
the pile driver(s) at each pier and returning to baseline levels 
quickly. Additionally, the timing of the in-water work window for the 
projects is intended to limit impacts to juvenile salmonids, which 
would accordingly reduce potential impacts to SRKW prey. We therefore 
conclude that the proposed activities would have a negligible impact on 
SRKW.

Gray Whales

    Puget Sound is part of a BIA for migrating gray whales 
(Calambokidis et al., 2015). While Elliott Bay is included in the BIA, 
gray whales typically remain further north in Puget Sound, primarily in 
the waters around Whidbey Island (Calambokidis et al., 2018). Gray 
whales are rarely observed in Elliott Bay. Therefore, even though the 
project areas overlap with the BIA, the infrequent occurrence of gray 
whales suggests that the proposed projects would have minimal, if any, 
impact on the migration of gray whales in the BIA, and would therefore 
not affect reproduction or survival.
    There is an ongoing UME for gray whales (see the Description of 
Marine Mammals in the Area of Specified Activities section of this 
notice). However, we do not expect the takes estimated to occur and 
proposed for authorization to exacerbate or compound upon these ongoing 
UMEs. As noted previously, no Level A harassment, serious injury, or 
mortality is expected or proposed for authorization, and any Level B 
harassment takes of gray whales would most likely be in the form of 
behavioral disturbance. The project areas have not been identified as 
important for feeding or mating gray whales, and therefore the projects 
are unlikely to disrupt any critical behaviors or have any effect on 
the reproduction or survival of gray whales, even in light of the 
ongoing UME.
    In summary and as described above, the following factors primarily 
support our preliminary determination that the impacts resulting from 
these activities are not expected to adversely affect any of the 
species or stocks through effects on annual rates of recruitment or 
survival:
     No mortality or serious injury is anticipated or proposed 
to be authorized for either project;
     No take of any species by Level A harassment is 
anticipated or proposed to be authorized for the Pier 63 Removal 
Project;
     For the Pier 58 Reconstruction Project, Level A harassment 
is not anticipated or proposed to be authorized for 10 of the 13 
species. For the other three species, the amount of Level A harassment 
is low and would be in the form of a slight degree of PTS;
     For both projects, Level B harassment would be in the form 
of behavioral disturbance, primarily resulting in avoidance of the 
project areas around where impact or vibratory pile driving is 
occurring, and some low-level TTS that may limit the detection of 
acoustic cues for relatively brief amounts of time in relatively 
confined footprint of the activities;
     Nearby areas of similar habitat value within Puget Sound 
are available for marine mammals that may temporarily vacate the 
project areas during construction activities for both projects;
     Effects on species that serve as prey for marine mammals 
from the activities are expected to be short-term and, therefore, any 
associated impacts on marine mammal feeding are not expected to result 
in significant or long-term consequences for individuals, or to accrue 
to adverse impacts on their populations from either project;
     The number of anticipated takes by Level B harassment is 
relatively low for all stocks for both projects;
     The ensonifed areas from both projects are very small 
relative to the overall habitat ranges of all species and stocks, and 
will not adversely affect ESA-designated critical habitat, or cause 
more than minor impacts in any BIAS or any other areas of known 
biological importance;
     The lack of anticipated significant or long-term negative 
effects to marine mammal habitat from either project;
     The efficacy of the mitigation measures in reducing the 
effects of the specified activities on all species and stocks for both 
projects;
     The enhanced mitigation measures (e.g., shutdown zones 
equivalent to the Level B harassment zones) to eliminate (for the Pier 
63 Removal Project) and reduce (for the Pier 58 Reconstruction Project) 
the potential for any take of SRKW; and
     Monitoring reports from similar work in Puget Sound that 
have documented little to no effect on individuals of the same species 
that could be impacted by the specified activities from both projects.
    Based on the analysis contained herein of the likely effects of the 
specified activities on marine mammals and their habitat, and taking 
into consideration the implementation of the proposed monitoring and 
mitigation measures, NMFS preliminarily finds that the total marine 
mammal take from the Pier 58 Reconstruction Project will have a 
negligible impact on all affected marine mammal species or stocks. NMFS 
also preliminarily finds that the total marine mammal take from the 
Pier 63 Removal project will have a negligible impact on all affected 
marine mammal species or stocks.

Small Numbers

    As noted above, only small numbers of incidental take may be 
authorized under sections 101(a)(5)(A) and (D) of the MMPA for 
specified activities other than military readiness activities. The MMPA 
does not define small numbers and so, in practice, where estimated 
numbers are available, NMFS compares the number of individuals taken to 
the most appropriate estimation of abundance of the relevant species or 
stock in our determination of whether an authorization is limited to 
small numbers of marine mammals. When the predicted number of 
individuals to be taken is fewer than one third of the species or stock 
abundance, the take is considered to be of small numbers. Additionally, 
other qualitative factors may be considered in the analysis, such as 
the temporal or spatial scale of the activities.
    The estimated take proposed to be authorized for each project is 
below one third of the population for all marine mammal stocks (Table 
10 and 11).
    Based on the analysis contained herein of the proposed activities 
(including the proposed mitigation and

[[Page 12114]]

monitoring measures) and the anticipated take of marine mammals, NMFS 
preliminarily finds that small numbers of marine mammals would be taken 
relative to the population size of the affected species or stocks for 
the Pier 58 Reconstruction Project. NMFS also preliminarily finds that 
small numbers of marine mammals would be taken relative to the 
population size of the affected species or stocks for the Pier 63 
Removal Project.

Unmitigable Adverse Impact Analysis and Determination

    There are no relevant subsistence uses of the affected marine 
mammal stocks or species implicated by either of these projects. 
Therefore, NMFS has determined that the total taking of affected 
species or stocks would not have an unmitigable adverse impact on the 
availability of such species or stocks for taking for subsistence 
purposes.

Endangered Species Act

    Section 7(a)(2) of the Endangered Species Act of 1973 (ESA: 16 
U.S.C. 1531 et seq.) requires that each Federal agency insure that any 
action it authorizes, funds, or carries out is not likely to jeopardize 
the continued existence of any endangered or threatened species or 
result in the destruction or adverse modification of designated 
critical habitat. To ensure ESA compliance for the issuance of IHAs, 
NMFS consults internally whenever we propose to authorize take for 
endangered or threatened species, in this case with the West Coast 
Region Resources Division Office.
    NMFS is proposing to authorize take of Southern Resident killer 
whales and Central America and Mexico DPSs of humpback whales, which 
are listed under the ESA.
    The Permit and Conservation Division has requested initiation of 
Section 7 consultation with the West Coast Region for the issuance of 
these IHAs. NMFS will conclude the ESA consultation prior to reaching a 
determination regarding the proposed issuance of the authorizations.

Proposed Authorization

    As a result of these preliminary determinations, NMFS proposes to 
issue two IHAs to the City, one each for their Pier 58 Reconstruction 
Project and their Pier 63 Removal Project on the Seattle Waterfront in 
Seattle, Washington, effective as of August 2022, provided the 
previously discussed mitigation, monitoring, and reporting requirements 
are incorporated. The proposed IHAs can be found at https://www.fisheries.noaa.gov/permit/incidental-take-authorizations-under-
marine-mammal-protection-act.

Request for Public Comments

    We request comment on our analyses, the proposed authorizations, 
and any other aspect of this notice of proposed IHAs for the proposed 
Pier 58 Reconstruction and Pier 63 Removal Projects. We also request at 
this time comment on the potential Renewal of these proposed IHAs as 
described in the paragraph below. Please include with your comments any 
supporting data or literature citations to help inform decisions on the 
request for these IHAs or subsequent Renewal IHAs.
    On a case-by-case basis, NMFS may issue a one-time, one-year 
Renewal IHA following notice to the public providing an additional 15 
days for public comments when (1) up to another year of identical or 
nearly identical activities as described in the Description of Proposed 
Activities section of this notice is planned or (2) the activities as 
described in the Description of Proposed Activities section of this 
notice would not be completed by the time the IHA expires and a Renewal 
would allow for completion of the activities beyond that described in 
the Dates and Duration section of this notice, provided all of the 
following conditions are met:
    (1) A request for renewal is received no later than 60 days prior 
to the needed Renewal IHA effective date (recognizing that the Renewal 
IHA expiration date cannot extend beyond one year from expiration of 
the initial IHA);
    (2) The request for renewal must include the following:
     An explanation that the activities to be conducted under 
the requested Renewal IHA are identical to the activities analyzed 
under the initial IHA, are a subset of the activities, or include 
changes so minor (e.g., reduction in pile size) that the changes do not 
affect the previous analyses, mitigation and monitoring requirements, 
or take estimates (with the exception of reducing the type or amount of 
take); and
     A preliminary monitoring report showing the results of the 
required monitoring to date and an explanation showing that the 
monitoring results do not indicate impacts of a scale or nature not 
previously analyzed or authorized.
    (3) Upon review of the request for Renewal, the status of the 
affected species or stocks, and any other pertinent information, NMFS 
determines that there are no more than minor changes in the activities, 
the mitigation and monitoring measures will remain the same and 
appropriate, and the findings in the initial IHA remain valid.

    Dated: February 28, 2022.
Kimberly Damon-Randall,
Director, Office of Protected Resources, National Marine Fisheries 
Service.
[FR Doc. 2022-04499 Filed 3-2-22; 8:45 am]
BILLING CODE 3510-22-P