[Federal Register Volume 84, Number 113 (Wednesday, June 12, 2019)]
[Notices]
[Pages 27270-27286]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-12318]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XG874
Taking of Marine Mammals Incidental to Specific Activities;
Taking of Marine Mammals Incidental to Pile Driving and Removal
Activities During Construction of a Cruise Ship Berth, Hoonah, Alaska
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; Issuance of an Incidental Harassment Authorization.
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SUMMARY: In accordance with the regulations implementing the Marine
Mammal Protection Act (MMPA) as amended, notification is hereby given
that NMFS has issued an incidental harassment authorization (IHA) to
Duck Point Development II, LLC. (DPD) to incidentally harass, by Level
A and B harassment, marine mammals during construction of a second
cruise ship berth and new lightering float at Cannery Point (Icy
Strait) on Chichagof Island near Hoonah, Alaska.
DATES: This Authorization is effective from June 3, 2019 through June
2, 2020.
FOR FURTHER INFORMATION CONTACT: Stephanie Egger, 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 issued or, if the taking is limited to harassment, a notice of a
proposed incidental take authorization may be 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 such 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 such takings are set forth.
Summary of Request
On December 28, 2018, NMFS received a request DPD for an IHA to
take marine mammals incidental to pile driving and removal activities
during construction of a second cruise ship berth and new lightering
float at Cannery Point (Icy Strait) on Chichagof Island near Hoonah,
Alaska. The application was deemed adequate and complete on April 3,
2019. DPD requested take of nine species of marine mammals by Level B
harassment and three species by Level A harassment. Neither DPD nor
NMFS expects serious injury or mortality to result from this activity
and, therefore, an IHA is appropriate. NMFS previously issued an IHA to
the Huna Totem Corporation for the first cruise ship berth in Hoonah,
AK in 2015 (80 FR 31352; June 2, 2015).
Description of Specified Activity
DPD proposed to construct a second cruise ship berth and new
lightering float at Cannery Point (Icy Strait) on Chichagof Island near
Hoonah, Alaska, in order to accommodate the increase in cruise ship and
visitor traffic since completion of the first permanent cruise ship
berth completion in 2016 (80 FR 31352; June 2, 2015). The in-water
sound from the pile driving and removal activities, may incidentally
take marine mammals by Level A and B harassment. A detailed description
of the planned Hoonah Berth II project is provided in the Federal
Register notice for the proposed IHA (84 FR 18495; May 1, 2019).
Pile driving and removal is expected to occur over 75 working days
(not necessarily consecutive) beginning June 3, 2019 and extending into
November 2019 as needed. Approximately 39 days of vibratory and 8 days
of impact hammering will occur. An additional 14 days of socketing and
14 days of anchoring will occur to stabilize the piles. As a
contingency, the IHA is effective for a period of one year, from June
3, 2019 through June 2, 2020.
To construct a new cruise ship berth (Berth II), lightering float,
associated support structures, and pedestrian walkway connections to
shore, the project would require the following (see also Table 1):
[ssquf] Installation of 62 temporary 30-inch (in) diameter steel
piles as templates to guide proper installation of permanent piles
(these piles would be removed prior to project completion);
[ssquf] Installation of 8 permanent 42-in diameter steel piles, 16
permanent 36-in diameter steel piles, and 18 permanent 24-in diameter
steel piles to support a new 500 feet (ft) x 50 ft floating pontoon
dock, its attached 400 ft x 12 ft small craft float, mooring
structures, and shore-access fixed-pier walkway (Figure 6 of the
application)
[ssquf] Installation of three permanent 30-in diameter steel piles
to support a 120 ft x 20 ft lightering float, and four permanent 16-in
diameter steel piles above the high tide line to construct a 12 ft x 40
ft fixed pier for lightering float shore access (Figure 7 of the
application);
[ssquf] Installation of bull rail, floating fenders, mooring
cleats, and mast lights. (Note: these components would be installed out
of the water.)
[[Page 27271]]
[ssquf] Socketing and rock anchoring to stabilize the piles.
Table 1--Pile Driving and Removal Activities Required for the Hoonah Berth II and Lightering Float
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Project component
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Description Temporary pile Temporary pile Permanent pile Permanent pile Permanent pile Permanent pile
installation removal installation installation installation installation
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Diameter of Steel Pile (inches)......................... 30 30 24 30 36 42
Number of Piles......................................... 62 62 18 3 16 8
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Vibratory Pile Driving
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Total Quantity.......................................... 62 62 18 3 16 8
Max Number Piles Vibrated per Day....................... 6 6 4 2 2 2
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Impact Pile Driving
-----------------------------------------------------------------------------------------------
Total Quantity.......................................... 0 0 0 0 16 8
Max Number Piles Impacted per Day....................... 0 0 0 0 4 2
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Socketed Pile Installation (Down-Hole Drilling)
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Total Quantity.......................................... 10 0 18 0 0 0
Max Number Piles Socketed per Day....................... 2 0 2 0 0 0
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Rock Anchor Installation (Drilled Shaft)
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Total Quantity.......................................... 0 0 2 0 16 8
Diameter of Anchor...................................... .............. .............. 8 0 33 33
Max Number Piles Anchored per Day....................... 0 0 1 0 2 2
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In addition to the activities described above, the planned action
will involve other in-water construction and heavy machinery
activities. Other types of in-water work including with heavy machinery
will occur using standard barges, tug boats, barge-mounted excavators,
or clamshell equipment to place or remove material; and positioning
piles on the substrate via a crane (i.e., ``stabbing the pile'').
Workers will be transported from shore to the barge work platform by a
25-ft skiff with a 125-250 horsepower motor in the morning and at the
end of the work day. The travel distance will be less than 300 ft.
There could be multiple (up to eight) shore-to-barge trips during the
day; however, the area of travel will be relatively small and close to
shore. We do not expect any of these other in-water construction and
heavy machinery activities to take marine mammals as these activities
occur close to the shoreline (less than 300 ft), but as additional
mitigation, DPD is proposing a 10 m shutdown zone for these additional
in-water activities. Therefore, these other in-water construction and
heavy machinery activities will not be discussed further.
Further details of the planned DPD project is provided in the
Federal Register notice for the proposed IHA (84 FR 18495; May 1,
2019).
Comments and Responses
A notice of NMFS's proposal to issue an IHA to DPD was published in
the Federal Register on May 1, 2019 (84 FR 18495). That notice
described, in detail, DPD's activity, the marine mammal species that
may be affected by the activity, and the anticipated effects on marine
mammals. During the 30-day public comment period, NMFS received
comments from the Marine Mammal Commission (Commission). The Commission
recommended that NMFS issue the IHA, subject to inclusion of the
proposed mitigation, monitoring, and reporting measures.
Comment: The Commission questioned whether the public notice
provisions for IHA Renewals fully satisfy the public notice and comment
provision in the MMPA and discussed the potential burden on reviewers
of reviewing key documents and developing comments quickly.
Additionally, the Commission recommended that NMFS use the IHA Renewal
process sparingly and selectively for activities expected to have the
lowest levels of impacts to marine mammals and that require less
complex analysis.
Response: NMFS has taken a number of steps to ensure the public has
adequate notice, time, and information to be able to comment
effectively on IHA Renewals within the limitations of processing IHA
applications efficiently. The Federal Register notice for the initial
proposed IHA (84 FR 18495; May 1, 2019) previously identified the
conditions under which a one-year Renewal IHA might be appropriate.
This information is presented in the Request for Public Comments
section of the initial proposed IHA and thus encourages submission of
comments on the potential of a one-year renewal as well as the initial
IHA during the 30-day comment period. In addition, when we receive an
application for a Renewal IHA, we publish a notice of the proposed IHA
Renewal in the Federal Register and provide an additional 15 days for
public comment, for a total of 45 days of public comment. We will also
directly contact all commenters on the initial IHA by email, phone, or,
if the commenter did not provide email or phone information, by postal
service to provide them the opportunity to submit any additional
comments on the proposed Renewal IHA.
NMFS also strives to ensure the public has access to key
information needed to submit comments on a proposed IHA, whether an
initial IHA or a Renewal IHA. The agency's website includes information
for all projects under consideration, including the application,
references, and other supporting documents. Each Federal Register
notice also includes contact
[[Page 27272]]
information in the event a commenter has questions or cannot find the
information they seek.
Regarding the Commission's comment that Renewal IHAs should be
limited to certain types of projects, NMFS has explained on its website
and in individual Federal Register notices that Renewal IHAs are
appropriate where the continuing activities are identical, nearly
identical, or a subset of the activities for which the initial 30-day
comment period applied. Where the commenter has likely already reviewed
and commented on the initial proposed IHA for these activities, the
abbreviated additional comment period is sufficient for consideration
of the results of the preliminary monitoring report and new information
(if any) from the past year.
Change From the Proposed IHA to Final IHA
As described in the Federal Register notice for the proposed IHA
(84 FR 18495; May 1, 2019), a small amount of take by Level A
harassment take was proposed for Steller sea lions (Eumetopias
jubatus). However, after further consideration and additional
conversations with species experts in Alaska, NMFS has determined that
take by Level A harassment is unlikely and will not be authorized.
Originally, NMFS anticipated that Steller sea lions may appear within
the Level A harassment isopleth without being seen in time to shut down
pile driving activities, resulting in Level A harassment. They are
smaller in size and difficult to detect in bad weather, can approach
closely driven by curiosity, and are becoming habituated to feeding on
fish waste and known to follow charter boats into the docks around
southeast Alaska. In some cases, they are undeterred by noise, other
vessels, and other forms of deterrence. The location of the new cruise
ship dock construction site is not located near the fishing vessel
docks, and faces the open waters of Icy Strait instead of the internal
waters of Port Frederick (where habituation is more likely to occur).
Because of this spatial separation, NMFS expects that Steller sea lions
will not have the same motivation to come into the Level A harassment
isopleth, and does not predict take by Level A harassment of Steller
sea lions as a result of this project. Therefore, the Estimated Take
section has been revised to reflect this change.
Description of Marine Mammals in the Area of Specified Activities
Sections 3 and 4 of the application summarize available information
regarding status and trends, distribution and habitat preferences, and
behavior and life history, of the potentially affected species.
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 2 lists all species with expected potential for occurrence in
the project area 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 (2016). 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 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 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 managed stocks in this region are assessed in
NMFS' U.S. Pacific and Alaska SARs (Carretta et al., 2018; Muto et al.,
2018). All values presented in Table 2 are the most recent available at
the time of publication (draft SARS available online at: https://www.fisheries.noaa.gov/national/marine-mammal-protection/draft-marine-mammal-stock-assessment-reports).
Table 2--Marine Mammals Occurrence in the Project 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, 801 138
2016).
Family Balaenopteridae (rorquals):
Minke Whale..................... Balaenoptera Alaska................. -, -, N N/A (see SAR, N/A, see UND 0
acutorostrata. SAR).
Humpback Whale.................. Megaptera novaeangliae. Central N Pacific -, -, Y 10,103 (0.3, 7,890, 83 25
(Hawaii and Mexico 2006) (Hawaii DPS
DPS). 9,487 \a\, Mexico DPS
606 \a\).
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Superfamily Odontoceti (toothed whales, dolphins, and porpoises)
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Family Physeteridae:
Sperm whale..................... Physeter macrocephalus. North Pacific.......... E, D, Y N/A (see SAR, N/A, See SAR 4.4
2015).
Family Delphinidae:
Killer Whale.................... Orcinus orca........... Alaska Resident........ -, -, N 2,347 c (N/A, 2347, 24 1
2012).
Northern Resident...... -, -, N 261 c (N/A, 261, 2011) 1.96 0
West Coast Transient... -, -, N 243 c (N/A, 243, 2009) 2.4 0
Pacific White-Sided Dolphin..... Lagenorhynchus N Pacific.............. -, -, N 26,880 (N/A, N/A, UND 0
obliquidens. 1990).
Family Phocoenidae (porpoises):
[[Page 27273]]
Dall's Porpoise................. Phocoenoides dalli..... AK..................... -, -, N 83,400 (0.097, N/A, UND 38
1991).
Harbor Porpoise................. Phocoena phocoena...... Southeast Alaska....... -, -, Y see SAR (see SAR, see 8.9 34
SAR, 2012).
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Order Carnivora--Superfamily Pinnipedia
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Family Otariidae (eared seals and
sea lions):
Steller Sea Lion................ Eumetopias jubatus..... Western DPS............ E, D, Y 54,267 a (see SAR, 326 252
54,267, 2017).
Eastern DPS............ T, D, Y 41,638 a (see SAR, 2498 108
41,638, 2015).
Family Phocidae (earless seals):
Harbor Seal..................... Phoca vitulina......... Glacier Bay/Icy Strait. -, -, N 7,210 (see SAR, 5,647, 169 104
2011).
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1--Endangered Species Act (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: www.nmfs.noaa.gov/pr/sars/. CV is coefficient of variation; Nmin is the minimum estimate of
stock abundance. In some cases, CV is not applicable [explain if this is the case].
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 M/SI often cannot be determined precisely and is in some cases presented as a minimum value or range. A CV associated
with estimated mortality due to commercial fisheries is presented in some cases.
Note:--Italicized species are not expected to be taken or planned for authorization.
\a\ Under the MMPA humpback whales are considered a single stock (Central North Pacific); however, we have divided them here to account for distinct
population segments (DPSs) listed under the ESA. Using the stock assessment from Muto et al. 2018 for the Central North Pacific stock (10,103) and
calculations in Wade et al. 2016, 93.9% of the humpback whales in Southeast Alaska are expected to be from the Hawaii DPS and 6.1% are expected to be
from the Mexico DPS.
A detailed description of the of the species likely to be affected
by the DPD project, including brief introductions to the species and
relevant stocks as well as available information regarding population
trends and threats, and information regarding local occurrence, were
provided in the Federal Register notice for the proposed IHA (84 FR
18495; May 1, 2019) since that time, we are not aware of any changes in
the status of these species and stocks; therefore, detailed
descriptions are not provided here. Please refer to that Federal
Register notice for these descriptions. Please also refer to NMFS'
website (https://www.fisheries.noaa.gov/find-species) for generalized
species accounts.
Potential Effects of Specified Activities on Marine Mammals and Their
Habitat
Acoustic effects on marine mammals during the specified activity
can occur from vibratory and impact pile driving as well as during
socketing and anchoring of the piles. The effects of underwater noise
from DPD's planned activities have the potential to result in Level A
and B harassment of marine mammals in the vicinity of the action area.
The effects of pile driving on marine mammals are dependent on several
factors, including the size, type, and depth of the animal; the depth,
intensity, and duration of the pile driving sound; the depth of the
water column; the substrate of the habitat; the standoff distance
between the pile and the animal; and the sound propagation properties
of the environment. With both types, it is likely that the pile driving
could result in temporary, short term changes in an animal's typical
behavioral patterns and/or avoidance of the affected area. The Federal
Register notice for the proposed IHA (84 FR 18495; May 1, 2019)
included a discussion of the effects of anthropogenic noise on marine
mammals, therefore that information is not repeated here; please refer
to the Federal Register notice (84 FR 18495; May 1, 2019).
Anticipated Effects on Marine Mammal Habitat
The main impact issue associated with the planned activity would be
temporarily elevated sound levels and the associated direct effects on
marine mammals. The most likely impact to marine mammal habitat occurs
from pile driving effects on likely marine mammal prey (i.e., fish)
near where the piles are installed. Impacts to the immediate substrate
during installation and removal of piles are anticipated, but these
would be limited to minor, temporary suspension of sediments, which
could impact water quality and visibility for a short amount of time,
but which would not be expected to have any effects on individual
marine mammals. Impacts to substrate are therefore not discussed
further. These potential effects are discussed in detail in the Federal
Register notice for the proposed IHA (84 FR 18495; May 1, 2019),
therefore that information is not repeated here; please refer to that
Federal Register notice for that information.
Estimated Take
This section provides an estimate of the number of incidental takes
authorized through this IHA, which informed both NMFS' consideration of
``small numbers'' and the negligible impact determination.
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).
Take of marine mammals incidental to DPD's pile driving and removal
activities (as well as during socketing and anchoring) could occur as a
result of Level A and Level B harassment. Below we describe how the
potential take is estimated. As described previously, no mortality is
anticipated or authorized for this activity. Below we describe how the
take is estimated.
Generally speaking, we estimate take by considering: (1) Acoustic
thresholds
[[Page 27274]]
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) and 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 planned take estimate.
Acoustic Thresholds
Using the best available science, NMFS has developed 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--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 [mu]Pa (rms)
for continuous (e.g., vibratory pile driving) and above 160 dB re 1
[mu]Pa (rms) for impulsive sources (e.g., impact pile driving). DPD's
planned activity includes the use of continuous (vibratory pile
driving) and impulsive (impact pile driving) sources, and therefore the
120 and 160 dB re 1 [mu]Pa (rms) are applicable.
Level A harassment--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. The
technical guidance identifies the received levels, or thresholds, above
which individual marine mammals are predicted to experience changes in
their hearing sensitivity for all underwater anthropogenic sound
sources, and reflects the best available science on the potential for
noise to affect auditory sensitivity by:
[ssquf] Dividing sound sources into two groups (i.e., impulsive and
non-impulsive) based on their potential to affect hearing sensitivity;
[ssquf] Choosing metrics that best address the impacts of noise on
hearing sensitivity, i.e., sound pressure level (peak SPL) and sound
exposure level (SEL) (also accounts for duration of exposure); and
[ssquf] Dividing marine mammals into hearing groups and developing
auditory weighting functions based on the science supporting that not
all marine mammals hear and use sound in the same manner.
These thresholds were developed by compiling and synthesizing the
best available science, and are provided in Table 3 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.
DPD's pile driving and removal activity includes the use of
impulsive (impact pile driving) and non-impulsive (vibratory pile
driving and removal) sources.
Table 3--Thresholds Identifying the Onset of Permanent Threshold Shift
[Auditory injury]
----------------------------------------------------------------------------------------------------------------
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.
Ensonified Area
Here, we describe operational and environmental parameters of the
activity that will feed into identifying the area ensonified above the
acoustic thresholds, which include source levels and transmission loss
coefficient.
Sound Propagation
Transmission loss (TL) is the decrease in acoustic intensity as an
acoustic pressure wave propagates out from a
[[Page 27275]]
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:
B = transmission loss coefficient (assumed to be 15)
R1 = the distance of the modeled SPL from the driven
pile, and
R2 = the distance from the driven pile of the initial
measurement.
This formula neglects loss due to scattering and absorption, which
is assumed to be zero here. The degree to which underwater sound
propagates away from a sound source is dependent on a variety of
factors, most notably the water bathymetry and presence or absence of
reflective or absorptive conditions including in-water structures and
sediments. Spherical spreading occurs in a perfectly unobstructed
(free-field) environment not limited by depth or water surface,
resulting in a 6 dB reduction in sound level for each doubling of
distance from the source (20*log(range)). Cylindrical spreading occurs
in an environment in which sound propagation is bounded by the water
surface and sea bottom, resulting in a reduction of 3 dB in sound level
for each doubling of distance from the source (10*log(range)). As is
common practice in coastal waters, here we assume practical spreading
loss (4.5 dB reduction in sound level for each doubling of distance).
Practical spreading is a compromise that is often used under conditions
where water depth increases as the receiver moves away from the
shoreline, resulting in an expected propagation environment that would
lie between spherical and cylindrical spreading loss conditions.
Sound Source Levels
The intensity of pile driving sounds is greatly influenced by
factors such as the type of piles, hammers, and the physical
environment in which the activity takes place. There are source level
measurements available for certain pile types and sizes from the
similar environments recorded from underwater pile driving projects in
Alaska (e.g., JASCO Reports--Denes et al., 2017 and Austin et al.,
2016).) that were evaluated and used as proxy sound source levels to
determine reasonable sound source levels likely result from DPD's pile
driving and removal activities (Table 4). Many source levels used were
more conservation as the values were from larger pile sizes.
Table 4--Assumed Sound Source Levels
------------------------------------------------------------------------
Sound source level
Activity at 10 meters Sound Source
------------------------------------------------------------------------
Vibratory Pile Driving/Removal
------------------------------------------------------------------------
24-in steel pile permanent...... 161.9 SPL......... The 24-in-diameter
30-in steel pile temporary 161.9 SPL......... source level for
installation. 161.9 SPL......... vibratory driving
30-in steel pile removal........ 161.9 SPL......... are proxy from
30-in steel pile permanent median measured
installation. source levels
from pile driving
of 30-in-diameter
piles to
construct the
Ketchikan Ferry
Terminal (Denes
et al. 2016,
Table 72).
36-in steel pile permanent...... 168.2 SPL......... The 36-in And 42-
42-in steel pile permanent...... 168.2 SPL......... in pile source
level is a proxy
from median
measured source
level from
vibratory
hammering of 48-
in piles for the
Port of Anchorage
test pile project
(Austin et al.,
2016).
------------------------------------------------------------------------
Impact Pile Driving
------------------------------------------------------------------------
36-in steel pile permanent...... 186.7 SEL/198.6 The 36-inch and 42-
42-in steel pile permanent...... SPL. inch diameter
186.7 SEL/198.6 pile source level
SPL.. is a proxy from
median measured
source level from
impact hammering
of 48-in piles
for the Port of
Anchorage test
pile project
(Austin et al.,
2016).
------------------------------------------------------------------------
Socketed Pile Installation
------------------------------------------------------------------------
24-in steel pile permanent...... 166.2 SPL......... The socketing and
30-in steel pile temporary...... 166.2 SPL......... rock anchor
source level is a
proxy from median
measured source
level from down-
hole drilling of
24-in-diameter
piles to
construct the
Kodiak Ferry
Terminal (Denes
et al., 2016,
Table 72).
------------------------------------------------------------------------
Rock Anchor Installation
------------------------------------------------------------------------
8-in anchor permanent (for 24- 166.2 SPL......... The socketing and
inch piles). 166.2 SPL......... rock anchor
33-in anchor permanent (for 36- 166.2 SPL......... source level is a
inch piles). proxy from median
33-in anchor permanent (for 42- measured source
inch piles). level from down-
hole drilling of
24-in-diameter
piles to
construct the
Kodiak Ferry
Terminal (Denes
et al., 2016,
Table 72).
------------------------------------------------------------------------
Notes: Denes et al., 2016--Alaska Department of Transportation's
Hydroacoustic Pile Driving Noise Study--Comprehensive Report and
Austin et al., 2016--Hydroacoustic Monitoring Report: Anchorage Port
Modernization Project Test Pile Program. Version 3.0. Technical report
by JASCO Applied Sciences for Kiewit Infrastructure West Co.
Level A Harassment
When the NMFS Technical Guidance (2016) was published, in
recognition of the fact that ensonified area/volume could be more
technically challenging to predict because of the duration component in
the new thresholds, we developed 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 take by 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
[[Page 27276]]
quantitatively refine these tools, and will qualitatively address the
output where appropriate. For stationary sources (such as from impact
and vibratory pile driving), NMFS User Spreadsheet predicts the closest
distance at which, if a marine mammal remained at that distance the
whole duration of the activity, it would incur PTS. Inputs used in the
User Spreadsheet (Tables 5 and 6), and the resulting isopleths are
reported below (Table 7).
Table 5--NMFS Technical Guidance (2018) User Spreadsheet Input to Calculate PTS Isopleths for Vibratory Pile Driving
[User spreadsheet input--vibratory pile driving/anchoring and socketing spreadsheet tab A.1 vibratory pile driving used]
--------------------------------------------------------------------------------------------------------------------------------------------------------
30-in piles 30-in piles 24-in and
24-in piles (temporary (temporary 30-in piles 36-in piles 42-in piles 8-in 33-in 30-in
(permanent) install) removal) (permanent) (permanent) (permanent) anchoring anchoring socketing
--------------------------------------------------------------------------------------------------------------------------------------------------------
Source Level (RMS SPL)............. 161.9 161.9 161.9 161.9 168.2 168.2 166.2 166.2 166.2
Weighting Factor Adjustment (kHz).. 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5
Number of piles within 24-hr period 4 6 6 2 2 2 1 2 2
Duration to drive a single pile 10 20 10 30 30 60 60 240 60
(min).............................
Propagation (xLogR)................ 15 15 15 15 15 15 15 15 15
Distance of source level 10 10 10 10 10 10 10 10 10
measurement (meters) +............
--------------------------------------------------------------------------------------------------------------------------------------------------------
Table 6--NMFS Technical Guidance (2018) User Spreadsheet Input To
Calculate PTS Isopleths for Impact Pile Driving
[User spreadsheet input--impact pile driving spreadsheet Tab E.1 impact
pile driving used]
------------------------------------------------------------------------
36-in piles 42-in piles
(permanent) (permanent)
------------------------------------------------------------------------
Source Level (Single Strike/shot SEL)... 186.7 186.7
Weighting Factor Adjustment (kHz)....... 2 2
Number of strikes per pile.............. 100 135
Number of piles per day................. 4 2
Propagation (xLogR)..................... 15 15
Distance of source level measurement 10 10
(meters)+..............................
------------------------------------------------------------------------
Table 7--NMFS Technical Guidance (2018) User Spreadsheet Outputs To Calculate Level A Harassment PTS Isopleths
[User spreadsheet output]
--------------------------------------------------------------------------------------------------------------------------------------------------------
PTS isopleths (meters)
-------------------------------------------------------------------------------
Level A harassment
Activity Sound source level at 10 m -------------------------------------------------------------------------------
High-
Low- frequency Mid- frequency frequency Phocid Otariid
cetaceans cetaceans cetaceans
--------------------------------------------------------------------------------------------------------------------------------------------------------
Vibratory Pile Driving/Removal
--------------------------------------------------------------------------------------------------------------------------------------------------------
24-in steel installation.................. 161.9 SPL\1\................ 6.0 0.5 8.8 3.6 0.3
30-in steel temporary installation........ 161.9 SPL\1\................ 12.4 1.1 18.4 7.6 0.5
30-in steel removal....................... 161.9 SPL\1\................ 7.8 0.7 11.6 4.8 0.3
30-in steel permanent installation........ 161.9 SPL\1\................ 7.8 0.7 11.6 4.8 0.3
36-in steel permanent installation........ 168.2 SPL\2\................ 20.6 1.8 30.5 12.5 0.9
42-in steel permanent installation........ 168.2 SPL\2\................ 32.7 2.9 48.4 19.9 1.4
--------------------------------------------------------------------------------------------------------------------------------------------------------
Impact Pile Driving
--------------------------------------------------------------------------------------------------------------------------------------------------------
36-in steel permanent installation........ 186.7 SEL/198.6 SPL\2\...... 956.7 34.0 1,139.6 512.0 37.3
42-in steel permanent installation........ 186.7 SEL/198.6 SPL\2\...... 736.2 26.2 876.9 394.0 28.7
--------------------------------------------------------------------------------------------------------------------------------------------------------
Socketed Pile Installation
--------------------------------------------------------------------------------------------------------------------------------------------------------
24-in steel permanent installation........ 166.2 SPL\3\................ 24.1 2.1 35.6 14.6 1.0
30-in steel temporary installation........ 166.2 SPL\3\................ 24.1 2.1 35.6 14.6 1.0
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 27277]]
Rock Anchor Installation
--------------------------------------------------------------------------------------------------------------------------------------------------------
8-in anchor permanent installation (for 24- 166.2 SPL\3\................ 15.2 1.3 22.4 9.2 0.6
in piles).
33-in anchor permanent installation (for 166.2 SPL\3\................ 60.7 5.4 89.7 36.9 2.6
36-in piles).
33-in anchor permanent installation (for 166.2 SPL\3\................ 60.7 5.4 89.7 36.9 2.6
42-in piles).
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ The 24-in and 30-in-diameter source levels for vibratory driving are proxy from median measured source levels from pile driving of 30-in-diameter
piles to construct the Ketchikan Ferry Terminal (Denes et al. 2016, Table 72).
\2\ The 36-in and 42-in-diameter pile source levels are proxy from median measured source levels from pile driving (vibratory and impact hammering) of
48-in piles for the Port of Anchorage test pile project (Austin et al. 2016, Tables 9 and 16). We calculated the distances to impact pile driving
Level A harassment thresholds for 36-in piles assuming 100 strikes per pile and a maximum of 4 piles installed in 24 hours; for 42-in piles we assumed
135 strikes per pile and a maximum of 2 piles installed in 24 hours.
\3\ The socketing and rock anchoring source level is proxy from median measured sources levels from down-hole drilling of 24-in-diameter piles to
construct the Kodiak Ferry Terminal (Denes et al. 2016, Table 72).
Level B Harassment
Utilizing the practical spreading loss model, DPD determined
underwater noise will fall below the behavioral effects threshold of
120 dB rms for marine mammals at the distances shown in Table 8 for
vibratory pile driving/removal, socketing, and rock anchoring. With
these radial distances, and due to the occurrence of landforms (See
Figure 8, 12, 13 of the application, the largest Level B Harassment
Zone calculated for vibratory pile driving for 36-in and 42-in steel
piles equaled 193 km\2\ and socket and rock anchoring equaled 116
km\2\. For calculating the Level B Harassment Zone for impact driving,
the practical spreading loss model was used with a behavioral threshold
of 160 dB rms. The maximum radial distance of the Level B Harassment
Zone for impact piling equaled 3,744 m. At this radial distance, the
entire Level B Harassment Zone for impact piling equaled 19 km\2\.
Table 8 below provides all Level B Harassment radial distances (m) and
their corresponding areas (km\2\) during DPD's planned activities.
Table 8--Radial Distances (Meters) to Relevant Behavioral Isopleths and Associated Ensonified Areas (Square
Kilometers (km\2\)) Using the Practice Spreading Model
----------------------------------------------------------------------------------------------------------------
Level B
Activity Received level at 10 Level B Harassment Zone Harassment
meters (m) * Zone (km\2\)
----------------------------------------------------------------------------------------------------------------
Vibratory Pile Driving/Removal
----------------------------------------------------------------------------------------------------------------
24-in steel installation................ 161.9 SPL................. 6,215 (calculated 6,213).. 39
30-in steel temporary installation...... 161.9 SPL................. 6,215 (calculated 6,213).. ..............
30-in steel removal..................... 161.9 SPL................. 6,215 (calculated 6,213).. ..............
30-in steel permanent installation...... 161.9 SPL................. 6,215 (calculated 6,213).. ..............
36-in steel permanent installation...... 168.2 SPL................. 16,345 (calculated 16,343) 193
42-in steel permanent installation...... 168.2 SPL................. 16,345 (calculated 16,343) ..............
----------------------------------------------------------------------------------------------------------------
Impact Pile Driving
----------------------------------------------------------------------------------------------------------------
36-in steel permanent installation...... 186.7 SEL/198.6 SPL....... 3,745 (calculated 3,744).. 19
42-in steel permanent installation...... 186.7 SEL/198.6 SPL....... 3,745 (calculated 3,744).. ..............
----------------------------------------------------------------------------------------------------------------
Socketed Pile Installation
----------------------------------------------------------------------------------------------------------------
24-in steel permanent installation...... 166.2 SPL................. 12,025 (calculated 12,023) 116
30-in steel temporary installation...... 166.2 SPL................. 12,025 (calculated 12,023) ..............
----------------------------------------------------------------------------------------------------------------
Rock Anchor Installation
----------------------------------------------------------------------------------------------------------------
8-in anchor permanent installation (for 166.2 SPL................. 12,025 (calculated 12,023) 116
24-in piles.
33-in anchor permanent installation (for 166.2 SPL................. 12,025 (calculated 12,023) ..............
36-in piles).
[[Page 27278]]
33-in anchor permanent installation (for 166.2 SPL................. 12,025 (calculated 12,023) ..............
42-in piles).
----------------------------------------------------------------------------------------------------------------
* Numbers rounded up to nearest 5 meters.
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 take
calculations. Potential exposures to impact pile driving, vibratory
pile driving/removal and socketing/rock anchoring noises for each
acoustic threshold were estimated using group size estimates and local
observational data. As previously stated, take by Level B harassment as
well as small numbers of take by Level A harassment will be will be
considered for this action. Take by Level B and Level A harassment are
calculated differently for some species based on monthly or daily
sightings data and average group sizes within the action area using the
best available data. Take by Level A harassment is planned for two
species where the Level A harassment isopleths are very large during
impact pile driving (harbor porpoise and harbor seal), and is based on
average group size multiplied by the number of days of impact pile
driving. Distances to Level A harassment thresholds for other project
activities (vibratory pile driving/removal, socketing, rock anchoring)
are considerably smaller compared to impact pile driving, and
mitigation is expected to avoid Level A harassment from these other
activities.
Minke Whales
There are no density estimates of minke whales available in the
project area. These whales are usually sighted individually or in small
groups of 2-3, but there are reports of loose aggregations of hundreds
of animals (NMFS 2018). There was one sighting of a minke whale during
the 135 days of monitoring during the Huna Berth I construction project
(June 2015 through January 2016) (BergerABAM 2016). To be conservative,
we predict that three minke whales in a group could be sighted 3 times
over the 6-month project period for a total of 9 minke whales
authorized to be taken by Level B harassment.
Humpback Whales
There are no density estimates of humpback whales available in the
project area. Humpback whale presence in the action area is likely
steady through the work period until November, when most humpbacks
migrate back to Hawaii or Mexico. NMFS has received a few reports of
humpback whales over-wintering in Southeast Alaska, but numbers of
animals and exact locations are very hard to predict, and NMFS assumes
the presence of much fewer humpbacks in the action area in November and
later winter months. During the previous Huna Berth I project, humpback
whales were observed on 84 of the 135 days of monitoring; most often in
September and October (BergerABAM 2016). The best available information
on the distribution of humpbacks in the project area was obtained from
several sources including: Icy Strait observations from 2015
(BergerABAM 2016), Glacier Bay/Icy Strait NPS Survey data 2014-2018
(provided by NPS, March 2019), Whale Alert opportunistic reported
sightings 2016-2018, and reported HB whale bubble-net feeding group to
NPS, 2015-2018 (provided by NPS, March 2019).
The National Park Service Glacier Bay/Icy Strait survey is designed
to observe humpback whales and has regular effort in June, July, and
August. This is the primary data source used to estimate exposures of
humpback whales in the action area during those months, except for when
a maximum group size reported in Whale Alert data was greater, then the
Whale Alert number was used (June and July maximum group size). The on-
site marine mammal monitoring data from BergerABAM (2016) was used to
estimate takes in September and October and Whale Alert data was the
only data source available in November and could represent a minimum
number of observations due to fewer opportunistic sightings recorded in
that month.
In addition, a single group of bubble-net feeding humpbacks of 10
animals was added to the total estimated exposures for June and
October, based on anecdotal data provided by NPS of bubble-net feeding
groups of humpbacks in the action area in those months of construction.
To estimate the number of exposures, NMFS looked at the proportion
of days of the month when the numbers of animals observed were within
one standard deviation of that month's average daily sightings. That
proportion was 0.7. The average number of sightings was estimated as
exposures on those days. For the remaining 30 percent of work days, the
maximum number of observations on any single day were estimated to be
exposed on those days.
For example, in June, the average number of daily observations
(1.31) was estimated to occur on 70 percent of the 17 work days, which
resulted in 15.59 exposures. On the other 30 percent of the 17 work
days, the maximum number of observations on any day (10) resulted in 51
estimated exposures. In addition, in June, NMFS estimates that one
bubble-net feeding group of 10 individuals could be exposed, due to
anecdotal evidence of this feeding activity occurring inside the
planned action area. NMFS estimates a total of 76.59 humpback whales
could be exposed in June. Humpback whales could be in larger groups
when large amounts of prey are available, but this is difficult to
predict with any precision. Although we are not proposing to authorize
takes by month, we are demonstrating how the total take was calculated.
The total number of exposures per month was calculated to be 76.59
(June), 68.02 (July), 71.93 (August), 132.07 (September), 78.82
(October), and 6.20 (November). The total number of whales authorized
to be taken by Level B harassment from June to November is 434 (433.63)
humpback whales with 26 (26.061) of those whales anticipated being from
the Mexico DPS (0.0601 percentage of the total animals).
Gray Whales
There are no density estimates of gray whales available in the
project area. Gray whales travel alone or in small, unstable groups,
although large aggregations may be seen in feeding and
[[Page 27279]]
breeding grounds (NMFS 2018e). Observations in Glacier Bay and nearby
waters recorded two gray whales documented over a 10-year period
(Keller et al., 2017). None were observed during Huna Berth I project
monitoring (BergerABAM 2016). We conservatively estimate a small group
to be 3 gray whales x 1 sighting over the 6-month work period for a
total of three gray whales authorized to be taken by Level B
harassment.
Killer Whales
There are no density estimates of killer whales available in the
project area. Killer whales occur commonly in the waters of the project
area, and could include members of several designated stocks that may
occur in the vicinity of the planned project area. Whales are known to
use the Icy Strait corridor to enter and exit inland waters and are
observed in every month of the year, with certain pods being observed
inside Port Frederick passing directly in front of Hoonah. Group size
of resident killer whale pods in the Icy Strait area ranges from 42 to
79 and occur in every month of the year (Dahlheim pers. comm. to NMFS
2015). As determined during a line-transect survey by Dalheim et al.
(2008), the greatest number of transient killer whale observed occurred
in 1993 with 32 animals seen over two months for an average of 16
sightings per month. NMFS estimates that group size of 79 resident
killer whales and 16 transient killer whales could occur each month
during the 6-month project period for a total of 570 takes authorized
by Level B harassment.
Pacific White-Sided Dolphin
There are no density estimates of Pacific white-sided dolphins
available in the project area. Pacific white-sided dolphins have been
observed in Alaska waters in groups ranging from 20 to 164 animals,
with the sighting of 164 animals occurring in Southeast Alaska near
Dixon Entrance (Muto et al., 2018). There were no Pacific white-sided
dolphins observed during the 135-day monitoring period during the Huna
Berth I project. However, to be conservative NMFS estimates 164 Pacific
white-sided dolphins may be seen once over the 6-month project period
for a total of 164 takes authorized by Level B harassment.
Dall's Porpoise
Little information is available on the abundance of Dall's porpoise
in the inland waters of Southeast Alaska. Dall's porpoise are most
abundant in spring, observed with lower numbers in the summer, and
lowest numbers in fall. Jefferson et al., 2019 presents the first
abundance estimates for Dall's porpoise in these waters and found the
abundance in summer (N = 2,680, CV = 19.6 percent), and lowest in fall
(N = 1,637, CV = 23.3 percent). Dall's porpoise are common in Icy
Strait and sporadic with very low densities in Port Frederick
(Jefferson et al., 2019). Dahlheim et al. (2008) observed 346 Dall's
porpoise in Southeast Alaska (inclusive of Icy Strait) during the
summer (June/July) of 2007 for an average of 173 animals per month as
part of a 17-year study period. During the previous Huna Berth I
project, only two Dall's porpoise were observed, and were transiting
within the waters of Port Frederick in the vicinity of Halibut Island.
Therefore, NMFS' estimates 173 Dall's porpoise per month may be seen
each month of the 6-month project period for a total of 1,038 takes
authorized by Level B harassment.
Harbor Porpoise
Dahlheim et al. (2015) observed 332 resident harbor porpoises
occurred in the Icy Strait area, and harbor porpoise are known to use
the Port Frederick area as part of their core range. During the Huna
Berth I project monitoring, a total of 32 harbor porpoise were observed
over 19 days during the 4-month project. The harbor porpoises were
observed in small groups with the largest group size reported was four
individuals and most group sizes consisting of three or fewer animals.
NMFS conservatively estimates that 332 harbor porpoises could occur in
the project area each month over the 6-month project period for a total
of 1,992 takes authorized by Level B harassment. Because the Level A
harassment zone is significantly larger than the shutdown zone during
impact pile driving, NMFS predicts that some take by Level A harassment
may occur. Based on the previous monitoring results, we estimate that a
group size of four harbor porpoises multiplied by 1 group per day over
8 days of impact pile driving would yield a total of 32 takes
authorized by Level A harassment.
Harbor Seal
There are no density estimates of harbor seals available in the
project area. Keller et al. (2017) observed an average of 26 harbor
seal sightings each month between June and August of 2014 in Glacier
Bay and Icy Strait. During the monitoring of the Huna Berth I project,
harbor seals typically occur in groups of one to four animals and a
total of 63 seals were observed during 19 days of the 135-day
monitoring period. NMFS conservatively estimate that 26 harbor seals
could occur in the project area each month during the 6-month project
period for a total of 156 takes by Level B harassment. Because the
Level A harassment zone is significantly larger than the shutdown zone
during impact pile driving, NMFS predicts that some take by Level A
harassment may occur. Based on the previous monitoring results, we
estimate that a group size of two harbor seals multiplied by 1 group
per day over 8 days of impact pile driving would yield a total of 16
takes authorized by Level A harassment.
Steller Sea Lion
There are no density estimates of Steller sea lions available in
the project area. NMFS expects that Steller sea lion presence in the
action area will vary due to prey resources and the spatial
distribution of breeding versus non-breeding season. In April and May,
Steller sea lions are likely feeding on herring spawn in the action
area. Then, most Steller sea lions likely move to the rookeries along
the outside coast (away from the action area) during breeding season,
and would be in the action area in greater numbers in August and later
months (J. Womble, NPS, pers. comm. to NMFS AK Regional Office, March
2019). However, Steller sea lions are also opportunistic predators and
their presence can be hard to predict.
Steller sea lions typically occur in groups of 1-10 animals, but
may congregate in larger groups near rookeries and haulouts. The
previous Huna Berth I project observed a total of 180 Steller sea lion
sightings over 135 days in 2015, amounting to an average of 1.3
sightings per day (BergerABAM 2016). During a test pile program
performed at the project location by the Hoonah Cruise Ship Dock
Company in May 2018, a total of 15 Steller sea lions were seen over the
course of 7 hours in one day (SolsticeAK 2018).
We used the same process to calculate Steller sea lion take as
explained above or humpback whales, except that 79 percent of the work
days in each month are expected to expose the average number of
animals, and 21 percent of the work days would expose the maximum
number of animals. For example, in June, the average number of daily
observations (1.6) was estimated to occur on 13.43 work days, which
would result in 21.48 exposures. On the other 21 percent of the 17 work
days, the maximum number of observations on any day (26) could result
in 92.82 estimated exposures. NMFS estimates a total of 114.31 Steller
sea lions could be exposed in June. Although we are not proposing to
authorize takes by month, we are demonstrating how the total take
[[Page 27280]]
was calculated. The total number of exposures per month was calculated
to be 114.31 (June), 57.19 (July), 92.89 (August), 199.23 (September),
79.10 (October), and 16.57 (November). Therefore, the total number of
Steller sea lions authorized to be taken by Level B harassment from
June to November is 559 (559.29) Steller sea lions with 39 (39.32) of
those sea lions anticipated being from the Western DPS (0.0703
percentage of the total animals (L. Jemison draft unpublished Steller
sea lion data, 2019).
Table 9 below summarizes the authorized take by Level A and B
harassment for all the species described above as a percentage of stock
abundance.
Table 9--Take Estimates as a Percentage of Stock Abundance
----------------------------------------------------------------------------------------------------------------
Authorized
Species Stock (NEST) Level A Authorized Level Percent of stock
harassment B harassment
----------------------------------------------------------------------------------------------------------------
Minke Whale................... N/A............. 0 9................ N/A.
Humpback Whale................ Hawaii DPS 0 408.............. 4.3.
(9,487) \a\. 26............... 4.5.
Mexico DPS (606) (Total 434)...... ...........................
\a\.
Gray Whale.................... Eastern North 0 3................ Less than 1 percent.
Pacific
(26,960).
Killer Whale.................. Alaska Resident 0 469.............. 19.9.\b\
(2,347).
Northern 52............... 19.9.\b\
Resident (261).
West Coast 49............... 20.2.\b\
Transient (243). (Total 570)......
Pacific White-Sided Dolphin... North Pacific 0 164.............. Less than 1 percent.
(26,880).
Dall's Porpoise............... Alaska (83,400) 0 1,038............ 1.2.
\c\.
Harbor Porpoise............... NA.............. 32 1,992............ NA.
Harbor Seal................... Glacier Bay/Icy 16 156.............. 2.16.
Strait (7,210).
Steller Sea Lion.............. Eastern U.S. 0 520.............. 1.25.
(41,638).
Western U.S. 39............... Less than 1 percent.
(53,303). (Total 559)......
----------------------------------------------------------------------------------------------------------------
\a\ Under the MMPA humpback whales are considered a single stock (Central North Pacific); however, we have
divided them here to account for DPSs listed under the ESA. Using the stock assessment from Muto et al., 2018
for the Central North Pacific stock (10,103 whales) and calculations in Wade et al., 2016; 9,487 whales are
expected to be from the Hawaii DPS and 606 from the Mexico DPS.
\b\ Take estimates are weighted based on calculated percentages of population for each distinct stock, assuming
animals present would follow same probability of presence in project area.
\c\ Jefferson et al., 2019 presents the first abundance estimates for Dall's porpoise in the waters of Southeast
Alaska with highest abundance recorded in spring (N = 5,381, CV = 25.4 percent), lower numbers in summer (N =
2,680, CV = 19.6 percent), and lowest in fall (N = 1,637, CV = 23.3 percent). However, NMFS currently
recognizes a single stock of Dall's porpoise in Alaskan waters and an estimate of 83,400 Dall's porpoises is
used by NMFS for the entire stock (Muto et al., 2018).
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 such
activity, and other means of effecting the least practicable impact on
such species or stock and its habitat, paying particular attention to
rookeries, mating grounds, and areas of similar significance, and on
the availability of such species or stock for taking for certain
subsistence uses (latter not applicable for this action). 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 such
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.
The following mitigation measures are planned in the IHA:
Timing Restrictions
All work will be conducted during daylight hours. If poor
environmental conditions restrict visibility full visibility of the
shutdown zone, pile installation would be delayed.
Sound Attenuation
To minimize noise during impact pile driving, pile caps (pile
softening material) will be used. DPD will use high-density
polyethylene (HDPE) or ultra-high-molecular-weight polyethylene (UHMW)
softening material on all templates to eliminate steel on steel noise
generation.
Shutdown Zone for In-Water Heavy Machinery Work
For in-water heavy machinery work (using, e.g., movement of the
barge to the pile location; positioning of the pile on the substrate
via a crane (i.e., stabling the pile), removal of the pile from the
water column/substrate via a crane (i.e., deadpull); or placement of
sound attenuation devices around the piles.) If a marine mammal comes
within 10 m of such operations, operations shall cease and vessels
shall reduce speed to the minimum level required to maintain steerage
and safe working conditions.
[[Page 27281]]
Shutdown Zones
For all pile driving/removal and drilling activities, DPD will
establish a shutdown zone for a marine mammal species that is greater
than its corresponding Level A harassment zone; except for a few
circumstances during impact pile driving, over the course of 8 days,
where the shutdown zone is smaller than the Level A harassment zone for
high frequency cetaceans and phocids due to the practicability of
shutdowns on the applicant and to the potential difficulty of observing
these animals in the large Level A harassment zones. The calculated PTS
isopleths were rounded up to a whole number to determine the actual
shutdown zones that the applicant will operate under (Table 10). 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).
Table 10--Pile Driving Shutdown Zones During Project Activities
--------------------------------------------------------------------------------------------------------------------------------------------------------
Shutdown zones (radial distance in meters, area in km\2\)
--------------------------------------------------------------------------------------------------------------------
Source Low-frequency Mid-frequency High-frequency
cetaceans cetaceans cetaceans Phocids Otariids
--------------------------------------------------------------------------------------------------------------------------------------------------------
In-Water Construction Activities
--------------------------------------------------------------------------------------------------------------------------------------------------------
Barge movements, pile positioning, 10 m (0.00093 km\2\).. 10 m (0.00093 km\2\).. 10 m (0.00093 km\2\). 10 m (0.00093 km\2\). 10 m (0.00093 km\2\).
sound attenuation placement *.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Vibratory Pile Driving/Removal
--------------------------------------------------------------------------------------------------------------------------------------------------------
24-in steel installation (18 piles; 25 m (0.005763 km\2\). 10 m (0.00093 km\2\).. 25 m (0.005763 km\2\) 10 m (0.00093 km\2\). 10 m (0.00093 km\2\).
~40 min per day on 4.5 days).
30-in steel temporary installation 25 m (0.005763 km\2\). 10 m (0.00093 km\2\).. 25 m (0.005763 km\2\) 10 m (0.00093 km\2\). 10 m (0.00093 km\2\).
(62 piles; ~2 hours per day on
10.5 days).
30-in steel removal (62 piles; ~1 25 m (0.005763 km\2\). 10 m (0.00093 km\2\).. 25 m (0.005763 km\2\) 10 m (0.00093 km\2\). 10 m (0.00093 km\2\).
hour per day on 10.5 days).
30-in steel permanent installation 25 m (0.005763 km\2\). 10 m (0.00093 km\2\).. 25 m (0.005763 km\2\) 10 m (0.00093 km\2\). 10 m (0.00093 km\2\).
(3 piles; ~1 hour per day on 1.5
days).
36-in steel permanent installation 25 m (0.005763 km\2\). 10 m (0.00093 km\2\).. 50 m (0.02307 km\2\). 25 m (0.005763 km\2\) 10 m (0.00093 km\2\).
(16 piles; ~1 hour per day on 8
days).
42-in steel permanent installation 50 m (0.02307 km\2\).. 10 m (0.00093 km\2\).. 50 m (0.02307 km\2\). 25 m (0.005763 km\2\) 10 m (0.00093 km\2\).
(8 piles; ~2 hours per day on 4
days).
--------------------------------------------------------------------------------------------------------------------------------------------------------
Impact Pile Driving
--------------------------------------------------------------------------------------------------------------------------------------------------------
36-in steel permanent installation 1,000 m (2.31 km\2\).. 50 m (0.02307 km\2\).. 100 m* (0.0875 km\2\) 50 m* (0.02307 km\2\) 50 m (0.02307 km\2\).
(16 piles; ~10 min per day on 4
days).
42-in steel permanent installation 750 m (1.44 km\2\).... 50 m (0.02307 km\2\).. 100 m* (0.0875 km\2\) 50 m* (0.02307 km\2\) 50 m (0.02307 km\2\).
(8 piles; ~6 min per day on 4
days).
--------------------------------------------------------------------------------------------------------------------------------------------------------
Socketed Pile Installation
--------------------------------------------------------------------------------------------------------------------------------------------------------
24-in steel permanent installation 25 m (0.005763 km\2\). 10 m (0.00093 km\2\).. 50 m (0.02307 km\2\). 15 m (0.0021 km\2\).. 10 m (0.00093 km\2\).
(18 piles; ~2 hours per day on 9
days).
30-in steel temporary installation 25 m (0.005763 km\2\). 10 m (0.00093 km\2\).. 50 m (0.02307 km\2\). 15 m (0.0021 km\2\).. 10 m (0.00093 km\2\).
(up to 10 piles; ~2 hours per day
on 5 days).
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 27282]]
Rock Anchor Installation
--------------------------------------------------------------------------------------------------------------------------------------------------------
8-in anchor permanent installation 25 m (0.005763 km\2\). 10 m (0.00093 km\2\).. 25 m (0.005763 km\2\) 10 m (0.00093 km\2\). 10 m (0.00093 km\2\).
(for 24-in piles, 2 anchors; ~1
hour per day on 2 days).
33-in anchor permanent installation 100 m (0.0875 km\2\).. 10 m (0.00093 km\2\).. 100 m (0.0875 km\2\). 50 m (0.02307 km\2\). 10 m (0.00093 km\2\).
(for 36- and 42-in piles, 24
anchors; ~8 hours per day on 12
days).
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Due to practicability of the applicant to shutdown and the difficulty of observing some species and low occurrence of some species in the project
area, such as high frequency cetaceans or pinnipeds out to this distance, the shutdown zones were reduced and Level A harassment takes were requested.
Non-Authorized Take Prohibited
If a species enters or approaches the Level B harassment zone and
that species is either not authorized for take or its authorized takes
are met, pile driving and removal activities must shut down immediately
using delay and shut-down procedures. Activities must not resume until
the animal has been confirmed to have left the area or an observation
time period of 15 minutes (min) has elapsed for pinnipeds and small
cetaceans and 30 min for large whales.
Soft Start
The use of a soft-start procedure are believed to provide
additional protection to marine mammals by providing warning and/or
giving marine mammals a chance to leave the area prior to the impact
hammer operating at full capacity. For impact pile driving, contractors
will be required to provide an initial set of three strikes from the
hammer at 40 percent energy, followed by a 1-min waiting period. Then
two subsequent three strike sets would occur. Soft Start is not
required during vibratory pile driving and removal activities.
Based on our evaluation of the applicant's planned measures, as
well as other measures considered by NMFS, NMFS has determined that the
planned 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.
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 in the
planned action area. 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:
[ssquf] Occurrence of marine mammal species or stocks in the area
in which take is anticipated (e.g., presence, abundance, distribution,
density);
[ssquf] Nature, scope, or context of likely marine mammal exposure
to potential 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);
[ssquf] Individual marine mammal responses (behavioral or
physiological) to acoustic stressors (acute, chronic, or cumulative),
other stressors, or cumulative impacts from multiple stressors;
[ssquf] How anticipated responses to stressors impact either: (1)
Long-term fitness and survival of individual marine mammals; or (2)
populations, species, or stocks;
[ssquf] Effects on marine mammal habitat (e.g., marine mammal prey
species, acoustic habitat, or other important physical components of
marine mammal habitat); and
[ssquf] Mitigation and monitoring effectiveness.
DPD Briefings
DPD is will conduct briefings between construction supervisors and
crews, marine mammal monitoring team, and DPD staff prior to the start
of all pile driving activities and when new personnel join the work, in
order to explain responsibilities, communication procedures, marine
mammal monitoring protocol, and operational procedures. The crew will
be requested to alert the PSO when a marine mammal is spotted in the
action area.
Protected Species Observer Check-In With Construction Crew
Each day prior to commencing pile driving activities, the lead NMFS
approved Protected Species Observer (PSO) will conduct a radio check
with the construction foreman or superintendent to confirm the
activities and zones to be monitored that day. The construction foreman
and lead PSO will maintain radio communications throughout the day so
that the PSOs may be alerted to any changes in the planned construction
activities and zones to be monitored.
[[Page 27283]]
Pre-Activity Monitoring
Prior to the start of daily in-water construction activity, or
whenever a break in pile driving of 30 min or longer occurs, PSOs will
observe the shutdown and monitoring zones for a period of 30 min. The
shutdown zone will be cleared when a marine mammal has not been
observed within the zone for that 30-min period. If a marine mammal is
observed within the shutdown zone, pile driving activities will not
begin until the animal has left the shutdown zone or has not been
observed for 15 min. If the Level B Harassment Monitoring Zone has been
observed for 30 min and no marine mammals (for which take has not been
authorized) are present within the zone, work can continue even if
visibility becomes impaired within the Monitoring Zone. When a marine
mammal permitted for Level B harassment take has been permitted is
present in the Monitoring zone, piling activities may begin and Level B
harassment take will be recorded.
Monitoring Zones
DPD will establish and observe monitoring zones for Level B
harassment as presented in Table 8. The monitoring zones for this
project are areas where SPLs are equal to or exceed 120 dB rms (for
vibratory pile driving/removal and socketing/rock anchoring) and 160 dB
rms (for impact pile driving). These zones provide utility for
monitoring conducted for mitigation purposes (i.e., shutdown zone
monitoring) by establishing monitoring protocols for areas adjacent to
the shutdown zones. Monitoring of the Level B harassment zones enables
observers to be aware of and communicate the presence of marine mammals
in the project area, but outside the shutdown zone, and thus prepare
for potential shutdowns of activity.
Visual Monitoring
Monitoring would be conducted 30 min before, during, and 30 min
after all pile driving/removal and socking/rock anchoring activities.
In addition, PSO shall record all incidents of marine mammal
occurrence, regardless of distance from activity, and shall document
any behavioral reactions in concert with distance from piles being
driven/removed or during socketing and rock anchoring. Pile driving/
removal and socketing/anchoring activities include the time to install,
remove, or socket/rock anchor 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 min.
Monitoring will be conducted by PSOs from on land and from a
vessel. The number of PSOs will vary from three to four, depending on
the type of pile driving, method of pile driving and size of pile, all
of which determines the size of the harassment zones. Monitoring
locations will be selected to provide an unobstructed view of all water
within the shutdown zone and as much of the Level B harassment zone as
possible for pile driving activities. Three PSOs will monitor during
all impact pile driving activity at the lightering float project site.
Three PSOs will monitor during all impact pile driving activities at
the Berth II project site. Three PSOs will monitor during vibratory
pile driving of 24-in and 30-in steel piles. Four PSOs will monitor
during vibratory pile driving of 36-in and 42-in steel piles and during
all socketing/rock anchoring activities.
Three PSOs will monitor during all pile driving activities at the
lightering float project site, with locations as follows: PSO #1:
Stationed at or near the site of pile driving; PSO #2: Stationed on
Long Island (southwest of Hoonah in Port Frederick Inlet) and
positioned to be able to view west into Port Frederick Inlet and north
towards the project area; and PSO #3: Stationed on a vessel traveling a
circuitous route through the Level B harassment monitoring zone. Three
PSOs will monitor during all impact pile driving activities at the
Berth II project site, with locations as follows: PSO #1: Stationed at
or near the site of pile driving; PSO #2: Stationed on Halibut Island
(northwest of the project site in Port Frederick Inlet) and positioned
to be able to view east towards Icy Strait and southeast towards the
project area; and PSO #3: Stationed on a vessel traveling a circuitous
route through the Level B monitoring zone.
Three PSOs will monitoring during vibratory pile driving of 24- and
30-in steel piles at the Berth II project site, with locations as
follows PSO #1: Stationed at or near the site of pile driving; PSO #2:
Stationed on Scraggy Island (northwest of the project site in Port
Frederick Inlet) an positioned to be able to view south towards the
project area; and PSO#3: Stationed on a vessel traveling a circuitous
route through the Level B harassment monitoring zone.
Four PSOs will monitor during vibratory pile driving of 36-in and
42-in steel piles and during all socketing/rock anchoring activities
with locations as follows: PSO #1: Stationed at or near the site of
pile driving; PSO #2: Stationed on Hoonah Island (northwest of the
project site in Port Frederick Inlet) and positioned to be able to view
south towards the project site; PSO #3: Stationed across Icy Strait
north of the project site (on the mainland or the Porpoise Islands) and
positioned to be able to view west into Icy Strait and southwest
towards the project site; and PSO #4: Stationed on a vessel traveling a
circuitous route through the Level B monitoring zone.
In addition, PSOs will work in shifts lasting no longer than 4
hours with at least a 1-hour break between shifts, and will not perform
duties as a PSO for more than 12 hours in a 24-hour period (to reduce
PSO fatigue).
Monitoring of pile driving shall be conducted by qualified, NMFS-
approved PSOs, who shall have no other assigned tasks during monitoring
periods. DPD shall adhere to the following conditions when selecting
PSOs:
[ssquf] Independent PSOs shall be used (i.e., not construction
personnel);
[ssquf] At least one PSO must have prior experience working as a
marine mammal observer during construction activities;
[ssquf] Other PSOs may substitute education (degree in biological
science or related field) or training for experience;
[ssquf] Where a team of three or more PSOs are required, a lead
observer or monitoring coordinator shall be designated. The lead
observer must have prior experience working as a marine mammal observer
during construction; and
[ssquf] DPD shall submit PSO CVs for approval by NMFS for all
observers prior to monitoring.
DPD shall ensure that the PSOs have the following additional
qualifications:
[ssquf] Visual acuity in both eyes (correction is permissible)
sufficient for discernment of moving targets at the water's surface
with ability to estimate target size and distance; use of binoculars
may be necessary to correctly identify the target;
[ssquf] Experience and ability to conduct field observations and
collect data according to assigned protocols;
[ssquf] Experience or training in the field identification of
marine mammals, including the identification of behaviors;
[ssquf] Sufficient training, orientation, or experience with the
construction operation to provide for personal safety during
observations;
[ssquf] 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,
[[Page 27284]]
and reason for implementation of mitigation (or why mitigation was not
implemented when required); and marine mammal behavior;
[ssquf] 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; and
[ssquf] Sufficient training, orientation, or experience with the
construction operations to provide for personal safety during
observations.
Notification of Intent To Commence Construction
DPD shall inform NMFS OPR and the NMFS Alaska Region Protected
Resources Division one week prior to commencing construction
activities.
Reporting of Injured or Dead Marine Mammals
In the unanticipated event that the planned activity clearly causes
the take of a marine mammal in a manner prohibited by the IHA, such as
serious injury, or mortality, DPD must immediately cease the specified
activities and report the incident to the NMFS Office of Protected
Resources and the Alaska Region Stranding Coordinator. The report must
include the following information:
[ssquf] Time and date of the incident;
[ssquf] Description of the incident;
[ssquf] Environmental conditions (e.g., wind speed and direction,
Beaufort sea state, cloud cover, and visibility);
[ssquf] Description of all marine mammal observations and active
sound source use in the 24 hours preceding the incident;
[ssquf] Species identification or description of the animal(s)
involved;
[ssquf] Fate of the animal(s); and
[ssquf] Photographs or video footage of the animal(s).
Activities must not resume until NMFS is able to review the
circumstances of the prohibited take. NMFS will work with DPD to
determine what measures are necessary to minimize the likelihood of
further prohibited take and ensure MMPA compliance. DPD may not resume
their activities until notified by NMFS.
In the event DPD discovers an injured or dead marine mammal, and
the lead observer determines that the cause of the injury or death is
unknown and the death is relatively recent (e.g., in less than a
moderate state of decomposition), DPD must immediately report the
incident to the Office of Protected Resources, NMFS, and the Alaska
Region Stranding Coordinator, NMFS. The report must include the same
information as the bullets described above. Activities may continue
while NMFS reviews the circumstances of the incident. NMFS will work
with DPD to determine whether additional mitigation measures or
modifications to the activities are appropriate.
In the event that DPD discovers an injured or dead marine mammal,
and the lead observer determines that the injury or death is not
associated with or related to the specified activities (e.g.,
previously wounded animal, carcass with moderate to advanced
decomposition, or scavenger damage), DPD must report the incident to
the Office of Protected Resources, NMFS, and the Alaska Region
Stranding Coordinator, NMFS, within 24 hours of the discovery.
Interim Monthly Reports
During construction, DPD will submit brief, monthly reports to the
NMFS Alaska Region Protected Resources Division that summarize PSO
observations and recorded takes. Monthly reporting will allow NMFS to
track the amount of take (including extrapolated takes), to allow
reinitiation of consultation in a timely manner, if necessary. The
monthly reports will be submitted by email to a NMFS representative.
The reporting period for each monthly PSO report will be the entire
calendar month, and reports will be submitted by close of business on
the fifth day of the month following the end of the reporting period
(e.g., the monthly report covering September 1-30, 2019, would be
submitted to the NMFS by close of business on October 5, 2019).
Final Report
DPD shall submit a draft report to NMFS no later than 90 days
following the end of construction activities or 60 days prior to the
issuance of any subsequent IHA for the project. DPD shall provide a
final report within 30 days following resolution of NMFS' comments on
the draft report. Reports shall contain, at minimum, the following:
[ssquf] Date and time that monitored activity begins and ends for
each day conducted (monitoring period);
[ssquf] Construction activities occurring during each daily
observation period, including how many and what type of piles driven;
[ssquf] Deviation from initial proposal in pile numbers, pile
types, average driving times, etc.;
[ssquf] Weather parameters in each monitoring period (e.g., wind
speed, percent cloud cover, visibility);
[ssquf] Water conditions in each monitoring period (e.g., sea
state, tide state);
[ssquf] For each marine mammal sighting:
[cir] Species, numbers, and, if possible, sex and age class of
marine mammals;
[cir] Description of any observable marine mammal behavior
patterns, including bearing and direction of travel and distance from
pile driving activity;
[cir] Type of construction activity that was taking place at the
time of sighting;
[cir] Location and distance from pile driving activities to marine
mammals and distance from the marine mammals to the observation point;
[cir] If shutdown was implemented, behavioral reactions noted and
if they occurred before or after shutdown.
[cir] Estimated amount of time that the animals remained in the
Level A or B Harassment Zone.
[ssquf] Description of implementation of mitigation measures within
each monitoring period (e.g., shutdown or delay);
[ssquf] Other human activity in the area within each monitoring
period.
[ssquf] A summary of the following:
[cir] Total number of individuals of each species detected within
the Level B Harassment Zone, and estimated as taken if correction
factor appropriate.
[cir] Total number of individuals of each species detected within
the Level A Harassment Zone and the average amount of time that they
remained in that zone.
[cir] Daily average number of individuals of each species
(differentiated by month as appropriate) detected within the Level B
Harassment Zone, and estimated as taken, if appropriate.
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
[[Page 27285]]
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).
As stated in the mitigation section, shutdown zones that are larger
than the Level A harassment zones will be implemented in the majority
of construction days, which, in combination with the fact that the
zones are so small to begin with, is expected avoid the likelihood of
Level A harassment for seven of the nine species. For the other two
species (harbor seals and harbor porpoises), a small amount of Level A
harassment has been conservatively authorized because the Level A
harassment zones are larger than the planned shutdown zones. However,
we expect, given the relatively short duration of the sound source
(minutes a day during impact pile driving) that these animals may
potentially be exposed to, could result in only a small degree of PTS
that would impact the fitness of any individual animals.
Exposures to elevated sound levels produced during pile driving
activities may cause behavioral responses by an animal, but they are
expected to be mild and temporary. Effects on individuals that are
taken by Level B harassment, on the basis of reports in the literature
as well as monitoring from other similar activities, will likely be
limited to reactions such as increased swimming speeds, increased
surfacing time, or decreased foraging (if such activity were occurring)
(e.g., Thorson and Reyff, 2006; Lerma, 2014). Most likely, individuals
will simply move away from the sound source and be temporarily
displaced from the areas of pile driving, although even this reaction
has been observed primarily only in association with impact pile
driving. These reactions and behavioral changes are expected to subside
quickly when the exposures cease.
To minimize noise during pile driving, DPC will use pile caps (pile
softening material). Much of the noise generated during pile
installation comes from contact between the pile being driven and the
steel template used to hold the pile in place. The contractor will use
high-density polyethylene (HDPE) or ultra-high-molecular- weight
polyethylene (UHMW) softening material on all templates to eliminate
steel on steel noise generation.
During all impact driving, implementation of soft start procedures
and monitoring of established shutdown zones will be required,
significantly reducing the possibility of injury. Given sufficient
notice through use of soft start (for impact driving), marine mammals
are expected to move away from an irritating sound source prior to it
becoming potentially injurious. In addition, PSOs will be stationed
within the action area whenever pile driving/removal and socketing/rock
anchoring activities are underway. Depending on the activity, DDP will
employ the use of three to four PSOs to ensure all monitoring and
shutdown zones are properly observed. Although the expansion of Berth
facilities would have some permanent removal of habitat available to
marine mammals, the area lost would be small, approximately equal to
the area of the cruise ship berth and associated pile placements. The
planned design would not impede migration of marine mammals through the
planned action area. The small lightering facility nearer to the
cannery would likely not impact any marine mammal habitat since its
planned location is in between two existing, heavily-traveled docks,
and within an active marine commercial and tourist area. There are no
known pinniped haulouts or other biologically important areas for
marine mammals near the action area.
In addition, impacts to marine mammal prey species are expected to
be minor and temporary. Overall, the area impacted by the project is
very small compared to the available habitat around Hoonah. The most
likely impact to prey will be temporary behavioral avoidance of the
immediate area. During pile driving/removal and socketing/rock
anchoring activities, it is expected that fish and marine mammals would
temporarily move to nearby locations and return to the area following
cessation of in-water construction activities. Therefore, indirect
effects on marine mammal prey during the construction are not expected
to be substantial.
In summary and as described above, the following factors primarily
support our determination that the impacts resulting from this activity
are not expected to adversely affect the species or stock through
effects on annual rates of recruitment or survival:
[ssquf] No mortality is anticipated or authorized;
[ssquf] Anticipated incidents of Level A harassment are very small
in number and would consist of no more than a small degree of PTS;
[ssquf] Anticipated incidents of Level B harassment consist of, at
worst, temporary modifications in behavior; and
[ssquf] There are no rookeries, or other known areas or features of
special significance for foraging or reproduction in the project area;
[ssquf] Minimal impacts to marine mammal habitat are expected;
[ssquf] The action area is located and within an active marine
commercial and tourist area;
[ssquf] The required mitigation measures (i.e. shutdown zones and
pile caps) are expected to be effective in reducing the effects of the
specified activity.
Based on the analysis contained herein of the likely effects of the
specified activity on marine mammals and their habitat, and taking into
consideration the implementation of the planned monitoring and
mitigation measures, NMFS finds that the total marine mammal take from
the planned activity 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 Section 101(a)(5)(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. Additionally, other qualitative factors may
be considered in the analysis, such as the temporal or spatial scale of
the activities.
The authorized take for six of the nine marine mammal stocks
comprises less than five percent of the stock abundance. For Alaska
resident, northern resident and transient killer whales, the number of
instances of take as compared to the stock abundance are 19.9 percent,
19.9, and 20.2 percent, respectively. However, since three stocks of
killer whales could occur in the action area, the 570 total killer
whale takes are likely split among the three stocks. Nonetheless, since
NMFS does not have a good way to predict exactly how take will be
split, NMFS
[[Page 27286]]
looked at the most conservative scenario, which is that all 570 takes
could potentially be distributed to each of the three stocks. This is a
highly unlikely scenario to occur and the percentages of each stock
taken are predicted to be significantly lower. Further, these
percentages do not take into consideration that some number of these
take instances are likely repeat takes incurred by the same
individuals, thereby lowering the number of individuals.
There are no official stock abundances for harbor porpoise and
minke whales; however, as discussed in greater detail in the
``Description of Marine Mammals in the Area of Specified Activities,''
we believe for the abundance information that is available, the
estimated takes are likely small percentages of the stock abundance.
For harbor porpoise, the abundance for the Southeast Alaska stock is
likely more represented by the aerial surveys that were conducted as
these surveys had better coverage and were corrected for observer bias.
Based on this data, the estimated take could potentially be
approximately 17 percent of the stock abundance. However, this is
unlikely and the percentage of the stock taken is likely lower as the
take estimates are conservative and the project occurs in a small
footprint compared to the available habitat in Southeast Alaska. For
minke whales, in the northern part of their range they are believed to
be migratory and so few minke whales have been seen during three
offshore Gulf of Alaska surveys that a population estimate could not be
determined. With only nine planned takes for this species, the
percentage of take in relation to the stock abundance is likely to be
very small.
Based on the analysis contained herein of the planned activity
(including the mitigation and monitoring measures) and the anticipated
take of marine mammals, NMFS finds that small numbers of marine mammals
will be taken relative to the population size of the affected species
or stocks.
Unmitigable Adverse Impact Analysis and Determination
In September 2018, DPD contacted the Indigenous People's Council
for Marine Mammals (IPCoMM), the Alaska Sea Otter and Steller Sea Lion
Commission, and the Hoonah Indian Association (HIA) to determine
potential project impacts on local subsistence activities. No comments
were received from IPCoMM or the Alaska Sea Otter and Steller Sea Lion
Commission. On October 23, 2018, a conference call between
representatives from DPD, Turnagain Marine Construction, SolsticeAK,
and the HIA were held to discuss tribal concerns regarding subsistence
impacts. The tribe confirmed that Steller sea lions and harbor seals
are harvested in and around the project area. The HIA referenced the
2012 subsistence technical paper by Wolf et al. (2013) as the most
recent information available on marine mammal harvesting in Hoonah and
agreed that the planned construction activities are unlikely to have
significant impacts to marine mammals as they are used in subsistence
applications. Information on the timing of the IHA issuance was
provided by DPD via email to the tribe on October 23, 2018. There have
been no further comments on this project.
Therefore, we believe there are no relevant subsistence uses of the
affected marine mammal stocks or species implicated by this action.
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.
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
incidental harassment authorization) with respect to potential impacts
on the human environment. This action is consistent with categories of
activities identified in Categorical Exclusion B4 (incidental
harassment authorizations 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 determined
that the issuance of the IHA qualifies to be categorically excluded
from further NEPA review.
Endangered Species Act (ESA)
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, in this case with the Alaska Regional Office
(AKRO) whenever we propose to authorize take for endangered or
threatened species.
NMFS is authorizing take of Mexico DPS humpback whales, which are
listed and Western DPS Steller sea lions under the ESA. The Permit and
Conservation Division completed a Section 7 consultation with the
Alaska Regional Office for the issuance of this IHA. The Alaska
Regional Office's biological opinion states that the action is not
likely to jeopardize the continued existence of Western DPS Steller sea
lions or Mexico DPS humpback whales.
Authorization
As a result of these determinations, NMFS authorizes an IHA to DPD
for conducting pile driving and removal activities for the construction
of the Hoonah Berth II cruise ship terminal and lightering float, Icy
Strait, Hoonah Alaska provided the previously mentioned mitigation,
monitoring, and reporting requirements are incorporated.
Dated: June 6, 2019.
Donna S. Wieting,
Director, Office of Protected Resources, National Marine Fisheries
Service.
[FR Doc. 2019-12318 Filed 6-11-19; 8:45 am]
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