Takes of Marine Mammals Incidental to Specified Activities; Seabird Monitoring and Research in Glacier Bay National Park, Alaska, 2015, 18359-18369 [2015-07734]
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Federal Register / Vol. 80, No. 65 / Monday, April 6, 2015 / Notices
The Department intends to issue the
final results of this administrative
review, including the results of its
analysis of the issues raised in any
written briefs, not later than 120 days
after the date of publication of this
notice, pursuant to section 751(a)(3)(A)
of the Act.
Assessment Rates
Upon issuance of the final results, the
Department shall determine, and CBP
shall assess, antidumping duties on all
appropriate entries covered by this
review. If the preliminary results are
unchanged for the final results we will
instruct CBP to apply an ad valorem
assessment rate of 55.60 percent to all
entries of subject merchandise during
the POR which were produced and/or
exported by Messingwerk, and an ad
valorem assessment rate of 22.61
percent to all entries of subject
merchandise during the POR which
were produced and/or exported by the
six aforementioned companies which
were not selected for individual
examination.
We intend to issue liquidation
instructions to CBP 15 days after
publication of the final results of
review.
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Cash Deposit Requirements
The following deposit requirements
will be effective upon publication of the
notice of final results of administrative
review for all shipments of brass sheet
and strip from Germany entered, or
withdrawn from warehouse, for
consumption on or after the date of
publication, as provided by section
751(a)(2) of the Act: (1) The cash deposit
rates for the reviewed companies will be
the rates established in the final results
of this review; (2) for merchandise
exported by manufacturers or exporters
not covered in this review but covered
in a prior segment of the proceeding, the
cash deposit rate will continue to be the
company-specific rate published for the
most recently completed segment of this
proceeding; (3) if the exporter is not a
firm covered in this review, a prior
review, or the less-than-fair-value
investigation but the manufacturer is,
the cash deposit rate will be the rate
established for the most recently
completed segment of this proceeding
for the manufacturer of the
merchandise; (4) if neither the exporter
nor the manufacturer has its own rate,
the cash deposit rate will be 7.30
percent.11 These deposit requirements,
11 See Preliminary Decision Memorandum for
additional details.
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when imposed, shall remain in effect
until further notice.
Notifications to Importers
This notice serves as a preliminary
reminder to importers of their
responsibility under 19 CFR
351.402(f)(2) to file a certificate
regarding the reimbursement of
antidumping duties prior to liquidation
of the relevant entries during this
review period. Failure to comply with
this requirement could result in the
Secretary’s presumption that
reimbursement of antidumping duties
occurred and the subsequent assessment
of doubled antidumping duties.
Notification to Interested Parties
This notice is issued and published in
accordance with sections 751(a)(1) and
777(i)(1) of the Act.
Dated: March 31, 2015.
Paul Piquado,
Assistant Secretary for Enforcement and
Compliance.
Appendix
List of Topics Discussed in the Preliminary
Decision Memorandum
A. Summary
B. Background
C. Scope of the Order
D. Discussion of the Methodology
1. Selection of Respondent
2. No Shipment Preliminary Determination
3. Use of Facts Otherwise Available
a. Use of Facts Available
b. Application of Facts Available With an
Adverse Inference
c. Selection and Corroboration of
Information Used as Facts Available
4. Rate for Companies Not Selected for
Individual Examination
E. Recommendation
[FR Doc. 2015–07844 Filed 4–3–15; 8:45 am]
BILLING CODE 3510–DS–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XD815
Takes of Marine Mammals Incidental to
Specified Activities; Seabird
Monitoring and Research in Glacier
Bay National Park, Alaska, 2015
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; proposed incidental
harassment authorization; request for
comments.
AGENCY:
NMFS has received an
application from Glacier Bay National
SUMMARY:
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18359
Park (Glacier Bay NP) to take marine
mammals, by harassment, incidental to
conducting seabird research from May
through September, 2015. The proposed
dates for this action are May 15, 2015,
through September 30, 2015. Per the
Marine Mammal Protection Act, we are
requesting comments on our proposal to
issue an Authorization to the Glacier
Bay NP to incidentally take, by Level B
harassment only, one species of marine
mammal during the specified activity.
DATES: NMFS must receive comments
and information on or before May 6,
2015.
ADDRESSES: Address comments on the
application to Jolie Harrison, Division
Chief, Permits and Conservation
Division, Office of Protected Resources,
National Marine Fisheries Service, 1315
East-West Highway, Silver Spring, MD
20910. The mailbox address for
providing email comments is ITP.Cody@
noaa.gov. Please include 0648–XD815
in the subject line. Comments sent via
email to ITP.Cody@noaa.gov, including
all attachments, must not exceed a 25megabyte file size. NMFS is not
responsible for email comments sent to
addresses other than the one provided
here.
Instructions: All submitted comments
are a part of the public record and
NMFS will post them to https://www.
nmfs.noaa.gov/pr/permits/incidental/
research.htm without change. All
Personal Identifying Information (for
example, name, address, etc.)
voluntarily submitted by the commenter
may be publicly accessible. Do not
submit confidential business
information or otherwise sensitive or
protected information.
To obtain an electronic copy of the
application containing a list of the
references used in this document, write
to the previously mentioned address,
telephone the contact listed here (see
FOR FURTHER INFORMATION CONTACT), or
visit the Internet at: https://www.nmfs.
noaa.gov/pr/permits/incidental/
research.htm.
Information in Glacier Bay NP’s
application, NMFS’ 2014 Environmental
Assessment titled, Environmental
Assessment for the Issuance of an
Incidental Harassment Authorization to
Take Marine Mammals by Harassment
Incidental to Conducting Seabird
Research in Glacier Bay Alaska, and this
notice collectively provide the
environmental information related to
proposed issuance of the Authorization
for public review and comment.
FOR FURTHER INFORMATION CONTACT:
Jeannine Cody, NMFS, Office of
Protected Resources, NMFS (301) 427–
8401.
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Federal Register / Vol. 80, No. 65 / Monday, April 6, 2015 / Notices
SUPPLEMENTARY INFORMATION:
Summary of Request
Background
On January 15, 2015, NMFS received
an application from Glacier Bay NP
requesting that we issue an
Authorization for the take of marine
mammals, incidental to conducting
monitoring and research studies on
glaucus-winged gulls (Larus
glaucescens) within Glacier Bay
National Park and Preserve in Alaska.
NMFS determined the application
complete and adequate on February 27,
2015. NMFS previously issued an
Authorization to Glacier Bay NP for the
same activities in 2014 (79 FR 56065,
September 18, 2014). No seabird
research activities occurred during the
effective period of the prior
Authorization.
Glacier Bay NP proposes to conduct
ground-based and vessel-based surveys
to collect data on the number and
distribution of nesting gulls within five
study sites in Glacier Bay, AK. Glacier
Bay NP proposes to complete up to five
visits per study site, from May through
September, 2015.
The proposed activities are within the
vicinity of pinniped haulout sites and
the following aspects of the proposed
activities are likely to result in the take
of marine mammals: Noise generated by
motorboat approaches and departures;
noise generated by researchers while
conducting ground surveys; and human
presence during the monitoring and
research activities. NMFS anticipates
that take by Level B harassment only, of
individuals of harbor seals (Phoca
vitulina) would result from the specified
activity. Although Steller sea lions
(Eumetopias jubatus) may be present in
the action area, Glacier Bay NP has
proposed to avoid any site used by
Steller sea lions.
Section 101(a)(5)(D) of the Marine
Mammal Protection Act of 1972, as
amended (MMPA; 16 U.S.C. 1361 et
seq.) directs the Secretary of Commerce
to allow, upon request, the incidental,
but not intentional, taking of small
numbers of marine mammals of a
species or population stock, by U.S.
citizens who engage in a specified
activity (other than commercial fishing)
within a specified geographical region
if, after NMFS provides a notice of a
proposed authorization to the public for
review and comment: (1) NMFS makes
certain findings; and (2) the taking is
limited to harassment.
An Authorization shall be granted for
the incidental taking of small numbers
of marine mammals 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 subsistence uses (where relevant).
The Authorization must also set forth
the permissible methods of taking; other
means of effecting the least practicable
adverse impact on the species or stock
and its habitat; and requirements
pertaining to the monitoring and
reporting of such taking. NMFS has
defined ‘‘negligible impact’’ in 50 CFR
216.103 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.’’
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Except with respect to certain
activities not pertinent here, 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].
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Description of the Specified Activity
Overview
Glacier Bay NP proposes to identify
the onset of gull nesting; conduct midseason surveys of adult gulls, and locate
and document gull nest sites within the
following study areas: Boulder, Lone,
and Flapjack Islands, and Geikie Rock.
Each of these study sites contains harbor
seal haulout sites and Glacier Bay NP
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proposes to visit each study site up to
five times during the research season.
Glacier Bay NP must conduct the gull
monitoring studies to meet the
requirements of a 2010 Record of
Decision for a Legislative Environmental
Impact Statement (NPS, 2010) which
states that Glacier Bay NP must initiate
a monitoring program for the gulls to
inform future native egg harvests by the
Hoonah Tlingit in Glacier Bay, AK.
Glacier Bay NP actively monitors harbor
seals at breeding and molting sites to
assess population trends over time (e.g.,
Mathews & Pendleton, 2006; Womble et
al., 2010). Glacier Bay NP also
coordinates pinniped monitoring
programs with NMFS’ National Marine
Mammal Laboratory and the Alaska
Department of Fish & Game and plans
to continue these collaborations and
sharing of monitoring data and
observations in the future.
Dates and Duration
Glacier Bay NP proposes to conduct
the proposed activities from the period
of May 15 through September 30, 2015.
Glacier Bay NP proposes to conduct a
maximum of three ground-based
surveys per each study site and a
maximum of two vessel-based surveys
per each study site.
Thus, the proposed Authorization, if
issued, would be effective from May 15,
2015 through September 30, 2015.
NMFS refers the reader to the Detailed
Description of Activities section later in
this notice for more information on the
scope of the proposed activities.
Specified Geographic Region
The proposed study sites would occur
in the vicinity of the following
locations: Boulder (58°33′18.08″ N;
136°1′13.36″ W), Lone (58°43′17.67″ N;
136°17′41.32″ W), and Flapjack
(58°35′10.19″ N; 135°58′50.78″ W)
Islands, and Geikie Rock (58°41′39.75″
N; 136°18′39.06″ W) in Glacier Bay,
Alaska. Glacier Bay NP will also
conduct studies at Tlingit Point Islet
located at 58°45′16.86″ N; 136°10′41.74″
W; however, there are no reported
pinniped haulout sites at that location.
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Detailed Description of Activities
Glacier Bay NP proposes to conduct:
(1) Ground-based surveys at a maximum
frequency of three visits per site; and (2)
vessel-based surveys at a maximum
frequency of two visits per site from the
period of May 15 through September 30,
2015.
Ground-Based Surveys: These surveys
involve two trained observers visiting
the largest gull colony on each island to:
(1) Obtain information on the numbers
of nests, their location, and contents
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(i.e., eggs or chicks); (2) determine the
onset of laying, distribution, abundance,
and predation of gull nests and eggs;
and (3) record the proximity of other
species relative to colony locations.
The observers would access each
island using a kayak, a 32.8 to 39.4-foot
(ft) (10 to 12 meter (m)) motorboat, or a
12 ft (4 m) inflatable rowing dinghy. The
landing craft’s transit speed would not
exceed 4 knots (4.6 miles per hour
(mph). Ground surveys generally last
from 30 minutes to up to two hours
depending on the size of the island and
the number of nesting gulls. Glacier Bay
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NP will discontinue ground surveys
after they detect the first hatchling to
minimize disturbance to the gull
colonies.
Vessel-Based Surveys: These surveys
involve two trained observers observing
and counting the number of adult and
fledgling gulls from the deck of a
motorized vessel which would transit
around each island at a distance of
approximately 328 ft (100 m) to avoid
flushing the birds from the colonies.
Vessel-based surveys generally last from
30 minutes to up to two hours
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depending on the size of the island and
the number of nesting gulls.
Description of Marine Mammals in the
Area of the Specified Activity
Table 1 in this notice provides the
following information: All marine
mammal species with possible or
confirmed occurrence in the proposed
survey areas on land; information on
those species’ regulatory status under
the MMPA and the Endangered Species
Act of 1973 (16 U.S.C. 1531 et seq.);
abundance; occurrence and seasonality
in the activity area.
TABLE 1—GENERAL INFORMATION ON MARINE MAMMALS THAT COULD POTENTIALLY HAUL OUT IN THE PROPOSED STUDY
AREAS IN MAY THROUGH SEPTEMBER, 2015
Species
Stock name
Regulatory status 1 2
Stock/Species
abundance 3
Occurrence and
range
Season
Harbor seal (Phoca vitulina) .................
Steller sea lion (Eumetopias jubatus) ...
Steller sea lion (Eumetopias jubatus) ...
Glacier Bay/Icy Strait
Eastern U.S. .............
Western U.S. ............
MMPA–NC ESA–NL
MMPA–D, S ESA–NL
MMPA–D, S ESA–T
5,042 ....................
63,160–78,198 .....
52,200 ..................
common coastal ...
uncommon coastal
rare coastal ...........
year-round
year-round
unknown
1 MMPA:
D = Depleted, S = Strategic, NC = Not Classified.
EN = Endangered, T = Threatened, DL = Delisted, NL = Not listed.
3 2013 NMFS Stock Assessment Report (Allen and Anglis, 2014).
2 ESA:
NMFS refers the public to the Glacier
Bay NP’s application and the 2014
NMFS Marine Mammal Stock
Assessment Report available online at:
https://www.nmfs.noaa.gov/pr/sars/
species.htm for further information on
the biology and local distribution of
these species.
Other Marine Mammals in the
Proposed Action Area
Northern sea otters (Enhydra lutris
kenyoni) and polar bears (Ursis
maritimus) listed as threatened under
the Endangered Species Act could occur
in the proposed area. The U.S. Fish and
Wildlife Service manages these species
and NMFS does not consider them
further in this notice.
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Potential Effects of the Specified
Activities on Marine Mammals
This section includes a summary and
discussion of the ways that the types of
stressors associated with the specified
activity (e.g., personnel presence) have
been observed to impact marine
mammals. This discussion may also
include reactions that NMFS considers
to rise to the level of a take and those
that we do not consider to rise to the
level of a take. This section serves as a
background of potential effects and does
not consider either the specific manner
in which the applicant will carry out the
activity or the mitigation that will be
implemented, and how either of those
will shape the anticipated impacts from
this specific activity. The ‘‘Estimated
Take by Incidental Harassment’’ section
later in this document will include a
quantitative analysis of the number of
individuals that NMFS expects Glacier
Bay NP to take during this activity. The
‘‘Negligible Impact Analysis’’ section
will include the analysis of how this
specific activity would impact marine
mammals. NMFS will consider the
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content of the following sections:
Estimated Take by Incidental
Harassment; Proposed Mitigation; and
Anticipated Effects on Marine Mammal
Habitat, to draw conclusions regarding
the likely impacts of this activity on the
reproductive success or survivorship of
individuals—and from that
consideration—the likely impacts of this
activity on the affected marine mammal
populations or stocks.
Potential Effects of Human Presence on
Marine Mammals
The appearance of Glacier Bay
researchers has the potential to cause
Level B harassment of pinnipeds hauled
out on Boulder, Lone, and Flapjack
Islands, and Geikie Rock. Disturbance
includes a variety of effects, including
subtle to conspicuous changes in
behavior, movement, and displacement.
Disturbance may result in reactions
ranging from an animal simply
becoming alert to the presence of the
surveyors (e.g., turning the head,
assuming a more upright posture) to
flushing from the haul-out site into the
water. NMFS does not consider the
lesser reactions to constitute behavioral
harassment, or Level B harassment
takes, but rather assumes that pinnipeds
that move greater than 1 meter (m) (3.3
feet (ft)) or change the speed or direction
of their movement in response to the
presence of surveyors are behaviorally
harassed, and thus subject to Level B
taking. Animals that respond to the
presence of researchers by becoming
alert, but that do not move or change the
nature of locomotion as described, are
not considered to have been subject to
behavioral harassment.
Reactions to human presence, if any,
depend on species, state of maturity,
experience, current activity,
reproductive state, time of day, and
many other factors (Richardson et al.,
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1995; Wartzok et al., 2004; Southall et
al., 2007; Weilgart, 2007). These
behavioral reactions are often shown as:
Changing durations of surfacing and
dives, number of blows per surfacing, or
moving direction and/or speed;
reduced/increased vocal activities;
changing/cessation of certain behavioral
activities (such as socializing or
feeding); visible startle response or
aggressive behavior; avoidance of areas;
and/or flight responses (e.g., pinnipeds
flushing into the water from haul-outs
or rookeries). If a marine mammal does
react briefly to human presence by
changing its behavior or moving a small
distance, the impacts of the change are
unlikely to be significant to the
individual, let alone the stock or
population. However, if visual stimuli
from human presence displaces marine
mammals from an important feeding or
breeding area for a prolonged period,
impacts on individuals and populations
could be significant (e.g., Lusseau and
Bejder, 2007; Weilgart, 2007).
Disturbances resulting from human
activity can impact short- and long-term
pinniped haul out behavior (Renouf et
al., 1981; Schneider and Payne, 1983;
Terhune and Almon, 1983; Allen et al.,
1984; Stewart, 1984; Suryan and
Harvey, 1999; Mortenson et al., 2000;
and Kucey and Trites, 2006). Numerous
studies have shown that human activity
can flush harbor seals off haulout sites
(Allen et al., 1984; Calambokidis et al.,
1991; Suryan and Harvey, 1999; and
Mortenson et al., 2000) or lead to
Hawaiian monk seal (Monachus
schauinslandi) avoidance of beach areas
(Kenyon, 1972). In one case, human
disturbance appeared to cause Steller
sea lions to desert a breeding area at
Northeast Point on St. Paul Island,
Alaska (Kenyon, 1962).
In cases where vessels actively
approached marine mammals (e.g.,
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whale watching or dolphin watching
boats), scientists have documented that
animals exhibit altered behavior such as
increased swimming speed, erratic
movement, and active avoidance
behavior (Bursk, 1983; Acevedo, 1991;
Baker and MacGibbon, 1991; Trites and
Bain, 2000; Williams et al., 2002;
Constantine et al., 2003), reduced blow
interval (Ritcher et al., 2003), disruption
of normal social behaviors (Lusseau,
2003; 2006), and the shift of behavioral
activities which may increase energetic
costs (Constantine et al., 2003; 2004). In
1997, Henry and Hammil (2001)
conducted a study to measure the
impacts of small boats (i.e., kayaks,
canoes, motorboats and sailboats) on
´
harbor seal haulout behavior in Metis
Bay, Quebec, Canada. During that study,
the authors noted that the most frequent
disturbances (n=73) were caused by
lower speed, lingering kayaks, and
canoes (33.3 percent) as opposed to
motorboats (27.8 percent) conducting
high speed passes. The seals’ flight
reactions could be linked to a surprise
factor by kayaks-canoes that approach
slowly, quietly and low on water,
making them look like predators.
However, the authors note that once the
animals were disturbed, there did not
appear to be any significant lingering
effect on the recovery of numbers to
their pre-disturbance levels. In
conclusion, the study showed that boat
traffic at current levels has only a
temporary effect on the haulout
´
behavior of harbor seals in the Metis
Bay area.
In 2004, Johnson and AcevedoGutierrez (2007) evaluated the efficacy
of buffer zones for watercraft around
harbor seal haulout sites on Yellow
Island, Washington. The authors
estimated the minimum distance
between the vessels and the haul-out
sites; categorized the vessel types; and
evaluated seal responses to the
disturbances. During the course of the
seven-weekend study, the authors
recorded 14 human-related disturbances
which were associated with stopped
powerboats and kayaks. During these
events, hauled out seals became
noticeably active and moved into the
water. The flushing occurred when
stopped kayaks and powerboats were at
distances as far as 453 and 1,217 ft (138
and 371 m) respectively. The authors
note that the seals were unaffected by
passing powerboats, even those
approaching as close as 128 ft (39 m),
possibly indicating that the animals had
become tolerant of the brief presence of
the vessels and ignored them. The
authors reported that on average, the
seals quickly recovered from the
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disturbances and returned to the
haulout site in less than or equal to 60
minutes. Seal numbers did not return to
pre-disturbance levels within 180
minutes of the disturbance less than one
quarter of the time observed. The study
concluded that the return of seal
numbers to pre-disturbance levels and
the relatively regular seasonal cycle in
abundance throughout the area counter
the idea that disturbances from
powerboats may result in site
abandonment (Johnson and AcevedoGutierrez, 2007). As a general statement
from the available information,
pinnipeds exposed to intense
(approximately 110 to 120 decibels re:
20 mPa) non-pulse sounds often leave
haulout areas and seek refuge
temporarily (minutes to a few hours) in
the water (Southall et al., 2007).
There are three ways in which
disturbance, as described previously,
could result in more than Level B
harassment of marine mammals. All
three are most likely to be consequences
of stampeding, a potentially dangerous
occurrence in which large numbers of
animals succumb to mass panic and
rush away from a stimulus. The three
situations are: (1) Falling when entering
the water at high-relief locations; (2)
extended separation of mothers and
pups; and (3) crushing of pups by large
males during a stampede. However,
NMFS does not expect any of these
scenarios to occur at the proposed
survey site.
Because hauled-out animals may
move towards the water when
disturbed, there is the risk of injury if
animals stampede towards shorelines
with precipitous relief (e.g., cliffs).
However, while high-elevation sites
exist on the islands, the haulout sites
consist of ridges with unimpeded and
non-obstructive access to the water. If
disturbed, the small number of hauledout adult animals may move toward the
water without risk of encountering
barriers or hazards that would otherwise
prevent them from leaving the area.
The probability of vessel and marine
mammal interactions (i.e., motorboat
strike) occurring during the proposed
research activities is unlikely due to the
motorboat’s slow operational speed,
which is typically 2 to 3 knots (2.3 to
3.4 mph) and the researchers
continually scanning the water for
marine mammals presence during
transit to the islands. Thus, NMFS does
not anticipate that strikes or collisions
would result from the movement of the
motorboat.
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Anticipated Effects on Marine Mammal
Habitat
We do not anticipate that the
proposed operations would result in any
temporary or permanent effects on the
habitats used by the marine mammals in
the proposed area, including the food
sources they use (i.e., fish and
invertebrates). While NMFS anticipates
that the specified activity may result in
marine mammals avoiding certain areas
due to motorboat operations or human
presence, this impact to habitat is
temporary and reversible. NMFS
considered these as behavioral
modification. The main impact
associated with the proposed activity
will be temporarily elevated noise levels
and the associated direct effects on
marine mammals, previously discussed
in this notice. Based on the preceding
discussion, NMFS does not anticipate
that the proposed activity would have
any habitat-related effects that could
cause significant or long-term
consequences for individual marine
mammals or their populations.
Proposed Mitigation
In order to issue an incidental take
authorization 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 adverse
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
(where relevant). Applications for
incidental take authorizations must
include the availability and feasibility
(economic and technological) of
equipment, methods, and manner of
conducting the activity or other means
of effecting the least practicable adverse
impact on the affected species or stock
and their habitat 50 CFR 216.104(a)(11).
The Glacier Bay NP has reviewed the
following source documents and has
incorporated a suite of proposed
mitigation measures into their project
description.
(1) Recommended best practices in
Womble et al. (2013); Richardson et al.
(1995); Pierson et al. (1998); and Weir
and Dolman, (2007).
To reduce the potential for
disturbance from acoustic and visual
stimuli associated with the activities
Glacier Bay NP and/or its designees has
proposed to implement the following
mitigation measures for marine
mammals:
• Perform pre-survey monitoring
before deciding to access a study site;
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• Avoid accessing a site based on a
pre-determined threshold number of
animals present; sites used by pinnipeds
for pupping; or sites used by Steller sea
lions;
• Perform controlled and slow ingress
to the study site to prevent a stampede
and select a pathway of approach to
minimize the number of marine
mammals harassed;
• Monitor for offshore predators at
study sites. Avoid approaching the
study site if killer whales (Orcinus orca)
are present. If Glacier Bay NP and/or its
designees see predators in the area, they
must not disturb the pinnipeds until the
area is free of predators.
• Maintain a quiet research
atmosphere in the visual presence of
pinnipeds.
Pre-Survey Monitoring: Prior to
deciding to land onshore to conduct the
study, the researchers would use highpowered image stabilizing binoculars
from the watercraft to document the
number, species, and location of hauled
out marine mammals at each island. The
vessels would maintain a distance of
328 to 1,640 ft (100 to 500 m) from the
shoreline to allow the researchers to
conduct pre-survey monitoring. During
every visit, the researchers will examine
each study site closely using high
powered image stabilizing binoculars
before approaching at distances of
greater than 500 m (1,640 ft) to
determine and document the number,
species, and location of hauled out
marine mammals.
Site Avoidance: Researchers would
decide whether or not to approach the
island based on the species present,
number of individuals, and the presence
of pups. If there are high numbers (more
than 25) harbor seals hauled out (with
or without young pups present), any
time pups are present, or any time that
Steller sea lions are present, the
researchers will not approach the island
and will not conduct gull monitoring
research.
Controlled Landings: The researchers
would determine whether to approach
the island based on the number and
type of animals present. If the island has
25 or fewer individuals without pups,
the researchers would approach the
island by motorboat at a speed of
approximately 2 to 3 knots (2.3 to 3.4
mph). This would provide enough time
for any marine mammals present to
slowly enter the water without panic or
stampede. The researchers would also
select a pathway of approach farthest
from the hauled out harbor seals to
minimize disturbance.
Minimize Predator Interactions: If the
researchers visually observe marine
predators (i.e. killer whales) present in
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the vicinity of hauled out marine
mammals, the researchers would not
approach the study site.
Noise Reduction Protocols: While
onshore at study sites, the researchers
would remain vigilant for hauled out
marine mammals. If marine mammals
are present, the researchers would move
slowly and use quiet voices to minimize
disturbance to the animals present.
Mitigation Conclusions
NMFS has carefully evaluated Glacier
Bay NP’s proposed mitigation measures
in the context of ensuring that we
prescribe the means of effecting the least
practicable impact on the affected
marine mammal species and stocks and
their habitat. Our evaluation of potential
measures included consideration of the
following factors in relation to one
another:
• The manner in which, and the
degree to which, the successful
implementation of the measure is
expected to minimize adverse impacts
to marine mammals;
• The proven or likely efficacy of the
specific measure to minimize adverse
impacts as planned; and
• The practicability of the measure
for applicant implementation.
Any mitigation measure(s) prescribed
by NMFS should be able to accomplish,
have a reasonable likelihood of
accomplishing (based on current
science), or contribute to the
accomplishment of one or more of the
general goals listed here:
1. Avoidance or minimization of
injury or death of marine mammals
wherever possible (goals 2, 3, and 4 may
contribute to this goal).
2. A reduction in the numbers of
marine mammals (total number or
number at biologically important time
or location) exposed to motorboat
operations or visual presence that we
expect to result in the take of marine
mammals (this goal may contribute to 1,
above, or to reducing harassment takes
only).
3. A reduction in the number of times
(total number or number at biologically
important time or location) individuals
exposed to motorboat operations or
visual presence that we expect to result
in the take of marine mammals (this
goal may contribute to 1, above, or to
reducing harassment takes only).
4. A reduction in the intensity of
exposures (either total number or
number at biologically important time
or location) to motorboat operations or
visual presence that we expect to result
in the take of marine mammals (this
goal may contribute to a, above, or to
reducing the severity of harassment
takes only).
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5. Avoidance or minimization of
adverse effects to marine mammal
habitat, paying special attention to the
food base, activities that block or limit
passage to or from biologically
important areas, permanent destruction
of habitat, or temporary destruction/
disturbance of habitat during a
biologically important time.
6. For monitoring directly related to
mitigation—an increase in the
probability of detecting marine
mammals, thus allowing for more
effective implementation of the
mitigation.
Based on the evaluation of Glacier
Bay NP’s proposed measures, NMFS has
preliminarily determined that the
proposed mitigation measures provide
the means of effecting the least
practicable impact on marine mammal
species or stocks and their habitat,
paying particular attention to rookeries,
mating grounds, and areas of similar
significance.
Proposed Monitoring
In order to issue an ITA 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 we
expect to be present in the proposed
action area. Glacier Bay NP submitted a
marine mammal monitoring plan in
section 13 of their Authorization
application.
Monitoring measures prescribed by
NMFS should accomplish one or more
of the following general goals:
1. An increase in our understanding
of the likely occurrence of marine
mammal species in the vicinity of the
action, (i.e., presence, abundance,
distribution, and/or density of species).
2. An increase in our understanding
of the nature, scope, or context of the
likely exposure of marine mammal
species to any of the potential stressor(s)
associated with the action (e.g., sound
or visual stimuli), through better
understanding of one or more of the
following: The action itself and its
environment (e.g., sound source
characterization, propagation, and
ambient noise levels); the affected
species (e.g., life history or dive
pattern); the likely co-occurrence of
marine mammal species with the action
(in whole or part) associated with
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specific adverse effects; and/or the
likely biological or behavioral context of
exposure to the stressor for the marine
mammal (e.g., age class of exposed
animals or known pupping, calving or
feeding areas).
3. An increase in our understanding
of how individual marine mammals
respond (behaviorally or
physiologically) to the specific stressors
associated with the action (in specific
contexts, where possible, e.g., at what
distance or received level).
4. An increase in our understanding
of how anticipated individual
responses, to individual stressors or
anticipated combinations of stressors,
may impact either: The long-term fitness
and survival of an individual; or the
population, species, or stock (e.g.
through effects on annual rates of
recruitment or survival).
5. An increase in our understanding
of how the activity affects marine
mammal habitat, such as through effects
on prey sources or acoustic habitat (e.g.,
through characterization of longer-term
contributions of multiple sound sources
to rising ambient noise levels and
assessment of the potential chronic
effects on marine mammals).
6. An increase in understanding of the
impacts of the activity on marine
mammals in combination with the
impacts of other anthropogenic
activities or natural factors occurring in
the region.
7. An increase in our understanding
of the effectiveness of mitigation and
monitoring measures.
8. An increase in the probability of
detecting marine mammals (through
improved technology or methodology),
both specifically within the safety zone
(thus allowing for more effective
implementation of the mitigation) and
in general, to better achieve the above
goals.
As part of its Authorization
application, Glacier Bay NP proposes to
sponsor marine mammal monitoring
during the project, in order to
implement the mitigation measures that
require real-time monitoring, and to
satisfy the monitoring requirements of
the MMPA.
The Glacier Bay NP researchers will
monitor the area for pinnipeds during
all research activities. Monitoring
activities will consist of conducting and
recording observations on pinnipeds
within the vicinity of the proposed
research areas. The monitoring notes
would provide dates and location of the
researcher’s activities and the number
and type of species present. The
researchers would document the
behavioral state of animals present, and
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any apparent disturbance reactions or
lack thereof.
Glacier Bay NP can add to the
knowledge of pinnipeds in the proposed
action area by noting observations of: (1)
Unusual behaviors, numbers, or
distributions of pinnipeds, such that
any potential follow-up research can be
conducted by the appropriate personnel;
(2) tag-bearing carcasses of pinnipeds,
allowing transmittal of the information
to appropriate agencies and personnel;
and (3) rare or unusual species of
marine mammals for agency follow-up.
If at any time injury, serious injury, or
mortality of the species for which take
is authorized should occur, or if take of
any kind of any other marine mammal
occurs, and such action may be a result
of the proposed land survey, Glacier Bay
NP would suspend research and
monitoring activities and contact NMFS
immediately to determine how best to
proceed to ensure that another injury or
death does not occur and to ensure that
the applicant remains in compliance
with the MMPA.
Encouraging and Coordinating
Research
Glacier Bay NP actively monitors
harbor seals at breeding and molting
haul out locations to assess trends over
time (e.g., Mathews & Pendleton, 2006;
Womble et al. 2010, Womble and
Gende, 2013b). This monitoring
program involves collaborations with
biologists from the Alaska Department
of Fish and Game, and the National
Marine Mammal Laboratory. Glacier Bay
NP will continue these collaborations
and encourage continued or renewed
monitoring of marine mammal species.
Additionally, they would report vesselbased counts of marine mammals,
branded, or injured animals, and all
observed disturbances to the
appropriate state and federal agencies.
Proposed Reporting
Glacier Bay NP will submit a draft
monitoring report to us no later than 90
days after the expiration of the
Incidental Harassment Authorization, if
we issue it. The report will describe the
operations conducted and sightings of
marine mammals near the proposed
project. The report will provide full
documentation of methods, results, and
interpretation pertaining to all
monitoring. The report will provide:
1. A summary and table of the dates,
times, and weather during all research
activities.
2. Species, number, location, and
behavior of any marine mammals
observed throughout all monitoring
activities.
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3. An estimate of the number (by
species) of marine mammals exposed to
acoustic or visual stimuli associated
with the research activities.
4. A description of the
implementation and effectiveness of the
monitoring and mitigation measures of
the Authorization and full
documentation of methods, results, and
interpretation pertaining to all
monitoring.
In the unanticipated event that the
specified activity clearly causes the take
of a marine mammal in a manner
prohibited by the authorization, such as
an injury (Level A harassment), serious
injury, or mortality (e.g., vessel-strike,
stampede, etc.), Glacier Bay NP shall
immediately cease the specified
activities and immediately report the
incident to the Division Chief, Permits
and Conservation Division, Office of
Protected Resources, NMFS, at 301–
427–8401 and the Alaska Regional
Stranding Coordinator at (907) 586–
7248. The report must include the
following information:
• Time, date, and location (latitude/
longitude) of the incident;
• Description and location of the
incident (including water depth, if
applicable);
• Environmental conditions (e.g.,
wind speed and direction, Beaufort sea
state, cloud cover, and visibility);
• Description of all marine mammal
observations in the 24 hours preceding
the incident;
• Species identification or
description of the animal(s) involved;
• Fate of the animal(s); and
• Photographs or video footage of the
animal(s) (if equipment is available).
Glacier Bay NP shall not resume its
activities until NMFS is able to review
the circumstances of the prohibited
take. We will work with Glacier Bay to
determine what is necessary to
minimize the likelihood of further
prohibited take and ensure MMPA
compliance. Glacier Bay NP may not
resume their activities until notified by
us via letter, email, or telephone.
In the event that Glacier Bay NP
discovers an injured or dead marine
mammal, and the lead researcher
determines that the cause of the injury
or death is unknown and the death is
relatively recent (i.e., in less than a
moderate state of decomposition as we
describe in the next paragraph), Glacier
Bay NP will immediately report the
incident to the Division Chief, Permits
and Conservation Division, Office of
Protected Resources, NMFS, at 301–
427–8401 and the Alaska Regional
Stranding Coordinator at (907) 586–
7248. The report must include the same
information identified in the paragraph
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above this section. Activities may
continue while we review the
circumstances of the incident. We will
work with Glacier Bay NP to determine
whether modifications in the activities
are appropriate.
In the event that Glacier Bay NP
discovers an injured or dead marine
mammal, and the lead visual observer
determines that the injury or death is
not associated with or related to the
authorized activities (e.g., previously
wounded animal, carcass with moderate
to advanced decomposition, or
scavenger damage), Glacier Bay will
report the incident to the incident to the
Division Chief, Permits and
Conservation Division, Office of
Protected Resources, NMFS, at 301–
427–8401 and the Alaska Regional
Stranding Coordinator at (907) 586–
7248 within 24 hours of the discovery.
Glacier Bay NP researchers will provide
photographs or video footage (if
available) or other documentation of the
stranded animal sighting to us. Glacier
Bay NP can continue their research
activities.
Estimated Take by Incidental
Harassment
Except with respect to certain
activities not pertinent here, 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].
All anticipated takes would be by
Level B harassment, involving
temporary changes in behavior. NMFS
expects that the proposed mitigation
and monitoring measures would
minimize the possibility of injurious or
lethal takes. NMFS considers the
potential for take by injury, serious
injury, or mortality as remote. NMFS
expects that the presence of Glacier Bay
NP personnel could disturb animals
hauled out and that the animals may
alter their behavior or attempt to move
away from the researchers.
As discussed earlier, NMFS considers
an animal to have been harassed if it
moved greater than 1 m (3.3 ft) in
response to the surveyors’ presence or if
the animal was already moving and
changed direction and/or speed, or if
the animal flushed into the water.
NMFS does not consider animals that
became alert without such movements
as harassed.
Based on pinniped survey counts
conducted by Glacier Bay NP (e.g.,
Mathews & Pendleton, 2006; Womble et
al., 2010), NMFS estimates that the
research activities could potentially
affect by Level B behavioral harassment
500 harbor seals over the course of the
Authorization (Table 2). This estimate
represents 9.9 percent of the Glacier
Bay/Icy Strait stock of harbor seals and
accounts for a maximum disturbance of
25 harbor seals each per visit at Boulder,
Lone, and Flapjack Islands, and Geikie
Rock, Alaska over a maximum level of
five visits.
TABLE 2—ESTIMATES OF THE POSSIBLE NUMBERS OF MARINE MAMMALS EXPOSED TO ACOUSTIC AND VISUAL STIMULI
DURING THE PROPOSED RESEARCH ACTIVITIES ON BOULDER, LONE, AND FLAPJACK ISLANDS, AND GEIKIE ROCK,
ALASKA, MAY THROUGH SEPTEMBER, 2015
Estimated
number of
individuals
exposed
Species
Harbor seal .........................................................................................................
Steller sea lion ...................................................................................................
Proposed take
authorization
500
0
500
0
Percent of
species or
stock 1
9.9
0
Population
trend 2
Declining.
Increasing.
1 Table
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2 The
1 in this notice lists the stock species abundance estimates that NMFS used to calculate the percentage of species/stock.
population trend information is from Allen and Angliss, 2014. No data = Insufficient data to determine population trend.
Harbor seals tend to haul out in small
numbers (on average, less than 50
animals) at most sites with the
exception of Flapjack Island (Womble,
Pers. Comm.). Animals on Flapjack
Boulder Islands generally haul out on
the south side of the Islands and are not
located near the research sites located
on the northern side of the Islands.
Aerial survey maximum counts show
that harbor seals sometimes haul out in
large numbers at all four locations (see
Table 2 in Glacier Bays NP’s
application), and sometimes individuals
and mother/pup pairs occupy different
terrestrial locations than the main
haulout (J. Womble, personal
observation).
Considering the conservation status
for the Western stock of the Steller sea
lion, the Glacier Bay NP researchers
would not conduct ground-based or
vessel-based surveys if they observe
Steller sea lions before accessing
Boulder, Lone, and Flapjack Islands,
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and Geikie Rock. Thus, NMFS expects
no takes to occur for this species during
the proposed activities.
NMFS does not propose to authorize
any injury, serious injury, or mortality.
NMFS expect all potential takes to fall
under the category of Level B
harassment only.
Analysis and Preliminary
Determinations
Negligible Impact
Negligible impact’ is ‘‘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). The lack of likely
adverse effects on annual rates of
recruitment or survival (i.e., population
level effects) forms the basis of a
negligible impact finding. An estimate
of the number of Level B harassment
takes alone is not enough information
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on which to base an impact
determination. In addition to
considering estimates of the number of
marine mammals that might be ‘‘taken’’
through behavioral harassment, NMFS
considers other factors, such as the
likely nature of any responses (e.g.,
intensity, duration), the context of any
responses (e.g., critical reproductive
time or location, migration), as well as
the number and nature of estimated
Level A harassment takes, the number of
estimated mortalities, and effects on
habitat.
Although Glacier Bay NP’s survey
activities may disturb harbor seals
hauled out at the survey sites, NMFS
expects those impacts to occur to a
small, localized group of animals for a
limited duration (e.g., 30 minutes to two
hours each visit). Pinnipeds would
likely become alert or, at most, flush
into the water in reaction to the
presence of Glacier Bay NP personnel
during the proposed activities.
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Disturbance will be limited to a short
duration, allowing the animals to
reoccupy the island within a short
amount of time. Thus, the proposed
action is unlikely to result in long-term
impacts such as permanent
abandonment of the haul-out.
For reasons stated previously in this
document and based on the following
factors, Glacier Bay NP’s specified
activities are not likely to cause longterm behavioral disturbance, injury,
serious injury, or death. These reasons
include:
1. The effects of the research activities
would be limited to short-term
responses and temporary behavioral
changes due to the short and sporadic
duration of the research activities.
Minor and brief responses are not likely
to constitute disruption of behavioral
patterns, such as migration, nursing,
breeding, feeding, or sheltering.
2. The availability of alternate areas
for pinnipeds to avoid the resultant
disturbances from the research
operations. Anecdotal reports from
previous Glacier Bay NP activities have
shown that the pinnipeds returned to
the various sites and did not
permanently abandon haul-out sites
after Glacier Bay NP conducted their
research activities.
3. There is no potential for large-scale
movements leading to injury, serious
injury, or mortality because the
researchers would delay ingress into the
landing areas only after the pinnipeds
have slowly entered the water.
4. Glacier Bay NP will limit access to
Boulder, Lone, and Flapjack Islands,
and Geikie Rock when there are high
numbers (more than 25) harbor seals
hauled out (with or without young pups
present), any time pups are present, or
any time that Steller sea lions are
present, the researchers will not
approach the island and will not
conduct gull monitoring research.
NMFS does not anticipate that any
injuries, serious injuries, or mortalities
would occur as a result of Glacier Bay
NP’s proposed activities with the
mitigation and related monitoring, and
NMFS does not propose to authorize
injury, serious injury, or mortality at
this time. In addition, the research
activities would not take place in areas
of significance for marine mammal
feeding, resting, breeding, or calving
and would not adversely impact marine
mammal habitat.
Due to the nature, degree, and context
of Level B (behavioral) harassment
anticipated and described (see
‘‘Potential Effects on Marine Mammals’’
section in this notice), we do not expect
the activity to impact annual rates of
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recruitment or survival for any affected
species or stock.
In summary, NMFS anticipates that
impacts to hauled-out harbor seals
during Glacier Bay NP’s research
activities would be behavioral
harassment of limited duration (i.e., up
to two hours per visit) and limited
intensity (i.e., temporary flushing at
most). NMFS does not expect
stampeding, and therefore injury or
mortality, to occur (see ‘‘Mitigation’’ for
more details). 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 proposed monitoring and
mitigation measures, NMFS
preliminarily finds that the total marine
mammal take from Glacier Bay’s
proposed research activities will have a
negligible impact on the affected marine
mammal species or stocks.
Small Numbers
As mentioned previously, NMFS
estimates that Glacier Bay NP’s
activities could potentially affect, by
Level B harassment only, one species of
marine mammal under our jurisdiction.
For harbor seals, this estimate is small
(9.9 percent) relative to the population
size and we have provided the
percentage of the harbor seal’s regional
population estimate that the activities
may take by Level B harassment in
Table 2 in this notice.
Based on the analysis contained in
this notice of the likely effects of the
specified activity on marine mammals
and their habitat, and taking into
consideration the implementation of the
mitigation and monitoring measures,
NMFS preliminarily finds that Glacier
Bay NP’s proposed activities would take
small numbers of marine mammals
relative to the populations of the
affected species or stocks.
Impact on Availability of Affected
Species or Stock for Taking for
Subsistence Uses
There are no relevant subsistence uses
of marine mammals implicated by this
action. Glacier Bay National Park
prohibits subsistence harvest of harbor
seals within the Park (Catton, 1995).
Endangered Species Act (ESA)
NMFS does not expect that Glacier
Bay NP’s proposed research activities
(which includes mitigation measures to
avoid harassment of Steller sea lions)
would affect any species listed under
the ESA. Therefore, NMFS has
determined that a section 7 consultation
under the ESA is not required.
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National Environmental Policy Act
(NEPA)
In 2014, NMFS prepared an
Environmental Assessment (EA)
analyzing the potential effects to the
human environment from NMFS’
issuance of a Authorization to Glacier
Bay NP for their seabird research
activities.
In September 2014, NMFS issued a
Finding of No Significant Impact
(FONSI) on the issuance of an
Authorization for Point Blue’s research
activities in accordance with section
6.01 of the NOAA Administrative Order
216–6 (Environmental Review
Procedures for Implementing the
National Environmental Policy Act, May
20, 1999). Glacier Bay NP’s proposed
activities and impacts for 2015 are
within the scope of the 2014 EA and
FONSI. NMFS provided relevant
environmental information to the public
through a previous notice for the
proposed Authorization (79 FR 32226,
June 4, 2014) and considered public
comments received in response prior to
finalizing the 2014 EA and deciding
whether or not to issue a Finding of No
Significant Impact (FONSI).
NMFS has reviewed the 2014 EA and
determined that there are no new direct,
indirect, or cumulative impacts to the
human and natural environment
associated with the Authorization
requiring evaluation in a supplemental
EA and NMFS, therefore, proposes to
reaffirm the 2014 FONSI. NMFS’ EA
and FONSI for this activity are available
upon request (see ADDRESSES).
Proposed Authorization
As a result of these preliminary
determinations, NMFS proposes issuing
an Incidental Harassment Authorization
to Glacier Bay National Park for
conducting seabird research May
through September, 2015, provided they
incorporate the previously mentioned
mitigation, monitoring, and reporting
requirements.
Draft Proposed Authorization
This section contains the draft text for
the proposed Authorization. NMFS
proposes to include this language in the
Authorization if issued.
Proposed Authorization Language
Glacier Bay National Park, P.O. Box
140, Gustavus, Alaska 99826 and/or its
designees (holders of the Authorization)
are hereby authorized under section
101(a)(5)(D) of the Marine Mammal
Protection Act (16 U.S.C. 1371(a)(5)(D))
to harass small numbers of marine
mammals incidental to conducting
monitoring and research studies on
glaucus-winged gulls (Larus
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glaucescens) within Glacier Bay
National Park and Preserve in Alaska.
1. This Authorization is valid from
May 15 through September 30, 2015.
2. This Authorization is valid only for
research activities that occur in the
following specified geographic areas:
Boulder (58°33′18.08″ N; 136°1′13.36″
W); Lone (58°43′17.67″ N; 136°17′41.32″
W), and Flapjack (58°35′10.19″ N;
135°58′50.78″ W) Islands, and Geikie
Rock (58°41′39.75″ N; 136°18′39.06″ W);
and Tlingit Point Islet (58°45′16.86″ N;
136°10′41.74″ W) in Glacier Bay, Alaska.
3. Species Authorized and Level of
Takes
a. The taking, by Level B harassment
only, is limited to the following species:
500 Pacific harbor seals (Phoca
vitulina).
b. The taking by injury (Level A
harassment), serious injury or death of
any of the species listed in Condition
3(a) or the taking of any kind of any
other species of marine mammal is
prohibited and may result in the
modification, suspension or revocation
of this Authorization.
c. The taking of any marine mammal
in a manner prohibited under this
Authorization must be reported
immediately to the Chief, Permits and
Conservation Division, Office of
Protected Resources, NMFS, at (301)
427–8401.
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4. General Conditions
A copy of this Authorization must be
in the possession of Glacier Bay
National Park, its designees, and field
crew personnel (including research
collaborators) operating under the
authority of this Authorization at all
times.
5. Mitigation Measures
The Holder of this Authorization is
required to implement the following
mitigation measures:
a. Conduct pre-survey monitoring
before deciding to access a study site.
Prior to deciding to land onshore of
Boulder, Lone, or Flapjack Island or
Geikie Rock, the Holder of this
Authorization will use high-powered
image stabilizing binoculars before
approaching at distances of greater than
500 m (1,640 ft) to determine and
document the number, species, and
location of hauled out marine
mammals.. The vessels will maintain a
distance of 328 to 1,640 ft (100 to 500
m) from the shoreline.
i. If the Holder of the Authorization
determines that there are 25 or more
harbor seals (with or without young
pups present) hauled out on the
shoreline, the holder will not access the
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island and will not conduct the study at
that time.
ii. If the Holder of the Authorization
determines that any Steller sea lions
(Eumetopias jubatus) are present at the
study site, the Holder will not access the
island and will not conduct the study at
that time.
iii. If the Holder of the Authorization
determines that there are any pups
hauled out on the shoreline and
vulnerable to being separated from their
mothers, the Holder will not access the
island and will not conduct the study at
that time.
b. Minimize the potential for
disturbance by: (1) Performing
controlled and slow ingress to the study
site to prevent a stampede; and (2)
selecting a pathway of approach farthest
from the hauled out harbor seals to
minimize disturbance.
c. Monitor for offshore predators at
the study sites and avoid research
activities when predators area present.
Avoid approaching the study site if
killer whales (Orcinus orca) are present.
If the Holder of this Authorization
observes predators in the area, they
must not disturb the pinnipeds until the
area is free of predators.
d. Maintain a quiet working
atmosphere, avoid loud noises, and use
hushed voices in the presence of hauled
out pinnipeds.
6. Monitoring
Glacier Bay NP is required to record
the following:
a. BLM and/or its designees shall
record the following:
i. Species counts (with numbers of
adults/juveniles); and:
ii. Numbers of disturbances, by
species and age, according to a threepoint scale of intensity including: (1)
Head orientation in response to
disturbance, which may include turning
head towards the disturbance, craning
head and neck while holding the body
rigid in a u-shaped position, or changing
from a lying to a sitting position and/or
slight movement of less than 1 meter;
‘‘alert’’; (2) Movements in response to or
away from disturbance, typically over
short distances (1–3 meters) and
including dramatic changes in direction
or speed of locomotion for animals
already in motion; ‘‘movement’’; and (3)
All flushes to the water as well as
lengthier retreats (>3 meters); ‘‘flight’’.
iii. Information on the weather,
including the tidal state and horizontal
visibility.
b. If applicable, the observer shall
note observations of marked or tagbearing pinnipeds or carcasses, as well
as any rare or unusual species of marine
mammal.
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c. If applicable, the observer shall
note the presence of any offshore
predators (date, time, number, and
species).
7. Reporting
The holder of this Authorization is
required to:
a. Draft Report: Submit a draft
monitoring report to the Division Chief,
Permits and Conservation Division,
Office of Protected Resources, National
Marine Fisheries Service within 90 days
after the Authorization expires. NMFS
will review the Draft Report which is
subject to review and comment by
NMFS. Glacier Bay NP must address
any recommendations made by NMFS
in the Final Report prior to submission
to NMFS. If NMFS decides that the draft
final report needs no comments, NMFS
will consider the draft report as the
Final Report.
b. Final Report: Glacier Bay shall
prepare and submit a Final Report to
NMFS within 30 days following
resolution of any comments on the draft
report from NMFS.
8. Reporting Injured or Dead Marine
Mammals
In the unanticipated event that the
specified activity clearly causes the take
of a marine mammal in a manner
prohibited by the authorization, such as
an injury (Level A harassment), serious
injury, or mortality (e.g., vessel-strike,
stampede, etc.), BLM and/or its
designees shall immediately cease the
specified activities and immediately
report the incident to the Division Chief,
Permits and Conservation Division,
Office of Protected Resources, NMFS, at
301–427–8401 and the Alaska Regional
Stranding Coordinator at (907) 586–
7248. The report must include the
following information:
• Time, date, and location (latitude/
longitude) of the incident;
• Description and location of the
incident (including water depth, if
applicable);
• Environmental conditions (e.g.,
wind speed and direction, Beaufort sea
state, cloud cover, and visibility);
• Description of all marine mammal
observations in the 24 hours preceding
the incident;
• Species identification or
description of the animal(s) involved;
• Fate of the animal(s); and
• Photographs or video footage of the
animal(s) (if equipment is available).
Glacier Bay NP shall not resume its
activities until NMFS is able to review
the circumstances of the prohibited
take. NMFS will work with Glacier Bay
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Federal Register / Vol. 80, No. 65 / Monday, April 6, 2015 / Notices
NP to determine what is necessary to
minimize the likelihood of further
prohibited take and ensure MMPA
compliance. Glacier Bay NP may not
resume their activities until notified by
us via letter, email, or telephone.
In the event that Glacier Bay NP
discovers an injured or dead marine
mammal, and the marine mammal
observer determines that the cause of
the injury or death is unknown and the
death is relatively recent (i.e., in less
than a moderate state of decomposition
as we describe in the next paragraph),
Glacier Bay NP will immediately report
the incident to the Division Chief,
Permits and Conservation Division,
Office of Protected Resources, NMFS, at
301–427–8401 and the Alaska Regional
Stranding Coordinator at (907) 586–
7248. The report must include the same
information identified in the paragraph
above this section. Activities may
continue while NMFS reviews the
circumstances of the incident. NMFS
would work with Glacier Bay NP to
determine whether modifications in the
activities are appropriate.
In the event that Glacier Bay NP
discovers an injured or dead marine
mammal, and the lead visual observer
determines that the injury or death is
not associated with or related to the
authorized activities (e.g., previously
wounded animal, carcass with moderate
to advanced decomposition, or
scavenger damage), Glacier Bay NP will
report the incident to the Division Chief,
Permits and Conservation Division,
Office of Protected Resources, NMFS, at
301–427–8401 and the Alaska Regional
Stranding Coordinator at (907) 586–
7248 within 24 hours of the discovery.
Glacier Bay NP personnel will provide
photographs or video footage (if
available) or other documentation of the
stranded animal sighting to us. Glacier
Bay NP can continue their survey
activities while NMFS reviews the
circumstances of the incident.
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Request for Public Comments
NMFS invites comments on our
analysis, the draft authorization, and
any other aspect of the notice of
proposed Authorization for Glacier Bay
NP’s activities. Please include any
supporting data or literature citations
with your comments to help inform our
final decision on Glacier Bay NP’s
request for an Authorization.
Dated: March 31, 2015.
Donna S. Wieting,
Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. 2015–07734 Filed 4–3–15; 8:45 am]
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DEPARTMENT OF COMMERCE
International Trade Administration
[C–570–025, C–533–862, C–523–811]
Certain Polyethylene Terephthalate
Resin From the People’s Republic of
China, India, and the Sultanate of
Oman: Initiation of Countervailing Duty
Investigations
Enforcement and Compliance,
International Trade Administration,
Department of Commerce.
DATES: Effective April 6, 2015.
FOR FURTHER INFORMATION CONTACT:
Yasmin Nair at (202) 482–3813 or Ilissa
Shefferman at (202) 482–4684, AD/CVD
Operations, Enforcement and
Compliance, International Trade
Administration, U.S. Department of
Commerce, 14th Street and Constitution
Avenue NW., Washington, DC 20230.
SUPPLEMENTARY INFORMATION:
AGENCY:
The Petitions
On March 10, 2015, the Department of
Commerce (Department) received
countervailing duty (CVD) petitions
concerning imports of certain
polyethylene terephthalate resin (PET
resin) from the People’s Republic of
China (PRC), India, and the Sultanate of
Oman (Oman) filed in proper form on
behalf of DAK Americas, LLC; M&G
Chemicals; and Nan Ya Plastic
Corporation, America (collectively,
Petitioners). The CVD petitions were
accompanied by antidumping duty (AD)
petitions also concerning imports of
PET resin from Canada, the PRC, India,
and Oman.1 Petitioners are domestic
producers of PET resin.2
On March 13, 2015, the Department
requested information and clarification
for certain areas of the Petitions.3
1 See ‘‘Petitions for the Imposition of
Antidumping Duties on Imports of Certain
Polyethylene Terephthalate Resin from Canada, The
People’s Republic of China, India, and the Sultanate
of Oman and Countervailing Duties on Imports from
The People’s Republic of China, India, and the
Sultanate of Oman,’’ dated March 10, 2015
(Petitions).
2 See Volume I of the Petitions, at I–2 and Exhibit
I–2.
3 See Letter from the Department to Petitioners
entitled ‘‘Petition for the Imposition of
Countervailing Duties on Imports of Certain
Polyethylene Terephthalate Resin from the People’s
Republic of China (PRC): Supplemental Questions,’’
dated March 13, 2015 (PRC Deficiency
Questionnaire); Letter from the Department to
Petitioners entitled ‘‘Petition for the Imposition of
Countervailing Duties on Imports of Certain
Polyethylene Terephthalate Resin from India:
Supplemental Questions,’’ dated March 13, 2015
(India Deficiency Questionnaire); Letter from the
Department to Petitioners entitled ‘‘Petition for the
Imposition of Countervailing Duties on Imports of
Certain Polyethylene Terephthalate Resin from the
Sultanate of Oman: Supplemental Questions,’’
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18369
Petitioners filed responses to these
requests on March 17 and 19, 2015.4
Petitioners filed a revised scope on
March 24, 2015.5
In accordance with section 702(b)(1)
of the Tariff Act of 1930, as amended
(the Act), Petitioners allege that the
Government of the PRC (GOC), the
Government of India (GOI), and the
Government of the Sultanate of Oman
(GSO) are providing countervailable
subsidies (within the meaning of
sections 701 and 771(5) of the Act) to
imports of certain PET resin from the
PRC, India and Oman, respectively, and
that such imports are materially
injuring, or threatening material injury
to, an industry in the United States.
Also, consistent with section 702(b)(1)
of the Act, the Petitions are
accompanied by information reasonably
available to Petitioners supporting their
allegations.
The Department finds that Petitioners
filed the Petitions on behalf of the
domestic industry because Petitioners
are interested parties as defined in
sections 771(9)(C) and (D) of the Act.
The Department also finds that
Petitioners demonstrated sufficient
industry support with respect to the
initiation of the CVD investigations that
Petitioners are requesting.6
Period of Investigation
The period of investigation for the
PRC, India and Oman is January 1, 2014,
through December 31, 2014.7
Scope of the Investigations
The product covered by these
investigations is PET resin from the
dated March 13, 2015 (Oman Deficiency
Questionnaire); Letter from the Department to
Petitioners entitled ‘‘Petition for the Imposition of
Countervailing Duties on Imports of Certain
Polyethylene Terephthalate Resin from Canada, the
People’s Republic of China, India, and the Sultanate
of Oman: Supplemental Questions,’’ dated March
13, 2015 (General Issues Supplement).
4 See Letter from Petitioners entitled ‘‘Certain
Polyethylene Terephthalate Resin From The
People’s Republic Of China—Petitioners’ Response
To Supplemental Questionnaire,’’ dated March 17,
2015 (PRC CVD Supplement); Letter from
Petitioners entitled ‘‘Certain Polyethylene
Terephthalate Resin From India—Petitioners’
Response To Supplemental Questionnaire,’’ dated
March 17, 2015 (India CVD Supplement); Letter
from Petitioners entitled ‘‘Certain Polyethylene
Terephthalate Resin From the Sultanate of Oman—
Petitioners’ Response To Supplemental
Questionnaire,’’ dated March 17, 2015 (Oman CVD
Supplement); and Letter from Petitioners entitled
‘‘Certain Polyethylene Terephthalate Resin From
The People’s Republic Of China, India, and the
Sultanate of Oman—Petitioner’s Response to
Supplemental Questionnaire,’’ dated March 19,
2015 (General Issues Supplement).
5 See Scope Supplement to the Petitions, dated
March 24, 2015 (Scope Supplement).
6 See the ‘‘Determination of Industry Support for
the Petitions’’ section below.
7 19 CFR 351.204(b)(2).
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Agencies
[Federal Register Volume 80, Number 65 (Monday, April 6, 2015)]
[Notices]
[Pages 18359-18369]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2015-07734]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XD815
Takes of Marine Mammals Incidental to Specified Activities;
Seabird Monitoring and Research in Glacier Bay National Park, Alaska,
2015
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; proposed incidental harassment authorization; request
for comments.
-----------------------------------------------------------------------
SUMMARY: NMFS has received an application from Glacier Bay National
Park (Glacier Bay NP) to take marine mammals, by harassment, incidental
to conducting seabird research from May through September, 2015. The
proposed dates for this action are May 15, 2015, through September 30,
2015. Per the Marine Mammal Protection Act, we are requesting comments
on our proposal to issue an Authorization to the Glacier Bay NP to
incidentally take, by Level B harassment only, one species of marine
mammal during the specified activity.
DATES: NMFS must receive comments and information on or before May 6,
2015.
ADDRESSES: Address comments on the application to Jolie Harrison,
Division Chief, Permits and Conservation Division, Office of Protected
Resources, National Marine Fisheries Service, 1315 East-West Highway,
Silver Spring, MD 20910. The mailbox address for providing email
comments is ITP.Cody@noaa.gov. Please include 0648-XD815 in the subject
line. Comments sent via email to ITP.Cody@noaa.gov, including all
attachments, must not exceed a 25-megabyte file size. NMFS is not
responsible for email comments sent to addresses other than the one
provided here.
Instructions: All submitted comments are a part of the public
record and NMFS will post them to https://www.nmfs.noaa.gov/pr/permits/incidental/research.htm without change. All Personal Identifying
Information (for example, name, address, etc.) voluntarily submitted by
the commenter may be publicly accessible. Do not submit confidential
business information or otherwise sensitive or protected information.
To obtain an electronic copy of the application containing a list
of the references used in this document, write to the previously
mentioned address, telephone the contact listed here (see FOR FURTHER
INFORMATION CONTACT), or visit the Internet at: https://www.nmfs.noaa.gov/pr/permits/incidental/research.htm.
Information in Glacier Bay NP's application, NMFS' 2014
Environmental Assessment titled, Environmental Assessment for the
Issuance of an Incidental Harassment Authorization to Take Marine
Mammals by Harassment Incidental to Conducting Seabird Research in
Glacier Bay Alaska, and this notice collectively provide the
environmental information related to proposed issuance of the
Authorization for public review and comment.
FOR FURTHER INFORMATION CONTACT: Jeannine Cody, NMFS, Office of
Protected Resources, NMFS (301) 427-8401.
[[Page 18360]]
SUPPLEMENTARY INFORMATION:
Background
Section 101(a)(5)(D) of the Marine Mammal Protection Act of 1972,
as amended (MMPA; 16 U.S.C. 1361 et seq.) directs the Secretary of
Commerce to allow, upon request, the incidental, but not intentional,
taking of small numbers of marine mammals of a species or population
stock, by U.S. citizens who engage in a specified activity (other than
commercial fishing) within a specified geographical region if, after
NMFS provides a notice of a proposed authorization to the public for
review and comment: (1) NMFS makes certain findings; and (2) the taking
is limited to harassment.
An Authorization shall be granted for the incidental taking of
small numbers of marine mammals 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 subsistence uses (where relevant). The Authorization must
also set forth the permissible methods of taking; other means of
effecting the least practicable adverse impact on the species or stock
and its habitat; and requirements pertaining to the monitoring and
reporting of such taking. NMFS has defined ``negligible impact'' in 50
CFR 216.103 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.''
Except with respect to certain activities not pertinent here, 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].
Summary of Request
On January 15, 2015, NMFS received an application from Glacier Bay
NP requesting that we issue an Authorization for the take of marine
mammals, incidental to conducting monitoring and research studies on
glaucus-winged gulls (Larus glaucescens) within Glacier Bay National
Park and Preserve in Alaska. NMFS determined the application complete
and adequate on February 27, 2015. NMFS previously issued an
Authorization to Glacier Bay NP for the same activities in 2014 (79 FR
56065, September 18, 2014). No seabird research activities occurred
during the effective period of the prior Authorization.
Glacier Bay NP proposes to conduct ground-based and vessel-based
surveys to collect data on the number and distribution of nesting gulls
within five study sites in Glacier Bay, AK. Glacier Bay NP proposes to
complete up to five visits per study site, from May through September,
2015.
The proposed activities are within the vicinity of pinniped haulout
sites and the following aspects of the proposed activities are likely
to result in the take of marine mammals: Noise generated by motorboat
approaches and departures; noise generated by researchers while
conducting ground surveys; and human presence during the monitoring and
research activities. NMFS anticipates that take by Level B harassment
only, of individuals of harbor seals (Phoca vitulina) would result from
the specified activity. Although Steller sea lions (Eumetopias jubatus)
may be present in the action area, Glacier Bay NP has proposed to avoid
any site used by Steller sea lions.
Description of the Specified Activity
Overview
Glacier Bay NP proposes to identify the onset of gull nesting;
conduct mid-season surveys of adult gulls, and locate and document gull
nest sites within the following study areas: Boulder, Lone, and
Flapjack Islands, and Geikie Rock. Each of these study sites contains
harbor seal haulout sites and Glacier Bay NP proposes to visit each
study site up to five times during the research season.
Glacier Bay NP must conduct the gull monitoring studies to meet the
requirements of a 2010 Record of Decision for a Legislative
Environmental Impact Statement (NPS, 2010) which states that Glacier
Bay NP must initiate a monitoring program for the gulls to inform
future native egg harvests by the Hoonah Tlingit in Glacier Bay, AK.
Glacier Bay NP actively monitors harbor seals at breeding and molting
sites to assess population trends over time (e.g., Mathews & Pendleton,
2006; Womble et al., 2010). Glacier Bay NP also coordinates pinniped
monitoring programs with NMFS' National Marine Mammal Laboratory and
the Alaska Department of Fish & Game and plans to continue these
collaborations and sharing of monitoring data and observations in the
future.
Dates and Duration
Glacier Bay NP proposes to conduct the proposed activities from the
period of May 15 through September 30, 2015. Glacier Bay NP proposes to
conduct a maximum of three ground-based surveys per each study site and
a maximum of two vessel-based surveys per each study site.
Thus, the proposed Authorization, if issued, would be effective
from May 15, 2015 through September 30, 2015. NMFS refers the reader to
the Detailed Description of Activities section later in this notice for
more information on the scope of the proposed activities.
Specified Geographic Region
The proposed study sites would occur in the vicinity of the
following locations: Boulder (58[deg]33'18.08'' N; 136[deg]1'13.36''
W), Lone (58[deg]43'17.67'' N; 136[deg]17'41.32'' W), and Flapjack
(58[deg]35'10.19'' N; 135[deg]58'50.78'' W) Islands, and Geikie Rock
(58[deg]41'39.75'' N; 136[deg]18'39.06'' W) in Glacier Bay, Alaska.
Glacier Bay NP will also conduct studies at Tlingit Point Islet located
at 58[deg]45'16.86'' N; 136[deg]10'41.74'' W; however, there are no
reported pinniped haulout sites at that location.
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Detailed Description of Activities
Glacier Bay NP proposes to conduct: (1) Ground-based surveys at a
maximum frequency of three visits per site; and (2) vessel-based
surveys at a maximum frequency of two visits per site from the period
of May 15 through September 30, 2015.
Ground-Based Surveys: These surveys involve two trained observers
visiting the largest gull colony on each island to: (1) Obtain
information on the numbers of nests, their location, and contents
(i.e., eggs or chicks); (2) determine the onset of laying,
distribution, abundance, and predation of gull nests and eggs; and (3)
record the proximity of other species relative to colony locations.
The observers would access each island using a kayak, a 32.8 to
39.4-foot (ft) (10 to 12 meter (m)) motorboat, or a 12 ft (4 m)
inflatable rowing dinghy. The landing craft's transit speed would not
exceed 4 knots (4.6 miles per hour (mph). Ground surveys generally last
from 30 minutes to up to two hours depending on the size of the island
and the number of nesting gulls. Glacier Bay NP will discontinue ground
surveys after they detect the first hatchling to minimize disturbance
to the gull colonies.
Vessel-Based Surveys: These surveys involve two trained observers
observing and counting the number of adult and fledgling gulls from the
deck of a motorized vessel which would transit around each island at a
distance of approximately 328 ft (100 m) to avoid flushing the birds
from the colonies. Vessel-based surveys generally last from 30 minutes
to up to two hours
[[Page 18362]]
depending on the size of the island and the number of nesting gulls.
Description of Marine Mammals in the Area of the Specified Activity
Table 1 in this notice provides the following information: All
marine mammal species with possible or confirmed occurrence in the
proposed survey areas on land; information on those species' regulatory
status under the MMPA and the Endangered Species Act of 1973 (16 U.S.C.
1531 et seq.); abundance; occurrence and seasonality in the activity
area.
Table 1--General Information on Marine Mammals That Could Potentially Haul Out in the Proposed Study Areas in May Through September, 2015
--------------------------------------------------------------------------------------------------------------------------------------------------------
Regulatory status \1\ Stock/Species
Species Stock name \2\ abundance \3\ Occurrence and range Season
--------------------------------------------------------------------------------------------------------------------------------------------------------
Harbor seal (Phoca vitulina)....... Glacier Bay/Icy Strait MMPA-NC ESA-NL........ 5,042................ common coastal....... year-round
Steller sea lion (Eumetopias Eastern U.S........... MMPA-D, S ESA-NL...... 63,160-78,198........ uncommon coastal..... year-round
jubatus).
Steller sea lion (Eumetopias Western U.S........... MMPA-D, S ESA-T....... 52,200............... rare coastal......... unknown
jubatus).
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ MMPA: D = Depleted, S = Strategic, NC = Not Classified.
\2\ ESA: EN = Endangered, T = Threatened, DL = Delisted, NL = Not listed.
\3\ 2013 NMFS Stock Assessment Report (Allen and Anglis, 2014).
NMFS refers the public to the Glacier Bay NP's application and the
2014 NMFS Marine Mammal Stock Assessment Report available online at:
https://www.nmfs.noaa.gov/pr/sars/species.htm for further information on
the biology and local distribution of these species.
Other Marine Mammals in the Proposed Action Area
Northern sea otters (Enhydra lutris kenyoni) and polar bears (Ursis
maritimus) listed as threatened under the Endangered Species Act could
occur in the proposed area. The U.S. Fish and Wildlife Service manages
these species and NMFS does not consider them further in this notice.
Potential Effects of the Specified Activities on Marine Mammals
This section includes a summary and discussion of the ways that the
types of stressors associated with the specified activity (e.g.,
personnel presence) have been observed to impact marine mammals. This
discussion may also include reactions that NMFS considers to rise to
the level of a take and those that we do not consider to rise to the
level of a take. This section serves as a background of potential
effects and does not consider either the specific manner in which the
applicant will carry out the activity or the mitigation that will be
implemented, and how either of those will shape the anticipated impacts
from this specific activity. The ``Estimated Take by Incidental
Harassment'' section later in this document will include a quantitative
analysis of the number of individuals that NMFS expects Glacier Bay NP
to take during this activity. The ``Negligible Impact Analysis''
section will include the analysis of how this specific activity would
impact marine mammals. NMFS will consider the content of the following
sections: Estimated Take by Incidental Harassment; Proposed Mitigation;
and Anticipated Effects on Marine Mammal Habitat, to draw conclusions
regarding the likely impacts of this activity on the reproductive
success or survivorship of individuals--and from that consideration--
the likely impacts of this activity on the affected marine mammal
populations or stocks.
Potential Effects of Human Presence on Marine Mammals
The appearance of Glacier Bay researchers has the potential to
cause Level B harassment of pinnipeds hauled out on Boulder, Lone, and
Flapjack Islands, and Geikie Rock. Disturbance includes a variety of
effects, including subtle to conspicuous changes in behavior, movement,
and displacement. Disturbance may result in reactions ranging from an
animal simply becoming alert to the presence of the surveyors (e.g.,
turning the head, assuming a more upright posture) to flushing from the
haul-out site into the water. NMFS does not consider the lesser
reactions to constitute behavioral harassment, or Level B harassment
takes, but rather assumes that pinnipeds that move greater than 1 meter
(m) (3.3 feet (ft)) or change the speed or direction of their movement
in response to the presence of surveyors are behaviorally harassed, and
thus subject to Level B taking. Animals that respond to the presence of
researchers by becoming alert, but that do not move or change the
nature of locomotion as described, are not considered to have been
subject to behavioral harassment.
Reactions to human presence, if any, depend on species, state of
maturity, experience, current activity, reproductive state, time of
day, and many other factors (Richardson et al., 1995; Wartzok et al.,
2004; Southall et al., 2007; Weilgart, 2007). These behavioral
reactions are often shown as: Changing durations of surfacing and
dives, number of blows per surfacing, or moving direction and/or speed;
reduced/increased vocal activities; changing/cessation of certain
behavioral activities (such as socializing or feeding); visible startle
response or aggressive behavior; avoidance of areas; and/or flight
responses (e.g., pinnipeds flushing into the water from haul-outs or
rookeries). If a marine mammal does react briefly to human presence by
changing its behavior or moving a small distance, the impacts of the
change are unlikely to be significant to the individual, let alone the
stock or population. However, if visual stimuli from human presence
displaces marine mammals from an important feeding or breeding area for
a prolonged period, impacts on individuals and populations could be
significant (e.g., Lusseau and Bejder, 2007; Weilgart, 2007).
Disturbances resulting from human activity can impact short- and
long-term pinniped haul out behavior (Renouf et al., 1981; Schneider
and Payne, 1983; Terhune and Almon, 1983; Allen et al., 1984; Stewart,
1984; Suryan and Harvey, 1999; Mortenson et al., 2000; and Kucey and
Trites, 2006). Numerous studies have shown that human activity can
flush harbor seals off haulout sites (Allen et al., 1984; Calambokidis
et al., 1991; Suryan and Harvey, 1999; and Mortenson et al., 2000) or
lead to Hawaiian monk seal (Monachus schauinslandi) avoidance of beach
areas (Kenyon, 1972). In one case, human disturbance appeared to cause
Steller sea lions to desert a breeding area at Northeast Point on St.
Paul Island, Alaska (Kenyon, 1962).
In cases where vessels actively approached marine mammals (e.g.,
[[Page 18363]]
whale watching or dolphin watching boats), scientists have documented
that animals exhibit altered behavior such as increased swimming speed,
erratic movement, and active avoidance behavior (Bursk, 1983; Acevedo,
1991; Baker and MacGibbon, 1991; Trites and Bain, 2000; Williams et
al., 2002; Constantine et al., 2003), reduced blow interval (Ritcher et
al., 2003), disruption of normal social behaviors (Lusseau, 2003;
2006), and the shift of behavioral activities which may increase
energetic costs (Constantine et al., 2003; 2004). In 1997, Henry and
Hammil (2001) conducted a study to measure the impacts of small boats
(i.e., kayaks, canoes, motorboats and sailboats) on harbor seal haulout
behavior in M[eacute]tis Bay, Quebec, Canada. During that study, the
authors noted that the most frequent disturbances (n=73) were caused by
lower speed, lingering kayaks, and canoes (33.3 percent) as opposed to
motorboats (27.8 percent) conducting high speed passes. The seals'
flight reactions could be linked to a surprise factor by kayaks-canoes
that approach slowly, quietly and low on water, making them look like
predators. However, the authors note that once the animals were
disturbed, there did not appear to be any significant lingering effect
on the recovery of numbers to their pre-disturbance levels. In
conclusion, the study showed that boat traffic at current levels has
only a temporary effect on the haulout behavior of harbor seals in the
M[eacute]tis Bay area.
In 2004, Johnson and Acevedo-Gutierrez (2007) evaluated the
efficacy of buffer zones for watercraft around harbor seal haulout
sites on Yellow Island, Washington. The authors estimated the minimum
distance between the vessels and the haul-out sites; categorized the
vessel types; and evaluated seal responses to the disturbances. During
the course of the seven-weekend study, the authors recorded 14 human-
related disturbances which were associated with stopped powerboats and
kayaks. During these events, hauled out seals became noticeably active
and moved into the water. The flushing occurred when stopped kayaks and
powerboats were at distances as far as 453 and 1,217 ft (138 and 371 m)
respectively. The authors note that the seals were unaffected by
passing powerboats, even those approaching as close as 128 ft (39 m),
possibly indicating that the animals had become tolerant of the brief
presence of the vessels and ignored them. The authors reported that on
average, the seals quickly recovered from the disturbances and returned
to the haulout site in less than or equal to 60 minutes. Seal numbers
did not return to pre-disturbance levels within 180 minutes of the
disturbance less than one quarter of the time observed. The study
concluded that the return of seal numbers to pre-disturbance levels and
the relatively regular seasonal cycle in abundance throughout the area
counter the idea that disturbances from powerboats may result in site
abandonment (Johnson and Acevedo-Gutierrez, 2007). As a general
statement from the available information, pinnipeds exposed to intense
(approximately 110 to 120 decibels re: 20 [mu]Pa) non-pulse sounds
often leave haulout areas and seek refuge temporarily (minutes to a few
hours) in the water (Southall et al., 2007).
There are three ways in which disturbance, as described previously,
could result in more than Level B harassment of marine mammals. All
three are most likely to be consequences of stampeding, a potentially
dangerous occurrence in which large numbers of animals succumb to mass
panic and rush away from a stimulus. The three situations are: (1)
Falling when entering the water at high-relief locations; (2) extended
separation of mothers and pups; and (3) crushing of pups by large males
during a stampede. However, NMFS does not expect any of these scenarios
to occur at the proposed survey site.
Because hauled-out animals may move towards the water when
disturbed, there is the risk of injury if animals stampede towards
shorelines with precipitous relief (e.g., cliffs). However, while high-
elevation sites exist on the islands, the haulout sites consist of
ridges with unimpeded and non-obstructive access to the water. If
disturbed, the small number of hauled-out adult animals may move toward
the water without risk of encountering barriers or hazards that would
otherwise prevent them from leaving the area.
The probability of vessel and marine mammal interactions (i.e.,
motorboat strike) occurring during the proposed research activities is
unlikely due to the motorboat's slow operational speed, which is
typically 2 to 3 knots (2.3 to 3.4 mph) and the researchers continually
scanning the water for marine mammals presence during transit to the
islands. Thus, NMFS does not anticipate that strikes or collisions
would result from the movement of the motorboat.
Anticipated Effects on Marine Mammal Habitat
We do not anticipate that the proposed operations would result in
any temporary or permanent effects on the habitats used by the marine
mammals in the proposed area, including the food sources they use
(i.e., fish and invertebrates). While NMFS anticipates that the
specified activity may result in marine mammals avoiding certain areas
due to motorboat operations or human presence, this impact to habitat
is temporary and reversible. NMFS considered these as behavioral
modification. The main impact associated with the proposed activity
will be temporarily elevated noise levels and the associated direct
effects on marine mammals, previously discussed in this notice. Based
on the preceding discussion, NMFS does not anticipate that the proposed
activity would have any habitat-related effects that could cause
significant or long-term consequences for individual marine mammals or
their populations.
Proposed Mitigation
In order to issue an incidental take authorization 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 adverse 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 (where relevant).
Applications for incidental take authorizations must include the
availability and feasibility (economic and technological) of equipment,
methods, and manner of conducting the activity or other means of
effecting the least practicable adverse impact on the affected species
or stock and their habitat 50 CFR 216.104(a)(11).
The Glacier Bay NP has reviewed the following source documents and
has incorporated a suite of proposed mitigation measures into their
project description.
(1) Recommended best practices in Womble et al. (2013); Richardson
et al. (1995); Pierson et al. (1998); and Weir and Dolman, (2007).
To reduce the potential for disturbance from acoustic and visual
stimuli associated with the activities Glacier Bay NP and/or its
designees has proposed to implement the following mitigation measures
for marine mammals:
Perform pre-survey monitoring before deciding to access a
study site;
[[Page 18364]]
Avoid accessing a site based on a pre-determined threshold
number of animals present; sites used by pinnipeds for pupping; or
sites used by Steller sea lions;
Perform controlled and slow ingress to the study site to
prevent a stampede and select a pathway of approach to minimize the
number of marine mammals harassed;
Monitor for offshore predators at study sites. Avoid
approaching the study site if killer whales (Orcinus orca) are present.
If Glacier Bay NP and/or its designees see predators in the area, they
must not disturb the pinnipeds until the area is free of predators.
Maintain a quiet research atmosphere in the visual
presence of pinnipeds.
Pre-Survey Monitoring: Prior to deciding to land onshore to conduct
the study, the researchers would use high-powered image stabilizing
binoculars from the watercraft to document the number, species, and
location of hauled out marine mammals at each island. The vessels would
maintain a distance of 328 to 1,640 ft (100 to 500 m) from the
shoreline to allow the researchers to conduct pre-survey monitoring.
During every visit, the researchers will examine each study site
closely using high powered image stabilizing binoculars before
approaching at distances of greater than 500 m (1,640 ft) to determine
and document the number, species, and location of hauled out marine
mammals.
Site Avoidance: Researchers would decide whether or not to approach
the island based on the species present, number of individuals, and the
presence of pups. If there are high numbers (more than 25) harbor seals
hauled out (with or without young pups present), any time pups are
present, or any time that Steller sea lions are present, the
researchers will not approach the island and will not conduct gull
monitoring research.
Controlled Landings: The researchers would determine whether to
approach the island based on the number and type of animals present. If
the island has 25 or fewer individuals without pups, the researchers
would approach the island by motorboat at a speed of approximately 2 to
3 knots (2.3 to 3.4 mph). This would provide enough time for any marine
mammals present to slowly enter the water without panic or stampede.
The researchers would also select a pathway of approach farthest from
the hauled out harbor seals to minimize disturbance.
Minimize Predator Interactions: If the researchers visually observe
marine predators (i.e. killer whales) present in the vicinity of hauled
out marine mammals, the researchers would not approach the study site.
Noise Reduction Protocols: While onshore at study sites, the
researchers would remain vigilant for hauled out marine mammals. If
marine mammals are present, the researchers would move slowly and use
quiet voices to minimize disturbance to the animals present.
Mitigation Conclusions
NMFS has carefully evaluated Glacier Bay NP's proposed mitigation
measures in the context of ensuring that we prescribe the means of
effecting the least practicable impact on the affected marine mammal
species and stocks and their habitat. Our evaluation of potential
measures included consideration of the following factors in relation to
one another:
The manner in which, and the degree to which, the
successful implementation of the measure is expected to minimize
adverse impacts to marine mammals;
The proven or likely efficacy of the specific measure to
minimize adverse impacts as planned; and
The practicability of the measure for applicant
implementation.
Any mitigation measure(s) prescribed by NMFS should be able to
accomplish, have a reasonable likelihood of accomplishing (based on
current science), or contribute to the accomplishment of one or more of
the general goals listed here:
1. Avoidance or minimization of injury or death of marine mammals
wherever possible (goals 2, 3, and 4 may contribute to this goal).
2. A reduction in the numbers of marine mammals (total number or
number at biologically important time or location) exposed to motorboat
operations or visual presence that we expect to result in the take of
marine mammals (this goal may contribute to 1, above, or to reducing
harassment takes only).
3. A reduction in the number of times (total number or number at
biologically important time or location) individuals exposed to
motorboat operations or visual presence that we expect to result in the
take of marine mammals (this goal may contribute to 1, above, or to
reducing harassment takes only).
4. A reduction in the intensity of exposures (either total number
or number at biologically important time or location) to motorboat
operations or visual presence that we expect to result in the take of
marine mammals (this goal may contribute to a, above, or to reducing
the severity of harassment takes only).
5. Avoidance or minimization of adverse effects to marine mammal
habitat, paying special attention to the food base, activities that
block or limit passage to or from biologically important areas,
permanent destruction of habitat, or temporary destruction/disturbance
of habitat during a biologically important time.
6. For monitoring directly related to mitigation--an increase in
the probability of detecting marine mammals, thus allowing for more
effective implementation of the mitigation.
Based on the evaluation of Glacier Bay NP's proposed measures, NMFS
has preliminarily determined that the proposed mitigation measures
provide the means of effecting the least practicable impact on marine
mammal species or stocks and their habitat, paying particular attention
to rookeries, mating grounds, and areas of similar significance.
Proposed Monitoring
In order to issue an ITA 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 we expect to be present in the
proposed action area. Glacier Bay NP submitted a marine mammal
monitoring plan in section 13 of their Authorization application.
Monitoring measures prescribed by NMFS should accomplish one or
more of the following general goals:
1. An increase in our understanding of the likely occurrence of
marine mammal species in the vicinity of the action, (i.e., presence,
abundance, distribution, and/or density of species).
2. An increase in our understanding of the nature, scope, or
context of the likely exposure of marine mammal species to any of the
potential stressor(s) associated with the action (e.g., sound or visual
stimuli), through better understanding of one or more of the following:
The action itself and its environment (e.g., sound source
characterization, propagation, and ambient noise levels); the affected
species (e.g., life history or dive pattern); the likely co-occurrence
of marine mammal species with the action (in whole or part) associated
with
[[Page 18365]]
specific adverse effects; and/or the likely biological or behavioral
context of exposure to the stressor for the marine mammal (e.g., age
class of exposed animals or known pupping, calving or feeding areas).
3. An increase in our understanding of how individual marine
mammals respond (behaviorally or physiologically) to the specific
stressors associated with the action (in specific contexts, where
possible, e.g., at what distance or received level).
4. An increase in our understanding of how anticipated individual
responses, to individual stressors or anticipated combinations of
stressors, may impact either: The long-term fitness and survival of an
individual; or the population, species, or stock (e.g. through effects
on annual rates of recruitment or survival).
5. An increase in our understanding of how the activity affects
marine mammal habitat, such as through effects on prey sources or
acoustic habitat (e.g., through characterization of longer-term
contributions of multiple sound sources to rising ambient noise levels
and assessment of the potential chronic effects on marine mammals).
6. An increase in understanding of the impacts of the activity on
marine mammals in combination with the impacts of other anthropogenic
activities or natural factors occurring in the region.
7. An increase in our understanding of the effectiveness of
mitigation and monitoring measures.
8. An increase in the probability of detecting marine mammals
(through improved technology or methodology), both specifically within
the safety zone (thus allowing for more effective implementation of the
mitigation) and in general, to better achieve the above goals.
As part of its Authorization application, Glacier Bay NP proposes
to sponsor marine mammal monitoring during the project, in order to
implement the mitigation measures that require real-time monitoring,
and to satisfy the monitoring requirements of the MMPA.
The Glacier Bay NP researchers will monitor the area for pinnipeds
during all research activities. Monitoring activities will consist of
conducting and recording observations on pinnipeds within the vicinity
of the proposed research areas. The monitoring notes would provide
dates and location of the researcher's activities and the number and
type of species present. The researchers would document the behavioral
state of animals present, and any apparent disturbance reactions or
lack thereof.
Glacier Bay NP can add to the knowledge of pinnipeds in the
proposed action area by noting observations of: (1) Unusual behaviors,
numbers, or distributions of pinnipeds, such that any potential follow-
up research can be conducted by the appropriate personnel; (2) tag-
bearing carcasses of pinnipeds, allowing transmittal of the information
to appropriate agencies and personnel; and (3) rare or unusual species
of marine mammals for agency follow-up.
If at any time injury, serious injury, or mortality of the species
for which take is authorized should occur, or if take of any kind of
any other marine mammal occurs, and such action may be a result of the
proposed land survey, Glacier Bay NP would suspend research and
monitoring activities and contact NMFS immediately to determine how
best to proceed to ensure that another injury or death does not occur
and to ensure that the applicant remains in compliance with the MMPA.
Encouraging and Coordinating Research
Glacier Bay NP actively monitors harbor seals at breeding and
molting haul out locations to assess trends over time (e.g., Mathews &
Pendleton, 2006; Womble et al. 2010, Womble and Gende, 2013b). This
monitoring program involves collaborations with biologists from the
Alaska Department of Fish and Game, and the National Marine Mammal
Laboratory. Glacier Bay NP will continue these collaborations and
encourage continued or renewed monitoring of marine mammal species.
Additionally, they would report vessel-based counts of marine mammals,
branded, or injured animals, and all observed disturbances to the
appropriate state and federal agencies.
Proposed Reporting
Glacier Bay NP will submit a draft monitoring report to us no later
than 90 days after the expiration of the Incidental Harassment
Authorization, if we issue it. The report will describe the operations
conducted and sightings of marine mammals near the proposed project.
The report will provide full documentation of methods, results, and
interpretation pertaining to all monitoring. The report will provide:
1. A summary and table of the dates, times, and weather during all
research activities.
2. Species, number, location, and behavior of any marine mammals
observed throughout all monitoring activities.
3. An estimate of the number (by species) of marine mammals exposed
to acoustic or visual stimuli associated with the research activities.
4. A description of the implementation and effectiveness of the
monitoring and mitigation measures of the Authorization and full
documentation of methods, results, and interpretation pertaining to all
monitoring.
In the unanticipated event that the specified activity clearly
causes the take of a marine mammal in a manner prohibited by the
authorization, such as an injury (Level A harassment), serious injury,
or mortality (e.g., vessel-strike, stampede, etc.), Glacier Bay NP
shall immediately cease the specified activities and immediately report
the incident to the Division Chief, Permits and Conservation Division,
Office of Protected Resources, NMFS, at 301-427-8401 and the Alaska
Regional Stranding Coordinator at (907) 586-7248. The report must
include the following information:
Time, date, and location (latitude/longitude) of the
incident;
Description and location of the incident (including water
depth, if applicable);
Environmental conditions (e.g., wind speed and direction,
Beaufort sea state, cloud cover, and visibility);
Description of all marine mammal observations in the 24
hours preceding the incident;
Species identification or description of the animal(s)
involved;
Fate of the animal(s); and
Photographs or video footage of the animal(s) (if
equipment is available).
Glacier Bay NP shall not resume its activities until NMFS is able
to review the circumstances of the prohibited take. We will work with
Glacier Bay to determine what is necessary to minimize the likelihood
of further prohibited take and ensure MMPA compliance. Glacier Bay NP
may not resume their activities until notified by us via letter, email,
or telephone.
In the event that Glacier Bay NP discovers an injured or dead
marine mammal, and the lead researcher determines that the cause of the
injury or death is unknown and the death is relatively recent (i.e., in
less than a moderate state of decomposition as we describe in the next
paragraph), Glacier Bay NP will immediately report the incident to the
Division Chief, Permits and Conservation Division, Office of Protected
Resources, NMFS, at 301-427-8401 and the Alaska Regional Stranding
Coordinator at (907) 586-7248. The report must include the same
information identified in the paragraph
[[Page 18366]]
above this section. Activities may continue while we review the
circumstances of the incident. We will work with Glacier Bay NP to
determine whether modifications in the activities are appropriate.
In the event that Glacier Bay NP discovers an injured or dead
marine mammal, and the lead visual observer determines that the injury
or death is not associated with or related to the authorized activities
(e.g., previously wounded animal, carcass with moderate to advanced
decomposition, or scavenger damage), Glacier Bay will report the
incident to the incident to the Division Chief, Permits and
Conservation Division, Office of Protected Resources, NMFS, at 301-427-
8401 and the Alaska Regional Stranding Coordinator at (907) 586-7248
within 24 hours of the discovery. Glacier Bay NP researchers will
provide photographs or video footage (if available) or other
documentation of the stranded animal sighting to us. Glacier Bay NP can
continue their research activities.
Estimated Take by Incidental Harassment
Except with respect to certain activities not pertinent here, 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].
All anticipated takes would be by Level B harassment, involving
temporary changes in behavior. NMFS expects that the proposed
mitigation and monitoring measures would minimize the possibility of
injurious or lethal takes. NMFS considers the potential for take by
injury, serious injury, or mortality as remote. NMFS expects that the
presence of Glacier Bay NP personnel could disturb animals hauled out
and that the animals may alter their behavior or attempt to move away
from the researchers.
As discussed earlier, NMFS considers an animal to have been
harassed if it moved greater than 1 m (3.3 ft) in response to the
surveyors' presence or if the animal was already moving and changed
direction and/or speed, or if the animal flushed into the water. NMFS
does not consider animals that became alert without such movements as
harassed.
Based on pinniped survey counts conducted by Glacier Bay NP (e.g.,
Mathews & Pendleton, 2006; Womble et al., 2010), NMFS estimates that
the research activities could potentially affect by Level B behavioral
harassment 500 harbor seals over the course of the Authorization (Table
2). This estimate represents 9.9 percent of the Glacier Bay/Icy Strait
stock of harbor seals and accounts for a maximum disturbance of 25
harbor seals each per visit at Boulder, Lone, and Flapjack Islands, and
Geikie Rock, Alaska over a maximum level of five visits.
Table 2--Estimates of the Possible Numbers of Marine Mammals Exposed to Acoustic and Visual Stimuli During the
Proposed Research Activities on Boulder, Lone, and Flapjack Islands, and Geikie Rock, Alaska, May Through
September, 2015
----------------------------------------------------------------------------------------------------------------
Estimated
number of Proposed take Percent of
Species individuals authorization species or Population trend \2\
exposed stock \1\
----------------------------------------------------------------------------------------------------------------
Harbor seal.......................... 500 500 9.9 Declining.
Steller sea lion..................... 0 0 0 Increasing.
----------------------------------------------------------------------------------------------------------------
\1\ Table 1 in this notice lists the stock species abundance estimates that NMFS used to calculate the
percentage of species/stock.
\2\ The population trend information is from Allen and Angliss, 2014. No data = Insufficient data to determine
population trend.
Harbor seals tend to haul out in small numbers (on average, less
than 50 animals) at most sites with the exception of Flapjack Island
(Womble, Pers. Comm.). Animals on Flapjack Boulder Islands generally
haul out on the south side of the Islands and are not located near the
research sites located on the northern side of the Islands. Aerial
survey maximum counts show that harbor seals sometimes haul out in
large numbers at all four locations (see Table 2 in Glacier Bays NP's
application), and sometimes individuals and mother/pup pairs occupy
different terrestrial locations than the main haulout (J. Womble,
personal observation).
Considering the conservation status for the Western stock of the
Steller sea lion, the Glacier Bay NP researchers would not conduct
ground-based or vessel-based surveys if they observe Steller sea lions
before accessing Boulder, Lone, and Flapjack Islands, and Geikie Rock.
Thus, NMFS expects no takes to occur for this species during the
proposed activities.
NMFS does not propose to authorize any injury, serious injury, or
mortality. NMFS expect all potential takes to fall under the category
of Level B harassment only.
Analysis and Preliminary Determinations
Negligible Impact
Negligible impact' is ``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). The lack of
likely adverse effects on annual rates of recruitment or survival
(i.e., population level effects) forms the basis of a negligible impact
finding. An estimate of the number of Level B harassment 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 behavioral harassment, NMFS considers other
factors, such as the likely nature of any responses (e.g., intensity,
duration), the context of any responses (e.g., critical reproductive
time or location, migration), as well as the number and nature of
estimated Level A harassment takes, the number of estimated
mortalities, and effects on habitat.
Although Glacier Bay NP's survey activities may disturb harbor
seals hauled out at the survey sites, NMFS expects those impacts to
occur to a small, localized group of animals for a limited duration
(e.g., 30 minutes to two hours each visit). Pinnipeds would likely
become alert or, at most, flush into the water in reaction to the
presence of Glacier Bay NP personnel during the proposed activities.
[[Page 18367]]
Disturbance will be limited to a short duration, allowing the animals
to reoccupy the island within a short amount of time. Thus, the
proposed action is unlikely to result in long-term impacts such as
permanent abandonment of the haul-out.
For reasons stated previously in this document and based on the
following factors, Glacier Bay NP's specified activities are not likely
to cause long-term behavioral disturbance, injury, serious injury, or
death. These reasons include:
1. The effects of the research activities would be limited to
short-term responses and temporary behavioral changes due to the short
and sporadic duration of the research activities. Minor and brief
responses are not likely to constitute disruption of behavioral
patterns, such as migration, nursing, breeding, feeding, or sheltering.
2. The availability of alternate areas for pinnipeds to avoid the
resultant disturbances from the research operations. Anecdotal reports
from previous Glacier Bay NP activities have shown that the pinnipeds
returned to the various sites and did not permanently abandon haul-out
sites after Glacier Bay NP conducted their research activities.
3. There is no potential for large-scale movements leading to
injury, serious injury, or mortality because the researchers would
delay ingress into the landing areas only after the pinnipeds have
slowly entered the water.
4. Glacier Bay NP will limit access to Boulder, Lone, and Flapjack
Islands, and Geikie Rock when there are high numbers (more than 25)
harbor seals hauled out (with or without young pups present), any time
pups are present, or any time that Steller sea lions are present, the
researchers will not approach the island and will not conduct gull
monitoring research.
NMFS does not anticipate that any injuries, serious injuries, or
mortalities would occur as a result of Glacier Bay NP's proposed
activities with the mitigation and related monitoring, and NMFS does
not propose to authorize injury, serious injury, or mortality at this
time. In addition, the research activities would not take place in
areas of significance for marine mammal feeding, resting, breeding, or
calving and would not adversely impact marine mammal habitat.
Due to the nature, degree, and context of Level B (behavioral)
harassment anticipated and described (see ``Potential Effects on Marine
Mammals'' section in this notice), we do not expect the activity to
impact annual rates of recruitment or survival for any affected species
or stock.
In summary, NMFS anticipates that impacts to hauled-out harbor
seals during Glacier Bay NP's research activities would be behavioral
harassment of limited duration (i.e., up to two hours per visit) and
limited intensity (i.e., temporary flushing at most). NMFS does not
expect stampeding, and therefore injury or mortality, to occur (see
``Mitigation'' for more details). 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 proposed monitoring and mitigation measures, NMFS
preliminarily finds that the total marine mammal take from Glacier
Bay's proposed research activities will have a negligible impact on the
affected marine mammal species or stocks.
Small Numbers
As mentioned previously, NMFS estimates that Glacier Bay NP's
activities could potentially affect, by Level B harassment only, one
species of marine mammal under our jurisdiction. For harbor seals, this
estimate is small (9.9 percent) relative to the population size and we
have provided the percentage of the harbor seal's regional population
estimate that the activities may take by Level B harassment in Table 2
in this notice.
Based on the analysis contained in this notice of the likely
effects of the specified activity on marine mammals and their habitat,
and taking into consideration the implementation of the mitigation and
monitoring measures, NMFS preliminarily finds that Glacier Bay NP's
proposed activities would take small numbers of marine mammals relative
to the populations of the affected species or stocks.
Impact on Availability of Affected Species or Stock for Taking for
Subsistence Uses
There are no relevant subsistence uses of marine mammals implicated
by this action. Glacier Bay National Park prohibits subsistence harvest
of harbor seals within the Park (Catton, 1995).
Endangered Species Act (ESA)
NMFS does not expect that Glacier Bay NP's proposed research
activities (which includes mitigation measures to avoid harassment of
Steller sea lions) would affect any species listed under the ESA.
Therefore, NMFS has determined that a section 7 consultation under the
ESA is not required.
National Environmental Policy Act (NEPA)
In 2014, NMFS prepared an Environmental Assessment (EA) analyzing
the potential effects to the human environment from NMFS' issuance of a
Authorization to Glacier Bay NP for their seabird research activities.
In September 2014, NMFS issued a Finding of No Significant Impact
(FONSI) on the issuance of an Authorization for Point Blue's research
activities in accordance with section 6.01 of the NOAA Administrative
Order 216-6 (Environmental Review Procedures for Implementing the
National Environmental Policy Act, May 20, 1999). Glacier Bay NP's
proposed activities and impacts for 2015 are within the scope of the
2014 EA and FONSI. NMFS provided relevant environmental information to
the public through a previous notice for the proposed Authorization (79
FR 32226, June 4, 2014) and considered public comments received in
response prior to finalizing the 2014 EA and deciding whether or not to
issue a Finding of No Significant Impact (FONSI).
NMFS has reviewed the 2014 EA and determined that there are no new
direct, indirect, or cumulative impacts to the human and natural
environment associated with the Authorization requiring evaluation in a
supplemental EA and NMFS, therefore, proposes to reaffirm the 2014
FONSI. NMFS' EA and FONSI for this activity are available upon request
(see ADDRESSES).
Proposed Authorization
As a result of these preliminary determinations, NMFS proposes
issuing an Incidental Harassment Authorization to Glacier Bay National
Park for conducting seabird research May through September, 2015,
provided they incorporate the previously mentioned mitigation,
monitoring, and reporting requirements.
Draft Proposed Authorization
This section contains the draft text for the proposed
Authorization. NMFS proposes to include this language in the
Authorization if issued.
Proposed Authorization Language
Glacier Bay National Park, P.O. Box 140, Gustavus, Alaska 99826
and/or its designees (holders of the Authorization) are hereby
authorized under section 101(a)(5)(D) of the Marine Mammal Protection
Act (16 U.S.C. 1371(a)(5)(D)) to harass small numbers of marine mammals
incidental to conducting monitoring and research studies on glaucus-
winged gulls (Larus
[[Page 18368]]
glaucescens) within Glacier Bay National Park and Preserve in Alaska.
1. This Authorization is valid from May 15 through September 30,
2015.
2. This Authorization is valid only for research activities that
occur in the following specified geographic areas: Boulder
(58[deg]33'18.08'' N; 136[deg]1'13.36'' W); Lone (58[deg]43'17.67'' N;
136[deg]17'41.32'' W), and Flapjack (58[deg]35'10.19'' N;
135[deg]58'50.78'' W) Islands, and Geikie Rock (58[deg]41'39.75'' N;
136[deg]18'39.06'' W); and Tlingit Point Islet (58[deg]45'16.86'' N;
136[deg]10'41.74'' W) in Glacier Bay, Alaska.
3. Species Authorized and Level of Takes
a. The taking, by Level B harassment only, is limited to the
following species: 500 Pacific harbor seals (Phoca vitulina).
b. The taking by injury (Level A harassment), serious injury or
death of any of the species listed in Condition 3(a) or the taking of
any kind of any other species of marine mammal is prohibited and may
result in the modification, suspension or revocation of this
Authorization.
c. The taking of any marine mammal in a manner prohibited under
this Authorization must be reported immediately to the Chief, Permits
and Conservation Division, Office of Protected Resources, NMFS, at
(301) 427-8401.
4. General Conditions
A copy of this Authorization must be in the possession of Glacier
Bay National Park, its designees, and field crew personnel (including
research collaborators) operating under the authority of this
Authorization at all times.
5. Mitigation Measures
The Holder of this Authorization is required to implement the
following mitigation measures:
a. Conduct pre-survey monitoring before deciding to access a study
site. Prior to deciding to land onshore of Boulder, Lone, or Flapjack
Island or Geikie Rock, the Holder of this Authorization will use high-
powered image stabilizing binoculars before approaching at distances of
greater than 500 m (1,640 ft) to determine and document the number,
species, and location of hauled out marine mammals.. The vessels will
maintain a distance of 328 to 1,640 ft (100 to 500 m) from the
shoreline.
i. If the Holder of the Authorization determines that there are 25
or more harbor seals (with or without young pups present) hauled out on
the shoreline, the holder will not access the island and will not
conduct the study at that time.
ii. If the Holder of the Authorization determines that any Steller
sea lions (Eumetopias jubatus) are present at the study site, the
Holder will not access the island and will not conduct the study at
that time.
iii. If the Holder of the Authorization determines that there are
any pups hauled out on the shoreline and vulnerable to being separated
from their mothers, the Holder will not access the island and will not
conduct the study at that time.
b. Minimize the potential for disturbance by: (1) Performing
controlled and slow ingress to the study site to prevent a stampede;
and (2) selecting a pathway of approach farthest from the hauled out
harbor seals to minimize disturbance.
c. Monitor for offshore predators at the study sites and avoid
research activities when predators area present. Avoid approaching the
study site if killer whales (Orcinus orca) are present. If the Holder
of this Authorization observes predators in the area, they must not
disturb the pinnipeds until the area is free of predators.
d. Maintain a quiet working atmosphere, avoid loud noises, and use
hushed voices in the presence of hauled out pinnipeds.
6. Monitoring
Glacier Bay NP is required to record the following:
a. BLM and/or its designees shall record the following:
i. Species counts (with numbers of adults/juveniles); and:
ii. Numbers of disturbances, by species and age, according to a
three-point scale of intensity including: (1) Head orientation in
response to disturbance, which may include turning head towards the
disturbance, craning head and neck while holding the body rigid in a u-
shaped position, or changing from a lying to a sitting position and/or
slight movement of less than 1 meter; ``alert''; (2) Movements in
response to or away from disturbance, typically over short distances
(1-3 meters) and including dramatic changes in direction or speed of
locomotion for animals already in motion; ``movement''; and (3) All
flushes to the water as well as lengthier retreats (>3 meters);
``flight''.
iii. Information on the weather, including the tidal state and
horizontal visibility.
b. If applicable, the observer shall note observations of marked or
tag-bearing pinnipeds or carcasses, as well as any rare or unusual
species of marine mammal.
c. If applicable, the observer shall note the presence of any
offshore predators (date, time, number, and species).
7. Reporting
The holder of this Authorization is required to:
a. Draft Report: Submit a draft monitoring report to the Division
Chief, Permits and Conservation Division, Office of Protected
Resources, National Marine Fisheries Service within 90 days after the
Authorization expires. NMFS will review the Draft Report which is
subject to review and comment by NMFS. Glacier Bay NP must address any
recommendations made by NMFS in the Final Report prior to submission to
NMFS. If NMFS decides that the draft final report needs no comments,
NMFS will consider the draft report as the Final Report.
b. Final Report: Glacier Bay shall prepare and submit a Final
Report to NMFS within 30 days following resolution of any comments on
the draft report from NMFS.
8. Reporting Injured or Dead Marine Mammals
In the unanticipated event that the specified activity clearly
causes the take of a marine mammal in a manner prohibited by the
authorization, such as an injury (Level A harassment), serious injury,
or mortality (e.g., vessel-strike, stampede, etc.), BLM and/or its
designees shall immediately cease the specified activities and
immediately report the incident to the Division Chief, Permits and
Conservation Division, Office of Protected Resources, NMFS, at 301-427-
8401 and the Alaska Regional Stranding Coordinator at (907) 586-7248.
The report must include the following information:
Time, date, and location (latitude/longitude) of the
incident;
Description and location of the incident (including water
depth, if applicable);
Environmental conditions (e.g., wind speed and direction,
Beaufort sea state, cloud cover, and visibility);
Description of all marine mammal observations in the 24
hours preceding the incident;
Species identification or description of the animal(s)
involved;
Fate of the animal(s); and
Photographs or video footage of the animal(s) (if
equipment is available).
Glacier Bay NP shall not resume its activities until NMFS is able
to review the circumstances of the prohibited take. NMFS will work with
Glacier Bay
[[Page 18369]]
NP to determine what is necessary to minimize the likelihood of further
prohibited take and ensure MMPA compliance. Glacier Bay NP may not
resume their activities until notified by us via letter, email, or
telephone.
In the event that Glacier Bay NP discovers an injured or dead
marine mammal, and the marine mammal observer determines that the cause
of the injury or death is unknown and the death is relatively recent
(i.e., in less than a moderate state of decomposition as we describe in
the next paragraph), Glacier Bay NP will immediately report the
incident to the Division Chief, Permits and Conservation Division,
Office of Protected Resources, NMFS, at 301-427-8401 and the Alaska
Regional Stranding Coordinator at (907) 586-7248. The report must
include the same information identified in the paragraph above this
section. Activities may continue while NMFS reviews the circumstances
of the incident. NMFS would work with Glacier Bay NP to determine
whether modifications in the activities are appropriate.
In the event that Glacier Bay NP discovers an injured or dead
marine mammal, and the lead visual observer determines that the injury
or death is not associated with or related to the authorized activities
(e.g., previously wounded animal, carcass with moderate to advanced
decomposition, or scavenger damage), Glacier Bay NP will report the
incident to the Division Chief, Permits and Conservation Division,
Office of Protected Resources, NMFS, at 301-427-8401 and the Alaska
Regional Stranding Coordinator at (907) 586-7248 within 24 hours of the
discovery. Glacier Bay NP personnel will provide photographs or video
footage (if available) or other documentation of the stranded animal
sighting to us. Glacier Bay NP can continue their survey activities
while NMFS reviews the circumstances of the incident.
Request for Public Comments
NMFS invites comments on our analysis, the draft authorization, and
any other aspect of the notice of proposed Authorization for Glacier
Bay NP's activities. Please include any supporting data or literature
citations with your comments to help inform our final decision on
Glacier Bay NP's request for an Authorization.
Dated: March 31, 2015.
Donna S. Wieting,
Director, Office of Protected Resources, National Marine Fisheries
Service.
[FR Doc. 2015-07734 Filed 4-3-15; 8:45 am]
BILLING CODE 3510-22-P