Takes of Marine Mammals Incidental to Specified Activities; Taking Marine Mammals Incidental to Seabird and Shorebird Monitoring and Research at the Eastern Massachusetts National Wildlife Refuge Complex, Massachusetts, 12342-12348 [2017-04002]
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Federal Register / Vol. 82, No. 40 / Thursday, March 2, 2017 / Notices
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XF101
Takes of Marine Mammals Incidental to
Specified Activities; Taking Marine
Mammals Incidental to Seabird and
Shorebird Monitoring and Research at
the Eastern Massachusetts National
Wildlife Refuge Complex,
Massachusetts
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; issuance of an incidental
harassment authorization.
AGENCY:
In accordance with the
regulations implementing the Marine
Mammal Protection Act (MMPA) as
amended, notification is hereby given
that NMFS has issued an incidental
harassment authorization (IHA) to the
Eastern Massachusetts (MA) National
Wildlife Refuge (NWR) Complex, U.S.
Fish and Wildlife Service (USFWS) to
incidentally harass, by Level B
harassment only, marine mammals
during seabird and shorebird
monitoring and other research activities
in the Eastern MA NWR Complex
(Complex).
SUMMARY:
This Authorization is effective
from April 1, 2017 through March 31,
2018.
DATES:
National Environmental Policy Act
(NEPA)
NMFS prepared an Environmental
Assessment (EA) and analyzed the
potential impacts to marine mammals
that would result from the USFWS’s
monitoring and research activities. A
Finding of No Significant Impact
(FONSI) was signed in March 2017. A
copy of the EA and FONSI is available
on our Web site at https://
www.nmfs.noaa.gov/pr/permits/
incidental/research.htm.
FOR FURTHER INFORMATION CONTACT:
Laura McCue, NMFS, Office of
Protected Resources, NMFS (301) 427–
8401.
SUPPLEMENTARY INFORMATION:
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Background
Section 101(a)(5)(D) of the MMPA 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
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activity (other than commercial fishing)
within a specified geographical region if
certain findings are made and either
regulations are issued or, if the taking is
limited to harassment, a notice of a
proposed authorization is provided to
the public for review.
An authorization for incidental
takings shall be granted if NMFS finds
that the taking will have a negligible
impact on the species or stock(s), will
not have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (where
relevant), and if the permissible
methods of taking and requirements
pertaining to the mitigation, monitoring
and reporting of such takings are set
forth. 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.’’
Summary of Request
On March 16, 2016, NMFS received
an application from the USFWS for the
taking of marine mammals incidental to
seabird and shorebird monitoring and
research activities within the Complex.
NMFS received updated applications on
September 14 and December 16, 2016
with updated take numbers and
mitigation measures. NMFS determined
the application complete and adequate
on December 29, 2016.
The USFWS plans to conduct seabird
and shorebird monitoring and research
at several locations within the Complex
over a varying number of days for each
project. This authorization, will be valid
for one year, beginning on April 1, 2017.
The following specific aspects of the
planned activities would likely result in
the disturbance of marine mammals: (1)
Vessel landings; (2) research activities
(e.g., cannon nets, sign installation); and
(3) human presence. Thus, NMFS
anticipates that take, by Level B
harassment only, of gray seals
(Halichoerus grypus grypus) and harbor
seals (Phoca vitulina concolor) could
result from the specified activity.
Description of the Specified Activity
Overview
The USFWS plans to conduct
biological tasks for refuge purposes at
Monomoy NWR, Nantucket NWR, and
Nomans Land Island NWR in MA.
These three refuges are managed
through the Complex as part of the NWR
System of the USFWS. Complex staff
census and monitor the presence and
productivity of breeding and migrating
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shorebirds using the beaches of
Monomoy, Nantucket, and Nomans
Land Island NWRs from April 1–
November 30, annually. Monitoring
activities occur daily (on Monomoy and
Nantucket) from April–August and are
necessary to document the productivity
(number of chicks fledged per pair) and
population of protected shorebird and
seabird species. Monomoy NWR also
participates in several less frequent, but
equally important, high priority
conservation tasks to monitor for
threatened and endangered species,
including censusing northeastern beach
tiger beetles (Cicindela dorsalis) and
participating in a red knot (Calidris
canutus) migration study during
southward migration. Additionally, both
Monomoy and Nantucket NWRs serve
as vital staging grounds for migrating
roseate terns (Sterna dougallii), where
USFWS staff resight and stage counts. A
detailed description of the planned
monitoring and research project is
provided in the Federal Register notice
for the proposed IHA (82 FR 3738;
January 12, 2017). Since that time, no
changes have been made to the planned
activities. Therefore, a detailed
description is not provided here. Please
refer to that Federal Register notice for
the description of the specific activity,
including the dates and duration and
the specified geographic region.
Comment and Responses
A notice of NMFS’s proposal to issue
an IHA to the USFWS was published in
the Federal Register on January 12,
2017 (82 FR 3738). That notice
described, in detail, the USFWS’s
activity, the marine mammal species
that may be affected by the activity, and
the anticipated effects on marine
mammals. During the 30-day public
comment period, NMFS received
comments from the Marine Mammal
Commission. The Marine Mammal
Commission recommended that NMFS
issue the IHA, subject to inclusion of the
proposed mitigation, monitoring, and
reporting measures as described in our
notice of proposed IHA and the
application. All measures proposed in
the initial Federal Register notice are
included within the IHA.
Sound Sources and Sound
Characteristics
NMFS does not expect acoustic
stimuli to result from human presence,
and therefore, will not have the
potential to harass marine mammals,
incidental to the conduct of the planned
activities. One activity (cannon nets)
will have an acoustic component, but
take from this activity can be avoided
through implementation of mitigation.
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This section includes a brief
explanation of the sound measurements
frequently used in the discussions of
acoustic effects in this notice. Sound
pressure is the sound force per unit area
and is usually measured in micropascals
(mPa), where 1 pascal (Pa) is the
pressure resulting from a force of one
newton exerted over an area of 1 square
meter (m). Sound pressure level (SPL) is
the ratio of a measured sound pressure
and a reference level. The commonly
used reference pressure is 20 mPa for in
air, and the units for SPLs are dB re: 20
mPa.
SPL (in decibels (dB)) = 20 log
(pressure/reference pressure).
SPL is an instantaneous measurement
expressed as the peak, the peak-peak, or
the root mean square (rms). Root mean
square is the square root of the
arithmetic average of the squared
instantaneous pressure values. All
references to SPL in this document refer
to the root mean square unless
otherwise noted. SPL does not take into
account the duration of a sound.
Research Activities Sound
Characteristics
Activities that have an acoustic
component (e.g., cannon nets) are not
expected to reach the thresholds for
Level B harassment. Cannon nets are an
airborne source of noise, and have a
measured source level (SL) of 128 dB at
one m (estimated based on a
measurement of 98.4 dB at 30 m; L.
Niles, pers. comm., December 2016);
however, based on calculations using
the SL and spherical spreading, the SPL
is expected to be less than the
thresholds for airborne pinniped
disturbance (e.g. 90 dB for harbor seals,
and 100 dB for all other pinnipeds) at
25 m and 80 m from the source,
respectively. The USFWS will stay at
least 100 m from all pinnipeds if cannon
nets are used for research purposes.
Description of Marine Mammals in the
Area of the Specified Activity
Table 1 provides the following
information: All marine mammal
species with possible or confirmed
occurrence in the activity area;
information on those species’ regulatory
status under the MMPA and the ESA of
1973 (16 U.S.C. 1531 et seq.);
abundance; occurrence and seasonality
in the activity area. A detailed
description of the species likely to be
affected by the USFWS’s project,
including brief introductions to the
species and relevant stocks, available
information regarding population trends
and threats, and information regarding
local occurrence, were provided in the
Federal Register notice for the proposed
IHA (82 FR 3738; January 12, 2017);
since that time, we are not aware of any
changes in the status of these species
and stocks; therefore, detailed
descriptions are not provided here.
Please refer to that Federal Register
notice for these descriptions. Please also
refer to the draft 2016 NMFS Marine
Mammal Stock Assessment Report
available online at: https://
www.nmfs.noaa.gov/pr/sars/ for further
information on the biology and
distribution of these species.
TABLE 1—GENERAL INFORMATION ON MARINE MAMMALS THAT COULD POTENTIALLY HAUL OUT ON NORTHWEST SEAL
ROCK, NOVEMBER 2015 THROUGH NOVEMBER 2016
Species
Stock
Gray seal (Halichoerus grypus grypus)
Harbor seal (Phoca vitulina concolor) ...
Western North Atlantic.
Western North Atlantic.
Regulatory
status 1 2
MMPA–NC ESA–
NL.
MMPA–NC ESA–
NL.
Stock abundance
(CV, Nmin, most
recent abundance
survey) 3
Occurrence and
seasonality
PBR
505,000 (unk; unk;
unk) *.
75,834 (0.15;
66,884; 2012).
unk
2,006
Year-round presence.
Occasional.
1 MMPA:
D = Depleted, S = Strategic, NC = Not Classified.
EN = Endangered, T = Threatened, DL = Delisted, NL = Not listed.
draft NMFS Stock Assessment Reports: Waring et al. (2016).
* The Western North Atlantic stock of gray seals is comprised of the Canadian and U.S. populations. The U.S. population abundance estimate
is unknown, but the Canadian population abundance estimate is 505,000. The 2016 draft SAR states that the western North Atlantic stock is
equivalent to the Canada population.
2 ESA:
3 2016
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Potential Effects of the Specified
Activities on Marine Mammals and
Their Habitat
Anticipated Effects on Marine Mammal
Habitat
The effects of airborne noise and
visual disturbance from monitoring and
research activities for the USFWS’s
project have the potential to result in
behavioral harassment of marine
mammals in the vicinity of the action
area. The Federal Register notice for the
proposed IHA (82 FR 3738; January 12,
2017) included a discussion of the
effects of anthropogenic noise and
visual disturbance on marine mammals,
therefore that information is not
repeated here; please refer to that
Federal Register notice for that
information.
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The main impact associated with the
USFWS’s project would be visual and
acoustic disturbance from human
presence, vessels, and potential cannon
nets. The project would not result in
permanent impacts to habitats used
directly by marine mammals, such as
haulout sites, or short-term impacts to
food sources, but may have minor
impacts to the immediate substrate
during installation of signage during the
monitoring and research project. These
potential effects are discussed in detail
in the Federal Register notice for the
proposed IHA (82 FR 3738; January 12,
2017, therefore that information is not
repeated here; please refer to that
Federal Register notice for that
information.
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Mitigation Measures
In order to issue an IHA under section
101(a)(5)(D) of the MMPA, NMFS must
set forth the permissible methods of
taking pursuant to such activity, ‘‘and
other means of effecting the least
practicable impact on such species or
stock and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance, and on
the availability of such species or stock
for taking’’ for certain subsistence uses.
NMFS regulations require applicants for
incidental take authorizations to include
information about the availability and
feasibility (economic and technological)
of equipment, methods, and manner of
conducting such activity or other means
of effecting the least practicable adverse
impact upon the affected species or
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stocks, their habitat (50 CFR
216.104(a)(11)).
Time and Frequency: The USFWS
plans to conduct research activities
throughout the course of the year
between April 1 and November 30,
2017.
Vessel Approach and Timing
Techniques: The USFWS will ensure
that its vessel approaches to beaches
with pinniped haul outs are conducted
so as to minimize or avoid disturbing
marine mammals. To the extent
possible, the vessel should approach the
beaches in a slow and controlled
approach, as far away as possible from
haul outs to prevent or minimize
flushing. Staff will also avoid or proceed
cautiously when operating boats in the
direct path of swimming seals that may
be present in the area.
Avoidance of Acoustic Impacts from
Cannon Nets: Cannon nets have a
measured SL of 128 dB at one m
(estimated based on a measurement of
98.4 dB at 30 m; L. Niles, pers. comm.,
December 2016); however, the SPL is
expected to be less than the thresholds
for airborne pinniped disturbance (e.g.
90 dB for harbor seals, and 100 dB for
all other pinnipeds) at 80 m from the
source. The USFWS will stay at least
100 m from all pinnipeds if cannon nets
are to be used for research purposes.
Avoidance of Visual and Acoustic
Contact with People: The USFWS will
instruct its members and research staff
to avoid making unnecessary noise and
not visually reveal themselves to
pinnipeds whenever practicable.
USFWS staff will stay at least 50 m from
hauled out pinnipeds, unless it is
absolutely necessary to approach seals
closer in order to continue conducting
endangered species conservation work.
When disturbance is unavoidable, staff
will work quickly and efficiently to
minimize the length of disturbance.
Researchers and staff will do so by
proceeding in a slow and controlled
manner, which allows for the seals to
slowly flush into the water. Staff will
also maintain a quiet working
atmosphere, avoiding loud noises, and
using hushed voices in the presence of
hauled-out pinnipeds. Pathways of
approach to the desired study or nesting
site will be chosen to minimize seal
disturbance if an activity event may
result in the disturbance of seals.
USFWS staff will scan the surrounding
waters near the haul outs, and if
predators (i.e., sharks) are seen, seals
will not be flushed by USFWS staff.
Researchers, USFWS staff, and
volunteers will be properly informed
about the MMPA take prohibitions, and
will educate the public on the
importance of not disturbing marine
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mammals, when applicable. Staff at
Nantucket NWR will remain present on
the beaches utilized by pinnipeds to
prevent anthropogenic disturbance
during times of high public use (late
spring–early fall). Staff at Monomoy
NWR will also be present on beaches
utilized by seals during the same time
of year, and will inform the public to
keep a distance from haul outs if an
issue is noticed. Similar to the USFWS,
the National Park Service also takes
precautionary mitigation to help prevent
seal take by the public. In August and
on the weekends in September, staff and
volunteers are present on the National
Seashore beaches to share with the
public the importance of preventing
disturbance to seals by keeping people
at a proper viewing distance of at least
50 m.
The presence/proximity of seal haul
outs and the loud sound created by the
firing of cannon nets are taken into
consideration when selecting trapping
sites for the Red Knot Stopover Study.
Trapping sites are decided based on the
presence of red knots, the number of
juveniles located within roosts, and the
observation of birds with attached
geolocators and flags. Trapping will not
take place on sites where there is a
strong possibility of disturbing seals
(i.e., closer than 100 m). The Red Knot
Stopover Study occurs during the time
of year (July–Sept) when the least
number of seals are present at the
activity sites.
Mitigation Conclusions
NMFS has carefully evaluated the
USFWS’s mitigation measures in the
context of ensuring that we prescribe
the means of affecting the least
practicable impact on the affected
marine mammal species and stocks and
their habitat. The 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
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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 vessel or visual
presence that NMFS expects 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 vessel or visual presence that
NMFS expects 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 vessel or visual presence
that NMFS expects 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 the
USFWS’s planned measures, NMFS has
determined that the 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.
Monitoring Measures
In order to issue an incidental take
authorization 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
IHAs 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
NMFS expects to be present in the
action area.
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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
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)
to better achieve the above goals.
The USFWS will conduct marine
mammal monitoring, in order to
implement the mitigation measures that
require real-time monitoring, and to
satisfy the monitoring requirements of
the IHA. The USFWS submitted a
marine mammal monitoring plan in
Section 13 and Appendix A of their IHA
application. These include:
Monitoring seals as project activities
are being conducted. Monitoring
requirements in relation to the USFWS’s
planned activities will include species
counts, numbers of observed
disturbances, and descriptions of the
disturbance behaviors during the
research activities, including location,
date, and time of the event. In addition,
the USFWS will record observations
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regarding the number and species of any
marine mammals either observed in the
water or hauled out. Behavior of seals
will be recorded on a three point scale
(1 = alert reaction; not considered
harassment, 2 = moving at least 2 body
lengths, or change in direction >90
degrees, 3 = flushing) (Table 2). USFWS
staff will also record and report all
observations of sick, injured, or
entangled marine mammals on
Monomoy NWR to the International
Fund for Animal Welfare (IFAW)
marine mammal rescue team, and will
report to NOAA if injured seals or
unusual species of marine mammals are
found at Nantucket NWR and Nomans
NWR. Tagged or marked marine
mammals will also be recorded and
reported to the appropriate research
organization or federal agency.
Photographs will be taken when
possible. This information will be
incorporated into a report for NMFS at
the end of the season. The USFWS will
also coordinate with any university,
state, or federal researchers to attain
additional data or observations that may
be useful for monitoring marine
mammal usage at the activity sites.
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 USFWS’s activities, the USFWS
will suspend research 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.
TABLE 2—DISTURBANCE SCALE OF PINNIPED RESPONSES TO IN-AIR SOURCES TO DETERMINE TAKE
Level
Type of
response
Definition
1 ......................
Alert ...............
2 * ....................
Movement ......
3 * ....................
Flush ..............
Seal head orientation or brief movement 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, changing from
a lying to a sitting position, or brief movement of less than twice the animal’s body length.
Movements in response to the source of disturbance, ranging from short withdrawals at least twice the animal’s body length to longer retreats over the beach, or if already moving a change of direction of greater
than 90 degrees.
All retreats (flushes) to the water.
* Only Levels 2 and 3 are considered take, whereas Level 1 is not.
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Reporting Measures
The USFWS will submit a draft report
to NMFS’ Office of Protected Resources
no later than 90 days after the expiration
of the IHA. The report will include a
summary of the information gathered
pursuant to the monitoring
requirements set forth in the IHA. The
USFWS will submit a final report to the
NMFS within 30 days after receiving
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comments from NMFS on the draft
report. If the USFWS receives no
comments from NMFS on the report,
NMFS will consider the draft report to
be the final report.
The report will describe the
operations conducted and sightings of
marine mammals near the project
activities. The report will provide full
documentation of methods, results, and
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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
human presence associated with the
USFWS’s activities.
4. A description of the
implementation and effectiveness of the
monitoring and mitigation measures of
the IHA 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., stampede),
USFWS personnel shall immediately
cease the specified activities and
immediately report the incident to the
Chief, Permits and Conservation
Division, Office of Protected Resources,
NMFS, and the Northeast Regional
Stranding Coordinator. 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).
The USFWS shall not resume its
activities until NMFS is able to review
the circumstances of the prohibited
take. We will work with the USFWS to
determine what is necessary to
minimize the likelihood of further
prohibited take and ensure MMPA
compliance. The USFWS may not
resume their activities until notified by
us via letter, email, or telephone.
In the event that the USFWS
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),
the USFWS will immediately report the
incident to the Chief, Permits and
Conservation Division, Office of
Protected Resources, NMFS, and the
Northeast Regional Stranding
Coordinator. 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
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will work with the USFWS to determine
whether modifications in the activities
are appropriate.
In the event that the USFWS
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), the USFWS will
report the incident to the Chief, Permits
and Conservation Division, Office of
Protected Resources, NMFS, and the
Northeast Regional Stranding
Coordinator within 24 hours of the
discovery. The USFWS personnel will
provide photographs or video footage (if
available) or other documentation of the
stranded animal sighting to us. The
USFWS can continue their survey
activities while NMFS reviews the
circumstances of the incident.
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 mitigation and
monitoring measures will 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 the USFWS personnel could disturb
animals hauled out on beaches near
research activities and that the animals
may alter their behavior or attempt to
move away from the USFWS personnel.
As discussed earlier, NMFS assumes
that pinnipeds that move greater than
two body lengths to longer retreats over
the beach, or if already moving, a
change of direction of greater than 90
degrees in response to the presence of
surveyors, or pinnipeds that flush into
the water, are behaviorally harassed,
and thus subject to Level B taking (Table
2). NMFS estimates that 39,666 gray
seals will be taken, by Level B
harassment, over the course of the IHA
(Table 3).
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This estimate is based on the number
of seals observed in past research years
that have been flushed during research
activities. USFWS biologists used their
knowledge of the number of seals that
use the haul outs near their research
activities, and how many of those may
be taken (Levels 2 and 3 on the
disturbance scale). The majority of takes
will occur on Monomoy NWR, which is
one of the main haul outs for gray seals
in the country. While the average
number of gray seals present (in regards
to Monomoy NWR) is less than observed
counts (B. Josephson, NOAA, personal
communication), not every hauled-out
seal on the beach is impacted from each
activity and not all seals are impacted
from every activity event. This is
especially true for Monomoy NWR
because the seal haul out stretches
across over four miles of beach. For
example, the gray seal counts on
Monomoy NWR are very high, but the
beaches are very large, and most of the
work takes place on the upper berm
close to the dune (farther away from
seals). During April and May when seals
are hauled out in very large numbers on
the refuge, they may be present at
beaches of varying width, between 30 m
and 300 m. In narrower areas, all of the
seals may be flushed; in mid-width
areas, some of the younger and smaller
seals may flush, but large males may
remain on the beach; and in the widest
area, USFWS activities may have no
impact at all on the hauled out seals.
Also, the amount of disturbance to seals
may vary based on staff activities (e.g.,
if project activities require staff to walk
quickly through an area versus spending
more time in one area close to seals).
Take numbers were estimated from the
number of seals using the refuge and the
times that the activity might overlap
with seal use areas. For example, most
of the staging counts are not done in
areas where seals haul out so the
number of disturbances is very low
during this task. Group size also played
into the estimates. USFWS staff would
impact a smaller number of seals during
times of the year when group sizes are
smaller (e.g., outside of April and May).
USFWS staff who have conducted these
activities for multiple years is provide
best information available to us about
the number of takes these activities may
cause. In this IHA, we have included
monitoring requirements that should
inform our take numbers in future years.
The take numbers for gray seals is
thought to be conservative, and likely an
overestimate. USFWS staff believe these
estimates are realistic and do not expect
to exceed the take numbers.
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Federal Register / Vol. 82, No. 40 / Thursday, March 2, 2017 / Notices
TABLE 3—ESTIMATED NUMBER OF GRAY SEAL TAKES PER ACTIVITY AT MONOMOY, NANTUCKET, AND NOMANS LAND
ISLAND NWRS
Gray seal
Age: all
Sex: Male & female
Number
Shorebird and Seabird Monitoring & Research ........................
Roseate Tern Staging Counts & Resighting ............................
Red Knot Stopover Study .........................................................
Northeastern beach tiger beetle Census ..................................
Coastal Shoreline Change Survey ...........................................
takes/event a
1000 (Monomoy) .....................
50 (Nantucket) ........................
10 (Nomans) ...........................
10 (Monomoy) .........................
10 (Nantucket) ........................
250 (Monomoy) .......................
150 (CACO) ............................
750 (Monomoy) .......................
500 (Monomoy) .......................
Number events/activity b
34 (Monomoy) .........................
8 (Nantucket)
3 (Nomans)
6 (Monomoy) ...........................
4 (Nantucket)
5 (Monomoy) ...........................
5 (CACO)
3 (Monomoy) ...........................
1 (Monomoy) ...........................
Total takes
34,430
100
2,000
2,250
500
39,280
a Number
of takes/event are estimates based on NOAA unpublished data (B. Josephson, personal communication) and USFWS field observa-
tions.
b Number of events/activity were calculated using the numbers in Table 1 of the USFWS’s application for each site location and duration.
NMFS estimates that 1,964 harbor
seals could be affected by Level B
behavioral harassment over the course
of the IHA. USFWS staff estimate that of
all of the seals hauled out in mixed
species haul outs, approximately five
percent are harbor seals. We estimated
the number of Level B takes of harbor
seals by taking 5 percent of the total
takes of gray seals (i.e., 5 percent of
39,280 is 1,964). These incidental
harassment take numbers represent less
than three percent of the affected stocks
of harbor seals and less than eight
percent of the stock of gray seals (Table
4). However, actual take may be slightly
less if animals decide to haul out at a
different location for the day or if
animals are foraging at the time of the
survey activities. The number of
individual seals taken is also assumed
to be less than the take estimate since
these species show high philopatry
(Waring et al., 2016; Wood et al., 2011).
We expect the take numbers to represent
the number of exposures, but assume
that the same seals may be behaviorally
harassed over multiple days, and the
likely number of individual seals that
may be harassed will be less. For
example, the maximum number of seals
observed hauled out on Monomoy NWR
during the year is 19,166 (B. Josephson,
NOAA, personal communication);
therefore, we expect the actual number
of individual takes to be closer to that
number for activities at Monomoy NWR.
Raw counts are not available for
Nantucket NWR and Nomans NWR.
TABLE 4—THE PERCENTAGE OF STOCK AFFECTED BY THE NUMBER OF TAKES PER SPECIES
Take
number
Species
Gray seal (Halichoerus grypus grypus) .......................................................................................
Harbor seal (Phoca vitulina concolor) .........................................................................................
39,280
1,964
Stock
abundance
* 505,000
75,834
Percent of
stock
7.78
2.59
* The Western North Atlantic stock of gray seals is comprised of the Canadian and U.S. populations. The U.S. population abundance estimate
is unknown, but the Canadian population abundance estimate is 505,000. The 2016 draft SAR states that the western North Atlantic stock is
equivalent to the Canada population.
Because of the required mitigation
measures and the likelihood that some
pinnipeds will avoid the area, NMFS
does not expect any injury, serious
injury, or mortality to pinnipeds to
occur and NMFS has not authorized
take by Level A harassment for this
activity.
Analysis and Determinations
sradovich on DSK3GMQ082PROD with NOTICES
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
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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 the USFWS’s survey
activities may disturb a small number of
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marine mammals hauled out on beaches
in the Complex, NMFS expects those
impacts to occur to a localized group of
animals. Marine mammals would likely
become alert or, at most, flush into the
water in reaction to the presence of the
USFWS’s personnel during the
activities. Much of the disturbance will
be limited to a short duration, allowing
marine mammals to reoccupy haul outs
within a short amount of time. Thus, the
planned activities are unlikely to result
in long-term impacts such as permanent
abandonment of the area because of the
availability of alternate areas for
pinnipeds to avoid the resultant
acoustic and visual disturbances from
the research activities
The USFWS’s activities will occur
during the least sensitive time (e.g.,
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Federal Register / Vol. 82, No. 40 / Thursday, March 2, 2017 / Notices
sradovich on DSK3GMQ082PROD with NOTICES
April through November, outside of the
pupping season) for hauled out
pinnipeds in the Complex. Thus, pups
or breeding adults will not be present
during the planned activity days. If
mothers and pups are observed, USFWS
staff will avoid disturbing them by
rescheduling surveys, if possible, or by
refraining from activities that may cause
disturbance (e.g., large movements or
flushing).
Moreover, the USFWS’s mitigation
measures regarding vessel approaches
and procedures that attempt to
minimize the potential to harass the
seals will minimize the potential for
flushing and large-scale movements.
Thus, the potential for large-scale
movements and flushing leading to
injury, serious injury, or mortality is
low.
In summary, NMFS anticipates that
impacts to hauled-out pinnipeds during
the USFWS’s planned research activities
would be behavioral harassment of
limited intensity (i.e., temporary
flushing at most). NMFS does not expect
stampeding, and therefore does not
expect injury or mortality to occur (see
Mitigation Measures 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 monitoring
and mitigation measures, NMFS finds
that the total marine mammal take from
the USFWS’s survey activities will have
a negligible impact on the affected
marine mammal species or stocks.
Small Numbers
As mentioned previously, NMFS
estimates that the USFWS’s planned
activities could potentially affect, by
Level B harassment only, two species of
marine mammal under our jurisdiction.
For each species, these estimates are
small numbers (less than three percent
of the affected stock of harbor seals and
less than eight percent of the stock of
gray seals) relative to the population
size (Table 4). As stated before, the
number of individual seals taken is also
assumed to be less than the take
estimate (number of exposures) since we
assume that the same seals may be
behaviorally harassed over multiple
days.
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 finds that the USFWS’s activities
will take small numbers of marine
mammals relative to the populations of
the affected species or stocks.
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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. Therefore, NMFS has
determined that the total taking of
affected species or stocks would not
have an unmitigable adverse impact on
the availability of such species or stocks
for taking for subsistence purposes.
Endangered Species Act (ESA)
NMFS does not expect that the
USFWS’s planned research activities
will 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)
NMFS prepared an EA and analyzed
the potential impacts to marine
mammals that may result from the
USFWS’s monitoring and research
activities. A FONSI was signed in
February 2017. A copy of the EA and
FONSI is available on our Web site at
https://www.nmfs.noaa.gov/pr/permits/
incidental/research.htm.
Authorization
NMFS has issued an IHA to the
USFWS for the potential harassment of
small numbers of two marine mammal
species incidental to the seabird and
shorebird monitoring and other research
activities in the Complex, provided the
previously mentioned mitigation,
monitoring and reporting.
Dated: February 24, 2017.
Donna S. Wieting,
Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. 2017–04002 Filed 3–1–17; 8:45 am]
BILLING CODE 3510–22–P
COMMODITY FUTURES TRADING
COMMISSION
Sunshine Act Meetings
11:00 a.m., Thursday,
March 9, 2017.
PLACE: Three Lafayette Centre, 1155 21st
Street NW., Washington, DC, 9th Floor
Commission Conference Room.
STATUS: Closed.
MATTERS TO BE CONSIDERED:
Surveillance, enforcement, and
examinations matters. In the event that
the time, date, or location of this
meeting changes, an announcement of
the change, along with the new time,
date, and/or place of the meeting will be
TIME AND DATE:
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posted on the Commission’s Web site at
https://www.cftc.gov.
CONTACT PERSON FOR MORE INFORMATION:
Christopher Kirkpatrick, 202–418–5964.
Natise Allen,
Executive Assistant.
[FR Doc. 2017–04113 Filed 2–28–17; 11:15 am]
BILLING CODE 6351–01–P
DEPARTMENT OF DEFENSE
Department of the Army
Notice of Intent To Grant Exclusive
Patent License to Diamond B
Technology Solutions, LLC; Billings,
MT
Department of the Army, DoD.
Notice of intent.
AGENCY:
ACTION:
The Department of the Army
hereby gives notice of its intent to grant
to Diamond B Technology Solutions,
LLC; a corporation having its principle
place of business at 3529 Gabel Rd.,
Billings, MT 59102, an exclusive
license.
SUMMARY:
Written objections must be filed
not later than 15 days following
publication of this announcement.
ADDRESSES: Send written objections to
U.S. Army Research Laboratory
Technology Transfer and Outreach
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Building 321 Room 110, Aberdeen
Proving Ground, MD 21005–5425.
FOR FURTHER INFORMATION CONTACT:
Thomas Mulkern, (410) 278–0889, EMail: ORTA@arl.army.mil
SUPPLEMENTARY INFORMATION: The
Department of the Army plans to grant
an exclusive license to Diamond B
Technology Solutions, LLC in all fields
of use relative to the following: ‘‘System
to Evaluate Airborne Hazards’’, US
Patent Application No.: 13/452,047,
Filing Date April 20, 2012.
The prospective exclusive license
may be granted unless within fifteen
(15) days from the date of this published
notice, the U.S. Army Research
Laboratory receives written objections
including evidence and argument that
establish that the grant of the license
would not be consistent with the
requirements of 35 U.S.C. 209(e) and 37
CFR 404.7(a)(1)(i). Competing
applications completed and received by
the U.S. Army Research Laboratory
within fifteen (15) days from the date of
this published notice will also be
treated as objections to the grant of the
contemplated exclusive license.
Objections submitted in response to
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DATES:
E:\FR\FM\02MRN1.SGM
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Agencies
[Federal Register Volume 82, Number 40 (Thursday, March 2, 2017)]
[Notices]
[Pages 12342-12348]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2017-04002]
[[Page 12342]]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XF101
Takes of Marine Mammals Incidental to Specified Activities;
Taking Marine Mammals Incidental to Seabird and Shorebird Monitoring
and Research at the Eastern Massachusetts National Wildlife Refuge
Complex, Massachusetts
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; issuance of an incidental harassment authorization.
-----------------------------------------------------------------------
SUMMARY: In accordance with the regulations implementing the Marine
Mammal Protection Act (MMPA) as amended, notification is hereby given
that NMFS has issued an incidental harassment authorization (IHA) to
the Eastern Massachusetts (MA) National Wildlife Refuge (NWR) Complex,
U.S. Fish and Wildlife Service (USFWS) to incidentally harass, by Level
B harassment only, marine mammals during seabird and shorebird
monitoring and other research activities in the Eastern MA NWR Complex
(Complex).
DATES: This Authorization is effective from April 1, 2017 through March
31, 2018.
National Environmental Policy Act (NEPA)
NMFS prepared an Environmental Assessment (EA) and analyzed the
potential impacts to marine mammals that would result from the USFWS's
monitoring and research activities. A Finding of No Significant Impact
(FONSI) was signed in March 2017. A copy of the EA and FONSI is
available on our Web site at https://www.nmfs.noaa.gov/pr/permits/incidental/research.htm.
FOR FURTHER INFORMATION CONTACT: Laura McCue, NMFS, Office of Protected
Resources, NMFS (301) 427-8401.
SUPPLEMENTARY INFORMATION:
Background
Section 101(a)(5)(D) of the MMPA 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 certain findings are made and
either regulations are issued or, if the taking is limited to
harassment, a notice of a proposed authorization is provided to the
public for review.
An authorization for incidental takings shall be granted if NMFS
finds that the taking will have a negligible impact on the species or
stock(s), will not have an unmitigable adverse impact on the
availability of the species or stock(s) for subsistence uses (where
relevant), and if the permissible methods of taking and requirements
pertaining to the mitigation, monitoring and reporting of such takings
are set forth. 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.''
Summary of Request
On March 16, 2016, NMFS received an application from the USFWS for
the taking of marine mammals incidental to seabird and shorebird
monitoring and research activities within the Complex. NMFS received
updated applications on September 14 and December 16, 2016 with updated
take numbers and mitigation measures. NMFS determined the application
complete and adequate on December 29, 2016.
The USFWS plans to conduct seabird and shorebird monitoring and
research at several locations within the Complex over a varying number
of days for each project. This authorization, will be valid for one
year, beginning on April 1, 2017. The following specific aspects of the
planned activities would likely result in the disturbance of marine
mammals: (1) Vessel landings; (2) research activities (e.g., cannon
nets, sign installation); and (3) human presence. Thus, NMFS
anticipates that take, by Level B harassment only, of gray seals
(Halichoerus grypus grypus) and harbor seals (Phoca vitulina concolor)
could result from the specified activity.
Description of the Specified Activity
Overview
The USFWS plans to conduct biological tasks for refuge purposes at
Monomoy NWR, Nantucket NWR, and Nomans Land Island NWR in MA. These
three refuges are managed through the Complex as part of the NWR System
of the USFWS. Complex staff census and monitor the presence and
productivity of breeding and migrating shorebirds using the beaches of
Monomoy, Nantucket, and Nomans Land Island NWRs from April 1-November
30, annually. Monitoring activities occur daily (on Monomoy and
Nantucket) from April-August and are necessary to document the
productivity (number of chicks fledged per pair) and population of
protected shorebird and seabird species. Monomoy NWR also participates
in several less frequent, but equally important, high priority
conservation tasks to monitor for threatened and endangered species,
including censusing northeastern beach tiger beetles (Cicindela
dorsalis) and participating in a red knot (Calidris canutus) migration
study during southward migration. Additionally, both Monomoy and
Nantucket NWRs serve as vital staging grounds for migrating roseate
terns (Sterna dougallii), where USFWS staff resight and stage counts. A
detailed description of the planned monitoring and research project is
provided in the Federal Register notice for the proposed IHA (82 FR
3738; January 12, 2017). Since that time, no changes have been made to
the planned activities. Therefore, a detailed description is not
provided here. Please refer to that Federal Register notice for the
description of the specific activity, including the dates and duration
and the specified geographic region.
Comment and Responses
A notice of NMFS's proposal to issue an IHA to the USFWS was
published in the Federal Register on January 12, 2017 (82 FR 3738).
That notice described, in detail, the USFWS's activity, the marine
mammal species that may be affected by the activity, and the
anticipated effects on marine mammals. During the 30-day public comment
period, NMFS received comments from the Marine Mammal Commission. The
Marine Mammal Commission recommended that NMFS issue the IHA, subject
to inclusion of the proposed mitigation, monitoring, and reporting
measures as described in our notice of proposed IHA and the
application. All measures proposed in the initial Federal Register
notice are included within the IHA.
Sound Sources and Sound Characteristics
NMFS does not expect acoustic stimuli to result from human
presence, and therefore, will not have the potential to harass marine
mammals, incidental to the conduct of the planned activities. One
activity (cannon nets) will have an acoustic component, but take from
this activity can be avoided through implementation of mitigation.
[[Page 12343]]
This section includes a brief explanation of the sound measurements
frequently used in the discussions of acoustic effects in this notice.
Sound pressure is the sound force per unit area and is usually measured
in micropascals ([mu]Pa), where 1 pascal (Pa) is the pressure resulting
from a force of one newton exerted over an area of 1 square meter (m).
Sound pressure level (SPL) is the ratio of a measured sound pressure
and a reference level. The commonly used reference pressure is 20
[mu]Pa for in air, and the units for SPLs are dB re: 20 [mu]Pa.
SPL (in decibels (dB)) = 20 log (pressure/reference pressure).
SPL is an instantaneous measurement expressed as the peak, the
peak-peak, or the root mean square (rms). Root mean square is the
square root of the arithmetic average of the squared instantaneous
pressure values. All references to SPL in this document refer to the
root mean square unless otherwise noted. SPL does not take into account
the duration of a sound.
Research Activities Sound Characteristics
Activities that have an acoustic component (e.g., cannon nets) are
not expected to reach the thresholds for Level B harassment. Cannon
nets are an airborne source of noise, and have a measured source level
(SL) of 128 dB at one m (estimated based on a measurement of 98.4 dB at
30 m; L. Niles, pers. comm., December 2016); however, based on
calculations using the SL and spherical spreading, the SPL is expected
to be less than the thresholds for airborne pinniped disturbance (e.g.
90 dB for harbor seals, and 100 dB for all other pinnipeds) at 25 m and
80 m from the source, respectively. The USFWS will stay at least 100 m
from all pinnipeds if cannon nets are used for research purposes.
Description of Marine Mammals in the Area of the Specified Activity
Table 1 provides the following information: All marine mammal
species with possible or confirmed occurrence in the activity area;
information on those species' regulatory status under the MMPA and the
ESA of 1973 (16 U.S.C. 1531 et seq.); abundance; occurrence and
seasonality in the activity area. A detailed description of the species
likely to be affected by the USFWS's project, including brief
introductions to the species and relevant stocks, available information
regarding population trends and threats, and information regarding
local occurrence, were provided in the Federal Register notice for the
proposed IHA (82 FR 3738; January 12, 2017); since that time, we are
not aware of any changes in the status of these species and stocks;
therefore, detailed descriptions are not provided here. Please refer to
that Federal Register notice for these descriptions. Please also refer
to the draft 2016 NMFS Marine Mammal Stock Assessment Report available
online at: https://www.nmfs.noaa.gov/pr/sars/ for further information on
the biology and distribution of these species.
Table 1--General Information on Marine Mammals That Could Potentially Haul Out on Northwest Seal Rock, November
2015 Through November 2016
----------------------------------------------------------------------------------------------------------------
Stock abundance
(CV, Nmin, most
Species Stock Regulatory recent PBR Occurrence and
status 1 2 abundance seasonality
survey) \3\
----------------------------------------------------------------------------------------------------------------
Gray seal (Halichoerus Western North MMPA-NC ESA-NL. 505,000 (unk; unk Year-round
grypus grypus). Atlantic. unk; unk) *. presence.
Harbor seal (Phoca vitulina Western North MMPA-NC ESA-NL. 75,834 (0.15; 2,006 Occasional.
concolor). Atlantic. 66,884; 2012).
----------------------------------------------------------------------------------------------------------------
\1\ MMPA: D = Depleted, S = Strategic, NC = Not Classified.
\2\ ESA: EN = Endangered, T = Threatened, DL = Delisted, NL = Not listed.
\3\ 2016 draft NMFS Stock Assessment Reports: Waring et al. (2016).
* The Western North Atlantic stock of gray seals is comprised of the Canadian and U.S. populations. The U.S.
population abundance estimate is unknown, but the Canadian population abundance estimate is 505,000. The 2016
draft SAR states that the western North Atlantic stock is equivalent to the Canada population.
Potential Effects of the Specified Activities on Marine Mammals and
Their Habitat
The effects of airborne noise and visual disturbance from
monitoring and research activities for the USFWS's project have the
potential to result in behavioral harassment of marine mammals in the
vicinity of the action area. The Federal Register notice for the
proposed IHA (82 FR 3738; January 12, 2017) included a discussion of
the effects of anthropogenic noise and visual disturbance on marine
mammals, therefore that information is not repeated here; please refer
to that Federal Register notice for that information.
Anticipated Effects on Marine Mammal Habitat
The main impact associated with the USFWS's project would be visual
and acoustic disturbance from human presence, vessels, and potential
cannon nets. The project would not result in permanent impacts to
habitats used directly by marine mammals, such as haulout sites, or
short-term impacts to food sources, but may have minor impacts to the
immediate substrate during installation of signage during the
monitoring and research project. These potential effects are discussed
in detail in the Federal Register notice for the proposed IHA (82 FR
3738; January 12, 2017, therefore that information is not repeated
here; please refer to that Federal Register notice for that
information.
Mitigation Measures
In order to issue an IHA under section 101(a)(5)(D) of the MMPA,
NMFS must set forth the permissible methods of taking pursuant to such
activity, ``and other means of effecting the least practicable impact
on such species or stock and its habitat, paying particular attention
to rookeries, mating grounds, and areas of similar significance, and on
the availability of such species or stock for taking'' for certain
subsistence uses. NMFS regulations require applicants for incidental
take authorizations to include information about the availability and
feasibility (economic and technological) of equipment, methods, and
manner of conducting such activity or other means of effecting the
least practicable adverse impact upon the affected species or
[[Page 12344]]
stocks, their habitat (50 CFR 216.104(a)(11)).
Time and Frequency: The USFWS plans to conduct research activities
throughout the course of the year between April 1 and November 30,
2017.
Vessel Approach and Timing Techniques: The USFWS will ensure that
its vessel approaches to beaches with pinniped haul outs are conducted
so as to minimize or avoid disturbing marine mammals. To the extent
possible, the vessel should approach the beaches in a slow and
controlled approach, as far away as possible from haul outs to prevent
or minimize flushing. Staff will also avoid or proceed cautiously when
operating boats in the direct path of swimming seals that may be
present in the area.
Avoidance of Acoustic Impacts from Cannon Nets: Cannon nets have a
measured SL of 128 dB at one m (estimated based on a measurement of
98.4 dB at 30 m; L. Niles, pers. comm., December 2016); however, the
SPL is expected to be less than the thresholds for airborne pinniped
disturbance (e.g. 90 dB for harbor seals, and 100 dB for all other
pinnipeds) at 80 m from the source. The USFWS will stay at least 100 m
from all pinnipeds if cannon nets are to be used for research purposes.
Avoidance of Visual and Acoustic Contact with People: The USFWS
will instruct its members and research staff to avoid making
unnecessary noise and not visually reveal themselves to pinnipeds
whenever practicable. USFWS staff will stay at least 50 m from hauled
out pinnipeds, unless it is absolutely necessary to approach seals
closer in order to continue conducting endangered species conservation
work. When disturbance is unavoidable, staff will work quickly and
efficiently to minimize the length of disturbance. Researchers and
staff will do so by proceeding in a slow and controlled manner, which
allows for the seals to slowly flush into the water. Staff will also
maintain a quiet working atmosphere, avoiding loud noises, and using
hushed voices in the presence of hauled-out pinnipeds. Pathways of
approach to the desired study or nesting site will be chosen to
minimize seal disturbance if an activity event may result in the
disturbance of seals. USFWS staff will scan the surrounding waters near
the haul outs, and if predators (i.e., sharks) are seen, seals will not
be flushed by USFWS staff.
Researchers, USFWS staff, and volunteers will be properly informed
about the MMPA take prohibitions, and will educate the public on the
importance of not disturbing marine mammals, when applicable. Staff at
Nantucket NWR will remain present on the beaches utilized by pinnipeds
to prevent anthropogenic disturbance during times of high public use
(late spring-early fall). Staff at Monomoy NWR will also be present on
beaches utilized by seals during the same time of year, and will inform
the public to keep a distance from haul outs if an issue is noticed.
Similar to the USFWS, the National Park Service also takes
precautionary mitigation to help prevent seal take by the public. In
August and on the weekends in September, staff and volunteers are
present on the National Seashore beaches to share with the public the
importance of preventing disturbance to seals by keeping people at a
proper viewing distance of at least 50 m.
The presence/proximity of seal haul outs and the loud sound created
by the firing of cannon nets are taken into consideration when
selecting trapping sites for the Red Knot Stopover Study. Trapping
sites are decided based on the presence of red knots, the number of
juveniles located within roosts, and the observation of birds with
attached geolocators and flags. Trapping will not take place on sites
where there is a strong possibility of disturbing seals (i.e., closer
than 100 m). The Red Knot Stopover Study occurs during the time of year
(July-Sept) when the least number of seals are present at the activity
sites.
Mitigation Conclusions
NMFS has carefully evaluated the USFWS's mitigation measures in the
context of ensuring that we prescribe the means of affecting the least
practicable impact on the affected marine mammal species and stocks and
their habitat. The 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 vessel or
visual presence that NMFS expects 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 vessel
or visual presence that NMFS expects 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 vessel or
visual presence that NMFS expects 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 the USFWS's planned measures, NMFS has
determined that the 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.
Monitoring Measures
In order to issue an incidental take authorization 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 IHAs 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 NMFS expects to be
present in the action area.
[[Page 12345]]
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 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) to better achieve the
above goals.
The USFWS will conduct marine mammal monitoring, in order to
implement the mitigation measures that require real-time monitoring,
and to satisfy the monitoring requirements of the IHA. The USFWS
submitted a marine mammal monitoring plan in Section 13 and Appendix A
of their IHA application. These include:
Monitoring seals as project activities are being conducted.
Monitoring requirements in relation to the USFWS's planned activities
will include species counts, numbers of observed disturbances, and
descriptions of the disturbance behaviors during the research
activities, including location, date, and time of the event. In
addition, the USFWS will record observations regarding the number and
species of any marine mammals either observed in the water or hauled
out. Behavior of seals will be recorded on a three point scale (1 =
alert reaction; not considered harassment, 2 = moving at least 2 body
lengths, or change in direction >90 degrees, 3 = flushing) (Table 2).
USFWS staff will also record and report all observations of sick,
injured, or entangled marine mammals on Monomoy NWR to the
International Fund for Animal Welfare (IFAW) marine mammal rescue team,
and will report to NOAA if injured seals or unusual species of marine
mammals are found at Nantucket NWR and Nomans NWR. Tagged or marked
marine mammals will also be recorded and reported to the appropriate
research organization or federal agency. Photographs will be taken when
possible. This information will be incorporated into a report for NMFS
at the end of the season. The USFWS will also coordinate with any
university, state, or federal researchers to attain additional data or
observations that may be useful for monitoring marine mammal usage at
the activity sites.
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
USFWS's activities, the USFWS will suspend research 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.
Table 2--Disturbance Scale of Pinniped Responses to In-Air Sources To
Determine Take
------------------------------------------------------------------------
Level Type of response Definition
------------------------------------------------------------------------
1..................... Alert................. Seal head orientation or
brief movement 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,
changing from a lying
to a sitting position,
or brief movement of
less than twice the
animal's body length.
2 *................... Movement.............. Movements in response to
the source of
disturbance, ranging
from short withdrawals
at least twice the
animal's body length to
longer retreats over
the beach, or if
already moving a change
of direction of greater
than 90 degrees.
3 *................... Flush................. All retreats (flushes)
to the water.
------------------------------------------------------------------------
* Only Levels 2 and 3 are considered take, whereas Level 1 is not.
Reporting Measures
The USFWS will submit a draft report to NMFS' Office of Protected
Resources no later than 90 days after the expiration of the IHA. The
report will include a summary of the information gathered pursuant to
the monitoring requirements set forth in the IHA. The USFWS will submit
a final report to the NMFS within 30 days after receiving comments from
NMFS on the draft report. If the USFWS receives no comments from NMFS
on the report, NMFS will consider the draft report to be the final
report.
The report will describe the operations conducted and sightings of
marine mammals near the project activities. 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.
[[Page 12346]]
3. An estimate of the number (by species) of marine mammals exposed
to human presence associated with the USFWS's activities.
4. A description of the implementation and effectiveness of the
monitoring and mitigation measures of the IHA 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., stampede), USFWS personnel shall immediately cease
the specified activities and immediately report the incident to the
Chief, Permits and Conservation Division, Office of Protected
Resources, NMFS, and the Northeast Regional Stranding Coordinator. 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).
The USFWS shall not resume its activities until NMFS is able to
review the circumstances of the prohibited take. We will work with the
USFWS to determine what is necessary to minimize the likelihood of
further prohibited take and ensure MMPA compliance. The USFWS may not
resume their activities until notified by us via letter, email, or
telephone.
In the event that the USFWS 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), the USFWS will immediately report the incident to the
Chief, Permits and Conservation Division, Office of Protected
Resources, NMFS, and the Northeast Regional Stranding Coordinator. 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 will work with the USFWS to
determine whether modifications in the activities are appropriate.
In the event that the USFWS 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), the USFWS will report the incident
to the Chief, Permits and Conservation Division, Office of Protected
Resources, NMFS, and the Northeast Regional Stranding Coordinator
within 24 hours of the discovery. The USFWS personnel will provide
photographs or video footage (if available) or other documentation of
the stranded animal sighting to us. The USFWS can continue their survey
activities while NMFS reviews the circumstances of the incident.
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 mitigation and
monitoring measures will 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 the
USFWS personnel could disturb animals hauled out on beaches near
research activities and that the animals may alter their behavior or
attempt to move away from the USFWS personnel.
As discussed earlier, NMFS assumes that pinnipeds that move greater
than two body lengths to longer retreats over the beach, or if already
moving, a change of direction of greater than 90 degrees in response to
the presence of surveyors, or pinnipeds that flush into the water, are
behaviorally harassed, and thus subject to Level B taking (Table 2).
NMFS estimates that 39,666 gray seals will be taken, by Level B
harassment, over the course of the IHA (Table 3).
This estimate is based on the number of seals observed in past
research years that have been flushed during research activities. USFWS
biologists used their knowledge of the number of seals that use the
haul outs near their research activities, and how many of those may be
taken (Levels 2 and 3 on the disturbance scale). The majority of takes
will occur on Monomoy NWR, which is one of the main haul outs for gray
seals in the country. While the average number of gray seals present
(in regards to Monomoy NWR) is less than observed counts (B. Josephson,
NOAA, personal communication), not every hauled-out seal on the beach
is impacted from each activity and not all seals are impacted from
every activity event. This is especially true for Monomoy NWR because
the seal haul out stretches across over four miles of beach. For
example, the gray seal counts on Monomoy NWR are very high, but the
beaches are very large, and most of the work takes place on the upper
berm close to the dune (farther away from seals). During April and May
when seals are hauled out in very large numbers on the refuge, they may
be present at beaches of varying width, between 30 m and 300 m. In
narrower areas, all of the seals may be flushed; in mid-width areas,
some of the younger and smaller seals may flush, but large males may
remain on the beach; and in the widest area, USFWS activities may have
no impact at all on the hauled out seals. Also, the amount of
disturbance to seals may vary based on staff activities (e.g., if
project activities require staff to walk quickly through an area versus
spending more time in one area close to seals). Take numbers were
estimated from the number of seals using the refuge and the times that
the activity might overlap with seal use areas. For example, most of
the staging counts are not done in areas where seals haul out so the
number of disturbances is very low during this task. Group size also
played into the estimates. USFWS staff would impact a smaller number of
seals during times of the year when group sizes are smaller (e.g.,
outside of April and May). USFWS staff who have conducted these
activities for multiple years is provide best information available to
us about the number of takes these activities may cause. In this IHA,
we have included monitoring requirements that should inform our take
numbers in future years.
The take numbers for gray seals is thought to be conservative, and
likely an overestimate. USFWS staff believe these estimates are
realistic and do not expect to exceed the take numbers.
[[Page 12347]]
Table 3--Estimated Number of Gray Seal Takes per Activity at Monomoy, Nantucket, and Nomans Land Island NWRs
----------------------------------------------------------------------------------------------------------------
Gray seal
-----------------------------------------------------------------------------------------------------------------
Age: all Sex: Male & female
----------------------------------------------------------------------------------------------------------------
Number takes/event \a\ Number events/activity \b\ Total takes
----------------------------------------------------------------------------------------------------------------
Shorebird and Seabird Monitoring & 1000 (Monomoy)............ 34 (Monomoy).............. 34,430
Research. 50 (Nantucket)............ 8 (Nantucket).............
10 (Nomans)............... 3 (Nomans)................
Roseate Tern Staging Counts & Resighting 10 (Monomoy).............. 6 (Monomoy)............... 100
10 (Nantucket)............ 4 (Nantucket).............
Red Knot Stopover Study................. 250 (Monomoy)............. 5 (Monomoy)............... 2,000
150 (CACO)................ 5 (CACO)..................
Northeastern beach tiger beetle Census.. 750 (Monomoy)............. 3 (Monomoy)............... 2,250
Coastal Shoreline Change Survey......... 500 (Monomoy)............. 1 (Monomoy)............... 500
---------------
39,280
----------------------------------------------------------------------------------------------------------------
\a\ Number of takes/event are estimates based on NOAA unpublished data (B. Josephson, personal communication)
and USFWS field observations.
\b\ Number of events/activity were calculated using the numbers in Table 1 of the USFWS's application for each
site location and duration.
NMFS estimates that 1,964 harbor seals could be affected by Level B
behavioral harassment over the course of the IHA. USFWS staff estimate
that of all of the seals hauled out in mixed species haul outs,
approximately five percent are harbor seals. We estimated the number of
Level B takes of harbor seals by taking 5 percent of the total takes of
gray seals (i.e., 5 percent of 39,280 is 1,964). These incidental
harassment take numbers represent less than three percent of the
affected stocks of harbor seals and less than eight percent of the
stock of gray seals (Table 4). However, actual take may be slightly
less if animals decide to haul out at a different location for the day
or if animals are foraging at the time of the survey activities. The
number of individual seals taken is also assumed to be less than the
take estimate since these species show high philopatry (Waring et al.,
2016; Wood et al., 2011). We expect the take numbers to represent the
number of exposures, but assume that the same seals may be behaviorally
harassed over multiple days, and the likely number of individual seals
that may be harassed will be less. For example, the maximum number of
seals observed hauled out on Monomoy NWR during the year is 19,166 (B.
Josephson, NOAA, personal communication); therefore, we expect the
actual number of individual takes to be closer to that number for
activities at Monomoy NWR. Raw counts are not available for Nantucket
NWR and Nomans NWR.
Table 4--The Percentage of Stock Affected by the Number of Takes per Species
----------------------------------------------------------------------------------------------------------------
Stock Percent of
Species Take number abundance stock
----------------------------------------------------------------------------------------------------------------
Gray seal (Halichoerus grypus grypus)........................... 39,280 * 505,000 7.78
Harbor seal (Phoca vitulina concolor)........................... 1,964 75,834 2.59
----------------------------------------------------------------------------------------------------------------
* The Western North Atlantic stock of gray seals is comprised of the Canadian and U.S. populations. The U.S.
population abundance estimate is unknown, but the Canadian population abundance estimate is 505,000. The 2016
draft SAR states that the western North Atlantic stock is equivalent to the Canada population.
Because of the required mitigation measures and the likelihood that
some pinnipeds will avoid the area, NMFS does not expect any injury,
serious injury, or mortality to pinnipeds to occur and NMFS has not
authorized take by Level A harassment for this activity.
Analysis and 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 the USFWS's survey activities may disturb a small number
of marine mammals hauled out on beaches in the Complex, NMFS expects
those impacts to occur to a localized group of animals. Marine mammals
would likely become alert or, at most, flush into the water in reaction
to the presence of the USFWS's personnel during the activities. Much of
the disturbance will be limited to a short duration, allowing marine
mammals to reoccupy haul outs within a short amount of time. Thus, the
planned activities are unlikely to result in long-term impacts such as
permanent abandonment of the area because of the availability of
alternate areas for pinnipeds to avoid the resultant acoustic and
visual disturbances from the research activities
The USFWS's activities will occur during the least sensitive time
(e.g.,
[[Page 12348]]
April through November, outside of the pupping season) for hauled out
pinnipeds in the Complex. Thus, pups or breeding adults will not be
present during the planned activity days. If mothers and pups are
observed, USFWS staff will avoid disturbing them by rescheduling
surveys, if possible, or by refraining from activities that may cause
disturbance (e.g., large movements or flushing).
Moreover, the USFWS's mitigation measures regarding vessel
approaches and procedures that attempt to minimize the potential to
harass the seals will minimize the potential for flushing and large-
scale movements. Thus, the potential for large-scale movements and
flushing leading to injury, serious injury, or mortality is low.
In summary, NMFS anticipates that impacts to hauled-out pinnipeds
during the USFWS's planned research activities would be behavioral
harassment of limited intensity (i.e., temporary flushing at most).
NMFS does not expect stampeding, and therefore does not expect injury
or mortality to occur (see Mitigation Measures 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 monitoring and mitigation
measures, NMFS finds that the total marine mammal take from the USFWS's
survey activities will have a negligible impact on the affected marine
mammal species or stocks.
Small Numbers
As mentioned previously, NMFS estimates that the USFWS's planned
activities could potentially affect, by Level B harassment only, two
species of marine mammal under our jurisdiction. For each species,
these estimates are small numbers (less than three percent of the
affected stock of harbor seals and less than eight percent of the stock
of gray seals) relative to the population size (Table 4). As stated
before, the number of individual seals taken is also assumed to be less
than the take estimate (number of exposures) since we assume that the
same seals may be behaviorally harassed over multiple days.
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 finds that the USFWS's activities will 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. Therefore, NMFS has determined that the total taking of
affected species or stocks would not have an unmitigable adverse impact
on the availability of such species or stocks for taking for
subsistence purposes.
Endangered Species Act (ESA)
NMFS does not expect that the USFWS's planned research activities
will 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)
NMFS prepared an EA and analyzed the potential impacts to marine
mammals that may result from the USFWS's monitoring and research
activities. A FONSI was signed in February 2017. A copy of the EA and
FONSI is available on our Web site at https://www.nmfs.noaa.gov/pr/permits/incidental/research.htm.
Authorization
NMFS has issued an IHA to the USFWS for the potential harassment of
small numbers of two marine mammal species incidental to the seabird
and shorebird monitoring and other research activities in the Complex,
provided the previously mentioned mitigation, monitoring and reporting.
Dated: February 24, 2017.
Donna S. Wieting,
Director, Office of Protected Resources, National Marine Fisheries
Service.
[FR Doc. 2017-04002 Filed 3-1-17; 8:45 am]
BILLING CODE 3510-22-P