Taking and Importing Marine Mammals; U.S. Navy's Atlantic Fleet Active Sonar Training (AFAST), 4844-4885 [E9-1706]
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Federal Register / Vol. 74, No. 16 / Tuesday, January 27, 2009 / Rules and Regulations
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 216
[Docket No. 080724897–81621–02]
RIN 0648–AW90
Taking and Importing Marine
Mammals; U.S. Navy’s Atlantic Fleet
Active Sonar Training (AFAST)
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AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
SUMMARY: NMFS, upon application from
the U.S. Navy (Navy), is issuing
regulations to govern the unintentional
taking of marine mammals incidental to
activities conducted off the U.S.
Atlantic Coast and in the Gulf of Mexico
for the period of January 2009 through
January 2014. The Navy’s activities are
considered military readiness activities
pursuant to the Marine Mammal
Protection Act (MMPA), as amended by
the National Defense Authorization Act
for Fiscal Year 2004 (NDAA). These
regulations, which allow for the
issuance of ‘‘Letters of Authorization’’
(LOAs) for the incidental take of marine
mammals during the described activities
and specified timeframes, prescribe the
permissible methods of taking and other
means of affecting the least practicable
adverse impact on marine mammal
species and their habitat, as well as
requirements pertaining to the
monitoring and reporting of such taking.
DATES: Effective January 22, 2009
through January 22, 2014.
ADDRESSES: A copy of the Navy’s
application (which contains a list of the
references used in this document),
NMFS’ Record of Decision (ROD), and
other documents cited herein may be
obtained by writing to Michael Payne,
Chief, Permits, Conservation and
Education Division, Office of Protected
Resources, National Marine Fisheries
Service, 1315 East-West Highway, Silver
Spring, MD 20910–3225 or by telephone
via the contact listed here (see FOR
FURTHER INFORMATION CONTACT).
FOR FURTHER INFORMATION CONTACT: Jolie
Harrison, Office of Protected Resources,
NMFS, (301) 713–2289, ext. 166.
SUPPLEMENTARY INFORMATION: Extensive
Supplementary Information was
provided in the proposed rule for this
activity, which was published in the
Federal Register on Tuesday, October
14, 2008 (73 FR 60754). This
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information will not be reprinted here
in its entirety; rather, all sections from
the proposed rule will be represented
herein and will contain either a
summary of the material presented in
the proposed rule or a note referencing
the page(s) in the proposed rule where
the information may be found. Any
information that has changed since the
proposed rule was published will be
addressed herein. Additionally, this
final rule contains a section that
responds to the comments received
during the public comment period.
Background
Sections 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1361 et seq.) direct
the Secretary of Commerce (Secretary)
to allow, upon request, the incidental,
but not intentional taking of marine
mammals by U.S. citizens who engage
in a specified activity (other than
commercial fishing) during periods of
not more than five consecutive years
each if certain findings are made and
regulations are issued or, if the taking is
limited to harassment and of no more
than 1 year, the Secretary shall issue a
notice of proposed authorization for
public review.
Authorization 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,
and if the permissible methods of taking
and requirements pertaining to the
mitigation, monitoring and reporting of
such taking 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.
The NDAA (Pub. L. 108–136)
removed the ‘‘small numbers’’ and
‘‘specified geographical region’’
limitations and amended the definition
of ‘‘harassment’’ as it applies to a
‘‘military readiness activity’’ to read as
follows (Section 3(18)(B) of the MMPA):
(i) Any act that injures or has the
significant potential to injure a marine
mammal or marine mammal stock in the wild
[Level A Harassment]; or
(ii) Any act that disturbs or is likely to
disturb a marine mammal or marine mammal
stock in the wild by causing disruption of
natural behavioral patterns, including, but
not limited to, migration, surfacing, nursing,
breeding, feeding, or sheltering, to a point
where such behavioral patterns are
abandoned or significantly altered [Level B
Harassment].
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Summary of Request
On February 4, 2008, NMFS received
an application from the Navy requesting
authorization for the take of individuals
of 40 species of marine mammals
incidental to upcoming Navy training
activities, maintenance, and research,
development, testing, and evaluation
(RDT&E) activities to be conducted
within the Atlantic Fleet Active Sonar
Training (AFAST) Study Area, which
extends east from the Atlantic Coast of
the U.S. to 45° W. long. and south from
the Atlantic and Gulf of Mexico Coasts
to approximately 23° N. lat., but not
encompassing the Bahamas (see Figure
1–1 in the Navy’s Application), over the
course of 5 years. These activities are
military readiness activities under the
provisions of the NDAA. The Navy
states, and NMFS concurs, that these
military readiness activities may
incidentally take marine mammals
present within the AFAST Study Area
by exposing them to sound from midfrequency or high frequency active
sonar (MFAS/HFAS) or to employment
of the improved extended echo ranging
(IEER) system. The IEER consists of an
explosive source sonobuoy (AN/SSQ–
110A) and an air deployable active
receiver (ADAR) sonobuoy (AN/SSQ–
101). The Navy requested authorization
to take individuals of 40 species of
marine mammals by Level B
Harassment. Further, though they do not
anticipate it to occur, the Navy requests
authorization to take, by injury or
mortality, up to 10 beaked whales over
the course of the 5-yr regulations.
Background of Navy Request
The proposed rule contains a
description of the Navy’s mission, their
responsibilities pursuant to Title 10 of
the United States Code, and the specific
purpose and need for the activities for
which they requested incidental take
authorization. The description
contained in the proposed rule has not
changed (73 FR 60754).
Description of the Specified Activities
The proposed rule contains a
complete description of the Navy’s
specified activities that are covered by
these final regulations, and for which
the associated incidental take of marine
mammals will be authorized in the
related LOAs. The proposed rule
describes the nature and number of both
the anti-submarine warfare (ASW) and
mine warfare training (MIW) exercises
involving both mid- and high-frequency
active sonar (MFAS and HFAS), as well
as the IEER exercises involving small
explosive detonations. It also describes
the sound sources used (73 FR 60754,
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pages 60755–60762). The narrative
description of the action contained in
the proposed rule has not changed, with
the exception of the change from IEER
to the Advanced Extended Echo
Ranging (AEER) discussed below.
Tables 1 and 2 summarize the sonar and
IEER exercise types used in these
training exercises and the hours of
sonar.
Navy is developing the AEER system
as a replacement to the IEER system.
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AEER would use a new active sonobuoy
(AN/SSQ–125) that utilizes a tonal (or a
ping) vice impulsive (or explosive)
sound source as a replacement for the
AN/SSQ–110A. AEER will still use the
ADAR sonobuoy as the systems receiver
and will be deployed by Maritime Patrol
Aircraft. As AEER is introduced for
Fleet use, IEER will be removed. The
same total number of buoys will be
deployed as were presented in the
proposed rule, but a subset of them will
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be AEER instead of IEER. The small
difference in the number of anticipated
marine mammal takes that will result
from this change is indicated in the take
table (Table 6), along with other minor
modifications. This small change in the
take numbers did not affect NMFS’
analysis of and conclusions regarding
the proposed action.
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The AFAST proposed rule contains a
description of the AFAST Study Area
along with a description of the areas in
which certain types of activities will
occur. Table 3, included here,
summarizes the areas in which certain
exercise types will occur. This section
also contains a description of the North
Atlantic right whale (NARW) critical
habitat and the National Marine
Sanctuaries (NMS) within the AFAST
Study Area. The description of the
AFAST Study Area in the proposed rule
has not changed, with the exception of
the paragraph relating to the NMSs,
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Description of Marine Mammals in the
Area of the Specified Activities
There are 43 marine mammal species
with possible or confirmed occurrence
in the AFAST Study Area. As indicated
in Table 4, there are 36 cetacean species
(7 mysticetes and 29 odontocetes), six
pinnipeds, and one sirenian (manatee).
Six marine mammal species listed as
federally endangered under the
Endangered Species Act (ESA) and
under the jurisdiction of NMFS occur in
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below (73 FR 60754, pages 60762–
60764).
The paragraph related to NMSs in the
proposed rule should be replaced with
the following paragraph:
The Navy will not conduct active
sonar activities within the Stellwagen
Bank, Monitor, Gray’s Reef, Flower
Garden Banks, and Florida Keys
National Marine Sanctuaries and will
avoid these sanctuaries by observing a
5-km (2.7-NM) buffer. At all times, the
Navy will conduct AFAST activities in
a manner that avoids to the maximum
extent practicable any adverse impacts
on sanctuary resources. In the event the
Navy determines AFAST activities, due
to operational requirements, are likely
to destroy, cause the loss of, or injure
any sanctuary resource (for Stellwagen
Bank National Marine Sanctuary, the
threshold is ‘‘may’’ destroy, cause the
loss of, or injure), the Navy would first
consult with the Director, Office of
National Marine Sanctuaries in
accordance with 16 U.S.C. 1434(d).
Although activities in the Sanctuaries
are not planned or anticipated, NMFS’
analysis, for purposes of the MMPA
considers the effects on marine
mammals of the Navy’s conducting
activities in the biologically important
areas that occur in or near Sanctuaries.
the AFAST Study Area: The NARW,
humpback whale, sei whale, fin whale,
blue whale, and sperm whale. Manatees
are managed by the U.S. Fish and
Wildlife Service and will not be
addressed further here. The proposed
rule contains a discussion of two
species that are not considered further
in the analysis (beluga whales and
ringed seals) because of their rarity in
the AFAST Study Area. The proposed
rule also contains a discussion of
important areas, including NARW
critical habitat, humpback whale
feeding grounds in the northeast, and
sperm whale calving and nursing
grounds in the Mississippi Delta area.
Last, the proposed rule includes a
discussion of the methods used to
estimate marine mammal density in the
AFAST Study Area. The Description of
Marine Mammals in the Area of the
Specified Activities section has not
changed from what was in the proposed
rule (73 FR 60754, pages 60766–60767).
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AFAST Study Area
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A Brief Background on Sound
The proposed rule contains a section
that provides a brief background on the
principles of sound that are frequently
referred to in this rulemaking (73 FR
60754, pages 60767–60769). This
section also includes a discussion of the
functional hearing ranges of the
different groups of marine mammals (by
frequency) as well as a discussion of the
two main sound metrics used in NMFS
analysis (sound pressure level (SPL) and
sound energy level (SEL)). The
information contained in the proposed
rule has not changed.
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Potential Effects of Specified Activities
on Marine Mammals
With respect to the MMPA, NMFS’
effects assessment serves four primary
purposes: (1) To prescribe the
permissible methods of taking (i.e.,
Level B Harassment (behavioral
harassment), Level A Harassment
(injury), or mortality, including an
identification of the number and types
of take that could occur by Level A or
B harassment or mortality) and to
prescribe other means of affecting the
least practicable adverse impact on such
species or stock and its habitat (i.e.,
mitigation); (2) to determine whether
the specified activity will have a
negligible impact on the affected species
or stocks of marine mammals (based on
the likelihood that the activity will
adversely affect the species or stock
through effects on annual rates of
recruitment or survival); (3) to
determine whether the specified activity
will have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (however,
there are no subsistence communities
that would be affected in the AFAST
Study Area, so this determination is
inapplicable for this rulemaking); and
(4) to prescribe requirements pertaining
to monitoring and reporting.
In the Potential Effects of Specified
Activities on Marine Mammals section
of the proposed rule, NMFS included a
qualitative discussion of the different
ways that MFAS/HFAS and underwater
explosive detonations (IEER) may
potentially affect marine mammals
(some of which NMFS would not
classify as harassment). See 73 FR
60754, pages 60769–60781. Marine
mammals may experience direct
physiological effects (such as threshold
shift), acoustic masking, impaired
communications, stress responses, and
behavioral disturbance. This section
also included a discussion of some of
the suggested explanations for the
association between the use of MFAS
and marine mammal strandings (such as
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behaviorally mediated bubble growth)
that has been observed a limited number
of times in certain circumstances (the
specific events are also described). See
73 FR 60754, pages 60777–60781. The
information contained in Potential
Effects of Specified Activities on Marine
Mammals section from the proposed
rule has not changed, with the
exception of the following sentence. On
page 60779, NMFS said ‘‘Other species
(Stenella coeruleoalba, Kogia breviceps
and Balaenoptera acutorostrata) have
stranded, but in much lower numbers
and less consistently than beaked
whales.’’ As a member of the public
pointed out, and as NMFS has
previously stated, there was no likely
association between the minke whale
and spotted dolphin strandings referred
to here and the operation of MFAS.
Therefore, the sentence should read
‘‘Other species, such as Kogia breviceps,
have stranded in association with the
operation of MFAS, but in much lower
numbers and less consistently than
beaked whales.’’
Later, in the Estimated Take of Marine
Mammals section, NMFS relates and
quantifies the potential effects to marine
mammals from MFAS/HFAS and
underwater detonation of explosives
discussed here to the MMPA definitions
of Level A and Level B Harassment.
NMFS has also considered the effects of
mortality on these species.
Mitigation
In order to issue an incidental take
authorization (ITA) under Section
101(a)(5)(A) of the MMPA, NMFS must
prescribe regulations setting forth the
‘‘permissible methods of taking
pursuant to such activity, and other
means of affecting the least practicable
adverse impact on such species or stock
and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance.’’ The
National Defense Authorization Act
(NDAA) of 2004 amended the MMPA as
it relates to military readiness activities
and the incidental take authorization
process such that ‘‘least practicable
adverse impact’’ shall include
consideration of personnel safety,
practicality of implementation, and
impact on the effectiveness of the
‘‘military readiness activity’’. The
AFAST activities described in the
proposed rule are considered military
readiness activities.
NMFS reviewed the Navy’s proposed
AFAST activities and the proposed
AFAST mitigation measures (which the
Navy refers to as Protective Measures)
presented in the Navy’s application to
determine whether the activities and
mitigation measures were capable of
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achieving the least practicable adverse
effect on marine mammals. NMFS
determined that further discussion was
necessary regarding: (1) General
minimization of marine mammal
impacts; (2) minimization of impacts
within the southeastern NARW critical
habitat; and (3) the potential
relationship between the operation of
MFAS/HFAS and marine mammal
strandings.
Any mitigation measure prescribed by
NMFS should be known 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 below:
(a) Avoidance or minimization of
injury or death of marine mammals
wherever possible (goals b, c, and d may
contribute to this goal).
(b) A reduction in the numbers of
marine mammals (total number or
number at biologically important time
or location) exposed to received levels
of MFAS/HFAS, underwater
detonations, or other activities expected
to result in the take of marine mammals
(this goal may contribute to a, above, or
to reducing harassment takes only).
(c) A reduction in the number of times
(total number or number at biologically
important time or location) individuals
would be exposed to received levels of
MFAS/HFAS, underwater detonations,
or other activities expected to result in
the take of marine mammals (this goal
may contribute to a, above, or to
reducing harassment takes only).
(d) A reduction in the intensity of
exposures (either total number or
number at biologically important time
or location) to received levels of MFAS/
HFAS, underwater detonations, or other
activities expected to result in the take
of marine mammals (this goal may
contribute to a, above, or to reducing the
severity of harassment takes only).
(e) A reduction in 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.
(f) For monitoring directly related to
mitigation—an increase in the
probability of detecting marine
mammals, thus allowing for more
effective implementation of the
mitigation (shut-down zone, etc.).
NMFS worked with the Navy to
identify potential additional practicable
and effective mitigation measures,
which included a careful balancing of
the likely benefit of any particular
measure to the marine mammals with
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the likely effect of that measure on
personnel safety, practicality of
implementation, and impact on the
‘‘military-readiness activity.’’ NMFS and
the Navy developed additional
mitigation measures that address the
concerns mentioned above, including
the development of Planning Awareness
Areas (PAAs), additional minimization
of impacts in the southeastern NARW
critical habitat, and a Stranding
Response Plan.
The Navy’s proposed mitigation
measures, as well as the Planning
Awareness Areas (PAAs), additional
minimization of impacts in the
southeastern NARW critical habitat, and
Stranding Response Plan, which are
required under these regulations, were
described in detail in the proposed rule
(73 FR 60754, pages 60781–60789). The
Navy’s measures address personnel
training, lookout and watchstander
responsibilities, operating procedures
for training activities using both MFAS/
HFAS and IEER, additional measures for
TORPEXs in the northeastern NARW
critical habitat, and mitigation related to
vessel traffic and the NARW. No
changes have been made to the
mitigation measures described in the
proposed rule, with the exception of
adding that night vision devices shall be
available to all ship crews and air crews
for use as appropriate and making the
IEER mitigation applicable to the newly
described AEER system as well.
Additionally, the definition for
‘‘Exhibiting Indicators of Distress’’,
which was originally included in the
codified text of the proposed rule, has
been removed in the final rule. The
definition, which may be found in the
AFAST Stranding Response Plan, was
not included in the codified text
because it could potentially be modified
(pursuant to the adaptive management
component of the rule) based on new
data.
The final AFAST Stranding Response
Plan, which includes a shutdown
protocol, a stranding investigation plan,
and a requirement for Navy and NMFS
to implement a memorandum of
agreement (MOA) that will establish a
framework whereby the Navy can (and
provide the Navy examples of how they
can best) assist NMFS with stranding
investigations in certain circumstances,
may be viewed at: https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications.
Additionally, the mitigation measures
are included in full in the codified text
of the regulations.
NMFS has determined that the Navy’s
proposed mitigation measures (which
include a suite of measures that
specifically address vessel transit and
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the NARW), along with the Planning
Awareness Areas (PAAs), additional
minimization of impacts in the
southeastern NARW critical habitat, and
the Stranding Response Plan (and when
the Adaptive Management (see Adaptive
Management below) component is taken
into consideration) are adequate means
of effecting the least practicable adverse
impacts on marine mammal species or
stocks and their habitat, paying
particular attention to rookeries, mating
grounds, and areas of similar
significance, while also considering
personnel safety, practicality of
implementation, and impact on the
effectiveness of the military readiness
activity. The justification for this
conclusion is discussed in the
Mitigation Conclusion section of the
proposed rule (73 FR 60836, pages
60789–60790). The Mitigation
Conclusion Section of the proposed rule
has not changed.
Research and Conservation Measures
for Marine Mammals
The Navy provides a significant
amount of funding and support for
marine research. The Navy provided
$26 million in Fiscal Year 2008 and
plans for $22 million in Fiscal Year
2009 to universities, research
institutions, Federal laboratories,
private companies, and independent
researchers around the world to study
marine mammals. Over the past five
years the Navy has funded over $100
million in marine mammal research.
The Navy sponsors seventy percent of
all U.S. research concerning the effects
of human-generated sound on marine
mammals and 50 percent of such
research conducted worldwide. Major
topics of Navy-supported research
include the following:
• Better understanding of marine
species distribution and important
habitat areas,
• Developing methods to detect and
monitor marine species before and
during training,
• Understanding the effects of sound
on marine mammals, sea turtles, fish,
and birds, and
• Developing tools to model and
estimate potential effects of sound.
The Navy’s Office of Naval Research
currently coordinates six programs that
examine the marine environment and
are devoted solely to studying the
effects of noise and/or the
implementation of technology tools that
will assist the Navy in studying and
tracking marine mammals. The six
programs are as follows:
• Environmental Consequences of
Underwater Sound,
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• Non-Auditory Biological Effects of
Sound on Marine Mammals,
• Effects of Sound on the Marine
Environment,
• Sensors and Models for Marine
Environmental Monitoring,
• Effects of Sound on Hearing of
Marine Animals, and
• Passive Acoustic Detection,
Classification, and Tracking of Marine
Mammals.
The Navy has also developed the
technical reports referenced within this
document and the AFAST EIS, such as
the Marine Resource Assessments.
Furthermore, research cruises by NMFS
and by academic institutions have
received funding from the U.S. Navy.
The Navy has sponsored several
workshops to evaluate the current state
of knowledge and potential for future
acoustic monitoring of marine
mammals. The workshops brought
together acoustic experts and marine
biologists from the Navy and other
research organizations to present data
and information on current acoustic
monitoring research efforts and to
evaluate the potential for incorporating
similar technology and methods on
instrumented ranges. However, acoustic
detection, identification, localization,
and tracking of individual animals still
requires a significant amount of research
effort to be considered a reliable method
for marine mammal monitoring. The
Navy supports research efforts on
acoustic monitoring and will continue
to investigate the feasibility of passive
acoustics as a potential mitigation and
monitoring tool.
Overall, the Navy will continue to
fund ongoing marine mammal research,
and is planning to coordinate long term
monitoring/studies of marine mammals
on various established ranges and
operating areas. The Navy will continue
to research and contribute to university/
external research to improve the state of
the science regarding marine species
biology and acoustic effects. These
efforts include mitigation and
monitoring programs; data sharing with
NMFS and via the literature for research
and development efforts; and future
research as described previously.
Long-Term Prospective Study
Apart from this final rule, NMFS,
with input and assistance from the Navy
and several other agencies and entities,
will perform a longitudinal
observational study of marine mammal
strandings to systematically observe and
record the types of pathologies and
diseases and investigate the relationship
with potential causal factors (e.g., sonar,
seismic, weather). The proposed rule
contained an outline of the proposed
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(f) A better understanding and record
of the manner in which the authorized
entity complies with the incidental take
authorization.
Monitoring
In order to issue an ITA for an
activity, Section 101(a)(5)(A) 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 LOAs must
include the suggested means of
accomplishing the necessary monitoring
and reporting that will result in
increased knowledge of the species and
of the level of taking or impacts on
populations of marine mammals that are
expected to be present.
Monitoring measures prescribed by
NMFS should accomplish one or more
of the following general goals:
(a) An increase in the probability of
detecting marine mammals, both within
the safety zone (thus allowing for more
effective implementation of the
mitigation) and in general to generate
more data to contribute to the effects
analyses.
(b) An increase in our understanding
of how many marine mammals are
likely to be exposed to levels of MFAS/
HFAS (or explosives or other stimuli)
that we associate with specific adverse
effects, such as behavioral harassment,
TTS, or PTS.
(c) An increase in our understanding
of how marine mammals respond
(behaviorally or physiologically) to
MFAS/HFAS (at specific received
levels), explosives, or other stimuli
expected to result in take and how
anticipated adverse effects on
individuals (in different ways and to
varying degrees) may impact the
population, species, or stock
(specifically through effects on annual
rates of recruitment or survival).
(d) An increased knowledge of the
affected species.
(e) An increase in our understanding
of the effectiveness of certain mitigation
and monitoring measures.
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study (73 FR 60754, pages 60790–
60791). No changes have been made to
the longitudinal study as described in
the proposed rule.
Proposed Monitoring Plan for AFAST
Study Area
As NMFS indicated in the proposed
rule, the Navy has (with input from
NMFS) fleshed out the details of and
made improvements to the AFAST
Monitoring Plan. Additionally, NMFS
and the Navy have incorporated a
recommendation from the public, which
recommended the Navy hold a
workshop to discuss the Navy’s
Monitoring Plan (see Monitoring
Workshop section). The final AFAST
Monitoring Plan, which is summarized
below, may be viewed at https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications. The Navy
plans to implement all of the
components of the Monitoring Plan:
however, only the marine mammal
components (not the sea turtle
components) will be required by the
MMPA regulations and associated
LOAs.
The Monitoring Plan for AFAST has
been designed as a collection of focused
‘‘studies’’ (described fully in the AFAST
Monitoring Plan) to gather data that will
allow the Navy to address the following
questions:
(a) Are marine mammals exposed to
MFAS, especially at levels associated
with adverse effects (i.e., based on
NMFS’criteria for behavioral
harassment, TTS, or PTS)? If so, at what
levels are they exposed?
(b) If marine mammals are exposed to
MFAS in the AFAST Study Area, do
they redistribute geographically as a
result of continued exposure? If so, how
long does the redistribution last?
(c) If marine mammals are exposed to
MFAS, what are their behavioral
responses to various received levels?
(d) Is the Navy’s suite of mitigation
measures for MFAS (e.g., measures
agreed to by the Navy through
permitting) effective at avoiding TTS,
injury, and mortality of marine
mammals?
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Data gathered in these studies will be
collected by qualified, professional
marine mammal biologists that are
experts in their field. They will use a
combination of the following methods
to collect data:
• Contracted vessel and aerial
surveys.
• Passive acoustics.
• Marine mammal observers on Navy
ships.
In the four proposed study designs
(all of which cover multiple years), the
above methods will be used separately
or in combination to monitor marine
mammals in different combinations
before, during, and after training
activities utilizing MFAS/HFAS. Table 7
contains a summary of the Monitoring
effort that is planned for each study in
each year.
This monitoring plan has been
designed to gather data on all species of
marine mammals that are observed in
the AFAST study area. The Plan
recognizes that deep-diving and cryptic
species of marine mammals such as
beaked whales have a low probability of
detection (Barlow and Gisiner, 2006).
Therefore, methods will be utilized to
attempt to address this issue (e.g.,
passive acoustic monitoring).
North Atlantic right whales will also
be given particular attention during
monitoring in the AFAST study area,
although monitoring methods will be
the same for all species. Within the
AFAST study area, the Northwestern
Atlantic provides unique breeding and
calving habitat for NARW, and as a
result, critical habitat has been
designated for one calving ground (off
Georgia and northern Florida) and two
feeding areas (Cape Cod Bay and the
Great South Channel). Pursuant to the
Monitoring Plan, NARWs will be given
particular attention in the form of focal
follows (e.g. collect behavioral data
using the Big Eyes binoculars, and
observe the behavior of any animals that
are seen) when observed.
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Monitoring Workshop
During the public comment period on
the AFAST proposed rule (as well as the
Hawaii Range Complex and Southern
California Range Complex proposed
rules), NMFS received a comment
which, in consultation with the Navy,
we have chosen to incorporate into the
final rule (in a modified form). One
commenter recommended that a
workshop or panel be convened to
solicit input on the monitoring plan
from researchers, experts, and other
interested parties. The AFAST proposed
rule included an adaptive management
component and both NMFS and the
Navy believe that a workshop would
provide a means for Navy and NMFS to
consider input from participants in
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determining whether or how to modify
monitoring techniques to more
effectively accomplish the goals of
monitoring set forth earlier in the
document. NMFS and the Navy believe
that this workshop concept is valuable
in relation to all of the Range Complexes
and major training exercise rules and
LOAs that NMFS is working on with the
Navy at this time, and consequently this
single Monitoring Workshop will be
included as a component of all of the
rules and LOAs that NMFS will be
processing for the Navy in the next year
or so.
The Navy, with guidance and support
from NMFS, will convene a Monitoring
Workshop, including marine mammal
and acoustic experts as well as other
interested parties, in 2011. The
Monitoring Workshop participants will
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review the monitoring results from the
previous two years of monitoring
pursuant to the AFAST rule as well as
monitoring results from other Navy
rules and LOAs (e.g., the Southern
California Range Complex (SOCAL),
Hawaii Range Complex (HRC), and
other rules). The Monitoring Workshop
participants would provide their
individual recommendations to the
Navy and NMFS on the monitoring
plan(s) after also considering the current
science (including Navy research and
development) and working within the
framework of available resources and
feasibility of implementation. NMFS
and the Navy would then analyze the
input from the Monitoring Workshop
participants and determine the best way
forward from a national perspective.
Subsequent to the Monitoring
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Workshop, modifications would be
applied to monitoring plans as
appropriate.
Integrated Comprehensive Monitoring
Program
In addition to the Monitoring Plan for
AFAST, the Navy will complete the
Integrated Comprehensive Monitoring
Program (ICMP) Plan by the end of
2009. The ICMP will provide the
overarching coordination that will
support compilation of data from
project-specific monitoring plans (e.g.,
AFAST Monitoring Plan) as well as
Navy funded research and development
(R&D) studies. The ICMP will
coordinate the monitoring programs
progress towards meeting its goals and
develop a data management plan. The
ICMP will be evaluated annually to
provide a matrix for progress and goals
for the following year, and will make
recommendations on adaptive
management for refinement and analysis
of the monitoring methods.
The primary objectives of the ICMP
are to:
• Monitor and assess the effects of
Navy activities on protected species;
• Ensure that data collected at
multiple locations is collected in a
manner that allows comparison between
and among different geographic
locations;
• Assess the efficacy and practicality
of the monitoring and mitigation
techniques;
• Add to the overall knowledge-base
of marine species and the effects of
Navy activities on marine species.
The ICMP will be used both as: (1) A
planning tool to focus Navy monitoring
priorities (pursuant to ESA/MMPA
requirements) across Navy Range
Complexes and Exercises; and (2) an
adaptive management tool, through the
consolidation and analysis of the Navy’s
monitoring and watchstander data, as
well as new information from other
Navy programs (e.g., R&D), and other
appropriate newly published
information.
In combination with the 2011
Monitoring Workshop and the adaptive
management component of the AFAST
rule and the other planned Navy rules
(e.g. SOCAL and HRC), the ICMP could
potentially provide a framework for
restructuring the monitoring plans and
allocating monitoring effort based on the
value of particular specific monitoring
proposals (in terms of the degree to
which results would likely contribute to
stated monitoring goals, as well the
likely technical success of the
monitoring based on a review of past
monitoring results) that have been
developed through the ICMP
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framework, instead of allocating based
on maintaining an equal (or
commensurate to effects) distribution of
monitoring effort across Range
complexes. For example, if careful
prioritization and planning through the
ICMP (which would include a review of
both past monitoring results and current
scientific developments) were to show
that a large, intense monitoring effort in
Hawaii would likely provide extensive,
robust and much-needed data that could
be used to understand the effects of
sonar throughout different geographical
areas, it may be appropriate to have
other Range Complexes dedicate money,
resources, or staff to the specific
monitoring proposal identified as ‘‘high
priority’’ by the Navy and NMFS, in lieu
of focusing on smaller, lower priority
projects divided throughout their home
Range Complexes.
The ICMP will identify:
• A means by which NMFS and the
Navy would jointly consider prior years
monitoring results and advancing
science to determine if modifications
are needed in mitigation or monitoring
measures to better effect the goals laid
out in the Mitigation and Monitoring
sections of the AFAST rule.
• Guidelines for prioritizing
monitoring projects.
• If, as a result of the workshop and
similar to the example described in the
paragraph above, the Navy and NMFS
decide it is appropriate to restructure
the monitoring plans for multiple ranges
such that they are no longer evenly
allocated (by rule), but rather focused on
priority monitoring projects that are not
necessarily tied to the geographic area
addressed in the rule, the ICMP will be
modified to include a very clear and
unclassified recordkeeping system that
will allow NMFS and the public to see
how each Range Complex/project is
contributing to all of the ongoing
monitoring (resources, effort, money,
etc.).
Past Monitoring in AFAST
The proposed rule contained a
detailed review of the previous marine
mammal monitoring conducted in the
AFAST Study Area, which was
conducted in compliance with the terms
and conditions of multiple biological
opinions issued for MFAS training
activities (73 FR 60754, pages 60791–
60798). No changes have been made to
the discussion contained in the
proposed rule.
Adaptive Management
The final regulations governing the
take of marine mammals incidental to
Navy’s AFAST exercises contain an
adaptive management component. Our
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4857
understanding of the effects of MFAS/
HFAS and explosives on marine
mammals is still in its relative infancy,
and yet the science in this field
continues to improve. These
circumstances make the inclusion of an
adaptive management component both
valuable and necessary within the
context of 5-year regulations for
activities that have been associated with
marine mammal mortality in certain
circumstances and locations (though not
off the Atlantic Coast of the U.S.). The
use of adaptive management will give
NMFS the ability to consider new data
from different sources to determine (in
coordination with the Navy) on an
annual basis if mitigation or monitoring
measures should be modified or added
(or deleted) if new data suggests that
such modifications are appropriate (or
are not appropriate) for subsequent
annual LOAs.
Following are some of the possible
sources of applicable data:
• Results from the Navy’s monitoring
from the previous year (either from
AFAST or other locations).
• Findings of the Workshop that the
Navy will convene in 2011 to analyze
monitoring results to date, review
current science, and recommend
modifications, as appropriate to the
monitoring protocols to increase
monitoring effectiveness.
• Compiled results of Navy funded
research and development (R&D) studies
(presented pursuant to the ICMP, which
is discussed elsewhere in this
document).
• Results from specific stranding
investigations (either from AFAST or
other locations, and involving
coincident MFAS/HFAS of explosives
training or not involving coincident
use).
• Results from the Long Term
Prospective Study described above.
• Results from general marine
mammal and sound research (funded by
the Navy (described above) or
otherwise).
Mitigation measures could be
modified or added (or deleted) if new
data suggest that such modifications
would have (or do not have) a
reasonable likelihood of accomplishing
the goals of mitigation laid out in this
final rule and if the measures are
practicable. NMFS would also
coordinate with the Navy to modify or
add to (or delete) the existing
monitoring requirements if the new data
suggest that the addition of (or deletion
of) a particular measure would more
effectively accomplish the goals of
monitoring laid out in this final rule.
The reporting requirements associated
with this rule are designed to provide
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NMFS with monitoring data from the
previous year to allow NMFS to
consider the data and issue annual
LOAs. NMFS and the Navy will meet
annually, prior to LOA issuance, to
discuss the monitoring reports, Navy
R&D developments, and current science
and whether mitigation or monitoring
modifications are appropriate.
Reporting
In order to issue an ITA for an
activity, Section 101(a)(5)(A) of the
MMPA states that NMFS must set forth
‘‘requirements pertaining to the
monitoring and reporting of such
taking’’. Effective reporting is critical to
ensure compliance with the terms and
conditions of a LOA, and to provide
NMFS and the Navy with data of the
highest quality based on the required
monitoring.
As NMFS noted in its proposed rule,
additional detail has been added to the
reporting requirements since they were
outlined in the proposed rule. The
updated reporting requirements are all
included below. A subset of the
information provided in the monitoring
reports may be classified and not
releasable to the public.
NMFS will work with the Navy to
develop tables that allow for efficient
submission of the information required
below.
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General Notification of Injured or Dead
Marine Mammals
Navy personnel will ensure that
NMFS (regional stranding coordinator)
is notified immediately (or as soon as
operational security allows) if an
injured or dead marine mammal is
found during or shortly after, and in the
vicinity of, any Navy training exercise
utilizing MFAS, HFAS, or underwater
explosive detonations. The Navy will
provide NMFS with species or
description of the animal(s), the
condition of the animal(s) (including
carcass condition if the animal is dead),
location, time of first discovery,
observed behaviors (if alive), and photo
or video (if available). The Stranding
Response Plan contains more specific
reporting requirements for specific
circumstances.
Annual AFAST Monitoring Plan Report
The Navy shall submit a report
annually on October 1 describing the
implementation and results (through
August 1 of the same year) of the
AFAST Monitoring Plan, described
above. Data collection methods will be
standardized across range complexes to
allow for comparison in different
geographic locations. Although
additional information will also be
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gathered, the marine mammal observers
(MMOs) collecting marine mammal data
pursuant to the AFAST Monitoring Plan
shall, at a minimum, provide the same
marine mammal observation data
required in the MFAS/HFAS major
Training Exercises section of the Annual
AFAST Exercise Report referenced
below.
The AFAST Monitoring Plan Report
may be provided to NMFS within a
larger report that includes the required
Monitoring Plan Reports from multiple
Range Complexes.
Annual AFAST Exercise Report
The Navy will submit an Annual
AFAST Exercise Report on October 1 of
every year (covering data gathered
through August 1). This report shall
contain the subsections and information
indicated below.
MFAS/HFAS Major Training Exercises
This section shall contain the
following information for the following
Coordinated and Strike Group exercises,
which for simplicity will be referred to
as major training exercises for reporting
(MTERs): Southeastern ASW Integrated
Training Initiative (SEASWITI),
Integrated ASW Course (IAC),
Composite Training Unit Exercises
(COMPTUEX), and Joint Task Force
Exercises (JTFEX) conducted in AFAST:
(a) Exercise Information (for each
MTER):
(i) Exercise designator.
(ii) Date that exercise began and
ended.
(iii) Location.
(iv) Number and types of active
sources used in the exercise.
(v) Number and types of passive
acoustic sources used in exercise.
(vi) Number and types of vessels,
aircraft, etc., participating in exercise.
(vii) Total hours of observation by
watchstanders.
(viii) Total hours of all active sonar
source operation.
(ix) Total hours of each active sonar
source (along with explanation of how
hours are calculated for sources
typically quantified in alternate way
(buoys, torpedoes, etc.)).
(x) Wave height (high, low, and
average during exercise).
(b) Individual marine mammal
sighting info (for each sighting in each
MTER):
(i) Location of sighting.
(ii) Species (if not possible—
indication of whale/dolphin/pinniped).
(iii) Number of individuals.
(iv) Calves observed (y/n).
(v) Initial Detection Sensor.
(vi) Indication of specific type of
platform observation made from
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(including, for example, what type of
surface vessel, i.e., FFG, DDG, or CG).
(vii) Length of time observers
maintained visual contact with marine
mammal(s).
(viii) Wave height (in feet).
(ix) Visibility.
(x) Sonar source in use (y/n).
(xi) Indication of whether animal is
<200yd, 200–500yd, 500–1000yd, 1000–
2000yd, or >2000yd from sonar source
in (x) above.
(xiii) Mitigation Implementation—
Whether operation of sonar sensor was
delayed, or sonar was powered or shut
down, and how long the delay was.
(xiv) If source in use (x) is
hullmounted, true bearing of animal
from ship, true direction of ship’s travel,
and estimation of animal’s motion
relative to ship (opening, closing,
parallel)
(xv) Observed behavior—
Watchstanders shall report, in plain
language and without trying to
categorize in any way, the observed
behavior of the animals (such as animal
closing to bow ride, paralleling course/
speed, floating on surface and not
swimming, etc.)
(c) An evaluation (based on data
gathered during all of the MTERs) of the
effectiveness of mitigation measures
designed to avoid exposing marine
mammals to MFAS. This evaluation
shall identify the specific observations
that support any conclusions the Navy
reaches about the effectiveness of the
mitigation.
ASW Summary
This section shall include the
following information as summarized
from both MTERs and non-major
training exercises:
(i) Total annual hours of each type of
sonar source (along with explanation of
how hours are calculated for sources
typically quantified in alternate way
(buoys, torpedoes, etc.))
(iv) Cumulative Impact Report—To
the extent practicable, the Navy, in
coordination with NMFS, shall develop
and implement a method of annually
reporting non-major (i.e., other than
MTERs) training exercises utilizing hullmounted sonar. The report shall present
an annual (and seasonal, where
practicable) depiction of non-major
training exercises geographically across
the AFAST Study Area. To the extent
practicable, this report will also include
the total number of sonar hours (from
helicopter dipping sonar and object
detection exercises) conducted within
the southern NARW critical habitat plus
5 nm buffer area). The Navy shall
include (in the AFAST annual report) a
brief annual progress update on the
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status of the development of an effective
and unclassified method to report this
information until an agreed-upon (with
NMFS) method has been developed and
implemented.
Improved Extended Echo-Ranging
System (IEER)/Advanced Extended
Echo-Ranging System (AEER) Summary
This section shall include an annual
summary of the following IEER and
AEER information:
(i) Total number of IEER and AEER
events conducted in AFAST Study Area
(ii) Total expended/detonated rounds
(buoys).
(iii) Total number of self-scuttled
IEER rounds.
Sonar Exercise Notification
The Navy shall submit to the NMFS
Office of Protected Resources (specific
contact information to be provided in
LOA) either an electronic (preferably) or
verbal report within fifteen calendar
days after the completion of any MTER
indicating:
(1) Location of the exercise.
(2) Beginning and end dates of the
exercise.
(3) Type of exercise.
AFAST 5-Yr Comprehensive Report
The Navy shall submit to NMFS a
draft report that analyzes and
summarizes all of the multi-year marine
mammal information gathered during
ASW and IEER exercises for which
annual reports are required (Annual
AFAST Exercise Reports and AFAST
Monitoring Plan Reports). This report
will be submitted at the end of the
fourth year of the rule (November 2012),
covering activities that have occurred
through June 1, 2012.
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Comprehensive National ASW Report
By June 2014, the Navy shall submit
a draft National Report that analyzes,
compares, and summarizes the active
sonar data gathered (through January 1,
2014) from the watchstanders and
pursuant to the implementation of the
Monitoring Plans for AFAST, SOCAL,
the HRC, the Mariana Islands Range
Complex, the Northwest Training Range
Complex, the Gulf of Alaska, and the
East Coast Undersea Warfare Training
Range.
The Navy shall respond to NMFS
comments and requests for additional
information or clarification on the
AFAST Comprehensive Report, the
Comprehensive National ASW report,
the Annual AFAST Exercise Report, or
the Annual AFAST Monitoring Plan
Report (or the multi-Range Complex
Annual Monitoring Plan Report, if that
is how the Navy chooses to submit the
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information) if submitted within 3
months of receipt. These reports will be
considered final after the Navy has
addressed NMFS’ comments or
provided the requested information, or
three months after the submittal of the
draft if NMFS does not comment by
then.
Comments and Responses
On October 14, 2008 (73 FR 60754),
NMFS published a proposed rule in
response to the Navy’s request to take
marine mammals incidental to military
readiness training, maintenance, and
RDT&E activities in the AFAST Study
Area and requested comments,
information and suggestions concerning
the request. During the 30-day public
comment period, NMFS received
comments from 6 private citizens and
Senator Benjamin Cardin, comments
from the Marine Mammal Commission
(MMC), comments from the Maine
Department of Marine Resources and
the Georgia Department of Natural
Resources, and three sets of comments
from non-governmental organizations,
including, the Natural Resources
Defense Council (NRDC) (which
commented on behalf of The Humane
Society of the United States, the
International Fund for Animal Welfare,
Whale and Dolphin Conservation
Society, Cetacean Society International,
Pamlico Tar River Foundation, North
Carolinians for Responsible Use of
Sonar, League for Coastal Protection,
and Ocean Futures Society and its
founder Jean-Michel Cousteau), the
Cascadia Research Collective (CRC), and
the Ocean Mammal and Animal Welfare
Institutes. The comments are
summarized and sorted into general
topic areas and are addressed below.
Full copies of the comment letters may
be accessed at https://
www.regulations.gov.
NMFS worked with the Navy to
develop MMPA rules and LOAs for the
AFAST activities, SOCAL Range
Complex, and HRC Range Complex.
Many of the issues raised in the public
comments for this rule were also raised
for SOCAL and the HRC and NMFS
considered many of the broader issues
in the context of all three of these Navy
actions when determining how to
address the comments. Responses to
public comments on the HRC and
SOCAL rules (addressing similar issues
identified in the AFAST final rule) were
also published in January 2009 and may
provide the public with additional
detail, if needed.
North Atlantic Right Whales
Comment 1: Several commenters had
the following general comments/
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concerns regarding the way that NMFS’
rule analyzed the potential impacts to
right whales from sonar:
(a) As the only known calving ground,
the southern critical habitat is very
important to the survival of the species
and commenters were concerned about
the level of Navy activity in critical
habitat and how it will affect right
whales. Some suggested that NMFS
should restrict Navy activity within
critical habitat.
(b) The specific impacts to and
responses of newborn right whale calves
and their mothers are unknown and
commenters are concerned about the
effects of MFAS on this segment of the
population. One commenter notes that
NMFS has previously indicated that the
‘‘loss of even a single individual right
whale may contribute to the extinction
of the species,’’ and that ‘‘preventing the
mortality of one adult female alters the
projected outcome.’’ 69 FR 30858.
(c) The waters off of Gulf of Maine:
Cape Cod Bay, Great South Channel,
Bay of Fundy, and the Brown’s Bank
area are primary feeding grounds for the
North Atlantic right whale (and other
large whale species) and commenters
are concerned about impacts. Some
commenters recommended minimizing
activities in that area.
(d) One commenter stated that
although the Navy’s DEIS and NMFS’
Proposed Rule acknowledge that right
whales are expected to occur in the
AFAST area, the agencies arbitrarily
conclude that no right whales will be
injured by the thousands of hours of
sonar training exercises per year
spanning the entire East Coast and Gulf
of Mexico. One commenter further
asserts that right whales are hard to
detect because they spend the majority
of their time below the surface and are
often found alone or in pairs, which,
combined with rough weather reduces
the probability of detection. Also,
female right whales with young calves
are less mobile than adult whales
without young calves and may not be
able to avoid sonar sources.
(e) The commenters requested
clarification regarding why NMFS
believes that ship strikes are unlikely.
Commenters further state that the Navy
has been involved in ship strikes in the
past (specifically, a female NARW and
her near-term calf in the mid-Atlantic in
2004.)
Response: Following is NMFS’
response to the above comments:
(a) NMFS agrees that the southern
critical habitat for the North Atlantic
right is very important to the survival of
the species. The Navy intends to limit
sonar use to a relatively small amount
in the southern NARW critical habitat
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(see response to comment (1)(e) below).
As described in the proposed rule,
following are the details of the planned
sonar usage in the vicinity of the
southern critical habitat:
■ The Navy anticipates conducting
approximately 30 helicopter dipping
sonar maintenance events (< 1 hr)
annually in the NARW critical habitat
(and approximately 84 helicopter
training exercises in the vicinity of the
critical habitat but in deeper waters at
least more than 5 nm seaward of the
critical habitat boundaries). This means
that only a subset of those 30 activities
will occur in the critical habitat between
Nov 15 and April 15 (approximately 13
if one assumes they are distributed
equally throughout the year, for
example) and only a subset of the 84
helicopter training exercises would
occur near the critical habitat between
Nov 15 and April 15 (approximately 34
if one assumes they are distributed
equally throughout the year, for
example). Note that the source level of
a helicopter dipping sonar is
approximately 18 dB less than that of a
surface sonar source, which means that
the ensonified area is on the order of 65
times less (if spherical spreading is
assumed). Additionally, the mitigation
measures require that the Navy
minimize helicopter dipping activities
in the critical habitat.
■ The Navy would conduct
approximately 40 ship object detection
exercises (1–2 hours each) and 57
submarine object detection exercises (1–
2 hours each) annually while entering/
exiting port (within approximately 1
mile of shore). This means that only a
subset of those activities will occur
between Nov 15 and April 15,
approximately 41 if one assumes they
are distributed equally throughout the
year, for example. Additionally,
mitigation measures indicate that the
Navy shall reduce the time spent
conducting object detection exercises in
the critical habitat, contact
FACSFACJAX to obtain latest whale
sightings in vicinity of critical habitat,
and (to the extent operationally feasible)
avoid conducting training in vicinity of
recently sighted whales. Ships are
required to maneuver to maintain at
least 500 yds of separation from any
observed whale (consistent with safety
of ship).
■ The Navy’s model predicted that
approximately 20 takes of right whales
by behavioral harassment would occur
within the southern NARW critical
habitat (and no takes by injury or
mortality).
Time and area restrictions are one of
the most effective ways to reduce
impacts to protected species. By
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planning the limited sonar exercises
outlined above and implementing the
specific mitigation measures listed, the
Navy has minimized, to the extent
practicable, the impacts to right whales
in the southern critical habitat. NMFS
discusses the practicability and benefits
of time and area restrictions in the
Mitigation EA.
(b) The potential impacts to mothercalf pairs from sonar are specifically
discussed in Potential Effects of
Specified Activities on Marine
Mammals section of the proposed rule.
However, as the commenter suggests,
the specific effects of MFAS on right
whales and their calves are not
discussed because NMFS does not
possess data to draw any specific
conclusions regarding effects. As the
commenter suggests, the loss of even
one right whale would have serious
effects on the population; however, as
discussed in the proposed rule and
above, 20 instances of right whale
harassment are expected to occur within
the southern right whale critical habitat
(over the entire year, not just from
November to April) and none of these
are modeled to be at injurious levels.
Additionally, this take estimate does not
account for the mitigation measures
discussed in (a) above, which include
not approaching right whales within
closer than 500 yds and not conducting
training within the vicinity of recently
sighted whales, when feasible. For these
reasons and others (see Negligible
Impact section of proposed rule), NMFS
was able to determine that the Navy’s
AFAST activities would have a
negligible impact on the species.
(c) The Navy does not plan to conduct
any major ASW training exercises using
hull-mounted sonar in the Northeast.
All of the exercises in the Northeast will
consist of smaller scale unit-level
exercises predominantly utilizing
submarine sonar, active sonobuoys, and
torpedoes (see Table 3). In the
Northeast, the submarine object
detection exercises would occur
primarily in the near-shore submarine
transiting lanes exiting Groton,
Connecticut and Norfolk, Virginia
(neither of which are near the important
feeding areas the comment refers to). As
indicated in the rule, in the Northeast
the Navy is largely avoiding conducting
any training in the NARW critical
habitat, with one exception: Torpedo
exercises (a maximum of 32 MK–48
torpedo runs at 15 minutes each or up
to 24 lightweight MK–46 or MK–54
torpedoes) would occur in August
through December (when right whales
are less likely to be present). However,
the Navy included extensive TORPEX
mitigation measures that were worked
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out in a previous section 7 consultation
with NMFS (see 216.244(a)(1)(xxviii)).
Approximately 2000 sonobuoys (with
12 pings, spaced 30 seconds apart)
would be used annually. Time and area
restrictions are one of the most effective
ways to reduce impacts to protected
species. Based on the limited sonar
exercises outlined above and because of
the specific mitigation measures listed,
NMFS believes that impacts to right
whales and other large whales feeding
in important areas in the Northeast will
be minimal. NMFS discusses the
practicability and benefits of time and
area restrictions in the Mitigation EA.
(d) NMFS’ rationale for why right
whales will not be injured is not
arbitrary. Although the Navy is
proposing to conduct thousands of
hours (approximately 5,000 of hullmounted) of MFAS operation (see Table
1), several factors need to be considered.
For example, the AFAST Study Area
comprises over 2,170,175 square
nautical miles, the exercises are spread
out over the course of a year, and there
are only approximately 350 right whales
in the population (the number of whales
is germane because at the most basic
level the potential for injury is directly
based on the likelihood that the
ensonified area (above threshold)
around the MFAS sound sources will
overlap with a right whale in space and
time—the fewer right whales there are,
the less likely this is to happen.) The
model predicts 666 exposures to levels
above NMFS’ acoustic threshold for
behavioral harassment, but less than the
level associated with PTS (or injury).
Acknowledging that right whales may
be somewhat harder to detect than other
large whales, the Navy’s modeled takes,
as discussed in the Negligible Impact
Analysis section of the proposed rule,
do not take any mitigation measures or
any likely marine mammal avoidance
into consideration. Navy lookouts are
specifically trained to detect anomalies
in the water around the ship and both
the safety of Navy personnel and
success in the training exercise depend
on the lookout being able to detect
objects (or marine mammals) effectively
around the ship. The response to
Comment 2, below, explains more
specifically why injury is not expected.
(e) Regarding ship strikes, the Navy’s
EIS concluded that based on the
implementation of Navy mitigation
measures, especially during times of
anticipated NARW occurrence, and the
relatively low density of Navy ships in
the Study Area, the likelihood that a
vessel strike would occur is very low (as
NMFS indicated in the above comment,
the low abundance of NARWs also
supports this prediction). In addition to
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the standard operating procedures to
reduce the likelihood of collisions,
which include: (1) Use of lookouts
trained to detect all objects on the
surface of the water (including marine
mammals); (2) reasonable and prudent
actions to avoid the close interactions of
Navy assets and marine mammals; and
(3) maneuvering to keep away from any
observed marine mammal, the Navy has
issued extensive North Atlantic right
whale protective measures for all Fleet
Forces training activities (see
216.244(a)(3)). These measures, which
were developed with input from NMFS,
include additional training
requirements, designated areas of
caution (where caution includes speed
or direction adjustments and avoidance
of known groups of right whales when
feasible) and additional reporting
requirements. NMFS and the Navy
believe that the required measures will
allow the Navy to avoid colliding with
large whales during their specified
activities. The Navy neither requested,
nor did NMFS grant, authorization for
take of right whales from ship strikes
incidental to the specified activities.
Regarding the right whale strike in
2004, the commenter is most likely
referring to an event that took place on
November 17, 2004. On November 17 at
about 10:30 am a Navy amphibious
assault ship struck a large whale off the
Chesapeake Light House. A few hours
later, around noon, a fisherman
contacted the Virginia Aquarium
stranding hotline and reported a live
injured large whale with a fresh wound
on the tail where the left fluke lobe was
missing. On November 24, a dead right
whale was necropsied at Ocean Sands,
NC. The right whale was a pregnant
female and the cause of death was
determined to be blood loss owing to a
traumatic wound to the left fluke lobe,
which was missing, and damage to
surrounding tissue and bone. The
wound was consistent with that caused
by a ship strike. Neither NMFS, nor the
Navy can confirm or deny that the dead
right whale necropsied on November 24
was the same whale struck by the Navy
on November 17.
The USCG and Navy have standing
orders to report sightings or collisions.
Although the NMFS ship strike database
reflects a disproportionately high
number of ship strikes attributable to
USCG and Navy vessels over the years,
this is likely due to the high reporting
rate by those agencies relative to other
mariners and vessels, rather than a
higher incidence of right whale ship
strikes by Federal agency vessels. These
two Federal agencies are actively
involved in large whale protection
programs and reporting struck or dead
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whales to NMFS is part of their standard
operating procedures.
Comment 2: One commenter stated
that they disagree with NMFS’
conclusion that predicted Level B
harassment to right whales will likely
not occur because ‘‘many animals will
likely avoid sonar sources’’ and ‘‘Navy
monitors would detect these animals
prior to approach and implement sonar
power-down or shut-down’’
Response: NMFS did not predict that
Level B harassment of right whales is
not likely to occur. As indicated in the
rule, NMFS’ LOA may authorize up to
666 Level B harassment takes of right
whales. NMFS indicates that Level A
Harassment (injury) and TTS (one type
of Level B Harassment) are unlikely to
occur because of: The distance from the
source that an animal would need to
approach (approximately 10 m for
injury and 275–500 m for TTS) to be
exposed to levels associated with injury
or TTS; the fact that lookouts would
detect them at that close distance; the
fact that the Navy model (which does
not take mitigation or avoidance into
consideration) predicted that 0 right
whales would be exposed to injurious
levels of sound and 7 right whales
would be exposed to levels associated
with TTS, and; the fact that many (not
all) animals avoid sonar. Additionally,
the Navy is capable of effectively
monitoring a 1,000-meter safety zone
using night vision goggles, infrared
cameras, and passive acoustic
monitoring.
Monitoring and Reporting
Comment 3: One commenter stated:
‘‘The Navy should establish a long-term
research program, perhaps conducted by
NMFS or by an independent agent, on
the distribution, abundance, and
population structuring of protected
species in the AFAST Study Area, with
the goal of supporting adaptive
geographic avoidance of high-value
habitat.’’ Another commenter suggests
that the Navy should conduct research
and development of technologies to
reduce the impacts of active acoustic
sources on marine mammals.
Response: The MMPA does not
require that recipients of an incidental
take authorization conduct research.
However, NMFS has incorporated an
adaptive management component into
the AFAST rule which allows for yearly
review of Navy monitoring and current
science that could influence (allow for
the potential modification of)
monitoring and mitigation measures in
subsequent LOAs, if appropriate. NMFS’
Mitigation EA specifically addresses
NMFS’ and the Navy’s consideration of
geographic avoidance of high-value
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habitat. Separately, the Navy has
voluntarily developed and funded a
number of research plans that are
designed to address technologies to
reduce the impacts of active acoustic
sources on marine mammals (see
Research section).
Comment 4: One commenter states
that the Navy should engage in timely
and regular reporting to NOAA, state
coastal management authorities, and the
public to describe and verify use of
mitigation measures during testing and
training activities.
Response: The Navy will be required
to submit annual reports and the
unclassified portions of these reports
will be made available to the public
through a Federal Register document
announcing the issuance of subsequent
LOAs. The reports will include a
description of the mitigation measures
implemented during major exercises
and will also include an evaluation of
the effectiveness of any mitigation
measure implemented.
Comment 5: One commenter stated
that sighting information and other
behavioral data (including records of
breeding, feeding, interrupted or
unusual behavior) obtained by the Navy
should be provided to NMFS and other
interested organizations.
Response: Both the watchstanders,
who are engaged in the Navy activities
and responsible for detecting marine
mammals for mitigation
implementation, and the marine
mammal observers (MMOs)
implementing the Monitoring Plan, are
responsible for recording their
behavioral observations (the MMOs in
greater detail) and then submitting them
to NMFS in the required annual and
comprehensive reports. Upon
finalization of the reports, NMFS will
make them available to the public via
the NMFS Web site and through the
Federal Register.
Comment 6: Sightings of North
Atlantic right whales should be reported
regardless of the time of year or location
to NMFS immediately.
Response: In the southeast Atlantic,
the Navy requires that Ships, surfaced
subs, and aircraft shall report any
NARW sightings to Fleet Area Control
and Surveillance Facility
(FACSFACJAX), Jacksonville, by the
quickest and most practicable means.
The sighting report shall include the
time, latitude/longitude, direction of
movement and number and description
of whale (i.e., adult/calf). In the
northeast Atlantic, the Navy requires
that Ships, surfaced subs, and aircraft
shall report any NARW sightings (if the
whale is identifiable as a right whale)
off the northeastern U.S. to Patrol and
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Reconnaissance Wing
(COMPATRECONWING). The report
shall include the time of sighting, lat/
long, direction of movement (if
apparent) and number and description
of the whale(s). Both FACSFACJAX and
COMPATRECONWING then report the
information to NMFS. Because there is
no NARW critical habitat in the midAtlantic region (area is not quite as
critical as northeast and southeast) and
the whales are less concentrated when
migrating through the mid-Atlantic, the
Navy does not require NARW reporting
in the mid-Atlantic.
Mitigation
Comment 7: One commenter asserts
that NMFS’ analysis ignores or
improperly discounts an array of
options that have been considered and
imposed by other active sonar users,
including avoidance of coastal waters,
high-value habitat, and complex
topography; the employment of a safety
zone more protective than the 1000-yard
power-down and 200-yard shutdown
accepted by NMFS; general passive
acoustic monitoring for whales; special
rules for surface ducting and lowvisibility conditions; monitoring and
shutdown procedures for sea turtles and
large schools of fish; and many others.
The commenter further provides a
detailed list of 31 additional measures
that should be considered. Other
commenters made additional
recommendations of mitigation
measures that should be considered,
including, especially, time and area
closures in right whale calving grounds,
feeding grounds, and migration
corridors.
Response: NMFS considered a wide
range of mitigation options in our
analysis, including those listed by the
commenters. In order to issue an
incidental take authorization (ITA)
under Section 101(a)(5)(A) of the
MMPA, NMFS must set forth the
‘‘permissible methods of taking
pursuant to such activity, and other
means of affecting the least practicable
adverse impact on such species or stock
and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance.’’ The
National Defense Authorization Act
(NDAA) of 2004 amended the MMPA as
it relates to military-readiness activities
(which these Navy activities are) and
the incidental take authorization
process such that ‘‘least practicable
adverse impact’’ shall include
consideration of personnel safety,
practicality of implementation, and
impact on the effectiveness of the
‘‘military readiness activity’’. NMFS
worked with the Navy to identify
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practicable and effective mitigation
measures, which included a careful
balancing of the likely benefit of any
particular measure to the marine
mammals with the likely effect of that
measure on personnel safety,
practicality of implementation, and
impact on the ‘‘military-readiness
activity’’. NMFS developed an
Environmental Assessment (EA) that
analyzes a suite of possible mitigation
measures in regard to potential benefits
for marine mammals (see goals of
mitigation in the Mitigation section of
this proposed rule) and practicability for
the Navy. That EA, which considered all
of the measures recommended by these
public comments, is currently available
on the NMFS Web site (https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications) and has
been relied upon to inform NMFS’
MMPA decision.
Comment 8: NRDC recommends
prescription of specific mitigation
requirements for individual categories
(or sub-categories) of testing and
training activities, in order to maximize
mitigation given varying sets of
operational needs. Also, the Navy
should require that other nations abide
by U.S. mitigation measures when
training in the AFAST Study Area,
except where their own measures are
more stringent.
Response: The Navy’s standard
protective measures include measures
that are specific to certain categories of
activities. For example, different
exclusion zones are utilized for hullmounted sonar and dipping sonar, and
different range clearance procedures are
used for IEER sonobuoy exercises.
Pursuant to the Navy’s 2000 Policy for
Environmental Compliance at Sea, the
commander or officer in charge of a
major exercise shall provide
participating foreign units with a
description of the measures to protect
the environment required of similar U.S.
units as early as reasonable in the
exercise planning process and shall
encourage them to comply. However,
foreign sovereign immune vessels may
not be compelled to adopt such
mitigation measures.
Comment 9: The Marine Mammal
Commission recommends that NMFS
modify the Navy’s mitigation measures
by requiring the Navy to delay
resumption of full operational sonar use
following a power-down or shutdown
for 30 minutes if the sighted animal can
be identified to the species level and the
species is not deep diving and 60
minutes if it cannot be identified or is
known to be a member of a deep-diving
species such as sperm and beaked
whales. They further recommend that
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NMFS allow resumption of full
operations before the end of the 30minute period (when the species can be
identified and is not a deep diver) or 60minute period (the species cannot be
determined or can be determined but is
a deep diver) only when the Navy has
good evidence that the marine mammal
seen outside the safety zone is the same
animal originally sighted within the
zone.
Response: NMFS does not concur
with the MMC that we should expand
the delay (until sonar can be restarted
after a shutdown due to a marine
mammal sighting) to 60 minutes for
deep-diving species for the following
reasons:
• The ability of an animal to dive
longer than 30 minutes does not mean
that it will always do so. Therefore, the
60-minute delay would only potentially
add value in instances when animals
had remained under water for more than
30 minutes.
• Navy vessels typically move at 10–
12 knots (5–6 m/sec) when operating
active sonar and potentially much faster
when not. Fish et al. (2006) measured
speeds of 7 species of odontocetes and
found that they ranged from 1.4–7.30 m/
sec. Even if a vessel was moving at the
slower typical speed associated with
active sonar use, an animal would need
to be swimming near sustained
maximum speed for an hour in the
direction of the vessel’s course to stay
within the safety zone of the vessel.
Increasing the typical speed associated
with active sonar use would further
narrow the circumstances in which the
60-minute delay would add value.
• Additionally, the times when
marine mammals are deep-diving (i.e.,
the times when they are under the water
for longer periods of time) are the same
times that a large portion of their motion
is in the vertical direction, which means
that they are far less likely to keep pace
with a horizontally moving vessel.
• Given that, the animal would need
to have stayed in the immediate vicinity
of the sound source for an hour and
considering the maximum area that both
the vessel and the animal could cover in
an hour, it is improbable that this would
randomly occur. Moreover, considering
that many animals have been shown to
avoid both acoustic sources and ships
without acoustic sources, it is
improbable that a deep-diving cetacean
(as opposed to a dolphin that might bow
ride) would choose to remain in the
immediate vicinity of the source. NMFS
believes that it is unlikely that a single
cetacean would remain in the safety
zone of a Navy sound source for more
than 30 minutes.
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• Last, in many cases, the lookouts
are not able to differentiate species to
the degree that would be necessary to
implement this measure. Plus, Navy
operators have indicated that increasing
the number of mitigation decisions that
need to be made based on biological
information is more difficult for the
lookouts (because it is not their area of
expertise).
Comment 10: The MMC recommends
that NMFS work with the Navy to
validate the performance of Navy
lookouts, to conduct similar testing to
validate passive acoustic monitoring
methods, and to complete such tests
before the Navy proceeds with its
AFAST training operations.
Response: Navy lookouts are
specifically trained to detect anomalies
in the water around the ship and both
the safety of Navy personnel and
success in the training exercise depend
on the lookout being able to detect
objects (or marine mammals) effectively
around the ship. NMFS has reviewed
the Navy’s After Action Reports from
previous exercises and they show that
lookouts are detecting marine mammals,
and implementing sonar shutdowns as
required. That said, the AFAST
Monitoring Plan contains a study in
which Navy lookouts will be on watch
simultaneously with non-Navy marine
mammal observers and their detection
rates will be compared. NMFS and the
Navy have developed (since the
proposed rule) more rigorous reporting
requirements that should allow for more
meaningful comparisons between Navy
lookouts, Navy MMOs, and peerreviewed data, as well as meaningful
comparisons between both occurrence
and behavior of marine mammals in the
presence and absence of sonar
operation. NMFS agrees that the review
of post-exercise reports is critical, and
through the implementation of the more
rigorous reporting requirements that
have been laid out in the final rule
(versus the proposed rule) we should be
able to reach well-supported
conclusions regarding the effects of
MFAS on marine mammals.
Additionally, the regulations and
subsequent authorization would require
the Navy to provide ‘‘an evaluation
(based on data gathered during all of the
major training exercises) of the
effectiveness of mitigation measures
designed to minimize the exposure of
marine mammals to mid-frequency
sonar. This evaluation shall identify the
specific observations that support any
conclusions the Navy reaches about the
effectiveness of the mitigation included
in the authorization.’’ Last, the rule
contains an adaptive management
component that specifies that NMFS
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and the Navy will meet on an annual
basis to evaluate the Navy Reports (on
both Navy lookout observations as well
as Monitoring Plan reporting) and other
new information (such as Navy R & D
developments or new science) to
ascertain whether mitigation or
monitoring modifications are
appropriate.
The MMOs conducting the
Monitoring pursuant to the Monitoring
Plan are professional marine mammal
scientists and NMFS does not believe
that it is necessary to validate the
methods that they use for passive
acoustic monitoring. Currently, passive
acoustics are used by Navy operators to
increase awareness of nearby marine
mammals, but are not used to directly
trigger mitigation measures. Therefore,
NMFS does not believe that a validation
of those methods is necessary.
Additionally, any systems used in the
detection of marine mammals are the
same systems used for enemy detection
and NMFS is confidant that they are
fully operational. NMFS acknowledges
the opportunity for improvement via the
use of dedicated passive or active sonar
to detect marine mammals for
mitigation implementation. However,
current technology does not allow the
Navy to detect, identify, and localize
marine mammals and transmit this
information to operators real-time while
also not substantially reducing the
effectiveness of the fast-paced and
complicated exercises that the Navy
must conduct. The Navy is committed,
however, to technological development
in the area of marine mammal
protection and is currently funding
multiple research projects towards this
goal (see Research section).
Comment 11: One commenter stated:
The Navy’s proposed mitigation
methods are woefully inadequate. If a
marine mammal is spotted and reported
within 1,000 yards of the sonar dome
the sonar will not be stopped but will
be turned down by a mere 6 decibels
(from the normal operating level of 235
db) to 229 decibels—still over 10
million times more intense than the
Navy’s human diver standard of 145
decibels and over a million times more
than the noise level received by the
animals in the Bahamas incident of
2000.
Response: In order to analyze
potential effects to marine mammals
from sound it is important to
understand the difference between
source level (the sound level about 1
meter from the sound source) and
received level (the level that an animal
hears, which is largely based on how far
it is from the source). The commenter is
comparing source levels (235 and 229
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4863
dB) to a diver standard that is based on
received level (as are all of the levels
that are referenced by scientists in
relation to marine mammal responses).
Of note, many odontocete species
vocalizations have been recorded in the
field and the source levels estimated at
above 210 dB, including sperm whales
(up to 236 dB), Blainville’s and Cuvier’s
beaked whales, bottlenose dolphins and
pantropical and Atlantic spotted
dolphins. The ability of the Navy’s
mitigation measures to avoid injury is
discussed in the response to comment
#2.
Additionally, the reference to 145 dB
is incorrect. The Naval Sea Systems
Command Instruction (NAVSEAINST)
3150.2, ‘‘Safe Diving Distances from
Transmitting Sonar,’’ is the Navy’s
governing document for human divers
in relation to mid-frequency active
sonar systems. That instruction provides
procedures for calculating safe distances
from active sonars. Such procedures are
derived from experimental and
theoretical research conducted at the
Naval Submarine Medical Research
Laboratory and the Naval Experimental
Diving Unit. Inputs to those procedures
include diver dress, type of sonar, and
distance from the sonar. The output is
represented as a permissible exposure
limits (i.e., how long the diver can safely
stay at that exposure level). For
example, a diver wearing a wetsuit
without a hood has a permissible
exposure limit of 71 minutes at a
distance of 1000 yds from the AN/SQS–
53 sonar. That same instruction advises
that if the type of sonar is unknown,
divers should start 1000 yds from the
source and move closer (as needed) to
the limits of diver comfort. If an
interaction did occur, it is unlikely the
active sonar activity would not be
conducted close enough to a diver to
trigger the permissible exposure limit.
Assuming spherical spreading, the 1000
yd distance equates to a receive level of
approximately 175 dB.
Of note, if spherical spreading is
assumed, turning down the sonar by 6
dB reduces the radial distance to any
particular received level by half, which
means that the ensonified area is
decreased by approximately 75 percent.
Comment 12: One commenter stated:
‘‘According to the Navy’s proposed
mitigation measures, the sonar will only
be shut down when an animal is spotted
within 200 yards of the sonar dome. By
the time the sonar has traveled that far,
it will already have been ensonified for
many minutes with noise equivalent to
that which caused the Bahamas whales
to strand and die. To shut off the sonar
when an animal is observed and
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reported at 200 yards will already be too
late.’’
Response: The required powerdown
and shutdown zones, if properly
implemented, will avoid exposing
marine mammals to levels associated
with injury and minimize the number of
marine mammals exposed to levels
associated with TTS (see Mitigation
conclusion section of proposed rule).
Sonar is not shutdown until or unless
an animal approaches within 200 yds,
However, if it is sighted at distances
greater than 200 yds, the sound will
already have been reduced as a result of
either a 6-dB (1000 yds) or 10-dB (500
yds) powerdown, which will have
notably reduced the levels an animal is
exposed to prior to entering the 200-yd
safety zone. Separately, as discussed in
NMFS’ response to comment #13, there
is no way to know the levels that the
whales in the Bahamas were exposed to
that caused them to respond the way
that they did.
Comment 13: Several commenters
were concerned that visual observation
by lookouts would not be effective to
detect marine mammals (especially
beaked whales, which are only at
surface 8 percent of the time and for
which the chance of sighting has been
calculated at about 2 percent, and
especially in anything but calm
weather). They were further concerned
that, therefore, mitigation would not be
effectively implemented and the Navy
would not be able to avoid injuring
marine mammals, as asserted by NMFS.
Response: As explained in the
proposed rule, injury of marine
mammals is unlikely to occur because
an animal would need to approach to
within approximately 10 m of the
source to be exposed to levels associated
with injury (and animals are likely
avoiding both vessels and sound sources
at that close distance) combined with
the fact that lookouts would likely
detect most marine mammals at that
close distance. NMFS acknowledges
that beaked whales are notably more
difficult to detect: however, the Navy
model (which does not take mitigation
or avoidance into consideration)
predicted that 0 beaked whales would
be exposed to injurious levels of sound.
Nonetheless, NMFS acknowledges the
opportunity for improvement via the
use of dedicated passive or active sonar
to detect marine mammals for
mitigation implementation. However,
current technology does not allow the
Navy to detect, identify, and localize
marine mammals and transmit this
information to operators real-time while
also not substantially reducing the
effectiveness of the fast-paced and
complicated exercises that the Navy
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must conduct. The Navy is committed,
however, to technological development
in the area of marine mammal
protection and is currently funding
multiple research projects towards this
goal (see Research section).
Acoustic Thresholds for TTS and PTS
Comment 14: One commenter asserts
that NMFS disregards data gained from
actual whale mortalities. The
commenter cites to peer-reviewed
literature that indicates that sound
levels at the most likely locations of
beaked whales beached in the Bahamas
strandings run far lower than the Navy’s
threshold for injury here: approximately
150–160 dB re 1 μPa for 50–150
seconds, over the course of the transit.
A further modeling effort, undertaken in
part by the Office of Naval Research, the
commenter states, suggests that the
mean exposure level of beaked whales,
given their likely distribution in the
Bahamas’ Providence Channels and
averaging results from various
assumptions, may have been lower than
140 dB re 1 μPa. Last the commenter
suggests that when duration is factored
in, evidence would support a maximum
energy level (‘‘EL’’) threshold for serious
injury on the order of 182 dB re 1
μPa2•s, at least for beaked whales.
Response: No one knows where the
beaked whales were when they were
first exposed to MFAS in the Bahamas
or the duration of exposure for
individuals (in regards to maximum EL)
and, therefore, we cannot accurately
estimate the received level that triggered
the response that ultimately led to the
stranding. Therefore, NMFS is unable to
quantitatively utilize any data from this
event in the mathematical model
utilized to estimate the number of
animals that will be ‘‘taken’’ incidental
to the Navy’s proposed action. However,
NMFS does not disregard the data. The
proposed rule includes a qualitative
discussion of the Bahamas stranding
and four other strandings that NMFS
and the Navy agree were likely
attributable to MFAS. These data
illustrate a ‘‘worst case scenario’’ of the
range of potential effects from sonar and
the analysis of these strandings supports
the Navy’s request for authorization to
take 10 individuals of several species by
mortality over the 5-yr period.
Comment 15: One commenter notes
that in the SOCAL proposed rule, NMFS
sets its threshold for temporary hearing
loss and behavioral effects, or
‘‘temporary threshold shift’’ (‘‘TTS’’), at
183 dB re 1 μPa2•s for harbor seals, 204
dB re 1 μPa2•s for northern elephant
seals, and 206 dB re 1 FPa2•s for
California sea lions (73 FR. 60878).
However, the commenter notes, in the
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proposed rule for AFAST, NMFS
indicates that the TTS threshold for
pinnipeds is 183 dB re 1 μPa2•s for
pinnipeds. NMFS does not explain the
difference in thresholds. The
commenter makes the same comment
for the PTS thresholds (which are 20 dB
higher than the TTS thresholds).
Response: As noted in the SOCAL
proposed rule, the TTS thresholds are
183 dB re 1 FPa2•s for harbor seals (and
closely related species), 204 dB re 1
μPa2•s for northern elephant seals (and
closely related species), and 206 dB re
1 μPa2•s for California sea lions (and
closely related species) (73 FR 60878).
The commenter is correct, in the AFAST
proposed rule, NMFS did not fully
explain that all of the pinniped species
that might be exposed to MFAS are
‘‘closely related’’ to harbor seals (the
thresholds for northern elephant seals
and California sea lions are not
applicable because these species are not
present in the AFAST Study Area).
Therefore, the 183 dB SEL is the
pinniped threshold applied in AFAST.
Accordingly, the AFAST final rule has
been amended to clarify this issue and
be consistent with the SOCAL final rule.
The same answer applies to the
comment about PTS thresholds.
Comment 16: The Navy’s exclusive
reliance on energy flux density as its
unit of analysis does not take other
potentially relevant acoustic
characteristics into account. Reflecting
this uncertainty, the Navy should
establish a dual threshold for marine
mammal injury.
Response: NMFS currently uses the
injury threshold recommended by
Southall et al. (2007) for MFAS.
Specifically, NMFS uses the 215-dB SEL
sound exposure level threshold (the
commenter refers to it as energy flux
density level). Southall et al. (2007)
presents a dual threshold for injury,
which also includes a 230-dB peak
pressure level threshold. NMFS
discussed this issue with the Navy early
in the MMPA process and determined
that the 215-dB SEL injury threshold
was the more conservative of the two
thresholds (i.e., the 230-dB peak
pressure threshold occurs much closer
to the source than the 215-dB SEL
threshold) and therefore it was not
necessary to consider the 230-dB peak
pressure threshold further. For example,
an animal will be within the 215-dB
SEL threshold and counted as a take
before it is exposed to the 230-dB
threshold. NMFS concurs with Southall
et al. (2007), which asserts that for an
exposed individual, whichever criterion
is exceeded first, the more
precautionary of the two measures
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should be used as the operative injury
criterion.
Comment 17: One commenter states
that the calculation of PTS (which is
equated to the onset on injury) is based
on studies of TTS that, as discussed
below, are significantly limited.
Response: NMFS addressed this issue
in response to comments 13 through 15.
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Behavioral Harassment Threshold
Comment 18: The NRDC submitted a
comprehensive critique of the risk
function (authored by Dr. David Bain),
which NMFS has posted on our Web
site (https://www.nmfs.noaa.gov/pr/
permits/incidental.htm#applications).
NRDC summarized some general
limitations of the risk function and
included a fairly detailed critique of the
specific structure of and parameters
chosen for use in the model. Following
are some of the general topics addressed
in the letter:
• Factors that Dr. Bain thinks should
be addressed by the model, such as
social interactions and multiple sources.
• Critique of the datasets that NMFS
used to populate the risk function
(described Level B Harasssment—Risk
Function section of the proposed rule):
(1) Controlled Laboratory Experiments
with Odontocetes (SSC Dataset); (2)
Mysticete Field Study (Nowacek et al.,
2004), and (3) Odontocet Field Data
(Haro Strait—USS Shoup).
• Consideration of some datasets that
were considered by NMFS, but not used
in the risk function.
• A critique of the parameters (A, B,
and K) used in the risk function.
• A sensitivity analysis of the
parameters (i.e., takes were modeled
while applying variable values for the
A, B, and K values).
Dr. Bain included a summary of his
concerns and an abbreviated version is
included below. Additionally (and not
included in the summary), Dr. Bain
suggested that the effect of multiple
sources may be both different and
greater than the effects of fewer sources
and provided supporting examples.
(comments that were in Dr. Bain’s
summary, but have been addressed
elsewhere in this Comment Response
section are not included below):
• In summary, development of a
function that recognizes individual
variation is a step in the right direction.
• The selected equation is likely to
produce underestimates of takes due to
asymmetries in the number of
individuals affected if parameters are
either underestimated or overestimated
due to uncertainty. Thus it will be
important to use the risk function in a
precautionary manner.
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• The sensitivity analysis reveals the
importance of using as many datasets as
possible. First, for historical reasons,
there has been an emphasis on high
energy noise sources and the species
tolerant enough of noise to be observed
near them. Exclusion of the rarer
datasets demonstrating responses to low
levels of noise biases the average
parameter values, and hence
underestimates effects on sensitive
species.
• A similar mistake was made with
the right whale data. The level at which
100 percent of individuals responded
was used as the value at which 50
percent of individuals responded (B+K).
Likewise, the level at which 100 percent
of killer whales responded to midfrequency sonar is less than the value
derived for B+K in the HRC SDEIS
(Dept. Navy 2008b).
• It is likely that biological B values
should be in the range from just
detectable above ambient noise to 120
dB re 1 μPa. The resulting mathematical
B value could be tens of dB lower, not
the 120 dB re 1 μPa proposed. For many
species, risk may approach 100 percent
in the range from 120–135 dB re 1 μPa,
putting K in the 15–45 dB range.
• The A values do not seem well
supported by the data, and in any case,
are likely to be misleading in social
species as the risk function is likely to
be asymmetrical with a disproportionate
number of individuals responding at
low noise levels. Rather than one
equation fitting all species well,
parameters are likely to be species
typical.
• As realistic parameter values are
lower than those employed in the HRC
SDEIS (Dept. Navy 2008b), AFAST DEIS
(Dept. Navy 2008a) and related DEIS’s,
take numbers should be recalculated to
reflect the larger numbers of individuals
likely to be taken. The difference
between the parameter values estimated
here and those used in the SDEIS
suggests takes were underestimated by
two orders of magnitude.
Response: Many of the limitations
outlined in Dr. Bain’s document were
raised by other commenters and are
addressed elsewhere in this Comment
and Response Section and will not be
addressed again here. Below, NMFS
responds to the specific points
summarized above.
• The effects of multiple sources:
Mathematically, the Navy’s exposure
model has already accounted for takes
of animals exposed to multiple sources
in the number of estimated takes. NMFS
concurs with the commenter, however,
in noting that the severity of responses
of the small subset of animals that are
actually exposed to multiple sources
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simultaneously could potentially be
greater than animals exposed to a single
source due to the fact that received
level, both SPL and SEL, would be
slightly higher and because contextually
it could be perceived as more
threatening to an animal to receive
multiple stimuli coming from
potentially multiple directions at once
(for example, marine mammals have
been shown to respond more severely to
sources coming directly towards them,
vs. obliquely (Wartzok, 2004)).
However, it is also worth noting that
according to information provided by
the Navy, surface vessels do not
typically operate closer than 10–20
miles from another surface vessel (and
greater distance is ideal), and other
sonar sources, such as dipping sonar
and sonobuoys, are almost always used
20 or more miles away from the surface
vessel. This means that if the two most
powerful sources were operating at the
closest distance they are likely to (10
miles), in the worst case scenario,
animals that would have been exposed
to 150 dB SPL or less (taken from table
16 of the proposed rule) may be exposed
to slightly higher levels or to similar
levels or less coming from multiple
directions.
• Underestimates of takes due to
asymmetries in the number of
individuals affected when parameters
are underestimated and overestimated
due to uncertainty: The commenter’s
point is acknowledged. When a
sensitivity analysis is conducted and
parameters are varied (both higher and
lower values used)—the degree of
difference in take estimates is much
greater when the parameter is adjusted
in one direction than in the other,
which suggests the way that this
generalized model incorporates
uncertainty may not be conservative.
However, in all cases when the
adjustment of the parameter in a certain
direction results in a disproportionately
(as compared to an adjustment in the
other direction) large increase in the
number of takes, it is because the model
is now estimating that a larger
percentage of animals will be taken at
greater distances from the source. This
risk function is based completely on the
received level of sound. As discussed in
the proposed rule, there are other
contextual variables that are very
important to the way that an animal
responds to a sound, such as nearness
of the source, relative movement
(approaching or retreating), or the
animals familiarity with the source.
Southall et al. (2007) indicates that the
presence of high-frequency components
and a lack of reverberation (which are
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indicative of nearness) may be more
relevant acoustic cues of spatial
relationship than simply exposure level
alone. In the AFAST activities, an
animal exposed to between 120 and 130
dB may be more than 75 nm from the
sonar source. NMFS is not aware of any
data that describe the response of any
marine mammals to sounds at that
distance, much less data that indicate
that an animal responded in a way we
would classify as harassment at that
distance. Because of this, NMFS does
not believe it is currently possible or
appropriate to modify the model to
further address uncertainty if doing so
results in the model predicting that
much larger numbers of animals will be
taken at great distances from the source
when we have no data to suggest that
that would occur.
• Using many datasets: NMFS has
explained both in the rule, and then
again elsewhere in these comments,
why we chose the three datasets we did
to define the risk function. As Dr. Bain
points out, there are datasets that report
marine mammal responses to lower
levels of received sound. However,
because of the structure of the curve
NMFS is using and what it predicts
(Level B Harassment), we need datasets
that show a response that we have
determined qualifies as harassment (in
addition to needing a source that is
adequately representative of MFAS and
reliable specific received level
information), which many of the lower
level examples do not.
• 50 percent vs. 100 percent response:
Dr. Bain asserts that two of the three
datasets (Nowacek et al., 2004 and Haro
Strait—USS SHOUP) that NMFS uses to
derive the 50 percent response
probability in the risk function actually
report a 100 percent response at the
indicated received levels. For the Haro
Strait dataset, a range of estimated
received levels at the closest approach
to the J Pod were estimated. Given that
neither the number of individual
exposures or responses were available,
the mean of this range was used as a
surrogate for the 50 percent response
probability in the development of the
risk function. For the Nowacek data,
NMFS used 139.2 dB, which is the
mean of the received levels at which 5
of 6 animals showed a significant
response to the signal. However, viewed
another way, of 6 animals, one animal
did not respond to the signal and the
other five responded at received levels
of 133 dB, 135 dB, 137 dB, 143 dB, and
148 dB, which means that 3 of the 6
animals (50 percent) showed a
significant response at 139.2 dB or less.
• 120 dB basement value: When the
broad array of data reported from
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exposures across taxa and to varied
sources are reviewed, NMFS believes
that 120 dB is an appropriate B value for
a curve designed to predict responses
that rise to the level of an MMPA
harassment (not just any response). The
available data do not support the
commenter’s assertion that risk may
approach 100 percent in the range from
120–135 dB for many species. For
example, the Southall et al. (2007)
summary of behavioral response data
clearly shows, in almost every table (for
all sound types), reports of events in
which animals showed no observable
response, or low-level responses NMFS
would not likely consider harassment,
in the 120 to 135-dB range. For the
species (the harbor porpoise) for which
the data do support that assertion,
which the Southall et al. (2007) paper
considers ‘‘particularly sensitive’’,
NMFS has implemented the use of a
species-specific step function threshold
of 120 dB SPL.
• The A value: Please see the second
bullet of this response for the first part
of the answer. NMFS concurs with the
commenter that species-specific
parameters would likely be ideal,
however there are not currently enough
applicable data to support separate
curves for each species. We note,
though, that even with species-specific
parameters, the context of the exposure
will still likely result in a substantive
variability of behavioral responses to the
same received level by the same species.
• Recalculation: For the reasons
described in the bullets above in this
response, NMFS disagrees with the
commenter’s assertion that the
parameters used in the proposed rule
and the EIS are unrealistic and that they
result in take estimates that are too
small by two orders of magnitude. We
do not believe that a recalculation is
necessary.
The science in the field of marine
mammals and underwater sound is
evolving relatively rapidly. NMFS is in
the process of revisiting our acoustic
criteria with the goal of developing a
framework (Acoustic Guidelines) that
allows for the regular and scientifically
valid incorporation of new data into our
acoustic criteria. We acknowledge that
this model has limitations, however, the
limitations are primarily based on the
lack of applicable quantitative data. We
believe that the best available science
has been used in the development of the
criteria used in this and other
concurrent Navy rules and that this
behavioral harassment threshold far
more accurately represents the number
of marine mammals that will be taken
than the criteria used in the RIMPAC
2006 authorization. We appreciate the
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input from the public and intend to
consider it further as we move forward
and develop the Acoustic Guidelines.
Comment 19: One commenter
expressed the concern that NMFS
blindly relies on TTS studies conducted
on 7 captive animals of two species (to
the exclusion of copious data on
animals in the wild) as a primary source
of data for the behavioral harassment
threshold. The commenter further
asserts that these studies (on highly
trained animals that do not represent a
normal range of variation within their
own species, as they have been housed
in a noisy bay for most of their lives)
have major deficiencies, which NMFS
ignores by using the data.
Response: As mentioned in comment
#18, the SSC Dataset (Controlled
Laboratory Experiments with
Odontocetes) is not the primary source
of data for the behavioral harassment
threshold; rather, it is one of three
datasets (other two datasets are from
wild species exposed to noise in the
field) treated equally in the
determination of the K value (equates to
midpoint) of the behavioral risk
function. NMFS recognizes that certain
limitations may exist when one
develops and applies a risk function to
animals in the field based on captive
animal behavioral data. However, we
note that for the SSC Dataset: (1)
Researchers had superior control over
and ability to quantify noise exposure
conditions; (2) behavioral patterns of
exposed marine mammals were readily
observable and definable; and, (3)
fatiguing noise consisted of tonal noise
exposures with frequencies contained in
the tactical mid-frequency sonar
bandwidth. NMFS does not ignore the
deficiencies of these data, rather we
weighed them against the value of the
data and compared the dataset to the
other available datasets and decided
that the SSC dataset was one of the three
appropriate datasets to use in the
development of the risk function.
Comment 20: One commenter stated
‘‘NMFS excludes a substantial body of
research on wild animals (and some
research on other experimental animals
as well, within a behavioral
experimental protocol). Perhaps most
glaringly, while the related DEIS
prepared for the Navy’s AFAST
activities appears to acknowledge the
strong sensitivity of harbor porpoises by
setting an absolute take threshold of 120
dB (SPL)—a sensitivity that, as NMFS
has noted, is reflected in numerous wild
and captive animal studies—the
agencies improperly fail to include any
of these studies in their data set. The
result is clear bias, for even if one
assumes (for argument’s sake) that the
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SPAWAR data has value, NMFS has
included a relatively insensitive species
in setting its general standard for marine
mammals while excluding a relatively
sensitive one.’’
Response: As explained in the Level
B Harassment (Risk Function) section of
the proposed rule the risk function is
based primarily on three datasets (SSC
dataset, Nowacek et al. (2004), and Haro
Strait—USS SHOUP) in which marine
mammals exposed to mid-frequency
sound sources were reported to respond
in a manner that NMFS would classify
as Level B Harassment. NMFS
considered the ‘‘substantial body of
research’’ that the commenter refers to
but was unable to find other datasets
that were suitable in terms of all of the
following: The equivalency of the sound
source to MFAS, a reported behavioral
response that NMFS would definitively
consider Level B Harassment, and a
received level reported with high
confidence. The SSC dataset is only one
of three used and, in fact, the other 2
datasets (which are from wild animals—
killer whales and North Atlantic right
whales) both report behavioral
responses at substantively lower levels
(i.e., the ‘‘relatively insensitive’’ species
is not driving the values in the
function).
Comment 21: The risk function must
take into account the social ecology of
some marine mammal species. For
species that travel in tight-knit groups,
an effect on certain individuals can
adversely influence the behavior of the
whole. Should those individuals fall on
the more sensitive end of the spectrum,
the entire group or pod can suffer
significant harm at levels below what
the Navy would use as the mean. In
developing its ‘‘K’’ parameter, NMFS
must take into account the potential for
indirect effects.
Response: The risk function is
intended to define the received level of
MFAS at which exposed marine
mammals will experience behavioral
harassment. The issue the commenter
raises is related to the Navy’s exposure
model—not the risk function. However,
because of a lack of related data there
is no way to numerically address this
issue in the model. Although the point
the commenter raises could potentially
apply, one could also assert that if
certain animals in a tight knit group
were less sensitive it would have the
opposite effect on the group.
Additionally, the modeling is based on
uniform marine mammal density
(distributed evenly over the entire area
of potential effect), which does not
consider the fact that marine mammals
appearing in pods will be easier to
detect and therefore the Navy will be
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more likely to implement mitigation
measures that avoid exposing the
animals to the higher levels received
within 1000 m of the source.
Comment 22: One commenter stated
‘‘NMFS appears to have misused data
garnered from the Haro Strait incident—
one of only three data sets it considers—
by including only those levels of sound
received by the ‘‘J’’ pod of killer whales
when the USS Shoup was at its closest
approach. These numbers represent the
maximum level at which the pod was
harassed; in fact, the whales were
reported to have broken off their
foraging and to have engaged in
significant avoidance behavior at far
greater distances from the ship, where
received levels would have been orders
of magnitude lower. We must insist that
NMFS provide the public with the
Navy’s propagation analysis for the Haro
Strait event, which it used in preparing
its 2005 Assessment of the incident.’’
Response: For the specific application
in the risk function for behavioral
harassment, NMFS used the levels of
sound received by the ‘‘J’’ pod when the
USS Shoup was at its closest approach
because a review of the videotapes and
other materials by NMFS detailing the
behavior of the animals in relation to
the location of the Navy vessels showed
that it was after the closest approach of
the vessel that the whales were observed
responding in a manner that NMFS
would classify as ‘‘harassed’’. Though
animals were observed potentially
responding to the source at greater
distances, NMFS scientists believed that
the responses observed at greater
distances were notably less severe and
would not rise to the level of MMPA
harassment. Though the received levels
observed in relation to the lesser
responses could be used in some types
of analytical tools, the risk continuum
specifically requires that we use
received sound levels that are
representative of when MMPA
harassment likely occurred. The Navy’s
report may be viewed at: https://
www.acousticecology.org/docs/
SHOUPNavyReport0204.pdf.
Comment 23: One commenter asserts
that NMFS’ threshold is applied in such
a way as to preclude any assessment of
long-term behavioral impacts on marine
mammals. It does not account, to any
degree, for the problem of repetition: the
way that apparently insignificant
impacts, such as subtle changes in dive
times or vocalization patterns, can
become significant if experienced
repeatedly or over time.
Response: NMFS’ threshold does not
preclude any assessment of long-term
behavioral impacts on marine mammals.
The threshold is a quantitative tool that
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NMFS uses to estimate individual
behavioral harassment events.
Quantitative data relating to long-term
behavioral impacts are limited, and
therefore NMFS’ assessment of longterm behavioral impacts is qualitative in
nature (see Diel Cycle section in
Negligible Impact Analysis section).
NMFS’ analysis discusses the potential
significance of impacts that continue
more than 24 hours and/or are repeated
on subsequent days and, though it does
not quantify those impacts, further
indicates that these types of impacts are
not likely to occur because of the nature
of the Navy’s training activities and the
large area over which they are
conducted.
Effects Analysis
Comment 24: One commenter stated:
‘‘NMFS does not properly account for
reasonably foreseeable reverberation
effects (as in the Haro Strait incident),
giving no indication that its modeling
sufficiently represents areas in which
the risk of reverberation is greatest.’’
Response: The model does indirectly
incorporate surface-ducting (surface
reverberation), as conditions in the
model are based on nominal conditions
calculated from a generalized digitalized
monthly average. Though the model
does not directly consider
reverberations, these effects are
generally at received levels many orders
of magnitude below those of direct
exposures (as demonstrated in the Haro
Strait analysis associated with bottom
reverberation) and thus contribute
essentially nothing to the cumulative
SEL exposure and would not result in
the exposure of an animal to a higher
SPL than the direct exposure, which is
already considered by the model.
Comment 25: One commenter states
that though the numbers of animals that
the Navy predicts its proposal will
impact are worryingly high, they believe
them to be gross underestimates of the
real numbers of animals potentially at
risk because of the thresholds the Navy
is using to predict behavioral
disturbance and levels of deafness. The
Navy is using 215 dB (re 1 μPa2-s) as the
threshold above which it says
permanent deafness (PTS) will occur
and 195 dB (re 1 μPa2-s) as the threshold
above which it says temporary deafness
(TTS) will occur. Behavioral impacts are
predicted based on a dose response
function.
Response: Contrary to what the
commenter states, in the Model
Overestmation section of the proposed
rule NMFS clearly explains why the
authorized take numbers are likely
notably higher than the takes that will
actually occur.
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To clarify, PTS is not permanent
deafness, rather it is permanent
threshold shift, which means that the
hearing sensitivity has been
permanently reduced by a certain
amount, which could be a small amount
or a larger amount (the longer and
higher level the exposure to the sound,
the more likely PTS will be of a larger
amount). Of note, reduced hearing
sensitivity as a simple function of
development and aging has been
observed in marine mammals, as well as
humans and other taxa (Southall et al.,
2007), so we can infer that strategies
exist for coping with this condition to
some degree, though likely not without
cost. There is no empirical evidence that
exposure to MFAS/HFAS can cause PTS
in any marine mammals; instead the
probability of PTS has been inferred
from studies of TTS. Similarly, TTS is
not temporary deafness, rather a
temporary reduction in hearing
sensitivity.
Comment 26: NMFS fails to include
data from the July 2004 Hanalei Bay
event, in which 150–200 melon-headed
whales were embayed for more than 24
hours during the Navy’s Rim of the
Pacific exercise. According to the
Navy’s analysis, predicted mean
received levels (from mid-frequency
sonar) inside and at the mouth of
Hanalei Bay ranged from 137.9 dB to
149.2 dB. NMFS’ failure to incorporate
these numbers into its methodology as
another data set is not justifiable.
Response: NMFS’ investigation of the
Hanalei event concluded that there was
insufficient evidence to determine
causality. There are a number of
uncertainties about sonar exposure and
other potential contributing factors and
assumptions inherent to a
reconstruction of events in which sonar
was the causative agent that simply
preclude this determination. Because of
this, NMFS did not use the numbers
(137.9–149.2 dB) in our methodology.
Additionally, even if NMFS had
concluded that MFAS were the
causative agent, insufficient evidence
exists regarding the received level when
the animals responded (there is no
information regarding where they were
when they would have first heard the
sound).
Comment 27: Two commenters noted
that little is known about most species
of beaked whales and most of that
knowledge has come from carcasses, as
sightings of live animals are generally
rare. With few exceptions, there is
almost nothing known about beaked
whale population structure, sizes, or
trends in the waters off the east coast of
the U.S, so determining the impact of
the loss of a few individuals to the
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population is impossible. Since most
species are pelagic, there is also no way
to know the real number killed in a
particular event: not all injured animals
strand, and not all carcasses find their
way to a beach. There is even less
known about non-lethal impacts, such
as disruption of mother-calf bonds.
Response: The commenter is correct
that relatively little is known about
beaked whale population structure,
sizes, and trends off the east coast of the
U.S. However, we do know that the
Navy’s ASW exercises are spread
throughout the AFAST Study Area (as
opposed to focused in an area of known
particular importance) and that the
Navy is utilizing Planning Awareness
Areas (in both exercise planning and
implementation, where practicable) to
limit takes of marine mammals
(including beaked whales) in designated
areas of high productivity and steep
bathymetric contours, which are
frequented by deep diving marine
mammals like beaked whales (see
Planning Awareness Areas in proposed
rule). Comment responses 12 and 36
discuss the likelihood of beaked whales
being injured by MFAS. Though not all
dead or injured animals are expected to
end up on the shore (some may be eaten
or float out to sea), we would expect
that if marine mammals were being
harmed by active sonar with any
regularity, more evidence would have
been detected over the 40-yr period that
the Navy has been conducting sonar in
the area (30 of which, people have
actively been collecting stranding data).
Of note also, the MFAS use covered by
this rule is not an increase in the
amount of sonar conducted off the east
coast and in the Gulf of Mexico (i.e., the
amount of use is consistent with historic
effort). Last, the potential impacts to
cetacean mother-calf pairs from sonar
are specifically discussed in Potential
Effects of Specified Activities on Marine
Mammals section of the proposed rule.
However, as the commenter suggests,
the specific effects of MFAS on beaked
whales and their calves are not
discussed because specific data do not
exist. For the reasons listed here and
described in the Negligible Impact
Analysis section of the proposed rule,
NMFS has determined that the Navy’s
action will have a negligible impact on
beaked whales.
Comment 28: One commenter noted
that the Navy states that it is helping to
fund (with NMFS) a series of controlled
exposure experiments on wild whales,
the first of which took place in the
Bahamas in 2007. Yet preliminary
results from this experiment support a
much lower threshold for behavioral
impacts than the Navy is using. In the
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experiment, only one successful
playback experiment on a beaked whale
was achieved and in it a tagged
Blainville’s beaked whale displayed a
probable behavioral response at a
received level of MFA sonar of 145 dB
re 1μPa [rms]. The precautionary
principle should be applied and the
Navy should, at a minimum, curb its
activities around known areas of high
marine mammal density and at times
when marine animals are expected to be
present.
Response: As the commenter notes,
the results from the first in the series of
behavioral response studies conducted
by NMFS and other scientists did show
one beaked whale (Mesoplodon
densirostris) responding to an MFAS
playback. The BRS–07 Cruise report
indicates that the playback began when
the tagged beaked whale was vocalizing
at depth (at the deepest part of a typical
feeding dive), following a previous
control with no sound exposure. The
whale appeared to stop clicking
significantly earlier than usual, when
exposed to mid-frequency signals in the
130–140 dB (rms) range. After a few
more minutes of the playback, when the
received level reached a maximum of
140–150 dB, the whale ascended on the
slow side of normal ascent rates with a
longer than normal ascent, at which
point the exposure was terminated. As
the commenter noted, the whale
displayed a behavioral response:
However, further consideration by
NMFS is necessary to determine if this
behavioral response qualifies as a
behavioral harassment pursuant to the
MMPA, and if so, how the information
should be factored into NMFS’ analysis.
The advanced modeling tool that the
Navy uses to predict the take of marine
mammals incidental to any particular
activity takes weeks and sometimes
months to produce the take estimates.
NMFS worked at length, with input
from the Navy and from a panel of
marine mammal scientists, to develop
and finalize the risk continuum for
behavioral harassment. It took months
for NMFS to finalize the risk continuum
and months for the Navy to calculate the
estimated takes based on the current
continuum. NMFS and the Navy are
working together to bring the Navy’s
AFAST activities into compliance under
the MMPA in advance of the expiration
of the MMPA National Defense
Exemption, and it was necessary for
NMFS to continue moving forward (not
wait for new data) in the MMPA process
in order to complete the final rule in the
needed timeframe to accomplish this.
This is not to definitively say that this
new information will change the way
that NMFS quantitatively analyzes
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effects. The interpretation of data
presented in the report notes that the
results are from a single experiment and
that a greater sample size is needed
before robust conclusions can be drawn.
Also, the results from this study fall
under the curve that NMFS is using for
behavioral effects (though the low end
of the curve). That said, NMFS will
carefully consider these results and
subsequent BRS results in future
analyses.
This final rule contains an adaptive
management component that requires a
yearly review of monitoring reports and
new science and allows for the
modification of mitigation and
monitoring measures, when appropriate.
As noted in the response to comment
#30, the Navy currently uses the
Planning Awareness Areas (designated
based on high productivity and steep
bathymetric contour areas) to limit
marine mammal impacts during both
exercise planning and implementation.
Additional detail regarding the potential
use of other specific mitigation
measures can be found in the Mitigation
EA.
Comment 29: NMFS’ and the Navy’s
assessment glosses over stranding
events associated with active sonar.
Although NMFS briefly discusses
stranding events (73 FR 60776–80), the
Marine Mammal Protection Act requires
NMFS to fully consider the impacts of
sonar on marine mammals to determine
there is no more than a negligible
impact before issuing an incidental take
authorization.
Response: NMFS disagrees. The
proposed rule contains a detailed
discussion of stranding events (those
that were merely coincident with MFAS
use, as well as those for which the
evidence suggests that MFAS exposure
was a contributing factor), a detailed
discussion of the multiple hypotheses
that describe how acoustically-mediated
or behaviorally-mediated bubble growth
can lead to marine mammal strandings,
as well as a comprehensive discussion
of the more general potential effects to
marine mammals of MFAS exposure.
NMFS analyses fully considered the
impacts of MFAS use and other naval
exercises on marine mammals, which
allowed us to determine that the total
taking during the five-year period from
the specified activities will have a
negligible impact on the affected species
or stocks.
Comment 30: One commenter states:
‘‘NMFS fails to take proper account of
published research on bubble growth in
marine mammals, which separately
indicates the potential for injury and
death at lower [received sound] levels.
According to the best available scientific
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evidence, gas bubble growth is the
causal mechanism most consistent with
the observed injuries. NMFS’ argument
to the contrary simply misrepresents the
available literature.’’
Response: The proposed rule
contained a detailed discussion of the
many hypotheses involving both
acoustically-mediated and behaviorallymediated bubble growth. NMFS
concluded that there is not sufficient
evidence to definitively say that any of
these hypotheses accurately describe the
exact mechanism that leads from sonar
exposure to a stranding. Despite the
many theories involving bubble
formation (both as a direct cause of
injury and an indirect cause of
stranding), Southall et al., (2007)
summarizes that scientific disagreement
or complete lack of information exists
regarding the following important
points: (1) Received acoustical exposure
conditions for animals involved in
stranding events; (2) pathological
interpretation of observed lesions in
stranded marine mammals; (3) acoustic
exposure conditions required to induce
such physical trauma directly; (4)
whether noise exposure may cause
behavioral reactions (such as atypical
diving behavior) that secondarily cause
bubble formation and tissue damage;
and (5) the extent the post mortem
artifacts introduced by decomposition
before sampling, handling, freezing, or
necropsy procedures affect
interpretation of observed lesions.
Comment 31: One commenter stated
that NMFS’ take estimates do not reflect
other non-auditory physiological
impacts, such as from chronic exposure
during development, stress, and
exposure to toxic chemicals.
Response: The commenter is correct
that the NMFS’ estimated take numbers
do not reflect non-auditory
physiological impacts because the
quantitative data necessary to address
those factors in the Navy’s exposure
model do not exist. However, NMFS
acknowledges that a subset of the
animals that are taken by harassment
will also likely experience non-auditory
physiological effects (stress, etc.) and
these effects are addressed in the
proposed rule (see Stress Responses
section). Regarding toxins, the Navy did
not expect AFAST activities to result in
the production of any toxic chemicals
that would affect marine mammals,
although the EIS did analyze the
potential impacts from torpedo
guidance wires, torpedo flex hoses, and
parachutes and find that no significant
impacts to marine mammals were likely
to result from those expended materials.
Therefore, the Navy determined that
marine mammals would not be taken
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4869
via the ingestion of toxins or interaction
with the aforementioned expended
materials and they did not request (nor
did NMFS grant) authorization for take
of marine mammals via these methods.
Comment 32: The MMC recommends
that the Service work with the Navy to
prepare a more thorough analysis of
potential cumulative effects, the
measures that will be taken to avoid or
minimize them, and the basis for
concluding that those effects will be
negligible. They further note that the
DEIS, request for a letter of
authorization, and proposed rule, do not
describe how the effects of the Navy’s
operations and the effects of other
human activities (e.g., ship traffic,
commercial fishing) will be assessed
and minimized to the extent necessary
to avoid an excessive cumulative impact
on marine mammals.
Response: NMFS participated as a
cooperating agency in the development
of the Navy’s AFAST EIS and has
adopted it to support our issuance of
incidental take regulations and LOAs.
The FEIS contains a thorough analysis
of potential cumulative effects.
Throughout the FEIS, within the
separate resource sections, the Navy
addresses different ways that they will
minimize adverse effects. As an agency,
NMFS understands the importance of
cumulative effects, and we continually
look for ways to both better understand
and more effectively reduce cumulative
effects/impacts on marine mammals and
other marine resources through statute
implementation (ESA, NEPA, MSA,
CZMA, etc.) and more directly through
policy and other decisions, such as the
implementation of the Right Whale Ship
Strike Reduction rule or the convening
of the Potential Application of VesselQuieting Technology on Large
Commercial Vessels meeting in May
2007. However, the MMPA does not
require that cumulative effects be
factored into NMFS’ determination
whether to issue an incidental take
authorization under the MMPA. Rather,
the MMPA states that NMFS ‘‘shall
allow * * * the incidental taking * * *
if the Secretary * * * finds that the
total taking [meaning the taking NMFS
authorizes] during each five-year (or
less) period concerned will have a
negligible impact.’’
Comment 33: One commenter felt that
the rule discounts the potential impacts
on beaked whales from AFAST based on
assumptions that are unfounded. The
first is that strandings are unlikely to
occur because events are not planned
‘‘in a location having a constricted
channel less than 35 miles wide or with
limited egress similar to the Bahamas
(because none exist in the AFAST Study
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Area)’’. The commenter notes that
sonar-associated beaked whale
mortalities have occurred in other areas
(e.g. the Canary Islands in 2002 and
2004) where such bathymetry was not
present, suggesting this as not a
requisite characteristic for sonarinfluenced strandings. The second is the
observation that unusual strandings
have not been recorded to date in the
region is not an indication that
mortalities have not occurred. Given
that most species of cetaceans sink upon
death, and that most beaked whales
occur in very deep water which would
prevent decomposing carcasses from
eventually refloating, it is highly
unlikely that whales suffering mortal
injury at sea would have been detected.
This is especially true in offshore/island
regions, where there is limited shoreline
throughout much of the operational
area, and much of it is steep or rocky
and not conducive to holding moribund
individuals or carcasses.
Response: The rule does not discount
the potential impacts on beaked whales
from sonar. NMFS specifically
addresses the potential impacts to
beaked whales in the ‘‘Acoustically
Mediated Bubble Growth’’,
‘‘Behaviorally Mediated Responses to
MFAS That May Lead to Stranding’’,
‘‘Stranding and Mortality’’, and
‘‘Association Between Mass Stranding
Events and Exposure to MFAS’’ sections
of the proposed rule. Specifically, in
recognition of potential impacts to
beaked whales and the scientific
uncertainty surrounding the exact
mechanisms that lead to strandings, the
Navy requested, and NMFS has
authorized, the mortality of 10 beaked
whales over the course of 5 years in the
unlikely event that a stranding occurs as
a result of Navy training exercises.
Additionally, the commenter is
misrepresenting a piece of text from the
proposed rule—though NMFS points
out that the five factors that contributed
to the stranding in the Bahamas are not
all present in the AFAST Study Area,
we do not say that that alone means
strandings are unlikely to occur. We
also further suggest that caution is
recommended when any of the three
environmental factors are present
(constricted channels, steep bathymetry,
or surface ducts) in the presence of
MFAS and beaked whales. Also, NMFS
does not ever say that the fact that
strandings have not been recorded to
date in the region is an indication that
mortalities have not occurred. Rather,
we say that though not all dead or
injured animals are expected to end up
on the shore (some may be eaten or float
out to sea), one might expect that if
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marine mammals were being harmed by
active sonar with any regularity, more
evidence would have been detected over
the 40-yr period that the Navy has been
conducting sonar in the area (30 of
which, people have actively been
collecting stranding data).
Comment 34: The MMC
recommended that NMFS work with the
Navy to provide in the final rule and EIS
a side-by-side comparison of the
methods each agency used to generate
the sound exposure estimates so that
reviewers can understand the process by
which they were derived and the
uncertainties associated with that
process, and use that information to
assess the risks to marine mammal
species and the adequacy of mitigation
measures. The MMC also requested an
explanation of how NMFS ‘‘revised take
estimates and proposed take
authorization’’ ‘‘depict a more realistic
scenario than those adopted directly
from the Navy’s acoustic analysis.’’ Last,
MMC notes that they have requested in
the past that the Navy submit its sonar
exposure model for peer-review.
Response: As indicated in the
Estimates of Potential Marine Mammal
Exposures and Takes section of the
proposed rule, Appendix F of the
Navy’s AFAST EIS clearly describes the
analytical procedures and provides the
data used to estimate the number of
marine mammal exposures to NMFS
acoustic threshold levels in sufficient
detail that the reviewers can understand
and verify the estimated risks. However,
reviewers would not be able to
reconstruct the process exactly because
inherent to the overall exposure model
is the CASS/GRAB submodel, the
specific details of which cannot be
included in the EIS because the model
is a Navy owned, restricted distribution
model available only to U.S.
Government Agencies and their
contractors. This high fidelity acoustic
propagation model (CASS/GRAB) used
for marine mammal effects analysis is
the same model used for the operational
use of tactical sonar, and it is included
in the Navy’s Oceanographic and
Atmospheric Master Library (OAML),
which has a rigorous acceptance process
for all databases, models and algorithms
prior to being accepted into OAML.
The Navy provides the numbers of
estimated marine mammal exposures to
NMFS. These numbers (presented in the
‘‘Navy Modeled Exposure Estimates’’
columns of Table 6) do not take into
consideration any avoidance of vessels
or sound sources by marine mammals or
the implementation of mitigation
measures. As described in the
Mitigation Conclusion section of the
proposed rule, when the distance from
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the sonar source within which an
animal would need to approach to be
exposed to injurious levels (10 m), the
small number of modeled exposures to
injurious levels to a few species (of
relatively good detectibility: dolphins
and pilot whales), the implementation
of mitigation measures, and the
likelihood that most marine mammals
would avoid approaching the source at
this distance are taken into
consideration, NMFS and the Navy
believe that marine mammals will not
be injured by sonar exposure. Therefore,
NMFS has not authorized any Level A
Harassment, with the exception of the
10 beaked whales (by injury or
mortality) over the course of the 5-yr
regulations, the reasons for which are
explained in the Mortality section of the
proposed rule. These are the only
quantitative adjustments NMFS has
made to the authorized takes from the
Navy’s modeled exposure results. NMFS
has directly adopted the Navy’s Level B
Harassment exposures as modeled,
though we qualitatively explain in the
proposed rule why we believe these
numbers may be an overestimate (see
Overestimation section). Additionally,
although NMFS is not required to
identify the number of animals that will
be taken specifically by TTS versus
behavioral harassment (Level B
Harassment takes include both), we
have attempted to make more realistic
estimates by quantitatively refining the
Navy’s TTS estimates based on the same
factors listed above for refining the
injury estimates (see the Speciesspecific analysis section). The
authorized number of Level B
harassment takes remains the same as
the number of exposures estimated by
the Navy’s model.
Last, NMFS’ Office of Protected
Resources has funded a peer-review of
the Navy’s exposure model to be
conducted by the Center for
Independent Experts. The results of this
review are scheduled to be available at
the end of January, 2009.
Comment 35: One commenter asserts
that the Navy’s exposure model fails to
consider the following important points:
• Possible synergistic effects of using
multiple sources in the same exercise,
or the combined effects of multiple
exercises.
• Indirect effects, such as the
potential for mother-calf separation, that
can result from short-term disturbance.
• In assuming animals are evenly
distributed—the magnifying effects of
social structure, whereby impacts on a
single animal within a pod, herd, or
other unit may affect the entire group.
• In assuming that every whale
encountered during subsequent
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exercises is essentially a new whale—
the cumulative impacts on the breeding,
feeding, and other activities of species
and stocks.
Response: Though the Navy’s model
does not quantitatively consider the
points listed above (because the
quantitative data necessary to include
those concepts in a mathematical model
do not currently exist), NMFS and the
Navy have qualitatively addressed those
concerns in their effects analyses in the
rule and in the Navy’s EIS.
Comment 36: NMFS’ (and the Navy’s)
analysis of marine mammal distribution,
habitat abundance, population structure
and ecology contains false, misleading
or outdated assumptions that tend to
both underestimate impacts on species
and to impede consideration of
reasonable alternatives and mitigation
measures. For example, outdated stock
assessment data are used as the basis for
most density estimates. It also appears
that NMFS and the Navy do not
consider other sources of published
literature. For a number of species,
uniform distribution was assumed when
calculating density and risk. Although
the Navy and NMFS made repeated
assurances that this is a conservative
approach, it is not. Marine mammals
often concentrate in areas with greater
density of prey or more favorable
topography or currents for migration;
thus, assuming a uniform distribution
will overestimate presence in some
areas and dramatically underestimate it
in others.
Another commenter notes that the
Navy’s analysis of acoustic impacts to
marine mammals is through modeling
based on abundance estimates which
were largely determined from aerial
surveys, a difficult way to count marine
mammals, especially relatively small
animals and those that dive for
prolonged periods such as beaked
whales—the very animals thought to be
most susceptible to anthropogenic ocean
noise.
Response: The most current stock
assessment reports (Waring et al., 2007)
were used to calculate density
estimates. As summarized in the
proposed rule and described more fully
in the Navy’s FEIS, the Navy used the
best data and methods available to
calculate density, including other
literature as well as habitat modeling
that considered bathymetry, distance
from shelf break, sea surface
temperature, and Chlorophyll A
concentration. All spatial models and
density estimates were reviewed by
NMFS technical staff. The Navy’s model
utilizes uniform density, but it also
divides the east coast into meaningful
sections, such as on-shelf and off-shelf
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and the different OPAREAS. Using a
uniform density is a form of averaging
and the commenter has provided no
support for why the model would
‘‘overestimate’’ sometimes and
‘‘dramatically underestimate’’ in others
(all else being equal, a uniform
distribution should do these two things
in equal amounts).
Beaked whale densities in the SE (and
seaward of the shelf break in the NE)
were derived through the spatial model
approach which took environmental
and habitat parameters into
consideration. These models were built
using only shipboard survey data from
1998 through 2005 collected and
provided by NMFS. For areas in the NE
shoreward of the shelf break, beaked
whale density was actually calculated
by Palka (Palka, 2005) based on
geographic strata provided by Navy.
These estimates were developed using
data from both shipboard and aerial
surveys conducted by the NEFSC.
Density data provided by Palka
incorporated estimates of g(0)
(correction factor that incorporates
sightability) as discussed in Palka 2005.
Comment 37: One commenter states
that NMFS does not consider the
potential for acute synergistic [indirect]
effects from sonar training. For example,
the agency does not consider the greater
susceptibility to vessel strike of animals
that have been temporarily harassed or
disoriented. The absence of analysis is
particularly glaring in light of the 2004
Nowacek et al. study, which indicates
that mid-frequency sources provoke
surfacing and other behavior in North
Atlantic right whales that increases the
risk of vessel strike.
Response: In the proposed rule,
NMFS refers the reader to a conceptual
framework that illustrates the variety of
avenues of effects that can result from
sonar exposure, to include ‘‘risk prone
behavior’’ resulting somewhat indirectly
from attempting to avoid certain
received levels. Though we consider the
potential for this type of interaction,
NMFS does not include detailed
analysis of potential indirect effects that
have not been empirically
demonstrated. Though Nowacek
showed that right whales responded to
a signal with mid-frequency
components (not an actual MFAS
signal) in a way that appeared likely to
put them at greater risk for ship strike,
we do not have evidence that the
hypothesized sequence of behaviors has
actually led to a ship strike.
Additionally, in general and if affected,
marine mammals may be affected by (or
respond to) sonar in more than one
single way when exposed. However,
when analyzing impacts, NMFS
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4871
‘‘counts’’ the most severe response. In
the example given by the commenter,
NMFS considers the overall possibility
of ship strikes resulting from Navy
activities, regardless of whether or not
they would be preceded by a lesser
response.
General Opposition and Other
Comment 38: The Navy should avoid
fish spawning grounds and important
fish habitat. It should also avoid highvalue sea turtle habitat.
Response: These concerns are outside
of the purview of the MMPA. Impacts to
fish spawning grounds and habitat are
dealt with pursuant to the Magnusson
Stevens Act (MSA) as it relates to
Essential Fish Habitat (EFH). The Navy
determined that their activities would
not adversely impact EFH; therefore, the
Navy determined that a consultation
under the MSA was not necessary.
Measures to reduce impacts to sea
turtles are included in the terms and
conditions of the biological opinion that
NMFS issued to the Navy (view at:
https://www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications).
Comment 39: One commenter
suggested that no sonar testing should
be done in the waters of the Gulf and
Atlantic because dead marine life from
these tests would go ashore and
endanger the tourism industry for the
state.
Response: NMFS is aware of 5 cases,
worldwide, where science supports the
determination that MFAS was a
contributing factor in a marine mammal
stranding. None of these strandings
occurred on the Atlantic coast of the
U.S. or in the Gulf of Mexico.
Separately, potential adverse effects to
the tourism industry are not required to
be addressed under the MMPA.
Comment 40: The NRDC urged NMFS
to withdraw its proposed rule on
AFAST and to revise the document
prior to its recirculation for public
comment. They suggested NMFS revisit
its profoundly flawed analysis of
environmental impacts and prescribe
mitigation measures that truly result in
the least practicable adverse impact on
marine species.
Response: NMFS has addressed
specific comments related to the effects
analysis here and the mitigation
measures in the Mitigation
Environmental Assessment. We do not
believe that the analysis is flawed and
we believe that the prescribed measures
will result in the least practicable
adverse impacts on the affected species
or stock. Therefore, NMFS does not
intend to withdraw its AFAST rule.
Comment 41: A few commenters
expressed general opposition to Navy
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activities and NMFS’ issuance of an
MMPA authorization, because of the
danger to marine mammals, and
presented several reasons why MFAS
was not necessary.
Response: NMFS appreciates the
commenters’ concern for the marine
mammals that live in the area of the
proposed activities. However, the
MMPA directs NMFS to issue an
incidental take authorization if certain
findings can be made. Under the
MMPA, NMFS must make the decision
of whether or not to issue an
authorization based on the proposed
action that the applicant submits—the
MMPA does not contain a mechanism
for NMFS to question the need for the
action that the applicant has proposed
(unless the action is illegal). Similarly,
any U.S. citizen (including the Navy)
can request and receive an MMPA
authorization as long as all of the
necessary findings can be made. NMFS
has determined that the Navy’s AFAST
training activities will have a negligible
impact on the affected species or stocks
and, therefore, we plan to issue the
requested MMPA authorization.
Estimated Take of Marine Mammals
As mentioned previously, with
respect to the MMPA, NMFS’ effects
assessments serve four primary
purposes: (1) To put forth the
permissible methods of taking (i.e.,
Level B Harassment (behavioral
harassment), Level A Harassment
(injury), or mortality, including an
identification of the number and types
of take that could occur by Level A or
B harassment or mortality) and to
prescribe other means of effecting the
least practicable adverse impact on such
species or stock and its habitat (i.e.,
mitigation); (2) to determine whether
the specified activity will have a
negligible impact on the affected species
or stocks of marine mammals (based on
the likelihood that the activity will
adversely affect the species or stock
through effects on annual rates of
recruitment or survival); (3) to
determine whether the specified activity
will have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (however,
there are no subsistence communities
that would be affected in the AFAST
Study Area, so this determination is
inapplicable for AFAST); and (4) to
prescribe requirements pertaining to
monitoring and reporting.
In the Estimated Take of Marine
Mammals section of the proposed rule,
NMFS related the potential effects to
marine mammals from MFAS/HFAS
and underwater detonation of
explosives, i.e., IEER (discussed in the
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Potential Effects of Specified Activities
on Marine Mammals section) to the
MMPA regulatory definitions of Level A
and Level B Harassment and quantified
(estimated) the effects on marine
mammals that could result from the
specific activities that the Navy intends
to conduct. The subsections of this
analysis are discussed individually
below.
Definition of Harassment
The Definition of Harassment section
of the proposed rule contained the
definitions of Level A and Level B
Harassments, and a discussion of which
of the previously discussed potential
effects of MFAS/HFAS or explosive
detonations fall into the categories of
Level A Harassment (permanent
threshold shift (PTS), acoustically
mediated bubble growth, behaviorally
mediated bubble growth, and physical
disruption of tissues resulting from
explosive shock wave) or Level B
Harassment (temporary threshold shift
(TTS), acoustic masking and
communication impairment, and
behavioral disturbance rising to the
level of harassment). See 73 FR 60754,
pages 60800–60801. No changes have
been made to the discussion contained
in this section of the proposed rule.
Acoustic Take Criteria
In the Acoustic Take Criteria section
of the proposed rule, NMFS described
the development and application of the
acoustic criteria for both MFAS/HFAS
and explosive detonations (73 FR 60754,
pages 60801–60807). No changes have
been made to the discussion contained
in this section of the proposed rule,
with the exception of the issue
discussed below.
NMFS received one public comment
in which the commenter noted that the
acoustic thresholds for TTS and PTS for
pinnipeds presented in NMFS’ AFAST
proposed rule were different from those
presented in NMFS’ Southern California
Range Complex proposed rule. As noted
in the updated summary of acoustic
thresholds for TTS and PTS below,
NMFS has established three separate
TTS and PTS thresholds for pinnipeds
based on which species are being
considered. All of the pinnipeds that are
expected to be exposed to MFAS/HFAS
in the AFAST Study Area are more
closely related to harbor seals (see
below) and, therefore, only one of the
three pinniped criteria is applicable in
AFAST.
In the proposed rule, NMFS only
listed the single applicable threshold
without explaining that two other
pinniped TTS and PTS thresholds are
used for different taxa (that are present
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in southern California, but not in the
AFAST Study Area). These paragraphs
and the summary below serve as a
clarification and response to the
commenter’s comment.
NMFS’ TTS criteria (which indicate
the received level at which onset TTS
(>6dB) is induced) for MFAS/HFAS are
as follows:
• Cetaceans—195 dB re 1 μPa2-s
(based on mid-frequency cetaceans—no
published data exist on auditory effects
of noise in low or high frequency
cetaceans (Southall et al. (2007))
• Harbor Seals (and closely related
species, which include all of the species
present in the AFAST Study Area)—183
dB re 1 μPa2-s
• Northern Elephant Seals (and
closely related species)—204 dB re
1 μPa2-s
• California Sea Lions (and closely
related species)—206 dB re 1 μPa2-s
NMFS uses the following acoustic
criteria for injury (Level A Harassment):
• Cetaceans—215 dB re 1 μPa2-s
(based on mid-frequency cetaceans—no
published data exist on auditory effects
of noise in low or high frequency
cetaceans (Southall et al. (2007))
• Harbor Seals (and closely related
species)—203 dB re 1 μPa2-s
• Northern Elephant Seals (and
closely related species)—224 dB re 1
μPa2-s
• California Sea Lions (and closely
related species)—226 dB re 1 μPa2-s
For the behavioral harassment criteria
(for all species except harbor porpoises,
below), NMFS uses acoustic risk
functions developed by NMFS, with
input from the Navy, to estimate the
probability of behavioral responses to
MFAS/HFAS (interpreted as the
percentage of the exposed population)
that NMFS would classify as harassment
for the purposes of the MMPA given
exposure to specific received levels of
MFA sonar. For harbor porpoises,
currently available information suggests
a lower threshold level of response for
both captive and wild animals and,
therefore, NMFS uses a separate 120 dB
re 1 μPa step function to estimate take
by behavioral harassment (3 FR 60754,
pages 60802–60806).
Table 13 in the proposed rule
summarizes the acoustic criteria for
explosive detonations (73 FR 60754,
page 60807).
Estimates of Potential Marine Mammal
Exposures and Authorized Take
Information regarding the models
used, the assumptions used in the
models, and the process of estimating
take is available in the Navy’s EIS/OEIS
for AFAST. Estimating the take that will
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result from the proposed activities
entails the following general steps:
(1) In order to quantify the types of
take described in previous sections that
are predicted to result from the Navy’s
specified activities, the Navy first uses
a sound propagation model that predicts
the volume of water that will be
ensonified to a range of levels of
pressure and energy (of the metrics used
in the criteria) from MFAS/HFAS and
explosive detonations based on several
important pieces of information,
including:
• Characteristics of the sound
sources;
• Sonar source characteristics;
include: source level (with horizontal
and vertical directivity corrections),
source depth, center frequency, source
directivity (horizontal/vertical beam
width and horizontal/vertical steer
direction), and ping spacing;
• Explosive source characteristics
include: The net explosive weight, the
type of explosive, and the detonation
depth;
• Transmission loss (in 36
representative environmental provinces)
based on: Seasonal sound speed
profiles; seabed geoacoustics; wind
speed; and acoustics.
(2) The accumulated energy and
maximum received sound pressure level
within the waters in which the sonar is
operating is sampled over a two
dimensional grid. The zone of influence
(ZOI) for a given threshold is estimated
by summing the areas represented by
each grid point for which the threshold
is exceeded. For behavioral response,
the percentage of animals likely to
respond corresponding to the maximum
received level is found, and the area of
the grid point is multiplied by that
percentage to find the adjusted area.
Those adjusted area are summed across
all grid points to find the overall ZOI for
a particular source.
(3) The densities of each marine
mammal species, which are specific to
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certain geographic areas and seasons if
data are available, are applied to the
summed ZOIs for a particular training
event to determine how many times
individuals of each species are exposed
to levels that exceed the applicable
criteria for injury or harassment.
(4) Next, the criteria discussed in the
previous section are applied to the
estimated exposures to predict the
number of exposures that exceed the
criteria, i.e., the number of takes by
Level B Harassment, Level A
Harassment, and mortality.
(5) Last, NMFS and the Navy consider
the mitigation measures and modelcalculated estimates may be adjusted
based on a post-model assessment. For
example, in some cases the raw
modeled numbers of exposures to levels
predicted to result in Level A
Harassment from exposure to sonar
might indicate that 1 fin whale would
be exposed to levels of sonar anticipated
to result in PTS—however, a fin whale
would need to be within approximately
10 m of the source vessel in order to be
exposed to these levels. Because of the
mitigation measures (watchstanders and
shutdown zone), size of fin whales, and
nature of fin whale behavior, it is highly
unlikely that a fin whale would be
exposed to those levels, and therefore
the Navy would not request
authorization for Level A Harassment of
1 fin whale. Table 11 contains the
Navy’s estimated take estimates. The
‘‘takes’’ reported in the take table and
proposed to be authorized are based on
estimates of marine mammal exposures
to levels above those indicated in the
criteria. Every separate take does not
necessarily represent a different
individual because some individual
marine mammals may be exposed more
than once, either within one day and
one exercise, or on different days from
different exercise types.
(6) Last, the Navy’s specified activities
have been described based on best
estimates of the number of MFAS/HFAS
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4873
hours that the Navy will conduct. The
exact number of hours may vary from
year to year, but will not exceed the 5year total indicated in Table 1 (by
multiplying the yearly estimate by 5) by
more than 10 percent. NMFS estimates
that a 10-percent increase in sonar hours
would result in approximately a 10percent increase in the number of takes
(described in Table 6), and we have
considered this possibility and the effect
of this additional sonar use in our
analysis.
Table 6 remains unchanged from
Table 11 in the proposed rule (73 FR
60753, page 608090) with the exception
of minor modifications and one
correction. The number of estimated
and authorized Level B behavioral takes
of beaked whales increased by a total of
2238 (no increase in modeled TTS
takes) because the Navy corrected a
calculation related to submarine
maintenance. When submarine sonar is
used in exercises, the source emits a
ping approximately once every 2 hours.
However, when maintenance is being
conducted, the source emits
approximately 60 pings an hour, which
will result in more modeled takes than
the sub used in an exercise. The Navy
originally calculated the submarine
sonar takes using the number of pings
from an exercise—this has since been
corrected. Of note, all of the indicated
take increase will occur during sub
maintenance, which occurs
approximately 50% inshore (potentially
at a dock) and 50% at sea, but all of
which occurs with a single submarine,
not a group of sonar sources such as in
the large scale training exercises that
have been associated with strandings in
certain circumstances in approximately
5 cases outside of U.S. waters. This
change in the take numbers did not
change NMFS’ conclusions regarding
the effects of the proposed action.
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Mortality
Evidence from five beaked whale
strandings, all of which have taken
place outside of the AFAST Study Area,
and have occurred over approximately a
decade, suggests that the exposure of
beaked whales to MFAS in the presence
of certain conditions (e.g., multiple
units using tactical sonar, steep
bathymetry, constricted channels, strong
surface ducts, etc.) may result in
strandings, potentially leading to
mortality. Although these physical
factors believed to contribute to the
likelihood of beaked whale strandings
are not present on the Atlantic Coast of
the U.S. or in the Gulf of Mexico in the
aggregate, scientific uncertainty exists
regarding what other factors, or
combination of factors, may contribute
to beaked whale strandings.
Accordingly, to allow for scientific
uncertainty regarding contributing
causes of beaked whale strandings and
the exact behavioral or physiological
mechanisms that can lead to the
ultimate physical effects (stranding and/
or death), the Navy has requested
authorization for (and NMFS is
authorizing) take, by injury or mortality
of 10 beaked whales over the course of
the 5-yr regulations. Neither NMFS nor
the Navy anticipates that marine
mammal strandings or mortality will
result from the operation of MFAS
during Navy exercises within the
AFAST Study Area.
Effects on Marine Mammal Habitat
NMFS’ AFAST proposed rule
included a section that addressed the
effects of the Navy’s activities on Marine
Mammal Habitat (73 FR 60754, page
60810). The analysis preliminarily
concluded that the Navy’s activities
would have minimal effects on marine
mammal habitat. No changes have been
made to the discussion contained in this
section of the proposed rule.
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Analysis and Negligible Impact
Determination
Pursuant to NMFS’ regulations
implementing the MMPA, an applicant
is required to estimate the number of
animals that will be ‘‘taken’’ by the
specified activities (i.e., takes by
harassment only, or takes by
harassment, injury, and/or death). This
estimate informs the analysis that NMFS
must perform to determine whether the
activity will have a ‘‘negligible impact’’
on the species or stock. Level B
(behavioral) harassment occurs at the
level of the individual(s) and does not
assume any resulting population-level
consequences, though there are known
avenues through which behavioral
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disturbance of individuals can result in
population-level effects (for example:
pink-footed geese (Anser
brachyrhynchus) in undisturbed habitat
gained body mass and had about a 46percent reproductive success compared
with geese in disturbed habitat (being
consistently scared off the fields on
which they were foraging) which did
not gain mass and had a 17-percent
reproductive success). A negligible
impact finding is based on the lack of
likely adverse effects on annual rates of
recruitment or survival (i.e., populationlevel effects). 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 must consider other
factors, such as the likely nature of any
responses (their intensity, duration,
etc.), the context of any responses
(critical reproductive time or location,
migration, etc.), or any of the other
variables mentioned in the first
paragraph (if known), as well as the
number and nature of estimated Level A
takes, the number of estimated
mortalities, and effects on habitat.
Generally speaking, and especially with
other factors being equal, the Navy and
NMFS anticipate more severe effects
from takes resulting from exposure to
higher received levels (though this is in
no way a strictly linear relationship
throughout species, individuals, or
circumstances) and less severe effects
from takes resulting from exposure to
lower received levels.
In the Analysis and Negligible Impact
Determination section of the proposed
rule, NMFS addressed the issues
identified in the preceding paragraph in
combination with additional detailed
analysis regarding the severity of the
anticipated effects, and including
species (or group)-specific discussions,
to determine that Navy training,
maintenance, and RDT&E activities
utilizing MFAS/HFAS and underwater
detonations (IEER) will have a negligible
impact on the marine mammal species
and stocks present in the AFAST Study
Area. No changes have been made to the
discussion contained in this section of
the proposed rule (73 FR 60754, pages
60811–60823).
Subsistence Harvest of Marine
Mammals
NMFS has determined that the
issuance of these regulations and
subsequent LOAs for Navy AFAST
exercises would not have an
unmitigable adverse impact on the
availability of the affected species or
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4875
stocks for taking for subsistence uses,
since there are no such uses in the
specified area.
ESA
There are six marine mammal species
and six sea turtle species listed as
threatened or endangered under the
ESA with confirmed or possible
occurrence in the study area: Humpback
whale, NARW, sei whale, fin whale,
blue whale, sperm whale, loggerhead
sea turtle, the green sea turtle, hawksbill
sea turtle, leatherback sea turtle, olive
ridley sea turtle and the Kemp’s ridley
sea turtle. Pursuant to Section 7 of the
ESA, the Navy has consulted with
NMFS on this action. NMFS has also
consulted internally on the issuance of
regulations under section 101(a)(5)(A) of
the MMPA for this activity. In a
Biological Opinion (BiOp), NMFS
concluded that the Navy’s activities in
the AFAST Study Area and NMFS’
issuance of these regulations are not
likely to jeopardize the continued
existence of threatened or endangered
species or destroy or adversely modify
any designated critical habitat.
NMFS (the Endangered Species
Division) will also issue BiOps and
associated incidental take statements
(ITSs) to NMFS (the Permits,
Conservation, and Recreation Division)
to exempt the take (under the ESA) that
NMFS authorizes in the LOAs under the
MMPA. Because of the difference
between the statutes, it is possible that
ESA analysis of the applicant’s action
could produce a take estimate that is
different from the takes requested by the
applicant (and analyzed for
authorization by NMFS under the
MMPA process), despite the fact that the
same proposed action (i.e., number of
sonar hours and explosive detonations)
was being analyzed under each statute.
When this occurs, NMFS staff
coordinate to ensure that the most
conservative (lowest) number of takes is
authorized. For the Navy’s proposed
AFAST training, coordination with the
Endangered Species Division indicates
that they will likely allow for a lower
level of take of ESA-listed marine
mammals than was requested by the
applicant (because their analysis
indicates that fewer will be taken than
estimated by the applicant). Therefore,
the number of authorized takes in
NMFS’ LOA(s) will reflect the lower
take numbers from the ESA
consultation, though the specified
activities (i.e., number of sonar hours,
etc.) will remain the same. Alternately,
these regulations indicate the maximum
number of takes that may be authorized
under the MMPA.
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The ITS(s) issued for each LOA will
contain implementing terms and
conditions to minimize the effect of the
marine mammal take authorized
through the 2009 LOA (and subsequent
LOAs in 2010, 2011, 2012, and 2013).
With respect to listed marine mammals,
the terms and conditions of the ITSs
will be incorporated into the LOAs.
NEPA
NMFS participated as a cooperating
agency on the Navy’s Final
Environmental Impact Statement (FEIS)
for AFAST. NMFS subsequently
adopted the Navy’s EIS for the purpose
of complying with the MMPA.
Additionally, NMFS prepared an
Environmental Assessment (EA) that
tiered off the Navy’s FEIS. The EA
analyzed the environmental effects of
several different mitigation alternatives
for the issuance of the AFAST rule and
subsequent LOAs. A finding of no
significant impact was issued for the
mitigation EA on January 15, 2009.
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Determination
Based on the analysis contained
herein and in the proposed rule (and
other related documents) of the likely
effects of the specified activity on
marine mammals and their habitat and
dependent upon the implementation of
the mitigation measures, NMFS finds
that the total taking from Navy AFAST
training exercises utilizing MFAS/HFAS
and underwater explosives (IEER) over
the 5 year period will have a negligible
impact on the affected species or stocks
and will not result in an unmitigable
adverse impact on the availability of
marine mammal species or stocks for
taking for subsistence uses because no
subsistence uses exist in the AFAST
Study Area. NMFS has issued
regulations for these exercises that
prescribe the means of effecting the least
practicable adverse impact on marine
mammals and their habitat and set forth
requirements pertaining to the
monitoring and reporting of that taking.
Classification
This action does not contain a
collection of information requirement
for purposes of the Paperwork
Reduction Act.
Pursuant to the procedures
established to implement section 6 of
Executive Order 12866, the Office of
Management and Budget has
determined that this final rule is
significant.
Pursuant to the Regulatory Flexibility
Act, the Chief Counsel for Regulation of
the Department of Commerce has
certified to the Chief Counsel for
Advocacy of the Small Business
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Administration that this final rule, if
adopted, would not have a significant
economic impact on a substantial
number of small entities. The
Regulatory Flexibility Act requires
Federal agencies to prepare an analysis
of a rule’s impact on small entities
whenever the agency is required to
publish a notice of proposed
rulemaking. However, a Federal agency
may certify, pursuant to 5 U.S.C. section
605(b), that the action will not have a
significant economic impact on a
substantial number of small entities.
The Navy is the entity that will be
affected by this rulemaking, not a small
governmental jurisdiction, small
organization or small business, as
defined by the Regulatory Flexibility
Act. Any requirements imposed by a
Letter of Authorization issued pursuant
to these regulations, and any monitoring
or reporting requirements imposed by
these regulations, will be applicable
only to the Navy. Because this action, if
adopted, would directly affect the Navy
and not a small entity, NMFS concludes
the action would not result in a
significant economic impact on a
substantial number of small entities.
The Assistant Administrator for
Fisheries has determined that there is
good cause under the Administrative
Procedure Act (5 U.S.C. 553(d)(3)) to
waive the 30-day delay in effective date
of the measures contained in the final
rule. Since January 23, 2007, the Navy
has been conducting military readiness
activities employing mid-frequency
active sonar (MFAS) pursuant to a 2year MMPA National Defense
Exemption (NDE). The NDE serves as a
bridge to long-term compliance with the
MMPA while the Navy prepared its
Environmental Impact Statement and
pursued the necessary MMPA
incidental take authorization for the
AFAST exercises. The NDE will expire
on January 23, 2009, by which time it
is imperative that the regulations and
the measures identified in a subsequent
LOA become effective. Any delay of
these measures would result in either:
(1) A suspension of ongoing or planned
naval exercises, which would disrupt
vital sequential training and
certification processes essential to
national security; or (2) the Navy’s noncompliance with the MMPA (should the
Navy conduct exercises without an
LOA), thereby resulting in the potential
for unauthorized takes of marine
mammals upon expiration of the NDE.
National security and NMFS’ and
Navy’s preference that the Navy be in
compliance with the MMPA after
January 23, 2009, dictate that these
measures go into effect immediately.
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The Navy is the entity subject to the
regulations and has informed NMFS
that it is imperative that these measures
be effective on or before January 23,
2009. Finally, as recognized by the
President and the United States
Supreme Court, the AFAST exercises
proposed to be conducted are of
paramount interest to the United States.
Any delay in the implementation of
these measures would raise serious
national security implications.
Therefore, these measures will become
effective upon filing.
List of Subjects in 50 CFR Part 216
Exports, Fish, Imports, Incidental
take, Indians, Labeling, Marine
mammals, Navy, Penalties, Reporting
and recordkeeping requirements,
Seafood, Sonar, Transportation.
Dated: January 16, 2009.
James Balsiger,
Acting Assistant Administrator for Fisheries,
National Marine Fisheries Service.
For reasons set forth in the preamble,
50 CFR Part 216 is amended as follows:
■
PART 216—REGULATIONS
GOVERNING THE TAKING AND
IMPORTING OF MARINE MAMMALS
1. The authority citation for part 216
continues to read as follows:
■
Authority: 16 U.S.C. 1361 et seq.
2. Subpart V is added to part 216 to
read as follows:
■
Subpart V—Taking and Importing
Marine Mammals; U.S. Navy’s Atlantic
Fleet Active Sonar Training (AFAST)
Sec.
216.240 Specified activity and specified
geographical region.
216.241 Effective dates and definitions.
216.242 Permissible methods of taking.
216.243 Prohibitions.
216.244 Mitigation.
216.245 Requirements for monitoring and
reporting.
216.246 Applications for Letters of
Authorization.
216.247 Letters of Authorization.
216.248 Renewal of Letters of Authorization
and Adaptive Management.
216.249 Modifications to Letters of
Authorization.
Subpart V—Taking and Importing
Marine Mammals; U.S. Navy’s Atlantic
Fleet Active Sonar Training (AFAST)
§ 216.240 Specified activity and specified
geographical region.
(a) Regulations in this subpart apply
only to the U.S. Navy for the taking of
marine mammals that occurs in the area
outlined in paragraph (b) of this section
and that occurs incidental to the
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activities described in paragraph (c) of
this section.
(b) The taking of marine mammals by
the Navy is only authorized if it occurs
within the AFAST Study Area, which
extends east from the Atlantic Coast of
the U.S. to 45° W. long. and south from
the Atlantic and Gulf of Mexico Coasts
to approximately 23° N. lat., excluding
the Bahamas (see Figure 1–1 in the
Navy’s Application).
(c) The taking of marine mammals by
the Navy is only authorized if it occurs
incidental to the use of the following
mid-frequency active sonar (MFAS)
sources, high frequency active sonar
(HFAS) sources, or explosive sonobuoys
for U.S. Navy anti-submarine warfare
(ASW), mine warfare (MIW) training,
maintenance, or research, development,
testing, and evaluation (RDT&E) in the
amounts indicated below (+/¥10
percent):
(1) AN/SQS–53 (hull-mounted
sonar)—up to 16070 hours over the
course of 5 years (an average of 3214
hours per year).
(2) AN/SQS–56 (hull-mounted
sonar)—up to 8420 hours over the
course of 5 years (an average of 1684
hours per year).
(3) AN/SQS–56 or 53 (hull mounted
sonar in object detection mode)—up to
1080 hours over the course of 5 years
(an average of 216 hours per year).
(4) AN/BQQ–10 or 5 (submarine
sonar)—up to 49880 pings over the
course of 5 years (an average of 9976
pings per year) (an average of 1 ping per
two hours during training events, 60
pings per hour for maintenance).
(5) AN/AQS–22 or 13 (helicopter
dipping sonar)—up to 14760 dips over
the course of 5 years (an average of 2952
dips per year—10 pings per five-minute
dip).
(6) SSQ–62 (Directional Command
Activated Sonobuoy System (DICASS)
sonobuoys)—up to 29265 sonobuoys
over the course of 5 years (an average of
5853 sonobuoys per year).
(7) MK–48 (heavyweight torpedoes)—
up to 160 torpedoes over the course of
5 years (an average of 32 torpedoes per
year).
(8) MK–46 or 54 (lightweight
torpedoes)—up to 120 torpedoes over
the course of 5 years (an average of 24
torpedoes per year).
(9) AN/SSQ–110A (IEER explosive
sonobuoy) and AN/SSQ–125 (AEER
sonar sonobuoy)—up to 4360
sonobuoys, between these 2 sources,
over the course of 5 years (an average of
872 buoys per year).
(10) AN/SQQ–32 (over the side minehunting sonar)—up to 22370 hours over
the course of 5 years (an average of 4474
hours per year).
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(11) AN/SLQ–25 (NIXIE—towed
countermeasure)—up to 1660 hours
over the course of 5 years (an average of
332 hours per year).
(12) AN/BQS–15 (submarine
navigation)—up to 2250 hours over the
course of 5 years (an average of 450
hours per year).
(13) MK–1 or 2 or 3 or 4 (Submarinefired Acoustic Device Countermeasure
(ADC))—up to 1125 ADCs over the
course of 5 years (an average of 225
ADCs per year).
(14) Noise Acoustic Emitters (NAE—
Sub-fired countermeasure)—up to 635
NAEs over the course of 5 years (an
average of 127 NAEs per year).
§ 216.241
Effective dates and definitions.
(a) Regulations are effective January
22, 2009 through January 22, 2014.
(b) The following definitions are
utilized in these regulations:
(1) Uncommon Stranding Event
(USE)—A stranding event that takes
place during a major training exercise
(MTE) and involves any one of the
following:
(i) Two or more individuals of any
cetacean species (not including mother/
calf pairs), unless of species of concern
listed in § 216.241(b)(1)(ii) found dead
or live on shore within a 2-day period
and occurring within 30 miles of one
another.
(ii) A single individual or mother/calf
pair of any of the following marine
mammals of concern: beaked whale of
any species, dwarf or pygmy sperm
whales, melon-headed whales, pilot
whales, right whales, humpback whales,
sperm whales, blue whales, fin whales,
or sei whales.
(iii) A group of 2 or more cetaceans
of any species exhibiting indicators of
distress as defined in § 216.241(b)(3).
(2) Shutdown—The cessation of
MFAS/HFAS operation or detonation of
explosives within 14 nm nm (Atlantic
Ocean) or 17 nm (Gulf of Mexico) of any
live, in the water, animal involved in a
USE.
§ 216.242
Permissible methods of taking.
(a) Under Letters of Authorization
issued pursuant to §§ 216.106 and
216.247, the Holder of the Letter of
Authorization may incidentally, but not
intentionally, take marine mammals
within the area described in
§ 216.240(b), provided the activity is in
compliance with all terms, conditions,
and requirements of these regulations
and the appropriate Letter of
Authorization.
(b) The activities identified in
§ 216.240(c) must be conducted in a
manner that minimizes, to the greatest
extent practicable, any adverse impacts
on marine mammals and their habitat.
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(c) The incidental take of marine
mammals under the activities identified
in § 216.240(c) is limited to the
following species, by the identified
method of take and the indicated
number of times:
(1) Level B Harassment (+/¥10
percent of the number of takes indicated
below):
(i) Mysticetes:
(A) North Atlantic right whale
(Eubalaena glacialis)—3330 (an average
of 666 annually).
(B) Humpback whale (Megaptera
novaeangliae)—21010 (an average of
4202 annually).
(C) Minke whale (Balaenoptera
acutorostrata)—2075 (an average of 415
annually).
(D) Sei whale (Balaenoptera
borealis)—5285 (an average of 1057
annually).
(E) Fin whale (Balaenoptera
physalus)—4410 (an average of 882
annually).
(F) Bryde’s whale (Balaenoptera
edeni)—180 (an average of 36 annually).
(G) Blue whale (Balaenoptera
musculus)—4005 (an average of 801
annually).
(ii) Odontocetes:
(A) Sperm whales (Physeter
macrocephalus)—48790 (an average of
9758 annually).
(B) Pygmy or dwarf sperm whales
(Kogia breviceps or Kogia sima)—21920
(an average of 4384 annually).
(C) Beaked Whales (Cuvier’s, True’s,
Gervais’, Sowerby’s, Blainville’s,
Northern bottlenose whale) (Ziphius
cavirostris, Mesoplodon mirus, M.
europaeus, M. bidens, M. densirostris,
Hyperoodon ampullatus)—24535 (an
average of 4907 annually).
(D) Rough-toothed dolphin (Steno
bredanensis)—13540 (an average of
2708 annually).
(E) Bottlenose dolphin (Tursiops
truncatus)—3034010 (an average of
606802 annually).
(F) Pan-tropical dolphin (Stenella
attenuata)—696530 (an average of
139306 annually).
(G) Atlantic spotted dolphin (Stenella
frontalis)—1881805 (an average of
376361 annually).
(H) Spinner dolphin (Stenella
longirostris)—105775 (an average of
21155 annually).
(I) Clymene dolphin (Stenella
clymene)—232190 (an average of 46438
annually).
(J) Striped dolphin (Stenella
coeruleoalba)—873620 (an average of
174274 annually).
(K) Common dolphin (Delphinus
spp.)—482300 (an average of 96460
annually).
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(L) Fraser’s dolphin (Lagenodelphis
hosei)—1730 (an average of 346
annually).
(M) Risso’s dolphin (Grampus
griseus)—470375 (an average of 94075
annually).
(N) Atlantic white-sided dolphin
(Lagenorhynchus acutus)—103255 (an
average of 20651 annually).
(O) White-beaked dophin
(Lagenorhynchus albirostris)—17250 (an
average of 3450 annually).
(P) Melon-headed whale
(Peponocephala electra)—8270 (an
average of 1654 annually).
(Q) Pygmy killer whale (Feresa
attenuata)—1400 (an average of 280
annually).
(R) False killer whale (Pseudorca
crassidens)—2690 (an average of 538
annually).
(S) Killer whale (Orcinus orca)—2515
(an average of 503 annually).
(T) Pilot whales (Short-finned pilot or
long-finned) (Globicephala
macrorynchus or G. melas)—636965 (an
average of 127393 annually).
(U) Harbor porpoise (Phocoena
phocoena)—767405 (an average of
153481 annually).
(iii) Pinnipeds:
(A) Gray seal (Halichoerus grypus)—
39295 (an average of 7859 annually).
(B) Harbor seal (Phoca vitulina)—
63295 (an average of 12659 annually).
(C) Hooded seal (Cystophora
cristata)—78590 (an average of 15718
annually).
(D) Harp seal (Pagophilus
groenlandica)—55010 (an average of
11002 annually).
(2) Level A Harassment and/or
mortality of no more than 10 beaked
whales (total), of any of the species
listed in § 216.242(c)(1)(ii)(C) over the
course of the 5-year regulations.
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§ 216.243
Prohibitions.
Notwithstanding takings
contemplated in § 218.92 and
authorized by a Letter of Authorization
issued under §§ 216.106 and 216.247,
no person in connection with the
activities described in § 216.240 may:
(a) Take any marine mammal not
specified in § 216.242(c);
(b) Take any marine mammal
specified in § 216.242(c) other than by
incidental take as specified in
§ 216.242(c)(1) and (2);
(c) Take a marine mammal specified
in § 216.242(c) if such taking results in
more than a negligible impact on the
species or stocks of such marine
mammal; or
(d) Violate, or fail to comply with, the
terms, conditions, and requirements of
these regulations or a Letter of
Authorization issued under §§ 216.106
and 216.247.
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§ 216.244
Mitigation.
(a) When conducting training
activities identified in § 216.240(c), the
mitigation measures contained in the
Letter of Authorization issued under
§§ 216.106 and 216.247 must be
implemented. These mitigation
measures include, but are not limited to:
(1) Mitigation Measures for ASW and
MIW training:
(i) All lookouts onboard platforms
involved in ASW training events shall
review the NMFS-approved Marine
Species Awareness Training (MSAT)
material prior to use of mid-frequency
active sonar.
(ii) All Commanding Officers,
Executive Officers, and officers standing
watch on the Bridge shall review the
MSAT material prior to a training event
employing the use of mid- or highfrequency active sonar.
(iii) Navy lookouts shall undertake
extensive training in order to qualify as
a watchstander in accordance with the
Lookout Training Handbook
(NAVEDTRA, 12968–D).
(iv) Lookout training shall include onthe-job instruction under the
supervision of a qualified, experienced
watchstander. Following successful
completion of this supervised training
period, Lookouts shall complete the
Personal Qualification Standard
program, certifying that they have
demonstrated the necessary skills (such
as detection and reporting of partially
submerged objects).
(v) Lookouts shall be trained in the
most effective means to ensure quick
and effective communication within the
command structure in order to facilitate
implementation of mitigation measures
if marine mammals are spotted.
(vi) On the bridge of surface ships,
there shall always be at least three
people on watch whose duties include
observing the water surface around the
vessel.
(vii) All surface ships participating in
ASW exercises shall, in addition to the
three personnel on watch noted
previously, have at all times during the
exercise at least two additional
personnel on watch as lookouts.
(viii) Personnel on lookout and
officers on watch on the bridge shall
have at least one set of binoculars
available for each person to aid in the
detection of marine mammals.
(ix) On surface vessels equipped with
MFAS, pedestal mounted ‘‘Big Eye’’ (20
× 110) binoculars shall be present and
in good working order.
(x) Personnel on lookout shall employ
visual search procedures employing a
scanning methodology in accordance
with the Lookout Training Handbook
(NAVEDTRA 12968–D). Surface
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lookouts should scan the water from the
ship to the horizon and be responsible
for all contacts in their sector. In
searching the assigned sector, the
lookout should always start at the
forward part of the sector and search aft
(toward the back). To search and scan,
the lookout should hold the binoculars
steady so the horizon is in the top third
of the field of vision and direct the eyes
just below the horizon. The lookout
should scan for approximately five
seconds in as many small steps as
possible across the field seen through
the binoculars. They should search the
entire sector in approximately fivedegree steps, pausing between steps for
approximately five seconds to scan the
field of view. At the end of the sector
search, the glasses should be lowered to
allow the eyes to rest for a few seconds,
and then the lookout should search back
across the sector with the naked eye.
(xi) After sunset and prior to sunrise,
lookouts shall employ Night Lookouts
Techniques in accordance with the
Lookout Training Handbook. At night,
lookouts should not sweep the horizon
with their eyes because this method is
not effective when the vessel is moving.
Lookouts should scan the horizon in a
series of movements that should allow
their eyes to come to periodic rests as
they scan the sector. When visually
searching at night, they should look a
little to one side and out of the corners
of their eyes, paying attention to the
things on the outer edges of their field
of vision.
(xii) Personnel on lookout shall be
responsible for informing the Officer of
the Deck all objects or anomalies sighted
in the water (regardless of the distance
from the vessel) to the Officer of the
Deck, since any object or disturbance
(e.g., trash, periscope, surface
disturbance, discoloration) in the water
may be indicative of a threat to the
vessel and its crew or indicative of a
marine species that may need to be
avoided as warranted.
(xiii) Commanding Officers shall
make use of marine mammal detection
cues and information to limit
interaction with marine mammals to the
maximum extent possible consistent
with safety of the ship.
(xiv) All personnel engaged in passive
acoustic sonar operation (including
aircraft, surface ships, or submarines)
shall monitor for marine mammal
vocalizations and report the detection of
any marine mammal to the appropriate
watch station for dissemination and
appropriate action.
(xv) Units shall use training lookouts
to survey for marine mammals prior to
commencement and during the use of
active sonar.
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(xvi) During operations involving
sonar, personnel shall utilize all
available sensor and optical systems
(such as Night Vision Goggles) to aid in
the detection of marine mammals.
(xvii) Navy aircraft participating in
exercises at sea shall conduct and
maintain, when operationally feasible
and safe, surveillance for marine
mammals as long as it does not violate
safety constraints or interfere with the
accomplishment of primary operational
duties.
(xviii) Aircraft with deployed
sonobuoys shall use only the passive
capability of sonobuoys when marine
mammals are detected within 200 yards
(182 m) of the sonobuoy.
(xix) Marine mammal detections shall
be reported immediately to assigned
Aircraft Control Unit (if participating)
for further dissemination to ships in the
vicinity of the marine mammals. This
action shall occur when it is reasonable
to conclude that the course of the ship
will likely close the distance between
the ship and the detected marine
mammal.
(xx) Safety Zones—When marine
mammals are detected by any means
(aircraft, shipboard lookout, or
acoustically) the Navy shall ensure that
sonar transmission levels are limited to
at least 6 dB below normal operating
levels if any detected marine mammals
are within 1000 yards (914 m) of the
sonar dome (the bow).
(A) Ships and submarines shall
continue to limit maximum
transmission levels by this 6-dB factor
until the marine mammal has been seen
to leave the area, has not been detected
for 30 minutes, or the vessel has
transited more than 2,000 yards (1828
m) beyond the location of the last
detection.
(B) Should a marine mammal be
detected within or closing to inside 457
m (500 yd) of the sonar dome, active
sonar transmissions shall be limited to
at least 10 dB below the equipment’s
normal operating level. Ships and
submarines shall continue to limit
maximum ping levels by this 10-dB
factor until the marine mammal has
been seen to leave the area, has not been
detected for 30 minutes, or the vessel
has transited more than 2000 yards
(1828 m) beyond the location of the last
detection.
(C) Should the marine mammal be
detected within or closing to inside 183
m (200 yd) of the sonar dome, active
sonar transmissions shall cease. Sonar
shall not resume until the marine
mammal has been seen to leave the area,
has not been detected for 30 minutes, or
the vessel has transited more than 2,000
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yards (1828 m) beyond the location of
the last detection.
(D) If the need for power-down should
arise as detailed in ‘‘Safety Zones’’ in
paragraph (a)(1)(xx) of this section,
Navy shall follow the requirements as
though they were operating at 235 dB—
the normal operating level (i.e., the first
power-down shall be to 229 dB,
regardless of at what level above 235
sonar was being operated).
(xxi) Prior to startup or restart of
active sonar, operators shall check that
the Safety Zone radius around the
sound source is clear of marine
mammals.
(xxii) Sonar levels (generally)—The
Navy shall operate sonar at the lowest
practicable level, not to exceed 235 dB,
except as required to meet tactical
training objectives.
(xxiii) Helicopters shall observe/
survey the vicinity of an ASW
Operation for 10 minutes before the first
deployment of active (dipping) sonar in
the water.
(xxiv) Helicopters shall not dip their
sonar within 200 yards (183 m) of a
marine mammal and shall cease pinging
if a marine mammal closes within 200
yards of the helicopter dipping sonar
(183 m) after pinging has begun.
(xxv) Submarine sonar operators shall
review detection indicators of closeaboard marine mammals prior to the
commencement of ASW training
activities involving active sonar.
(xxvi) Night vision devices shall be
available to all ships and air crews, for
use as appropriate.
(xxvii) Dolphin bowriding—If, after
conducting an initial maneuver to avoid
close quarters with dolphins, the ship
concludes that dolphins are deliberately
closing in on the ship to ride the
vessel’s bow wave, no further mitigation
actions would be necessary because
dolphins are out of the main
transmission axis of the active sonar
while in the shallow-wave area of the
vessel bow.
(xxviii) TORPEXs conducted in the
northeast North Atlantic right whale
critical habitat (as designated in 50 CFR
Part 226) shall implement the following
measures.
(A) All torpedo-firing operations shall
take place during daylight hours.
(B) During the conduct of each test,
visual surveys of the test area shall be
conducted by all vessels and aircraft
involved in the exercise to detect the
presence of marine mammals.
Additionally, trained observers shall be
placed on the submarine, spotter
aircraft, and the surface support vessel.
All participants shall report sightings of
any marine mammals, including
negative reports, prior to torpedo firings.
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Reporting requirements shall be
outlined in the test plans and
procedures written for each individual
exercise, and shall be emphasized as
part of pre-exercise briefings conducted
with all participants.
(C) Observers shall receive NMFSapproved training in field identification,
distribution, and relevant behaviors of
marine mammals of the western north
Atlantic. Observers shall fill out
Standard Sighting Forms and the data
shall be housed at the Naval Undersea
Warfare Center Division Newport
(NUWCDIVNPT). Any sightings of
North Atlantic right whales shall be
immediately communicated to the
Sighting Advisory System (SAS). All
platforms shall have onboard a copy of:
(1) The Guide to Marine Mammals
and Turtles of the U.S. Atlantic and Gulf
of Mexico (Wynne and Schwartz 1999);
(2) The NMFS Critical Sightings
Program placard;
(3) Right Whales, Guidelines to
Mariners placard.
(D) In addition to the visual
surveillance discussed above, dedicated
aerial surveys shall be conducted
utilizing a fixed-wing aircraft. An
aircraft with an overhead wing (i.e.,
Cessna Skymaster or similar) shall be
used to facilitate a clear view of the test
area. Two trained observers, in addition
to the pilot, shall be embarked on the
aircraft. Surveys shall be conducted at
an approximate altitude of 1000 ft (305
m) flying parallel track lines at a
separation of 1 nmi (1.85 km), or as
necessary to facilitate good visual
coverage of the sea surface. While
conducting surveillance, the aircraft
shall maintain an approximate speed of
100 knots (185 km/hr). Since factors that
affect visibility are highly dependent on
the specific time of day of the survey,
the flight operator will have the
flexibility to adjust the flight pattern to
reduce glare and improve visibility. The
entire test site shall be surveyed
initially, but once preparations are being
made for an actual test launch, survey
effort shall be concentrated over the
vicinity of the individual test location.
Further, for approximately ten minutes
immediately prior to launch, the aircraft
shall racetrack back and forth between
the launch vessel and the target vessel.
(E) Commencement of an individual
torpedo test scenario shall not occur
until observers from all vessels and
aircraft involved in the exercise have
reported to the Officer in Tactical
Command (OTC) and the OTC has
declared that the range is clear of
marine mammals. Should marine
mammals be present within or seen
moving toward the test area, the test
shall be either delayed or moved as
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required to avoid interference with the
animals.
(F) The TORPEX shall be suspended
if the Beaufort Sea State exceeds 3 or if
visibility precludes safe operations.
(G) Vessel speeds:
(1) During transit through the
northeastern North Atlantic right whale
critical habitat, surface vessels and
submarines shall maintain a speed of no
more than 10 knots (19 km/hr) while not
actively engaged in the exercise
procedures.
(2) During TORPEX operations, a
firing vessel should, where feasible, not
exceed 10 knots. When a submarine is
used as a target, vessel speeds should,
where feasible, not exceed 18 knots.
However, on occasion, when surface
vessels are used as targets, the vessel
may exceed 18 kts in order to fully test
the functionality of the torpedoes. This
increased speed would occur for a short
period of time (e.g., 10–15 minutes) to
evade the torpedo when fired upon.
(H) In the event of an animal strike,
or if an animal is discovered that
appears to be in distress, the Navy shall
immediately report the discovery
through the appropriate Navy chain of
Command.
(xxix) The Navy shall abide by the
following additional measures:
(A) The Navy shall avoid planning
major exercises in the specified
planning awareness areas (PAAs—as
depicted in NMFS’ ‘‘Environmental
Assessment of Mitigation Alternatives
for Issuance of Incidental Take
Regulations to U.S. Navy for Atlantic
Fleet Active Sonar Training (AFAST)’’)
where feasible. Should national security
require the conduct of more than four
major exercises (C2X, JTFEX,
SEASWITI, or similar scale event) in
these areas (meaning all or a portion of
the exercise) per year the Navy shall
provide NMFS with prior notification
and include the information in any
associated after-action or monitoring
reports.
(B) The Navy shall conduct no more
than one of the four above-mentioned
major exercises (COMPTUEX, JTFEX,
SEASWITI or similar scale event) per
year in the Gulf of Mexico to the extent
operationally feasible. If national
security needs require more than one
major exercise to be conducted in the
Gulf of Mexico PAAs, the Navy shall
provide NMFS with prior notification
and include the information in any
associated after-action or monitoring
reports.
(C) The Navy shall include the PAAs
in the Navy’s Protective Measures
Assessment Protocol (PMAP)
(implemented by the Navy for use in the
protection of the marine environment)
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for unit level situational awareness (i.e.,
exercises other than COMPTUEX,
JTFEX, SEASWITI) and planning
purposes.
(D) Helicopter Dipping Sonar—Unless
otherwise dictated by national security
needs, the Navy shall minimize
helicopter dipping sonar activities
within the southeastern areas of North
Atlantic right whale critical habitat (as
designated in 50 CFR part 226) from
November 15–April 15.
(E) Object Detection Exercises—The
Navy shall implement the following
measures regarding object detection
activities in the southeastern areas of
the North Atlantic right whale critical
habitat:
(1) The Navy shall reduce the time
spent conducting object detection
exercises in the NARW critical habitat;
(2) Prior to conducting surface ship
object detection exercises in the
southeastern areas of the North Atlantic
right whale critical habitat during the
time of November 15–April 15, ships
shall contact FACSFACJAX to obtain
the latest North Atlantic right whale
sighting information. FACSFACJAX
shall advise ships of all reported whale
sightings in the vicinity of the critical
habitat and associated areas of concern
(which extend 9 km (5 NM) seaward of
the designated critical habitat
boundaries). To the extent operationally
feasible, ships shall avoid conducting
training in the vicinity of recently
sighted North Atlantic right whales.
Ships shall maneuver to maintain at
least 500 yards separation from any
observed whale, consistent with the
safety of the ship.
(xxx) The Navy shall abide by the
letter of the ‘‘Stranding Response Plan
for Major Navy Training Exercises in the
AFAST Study Area’’ (available at:
https://www.nmfs.noaa.gov/pr/permits/
incidental.htm), to include the
following measures:
(A) Shutdown Procedures—When an
Uncommon Stranding Event (USE—
defined in § 216.241) occurs during a
Major Training Exercise (MTE,
including SEASWITI, IAC, Group Sails,
JTFEX, or COMPTUEX) in the AFAST
Study Area, the Navy shall implement
the procedures described below.
(1) The Navy shall implement a
Shutdown (as defined § 216.241) when
advised by a NMFS Office of Protected
Resources Headquarters Senior Official
designated in the AFAST Stranding
Communication Protocol that a USE
involving live animals has been
identified and that at least one live
animal is located in the water. NMFS
and Navy shall communicate, as
needed, regarding the identification of
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the USE and the potential need to
implement shutdown procedures.
(2) Any shutdown in a given area
shall remain in effect in that area until
NMFS advises the Navy that the
subject(s) of the USE at that area die or
are euthanized, or that all live animals
involved in the USE at that area have
left the area (either of their own volition
or herded).
(3) If the Navy finds an injured or
dead animal of any species other than
North Atlantic right whale floating at
sea during an MTE, the Navy shall
notify NMFS immediately or as soon as
operational security considerations
allow. The Navy shall provide NMFS
with species or description of the
animal(s), the condition of the animal(s)
including carcass condition (if the
animal(s) is/are dead), location, time of
first discovery, observed behaviors (if
alive), and photo or video (if available).
Based on the information provided,
NMFS shall determine if, and advise the
Navy whether a modified shutdown is
appropriate on a case-by-case basis.
(4) If the Navy finds an injured (or
entangled) North Atlantic right whale
floating at sea during an MTE, the Navy
shall implement shutdown procedures
(14 or 17 nm, as defined below) around
the animal immediately (without
waiting for notification from NMFS).
The Navy shall then notify NMFS
(pursuant to the AFAST
Communication Protocol) immediately
or as soon as operational security
considerations allow. The Navy shall
provide NMFS with species or
description of the animal(s), the
condition of the animal(s) including
carcass condition (if the animal(s) is/are
dead), location, time of first discovery,
observed behaviors (if alive), and photo
or video (if available). Subsequent to the
discovery of the injured whale, any
Navy platforms in the area shall report
any North Atlantic right whale sightings
to NMFS (or to a contact that can alert
NMFS as soon as possible). Based on the
information provided, NMFS may
initiate/organize an aerial survey (by
requesting the Navy’s assistance
pursuant to the memorandum of
agreement (MOA) (see (a)(1)(xxx)(C) of
this section) or by other available
means) to see if other North Atlantic
right whales are in the vicinity. Based
on the information provided by the
Navy and, if necessary, the outcome of
the aerial surveys, NMFS shall
determine whether a continued
shutdown is appropriate on a case-bycase basis. Though it will be determined
on a case-by-case basis after Navy/
NMFS discussion of the situation,
NMFS anticipates that the shutdown
will continue within 14 or 17 nm of a
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live, injured/entangled North Atlantic
right whale until the animal dies or has
not been seen for at least 3 hours (either
by NMFS staff attending the injured
animal or Navy personnel monitoring
the area around where the animal was
last sighted).
(5) If the Navy finds a dead North
Atlantic right whale floating at sea
during an MTE, the Navy shall notify
NMFS (pursuant to AFAST Stranding
Communication Protocol) immediately
or as soon as operational security
considerations allow. The Navy shall
provide NMFS with species or
description of the animal(s), the
condition of the animal(s) (including
carcass condition if the animal(s) is/are
dead), location, time of first discovery,
observed behaviors (if alive), and photo
or video (if available). Subsequent to the
discovery of the dead whale, if the Navy
is operating sonar in the area they shall
use increased vigilance (in looking for
North Atlantic right whales) and all
platforms in the area shall report
sightings of North Atlantic right whales
to NMFS as soon as possible. Based on
the information provided, NMFS may
initiate/organize an aerial survey (by
requesting the Navy’s assistance
pursuant to the MOA (see (a)(1)(xxx)(C)
of this section) or by other available
means) to see if other North Atlantic
right whales are in the vicinity. Based
on the information provided by the
Navy and, if necessary, the outcome of
the aerial surveys, NMFS will determine
whether any additional mitigation
measures are necessary on a case-bycase basis.
(6) In the event, following a USE, that:
(a) Qualified individuals are attempting
to herd animals back out to the open
ocean and animals are not willing to
leave, or (b) animals are seen repeatedly
heading for the open ocean but turning
back to shore, NMFS and the Navy
should coordinate (including an
investigation of other potential
anthropogenic stressors in the area) to
determine if the proximity of MFAS/
HFAS training activities or explosive
detonations, though farther than 14 or
17 nm from the distressed animal(s), is
likely decreasing the likelihood that the
animals return to the open water. If so,
NMFS and the Navy shall further
coordinate to determine what measures
are necessary to further minimize that
likelihood and implement those
measures as appropriate.
(B) Within 72 hours of NMFS
notifying the Navy of the presence of a
USE, the Navy shall provide available
information to NMFS (per the AFAST
Communication Protocol) regarding the
location, number and types of acoustic/
explosive sources, direction and speed
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Jkt 217001
of units using MFAS/HFAS, and marine
mammal sightings information
associated with training activities
occurring within 80 nm (148 km) and 72
hours prior to the USE event.
Information not initially available
regarding the 80 nm (148 km), 72 hours,
period prior to the event shall be
provided as soon as it becomes
available. The Navy shall provide NMFS
investigative teams with additional
relevant unclassified information as
requested, if available.
(C) Memorandum of Agreement
(MOA)—The Navy and NMFS shall
develop a MOA, or other mechanism
consistent with Federal fiscal law
requirements (and all other applicable
laws), that will establish a framework
whereby the Navy can (and provide the
Navy examples of how they can best)
assist NMFS with stranding
investigations in certain circumstances.
This document shall be finalized in
2009 (unless NMFS notifies the Navy
that a delay is needed).
(2) Mitigation for IEER/AEER—The
following are mitigation measures for
use with Extended Echo Ranging/
Improved Extended Echo Ranging (EER/
IEER) and Advanced Extended Echo
Ranging given an explosive source
generates the acoustic wave used in this
sonobuoy.
(i) Navy crews shall conduct visual
reconnaissance of the drop area prior to
laying their intended sonobuoy pattern.
This search should be conducted below
500 yards (457 m) at a slow speed, if
operationally feasible and weather
conditions permit. In dual aircraft
training activities, crews are allowed to
conduct coordinated area clearances.
(ii) For IEER (AN/SSQ–110A), Navy
crews shall conduct a minimum of 30
minutes of visual and acoustic
monitoring of the search area prior to
commanding the first post (source/
receiver sonobuoy pair) detonation. This
30-minute observation period may
include pattern deployment time.
(iii) For any part of the briefed pattern
where a post (source/receiver sonobuoy
pair) will be deployed within 1,000
yards (914 m) of observed marine
mammal activity, deploy the receiver
ONLY and monitor while conducting a
visual search. When marine mammals
are no longer detected within 1,000
yards (914 m) of the intended post
position, co-locate the explosive source
sonobuoy (AN/SSQ–110A) (source) with
the receiver.
(iv) When operationally feasible, Navy
crews shall conduct continuous visual
and aural monitoring of marine mammal
activity. This is to include monitoring of
own-aircraft sensors from first sensor
placement to checking off station and
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4881
out of communication range of these
sensors.
(v) Aural Detection: If the presence of
marine mammals is detected aurally,
then that should cue the aircrew to
increase the diligence of their visual
surveillance. Subsequently, if no marine
mammals are visually detected, then the
Navy crew may continue multi-static
active search.
(vi) Visual Detection:
(A) If marine mammals are visually
detected within 1,000 yards (914 m) of
the explosive source sonobuoy (AN/
SSQ–110A) intended for use, then that
payload shall not be detonated.
(B) Navy Aircrews may utilize this
post once the marine mammals have not
been re-sighted for 30 minutes, or are
observed to have moved outside the
1,000 yards (914 m) safety buffer.
(C) Navy Aircrews may shift their
multi-static active search to another
post, where marine mammals are
outside the 1,000 yards (914 m) safety
buffer.
(vii) For IEER (AN/SSQ–110A), Navy
Aircrews shall make every attempt to
manually detonate the unexploded
charges at each post in the pattern prior
to departing the operations area by
using the ‘‘Payload 1 Release’’ command
followed by the ‘‘Payload 2 Release’’
command. Aircrews shall refrain from
using the ‘‘Scuttle’’ command when two
payloads remain at a given post.
Aircrews shall ensure that a 1,000 yard
(914 m) safety buffer, visually clear of
marine mammals, is maintained around
each post as is done during active
search operations.
(viii) Navy Aircrews shall only leave
posts with unexploded charges in the
event of a sonobuoy malfunction, an
aircraft system malfunction, or when an
aircraft must immediately depart the
area due to issues such as fuel
constraints, inclement weather, and inflight emergencies. In these cases, the
sonobuoy will self-scuttle using the
secondary or tertiary method.
(ix) The Navy shall ensure all
payloads are accounted for. Explosive
source sonobuoys (AN/SSQ–110A) that
cannot be scuttled shall be reported as
unexploded ordnance via voice
communications while airborne, then
upon landing via naval message.
(x) Marine mammal monitoring shall
continue until out of own-aircraft sensor
range.
(3) Mitigation Measures Related to
Vessel Transit and North Atlantic Right
Whales:
(i) Mid-Atlantic, Offshore of the
Eastern United States:
(A) All Navy vessels are required to
use extreme caution and operate at a
slow, safe speed consistent with mission
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and safety during the months indicated
below and within a 37 km (20 nm) arc
(except as noted) of the specified
associated reference points:
(1) South and East of Block Island (37
km (20 NM) seaward of line between
41–4.49° N. lat. 071–51.15° W. long. and
41–18.58° N. lat. 070–50.23° W. long):
Sept–Oct and Mar–Apr.
(2) New York/New Jersey (40–30.64°
N. lat. 073–57.76° W. long.): Sep–Oct
and Feb–Apr.
(3) Delaware Bay (Philadelphia) (38–
52.13° N. lat. 075–1.93° W. long.): Oct–
Dec and Feb–Mar.
(4) Chesapeake Bay (Hampton Roads
and Baltimore) (37–1.11° N. lat. 075–
57.56° W. long.): Nov–Dec and Feb–Apr.
(5) North Carolina (34–41.54° N. lat.
076–40.20° W. long.): Dec–Apr.
(6) South Carolina (33–11.84° N. lat.
079–8.99° W. long. and 32–43.39° N. lat.
079–48.72° W. long.): Oct–Apr.
(B) During the months indicated in
paragraph (a)(3)(i)(A) of this section,
Navy vessels shall practice increased
vigilance with respect to avoidance of
vessel-whale interactions along the midAtlantic coast, including transits to and
from any mid-Atlantic ports not
specifically identified in paragraph
(a)(3)(i)(A) of this section.
(C) All surface units transiting within
56 km (30 NM) of the coast in the midAtlantic shall ensure at least two
watchstanders are posted, including at
least one lookout who has completed
required MSAT training.
(D) Navy vessels shall not knowingly
approach any whale head on and shall
maneuver to keep at least 457 m (1,500
ft) away from any observed whale,
consistent with vessel safety.
(ii) Southeast Atlantic, Offshore of the
Eastern United States—for the purposes
of the measures below (within this
paragraph), the ‘‘southeast’’
encompasses sea space from Charleston,
South Carolina, southward to Sebastian
Inlet, Florida, and from the coast
seaward to 148 km (80 NM) from shore.
North Atlantic right whale critical
habitat is the area from 31–15° N. lat. to
30–15° N. lat. extending from the coast
out to 28 km (15 NM), and the area from
28–00° N. lat. to 30–15° N. lat. from the
coast out to 9 km (5 NM). All mitigation
measures described here that apply to
the critical habitat apply from
November 15–April 15 and also apply to
an associated area of concern which
extends 9 km (5 NM) seaward of the
designated critical habitat boundaries.
(A) Prior to transiting or training in
the critical habitat or associated area of
concern, ships shall contact Fleet Area
Control and Surveillance Facility,
Jacksonville, to obtain latest whale
sighting and other information needed
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18:27 Jan 26, 2009
Jkt 217001
to make informed decisions regarding
safe speed and path of intended
movement. Subs shall contact
Commander, Submarine Group Ten for
similar information.
(B) The following specific mitigation
measures apply to activities occurring
within the critical habitat and an
associated area of concern which
extends 9 km (5 NM) seaward of the
designated critical habitat boundaries:
(1) When transiting within the critical
habitat or associated area of concern,
vessels shall exercise extreme caution
and proceed at a slow safe speed. The
speed shall be the slowest safe speed
that is consistent with mission, training
and operations.
(2) Speed reductions (adjustments) are
required when a whale is sighted by a
vessel or when the vessel is within 9 km
(5 NM) of a reported new sighting less
then 12 hours old. Circumstances could
arise where, in order to avoid North
Atlantic right whale(s), speed
reductions could mean vessel must
reduce speed to a minimum at which it
can safely keep on course or vessels
could come to an all stop.
(3) Vessels shall avoid head-on
approaches to North Atlantic right
whale(s) and shall maneuver to
maintain at least 457 m (500 yd) of
separation from any observed whale if
deemed safe to do so. These
requirements do not apply if a vessel’s
safety is threatened, such as when a
change of course would create an
imminent and serious threat to a person,
vessel, or aircraft, and to the extent
vessels are restricted in the ability to
maneuver.
(4) Ships shall not transit through the
critical habitat or associated area of
concern in a North-South direction.
(5) Ships, surfaced subs, and aircraft
shall report any whale sightings to Fleet
Area Control and Surveillance Facility,
Jacksonville, by the quickest and most
practicable means. The sighting report
shall include the time, latitude/
longitude, direction of movement and
number and description of whale (i.e.,
adult/calf).
(iii) Northeast Atlantic, Offshore of
the Eastern United States:
(A) Prior to transiting the Great South
Channel or Cape Cod Bay critical habitat
areas, ships shall obtain the latest North
Atlantic right whale sightings and other
information needed to make informed
decisions regarding safe speed. The
Great South Channel critical habitat is
defined by the following coordinates:
41–00° N. lat., 69–05° W. long.; 41–45°
N. lat, 69–45° W. long; 42–10° N. lat.,
68–31° W. long.; 41–38° N. lat., 68–13°
W. long. The Cape Cod Bay critical
habitat is defined by the following
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coordinates: 42–04.8° N. lat., 70–10° W.
long.; 42–12° N. lat., 70–15° W. long.;
42–12° N. lat., 70–30° W. long.; 41–46.8°
N. lat., 70–30° W. long.
(B) Ships, surfaced subs, and aircraft
shall report any North Atlantic right
whale sightings (if the whale is
identifiable as a right whale) off the
northeastern U.S. to Patrol and
Reconnaissance Wing
(COMPATRECONWING). The report
shall include the time of sighting, lat/
long, direction of movement (if
apparent) and number and description
of the whale(s).
(C) Vessels or aircraft that observe
whale carcasses shall record the
location and time of the sighting and
report this information as soon as
possible to the cognizant regional
environmental coordinator. All whale
strikes must be reported. This report
shall include the date, time, and
location of the strike; vessel course and
speed; operations being conducted by
the vessel; weather conditions,
visibility, and sea state; description of
the whale; narrative of incident; and
indication of whether photos/videos
were taken. Navy personnel are
encouraged to take photos whenever
possible.
(D) Specific mitigation measures
related to activities occurring within the
critical habitat include the following:
(1) Vessels shall avoid head-on
approaches to North Atlantic right
whale(s) and shall maneuver to
maintain at least 457 m (500 yd) of
separation from any observed whale if
deemed safe to do so. These
requirements do not apply if a vessel’s
safety is threatened, such as when
change of course would create an
imminent and serious threat to person,
vessel, or aircraft, and to the extent
vessels are restricted in the ability to
maneuver.
(2) When transiting within the critical
habitat or associated area of concern,
vessels shall use extreme caution and
operate at a safe speed so as to be able
to avoid collisions with North Atlantic
right whales and other marine
mammals, and stop within a distance
appropriate to the circumstances and
conditions.
(3) Speed reductions (adjustments) are
required when a whale is sighted by a
vessel or when the vessel is within 9 km
(5 NM) of a reported new sighting less
than one week old.
(4) Ships transiting in the Cape Cod
Bay and Great South Channel critical
habitats shall obtain information on
recent whale sightings in the vicinity of
the critical habitat. Any vessel operating
in the vicinity of a North Atlantic right
whale shall consider additional speed
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§ 216.245 Requirements for monitoring
and reporting.
(a) As outlined in the AFAST
Stranding Communication Plan, the
Navy must notify NMFS immediately
(or as soon as clearance procedures
allow) if the specified activity identified
in § 216.240(c) is thought to have
resulted in the mortality or injury of any
marine mammals, or in any take of
marine mammals not identified in
§ 216.242(c).
(b) The Navy must conduct all
monitoring and required reporting
under the Letter of Authorization,
including abiding by the AFAST
Monitoring Plan, which is incorporated
herein by reference.
(c) The Navy shall complete an
Integrated Comprehensive Monitoring
Program (ICMP) Plan in 2009. This
planning and adaptive management tool
shall include:
(1) A method for prioritizing
monitoring projects that clearly
describes the characteristics of a
proposal that factor into its priority.
(2) A method for annually reviewing,
with NMFS, monitoring results, Navy
R&D, and current science to use for
potential modification of mitigation or
monitoring methods.
(3) A detailed description of the
Monitoring Workshop to be convened in
2011 and how and when Navy/NMFS
will subsequently utilize the findings of
the Monitoring Workshop to potentially
modify subsequent monitoring and
mitigation.
(4) An adaptive management plan.
(5) A method for standardizing data
collection for AFAST and across Range
Complexes
(d) General Notification of Injured or
Dead Marine Mammals—Navy
personnel shall ensure that NMFS
(regional stranding coordinator) is
notified immediately (or as soon as
clearance procedures allow) if an
injured or dead marine mammal is
found during or shortly after, and in the
vicinity of, any Navy training exercise
utilizing MFAS, HFAS, or underwater
explosive detonations. The Navy shall
provide NMFS with species or
description of the animal(s), the
condition of the animal(s) (including
carcass condition if the animal is dead),
location, time of first discovery,
observed behaviors (if alive), and photo
or video (if available). The Navy shall
consult the Stranding Response Plan to
obtain more specific reporting
requirements for specific circumstances.
(e) Annual AFAST Monitoring Plan
Report—The Navy shall submit a report
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annually on October 1 describing the
implementation and results (through
August 1 of the same year) of the
AFAST Monitoring Plan. Data collection
methods will be standardized across
range complexes to allow for
comparison in different geographic
locations. Although additional
information will also be gathered, the
marine mammal observers (MMOs)
collecting marine mammal data
pursuant to the AFAST Monitoring Plan
shall, at a minimum, provide the same
marine mammal observation data
required in the data required in
§ 216.245(f)(1). The AFAST Monitoring
Plan Report may be provided to NMFS
within a larger report that includes the
required Monitoring Plan Reports from
AFAST and multiple Range Complexes.
(f) Annual AFAST Exercise Report—
The Navy shall submit an Annual
AFAST Exercise Report on October 1 of
every year (covering data gathered
through August 1 of the same year). This
report shall contain information
identified in subsections § 216.245(f)(1)
through (f)(5).
(1) MFAS/HFAS Major Training
Exercises—This section shall contain
the following information for the major
training exercises for reporting (MTERs),
which include the Southeastern ASW
Integrated Training Initiative
(SEASWITI), Integrated ASW Course
(IAC), Composite Training Unit
Exercises (COMPTUEX), and Joint Task
Force Exercises (JTFEX) conducted in
the AFAST Study Area:
(i) Exercise Information (for each
MTER):
(A) Exercise designator;
(B) Date that exercise began and
ended;
(C) Location;
(D) Number and types of active
sources used in the exercise;
(E) Number and types of passive
acoustic sources used in exercise;
(F) Number and types of vessels,
aircraft, etc., participating in exercise;
(G) Total hours of observation by
watchstanders;
(H) Total hours of all active sonar
source operation;
(I) Total hours of each active sonar
source (along with explanation of how
hours are calculated for sources
typically quantified in alternate way
(buoys, torpedoes, etc.));
(J) Wave height (high, low, and
average during exercise).
(ii) Individual marine mammal
sighting info (for each sighting in each
MTER):
(A) Location of sighting;
(B) Species (if not possible—
indication of whale/dolphin/pinniped);
(C) Number of individuals;
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4883
(D) Calves observed (y/n);
(E) Initial Detection Sensor;
(F) Indication of specific type of
platform observation made from
(including, for example, what type of
surface vessel, i.e., FFG, DDG, or CG);
(G) Length of time observers
maintained visual contact with marine
mammal;
(H) Wave height (in feet);
(I) Visibility;
(J) Sonar source in use (y/n);
(K) Indication of whether animal is <
200 yd, 200–500 yd, 500–1000 yd,
1000–2000 yd, or > 2000 yd from sonar
source in paragraph (f)(1)(ii)(J) of this
section;
(L) Mitigation Implementation—
Whether operation of sonar sensor was
delayed, or sonar was powered or shut
down, and how long the delay was;
(M) If source in use (i.e., in paragraph
(f)(1)(ii)(J) of this section) is
hullmounted, true bearing of animal
from ship, true direction of ship’s travel,
and estimation of animal’s motion
relative to ship (opening, closing,
parallel);
(N) Observed behavior—
Watchstanders shall report, in plain
language and without trying to
categorize in any way, the observed
behavior of the animals (such as animal
closing to bow ride, paralleling course/
speed, floating on surface and not
swimming, etc.).
(iii) An evaluation (based on data
gathered during all of the MTERs) of the
effectiveness of mitigation measures
designed to avoid exposing marine
mammals to MFAS. This evaluation
shall identify the specific observations
that support any conclusions the Navy
reaches about the effectiveness of the
mitigation.
(2) ASW Summary—This section
shall include the following information
as summarized from both MTERs and
non-major training exercises:
(i) Total annual hours of each type of
sonar source (along with explanation of
how hours are calculated for sources
typically quantified in alternate way
(buoys, torpedoes, etc.)).
(ii) Cumulative Impact Report—To the
extent practicable, the Navy, in
coordination with NMFS, shall develop
and implement a method of annually
reporting non-major (i.e., other than
MTERs) training exercises utilizing hullmounted sonar. The report shall present
an annual (and seasonal, where
practicable) depiction of non-major
training exercises geographically across
the AFAST Study Area. To the extent
practicable, this report will also include
the total number of sonar hours (from
helicopter dipping sonar and object
detection exercises) conducted within
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the southern NARW critical habitat plus
5 nm buffer area. The Navy shall
include (in the AFAST annual report) a
brief annual progress update on the
status of the development of an effective
and unclassified method to report this
information until an agreed-upon (with
NMFS) method has been developed and
implemented.
(3) IEER/AEER Summary—This
section shall include an annual
summary of the following IEER and
AEER information:
(i) Total number of IEER and AEER
events conducted in the AFAST Study
Area;
(ii) Total expended/detonated rounds
(buoys);
(iii) Total number of self-scuttled
IEER rounds.
(g) Sonar Exercise Notification—The
Navy shall submit to the NMFS Office
of Protected Resources (specific contact
information to be provided in LOA)
either an electronic (preferably) or
verbal report within fifteen calendar
days after the completion of any MTER
indicating:
(1) Location of the exercise;
(2) Beginning and end dates of the
exercise;
(3) Type of exercise (e.g., COMPTUEX
or SEASWITI).
(h) AFAST 5-yr Comprehensive
Report—The Navy shall submit to
NMFS a draft report that analyzes and
summarizes all of the multi-year marine
mammal information gathered during
ASW, MIW and IEER/AEER exercises
for which annual reports are required
(Annual AFAST Exercise Reports and
AFAST Monitoring Plan Reports). This
report will be submitted at the end of
the fourth year of the rule (November
2012), covering activities that have
occurred through June 1, 2012.
(i) Comprehensive National ASW
Report—By June, 2014, the Navy shall
submit a draft National Report that
analyzes, compares, and summarizes the
active sonar data gathered (through
January 1, 2014) from the watchstanders
and pursuant to the implementation of
the Monitoring Plans for AFAST,
SOCAL, the HRC, the Marianas Range
Complex, the Northwest Training
Range, the Gulf of Alaska, and the East
Coast Undersea Warfare Training Range.
(j) The Navy shall respond to NMFS
comments and requests for additional
information or clarification on the
AFAST Comprehensive Report, the
Comprehensive National ASW report,
the Annual AFAST Exercise Report, or
the Annual AFAST Monitoring Plan
Report (or the multi-Range Complex
Annual Monitoring Plan Report, if that
is how the Navy chooses to submit the
information) if submitted within 3
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18:27 Jan 26, 2009
Jkt 217001
months of receipt. These reports will be
considered final after the Navy has
addressed NMFS’ comments or
provided the requested information, or
three months after the submittal of the
draft if NMFS does not comment by
then.
(k) In 2011, the Navy shall convene a
Monitoring Workshop in which the
Monitoring Workshop participants will
be asked to review the Navy’s
Monitoring Plans and monitoring results
and make individual recommendations
(to the Navy and NMFS) of ways of
improving the Monitoring Plans. The
recommendations shall be reviewed by
the Navy, in consultation with NMFS,
and modifications to the Monitoring
Plan shall be made, as appropriate.
§ 216.246 Applications for Letters of
Authorization.
To incidentally take marine mammals
pursuant to the regulations in this
subpart, the U.S. citizen (as defined by
§ 216.103) conducting the activity
identified in § 216.240(c) (the U.S.
Navy) must apply for and obtain either
an initial Letter of Authorization in
accordance with § 216.247 or a renewal
under § 216.248.
§ 216.247
Letters of Authorization.
(a) A Letter of Authorization, unless
suspended or revoked, will be valid for
a period of time not to exceed the period
of validity of this subpart, but must be
renewed annually subject to annual
renewal conditions in § 216.248.
(b) Each Letter of Authorization will
set forth:
(1) Permissible methods of incidental
taking;
(2) Means of effecting the least
practicable adverse impact on the
species, its habitat, and on the
availability of the species for
subsistence uses (i.e., mitigation); and
(3) Requirements for mitigation,
monitoring and reporting.
(c) Issuance and renewal of the Letter
of Authorization will be based on a
determination that the total number of
marine mammals taken by the activity
as a whole will have no more than a
negligible impact on the affected species
or stock of marine mammal(s).
§ 216.248 Renewal of Letters of
Authorization and Adaptive Management.
(a) A Letter of Authorization issued
under §§ 216.106 and 216.247 for the
activity identified in § 216.240(c) will be
renewed annually upon:
(1) Notification to NMFS that the
activity described in the application
submitted under § 216.246 will be
undertaken and that there will not be a
substantial modification to the
PO 00000
Frm 00042
Fmt 4701
Sfmt 4700
described work, mitigation or
monitoring undertaken during the
upcoming 12 months;
(2) Timely receipt (by the dates
indicated in these regulations) of the
monitoring reports required under
§ 216.245(c) through (j); and
(3) A determination by the NMFS that
the mitigation, monitoring and reporting
measures required under § 216.244 and
the Letter of Authorization issued under
§§ 216.106 and 216.247, were
undertaken and will be undertaken
during the upcoming annual period of
validity of a renewed Letter of
Authorization.
(b) If a request for a renewal of a
Letter of Authorization issued under
§§ 216.106 and 216.248 indicates that a
substantial modification, as determined
by NMFS, to the described work,
mitigation or monitoring undertaken
during the upcoming season will occur,
the NMFS will provide the public a
period of 30 days for review and
comment on the request. Review and
comment on renewals of Letters of
Authorization are restricted to:
(1) New cited information and data
indicating that the determinations made
in this document are in need of
reconsideration, and
(2) Proposed changes to the mitigation
and monitoring requirements contained
in these regulations or in the current
Letter of Authorization.
(c) A notice of issuance or denial of
a renewal of a Letter of Authorization
will be published in the Federal
Register.
(d) NMFS, in response to new
information and in consultation with
the Navy, may modify the mitigation or
monitoring measures in subsequent
LOAs if doing so creates a reasonable
likelihood of more effectively
accomplishing the goals of mitigation
and monitoring set forth in the preamble
of these regulations. Below are some of
the possible sources of new data that
could contribute to the decision to
modify the mitigation or monitoring
measures:
(1) Results from the Navy’s
monitoring from the previous year
(either from AFAST or other locations).
(2) Findings of the Monitoring
Workshop that the Navy will convene in
2011 (section 216.245(l)).
(3) Compiled results of Navy funded
research and development (R&D) studies
(presented pursuant to the ICMP
(§ 216.245(d))).
(4) Results from specific stranding
investigations (either from the AFAST
Study Area or other locations, and
involving coincident MFAS/HFAS or
explosives training or not involving
coincident use).
E:\FR\FM\27JAR3.SGM
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Federal Register / Vol. 74, No. 16 / Tuesday, January 27, 2009 / Rules and Regulations
(5) Results from the Long Term
Prospective Study described in the
preamble to these regulations.
(6) Results from general marine
mammal and sound research (funded by
the Navy (described below) or
otherwise).
§ 216.249 Modifications to Letters of
Authorization.
mstockstill on PROD1PC66 with RULES3
(a) Except as provided in paragraph
(b) of this section, no substantive
modification (including withdrawal or
suspension) to the Letter of
VerDate Nov<24>2008
18:27 Jan 26, 2009
Jkt 217001
Authorization by NMFS, issued
pursuant to §§ 216.106 and 216.247 and
subject to the provisions of this subpart
shall be made until after notification
and an opportunity for public comment
has been provided. For purposes of this
paragraph, a renewal of a Letter of
Authorization under § 216.248, without
modification (except for the period of
validity), is not considered a substantive
modification.
(b) If the Assistant Administrator
determines that an emergency exists
PO 00000
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Fmt 4701
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4885
that poses a significant risk to the wellbeing of the species or stocks of marine
mammals specified in § 216.242(c), a
Letter of Authorization issued pursuant
to §§ 216.106 and 216.247 may be
substantively modified without prior
notification and an opportunity for
public comment. Notification will be
published in the Federal Register
within 30 days subsequent to the action.
[FR Doc. E9–1706 Filed 1–22–09; 4:15 pm]
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Agencies
[Federal Register Volume 74, Number 16 (Tuesday, January 27, 2009)]
[Rules and Regulations]
[Pages 4844-4885]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-1706]
[[Page 4843]]
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Part III
Department of Commerce
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National Oceanic and Atmospheric Administration
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50 CFR Part 216
Taking and Importing Marine Mammals; U.S. Navy's Atlantic Fleet Active
Sonar Training (AFAST); Final Rule
Federal Register / Vol. 74, No. 16 / Tuesday, January 27, 2009 /
Rules and Regulations
[[Page 4844]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 216
[Docket No. 080724897-81621-02]
RIN 0648-AW90
Taking and Importing Marine Mammals; U.S. Navy's Atlantic Fleet
Active Sonar Training (AFAST)
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS, upon application from the U.S. Navy (Navy), is issuing
regulations to govern the unintentional taking of marine mammals
incidental to activities conducted off the U.S. Atlantic Coast and in
the Gulf of Mexico for the period of January 2009 through January 2014.
The Navy's activities are considered military readiness activities
pursuant to the Marine Mammal Protection Act (MMPA), as amended by the
National Defense Authorization Act for Fiscal Year 2004 (NDAA). These
regulations, which allow for the issuance of ``Letters of
Authorization'' (LOAs) for the incidental take of marine mammals during
the described activities and specified timeframes, prescribe the
permissible methods of taking and other means of affecting the least
practicable adverse impact on marine mammal species and their habitat,
as well as requirements pertaining to the monitoring and reporting of
such taking.
DATES: Effective January 22, 2009 through January 22, 2014.
ADDRESSES: A copy of the Navy's application (which contains a list of
the references used in this document), NMFS' Record of Decision (ROD),
and other documents cited herein may be obtained by writing to Michael
Payne, Chief, Permits, Conservation and Education Division, Office of
Protected Resources, National Marine Fisheries Service, 1315 East-West
Highway, Silver Spring, MD 20910-3225 or by telephone via the contact
listed here (see FOR FURTHER INFORMATION CONTACT).
FOR FURTHER INFORMATION CONTACT: Jolie Harrison, Office of Protected
Resources, NMFS, (301) 713-2289, ext. 166.
SUPPLEMENTARY INFORMATION: Extensive Supplementary Information was
provided in the proposed rule for this activity, which was published in
the Federal Register on Tuesday, October 14, 2008 (73 FR 60754). This
information will not be reprinted here in its entirety; rather, all
sections from the proposed rule will be represented herein and will
contain either a summary of the material presented in the proposed rule
or a note referencing the page(s) in the proposed rule where the
information may be found. Any information that has changed since the
proposed rule was published will be addressed herein. Additionally,
this final rule contains a section that responds to the comments
received during the public comment period.
Background
Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.)
direct the Secretary of Commerce (Secretary) to allow, upon request,
the incidental, but not intentional taking of marine mammals by U.S.
citizens who engage in a specified activity (other than commercial
fishing) during periods of not more than five consecutive years each if
certain findings are made and regulations are issued or, if the taking
is limited to harassment and of no more than 1 year, the Secretary
shall issue a notice of proposed authorization for public review.
Authorization 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, and if the permissible methods of taking
and requirements pertaining to the mitigation, monitoring and reporting
of such taking 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.
The NDAA (Pub. L. 108-136) removed the ``small numbers'' and
``specified geographical region'' limitations and amended the
definition of ``harassment'' as it applies to a ``military readiness
activity'' to read as follows (Section 3(18)(B) of the MMPA):
(i) Any act that injures or has the significant potential to
injure a marine mammal or marine mammal stock in the wild [Level A
Harassment]; or
(ii) Any act that disturbs or is likely to disturb a marine
mammal or marine mammal stock in the wild by causing disruption of
natural behavioral patterns, including, but not limited to,
migration, surfacing, nursing, breeding, feeding, or sheltering, to
a point where such behavioral patterns are abandoned or
significantly altered [Level B Harassment].
Summary of Request
On February 4, 2008, NMFS received an application from the Navy
requesting authorization for the take of individuals of 40 species of
marine mammals incidental to upcoming Navy training activities,
maintenance, and research, development, testing, and evaluation (RDT&E)
activities to be conducted within the Atlantic Fleet Active Sonar
Training (AFAST) Study Area, which extends east from the Atlantic Coast
of the U.S. to 45[deg] W. long. and south from the Atlantic and Gulf of
Mexico Coasts to approximately 23[deg] N. lat., but not encompassing
the Bahamas (see Figure 1-1 in the Navy's Application), over the course
of 5 years. These activities are military readiness activities under
the provisions of the NDAA. The Navy states, and NMFS concurs, that
these military readiness activities may incidentally take marine
mammals present within the AFAST Study Area by exposing them to sound
from mid-frequency or high frequency active sonar (MFAS/HFAS) or to
employment of the improved extended echo ranging (IEER) system. The
IEER consists of an explosive source sonobuoy (AN/SSQ-110A) and an air
deployable active receiver (ADAR) sonobuoy (AN/SSQ-101). The Navy
requested authorization to take individuals of 40 species of marine
mammals by Level B Harassment. Further, though they do not anticipate
it to occur, the Navy requests authorization to take, by injury or
mortality, up to 10 beaked whales over the course of the 5-yr
regulations.
Background of Navy Request
The proposed rule contains a description of the Navy's mission,
their responsibilities pursuant to Title 10 of the United States Code,
and the specific purpose and need for the activities for which they
requested incidental take authorization. The description contained in
the proposed rule has not changed (73 FR 60754).
Description of the Specified Activities
The proposed rule contains a complete description of the Navy's
specified activities that are covered by these final regulations, and
for which the associated incidental take of marine mammals will be
authorized in the related LOAs. The proposed rule describes the nature
and number of both the anti-submarine warfare (ASW) and mine warfare
training (MIW) exercises involving both mid- and high-frequency active
sonar (MFAS and HFAS), as well as the IEER exercises involving small
explosive detonations. It also describes the sound sources used (73 FR
60754,
[[Page 4845]]
pages 60755-60762). The narrative description of the action contained
in the proposed rule has not changed, with the exception of the change
from IEER to the Advanced Extended Echo Ranging (AEER) discussed below.
Tables 1 and 2 summarize the sonar and IEER exercise types used in
these training exercises and the hours of sonar.
Navy is developing the AEER system as a replacement to the IEER
system. AEER would use a new active sonobuoy (AN/SSQ-125) that utilizes
a tonal (or a ping) vice impulsive (or explosive) sound source as a
replacement for the AN/SSQ-110A. AEER will still use the ADAR sonobuoy
as the systems receiver and will be deployed by Maritime Patrol
Aircraft. As AEER is introduced for Fleet use, IEER will be removed.
The same total number of buoys will be deployed as were presented in
the proposed rule, but a subset of them will be AEER instead of IEER.
The small difference in the number of anticipated marine mammal takes
that will result from this change is indicated in the take table (Table
6), along with other minor modifications. This small change in the take
numbers did not affect NMFS' analysis of and conclusions regarding the
proposed action.
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AFAST Study Area
The AFAST proposed rule contains a description of the AFAST Study
Area along with a description of the areas in which certain types of
activities will occur. Table 3, included here, summarizes the areas in
which certain exercise types will occur. This section also contains a
description of the North Atlantic right whale (NARW) critical habitat
and the National Marine Sanctuaries (NMS) within the AFAST Study Area.
The description of the AFAST Study Area in the proposed rule has not
changed, with the exception of the paragraph relating to the NMSs,
below (73 FR 60754, pages 60762-60764).
The paragraph related to NMSs in the proposed rule should be
replaced with the following paragraph:
The Navy will not conduct active sonar activities within the
Stellwagen Bank, Monitor, Gray's Reef, Flower Garden Banks, and Florida
Keys National Marine Sanctuaries and will avoid these sanctuaries by
observing a 5-km (2.7-NM) buffer. At all times, the Navy will conduct
AFAST activities in a manner that avoids to the maximum extent
practicable any adverse impacts on sanctuary resources. In the event
the Navy determines AFAST activities, due to operational requirements,
are likely to destroy, cause the loss of, or injure any sanctuary
resource (for Stellwagen Bank National Marine Sanctuary, the threshold
is ``may'' destroy, cause the loss of, or injure), the Navy would first
consult with the Director, Office of National Marine Sanctuaries in
accordance with 16 U.S.C. 1434(d). Although activities in the
Sanctuaries are not planned or anticipated, NMFS' analysis, for
purposes of the MMPA considers the effects on marine mammals of the
Navy's conducting activities in the biologically important areas that
occur in or near Sanctuaries.
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Description of Marine Mammals in the Area of the Specified Activities
There are 43 marine mammal species with possible or confirmed
occurrence in the AFAST Study Area. As indicated in Table 4, there are
36 cetacean species (7 mysticetes and 29 odontocetes), six pinnipeds,
and one sirenian (manatee). Six marine mammal species listed as
federally endangered under the Endangered Species Act (ESA) and under
the jurisdiction of NMFS occur in the AFAST Study Area: The NARW,
humpback whale, sei whale, fin whale, blue whale, and sperm whale.
Manatees are managed by the U.S. Fish and Wildlife Service and will not
be addressed further here. The proposed rule contains a discussion of
two species that are not considered further in the analysis (beluga
whales and ringed seals) because of their rarity in the AFAST Study
Area. The proposed rule also contains a discussion of important areas,
including NARW critical habitat, humpback whale feeding grounds in the
northeast, and sperm whale calving and nursing grounds in the
Mississippi Delta area. Last, the proposed rule includes a discussion
of the methods used to estimate marine mammal density in the AFAST
Study Area. The Description of Marine Mammals in the Area of the
Specified Activities section has not changed from what was in the
proposed rule (73 FR 60754, pages 60766-60767).
[[Page 4852]]
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A Brief Background on Sound
The proposed rule contains a section that provides a brief
background on the principles of sound that are frequently referred to
in this rulemaking (73 FR 60754, pages 60767-60769). This section also
includes a discussion of the functional hearing ranges of the different
groups of marine mammals (by frequency) as well as a discussion of the
two main sound metrics used in NMFS analysis (sound pressure level
(SPL) and sound energy level (SEL)). The information contained in the
proposed rule has not changed.
Potential Effects of Specified Activities on Marine Mammals
With respect to the MMPA, NMFS' effects assessment serves four
primary purposes: (1) To prescribe the permissible methods of taking
(i.e., Level B Harassment (behavioral harassment), Level A Harassment
(injury), or mortality, including an identification of the number and
types of take that could occur by Level A or B harassment or mortality)
and to prescribe other means of affecting the least practicable adverse
impact on such species or stock and its habitat (i.e., mitigation); (2)
to determine whether the specified activity will have a negligible
impact on the affected species or stocks of marine mammals (based on
the likelihood that the activity will adversely affect the species or
stock through effects on annual rates of recruitment or survival); (3)
to determine whether the specified activity will have an unmitigable
adverse impact on the availability of the species or stock(s) for
subsistence uses (however, there are no subsistence communities that
would be affected in the AFAST Study Area, so this determination is
inapplicable for this rulemaking); and (4) to prescribe requirements
pertaining to monitoring and reporting.
In the Potential Effects of Specified Activities on Marine Mammals
section of the proposed rule, NMFS included a qualitative discussion of
the different ways that MFAS/HFAS and underwater explosive detonations
(IEER) may potentially affect marine mammals (some of which NMFS would
not classify as harassment). See 73 FR 60754, pages 60769-60781. Marine
mammals may experience direct physiological effects (such as threshold
shift), acoustic masking, impaired communications, stress responses,
and behavioral disturbance. This section also included a discussion of
some of the suggested explanations for the association between the use
of MFAS and marine mammal strandings (such as behaviorally mediated
bubble growth) that has been observed a limited number of times in
certain circumstances (the specific events are also described). See 73
FR 60754, pages 60777-60781. The information contained in Potential
Effects of Specified Activities on Marine Mammals section from the
proposed rule has not changed, with the exception of the following
sentence. On page 60779, NMFS said ``Other species (Stenella
coeruleoalba, Kogia breviceps and Balaenoptera acutorostrata) have
stranded, but in much lower numbers and less consistently than beaked
whales.'' As a member of the public pointed out, and as NMFS has
previously stated, there was no likely association between the minke
whale and spotted dolphin strandings referred to here and the operation
of MFAS. Therefore, the sentence should read ``Other species, such as
Kogia breviceps, have stranded in association with the operation of
MFAS, but in much lower numbers and less consistently than beaked
whales.''
Later, in the Estimated Take of Marine Mammals section, NMFS
relates and quantifies the potential effects to marine mammals from
MFAS/HFAS and underwater detonation of explosives discussed here to the
MMPA definitions of Level A and Level B Harassment. NMFS has also
considered the effects of mortality on these species.
Mitigation
In order to issue an incidental take authorization (ITA) under
Section 101(a)(5)(A) of the MMPA, NMFS must prescribe regulations
setting forth the ``permissible methods of taking pursuant to such
activity, and other means of affecting the least practicable adverse
impact on such species or stock and its habitat, paying particular
attention to rookeries, mating grounds, and areas of similar
significance.'' The National Defense Authorization Act (NDAA) of 2004
amended the MMPA as it relates to military readiness activities and the
incidental take authorization process such that ``least practicable
adverse impact'' shall include consideration of personnel safety,
practicality of implementation, and impact on the effectiveness of the
``military readiness activity''. The AFAST activities described in the
proposed rule are considered military readiness activities.
NMFS reviewed the Navy's proposed AFAST activities and the proposed
AFAST mitigation measures (which the Navy refers to as Protective
Measures) presented in the Navy's application to determine whether the
activities and mitigation measures were capable of achieving the least
practicable adverse effect on marine mammals. NMFS determined that
further discussion was necessary regarding: (1) General minimization of
marine mammal impacts; (2) minimization of impacts within the
southeastern NARW critical habitat; and (3) the potential relationship
between the operation of MFAS/HFAS and marine mammal strandings.
Any mitigation measure prescribed by NMFS should be known 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 below:
(a) Avoidance or minimization of injury or death of marine mammals
wherever possible (goals b, c, and d may contribute to this goal).
(b) A reduction in the numbers of marine mammals (total number or
number at biologically important time or location) exposed to received
levels of MFAS/HFAS, underwater detonations, or other activities
expected to result in the take of marine mammals (this goal may
contribute to a, above, or to reducing harassment takes only).
(c) A reduction in the number of times (total number or number at
biologically important time or location) individuals would be exposed
to received levels of MFAS/HFAS, underwater detonations, or other
activities expected to result in the take of marine mammals (this goal
may contribute to a, above, or to reducing harassment takes only).
(d) A reduction in the intensity of exposures (either total number
or number at biologically important time or location) to received
levels of MFAS/HFAS, underwater detonations, or other activities
expected to result in the take of marine mammals (this goal may
contribute to a, above, or to reducing the severity of harassment takes
only).
(e) A reduction in 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.
(f) For monitoring directly related to mitigation--an increase in
the probability of detecting marine mammals, thus allowing for more
effective implementation of the mitigation (shut-down zone, etc.).
NMFS worked with the Navy to identify potential additional
practicable and effective mitigation measures, which included a careful
balancing of the likely benefit of any particular measure to the marine
mammals with
[[Page 4854]]
the likely effect of that measure on personnel safety, practicality of
implementation, and impact on the ``military-readiness activity.'' NMFS
and the Navy developed additional mitigation measures that address the
concerns mentioned above, including the development of Planning
Awareness Areas (PAAs), additional minimization of impacts in the
southeastern NARW critical habitat, and a Stranding Response Plan.
The Navy's proposed mitigation measures, as well as the Planning
Awareness Areas (PAAs), additional minimization of impacts in the
southeastern NARW critical habitat, and Stranding Response Plan, which
are required under these regulations, were described in detail in the
proposed rule (73 FR 60754, pages 60781-60789). The Navy's measures
address personnel training, lookout and watchstander responsibilities,
operating procedures for training activities using both MFAS/HFAS and
IEER, additional measures for TORPEXs in the northeastern NARW critical
habitat, and mitigation related to vessel traffic and the NARW. No
changes have been made to the mitigation measures described in the
proposed rule, with the exception of adding that night vision devices
shall be available to all ship crews and air crews for use as
appropriate and making the IEER mitigation applicable to the newly
described AEER system as well. Additionally, the definition for
``Exhibiting Indicators of Distress'', which was originally included in
the codified text of the proposed rule, has been removed in the final
rule. The definition, which may be found in the AFAST Stranding
Response Plan, was not included in the codified text because it could
potentially be modified (pursuant to the adaptive management component
of the rule) based on new data.
The final AFAST Stranding Response Plan, which includes a shutdown
protocol, a stranding investigation plan, and a requirement for Navy
and NMFS to implement a memorandum of agreement (MOA) that will
establish a framework whereby the Navy can (and provide the Navy
examples of how they can best) assist NMFS with stranding
investigations in certain circumstances, may be viewed at: https://
www.nmfs.noaa.gov/pr/permits/incidental.htm#applications. Additionally,
the mitigation measures are included in full in the codified text of
the regulations.
NMFS has determined that the Navy's proposed mitigation measures
(which include a suite of measures that specifically address vessel
transit and the NARW), along with the Planning Awareness Areas (PAAs),
additional minimization of impacts in the southeastern NARW critical
habitat, and the Stranding Response Plan (and when the Adaptive
Management (see Adaptive Management below) component is taken into
consideration) are adequate means of effecting the least practicable
adverse impacts on marine mammal species or stocks and their habitat,
paying particular attention to rookeries, mating grounds, and areas of
similar significance, while also considering personnel safety,
practicality of implementation, and impact on the effectiveness of the
military readiness activity. The justification for this conclusion is
discussed in the Mitigation Conclusion section of the proposed rule (73
FR 60836, pages 60789-60790). The Mitigation Conclusion Section of the
proposed rule has not changed.
Research and Conservation Measures for Marine Mammals
The Navy provides a significant amount of funding and support for
marine research. The Navy provided $26 million in Fiscal Year 2008 and
plans for $22 million in Fiscal Year 2009 to universities, research
institutions, Federal laboratories, private companies, and independent
researchers around the world to study marine mammals. Over the past
five years the Navy has funded over $100 million in marine mammal
research. The Navy sponsors seventy percent of all U.S. research
concerning the effects of human-generated sound on marine mammals and
50 percent of such research conducted worldwide. Major topics of Navy-
supported research include the following:
Better understanding of marine species distribution and
important habitat areas,
Developing methods to detect and monitor marine species
before and during training,
Understanding the effects of sound on marine mammals, sea
turtles, fish, and birds, and
Developing tools to model and estimate potential effects
of sound.
The Navy's Office of Naval Research currently coordinates six
programs that examine the marine environment and are devoted solely to
studying the effects of noise and/or the implementation of technology
tools that will assist the Navy in studying and tracking marine
mammals. The six programs are as follows:
Environmental Consequences of Underwater Sound,
Non-Auditory Biological Effects of Sound on Marine
Mammals,
Effects of Sound on the Marine Environment,
Sensors and Models for Marine Environmental Monitoring,
Effects of Sound on Hearing of Marine Animals, and
Passive Acoustic Detection, Classification, and Tracking
of Marine Mammals.
The Navy has also developed the technical reports referenced within
this document and the AFAST EIS, such as the Marine Resource
Assessments. Furthermore, research cruises by NMFS and by academic
institutions have received funding from the U.S. Navy.
The Navy has sponsored several workshops to evaluate the current
state of knowledge and potential for future acoustic monitoring of
marine mammals. The workshops brought together acoustic experts and
marine biologists from the Navy and other research organizations to
present data and information on current acoustic monitoring research
efforts and to evaluate the potential for incorporating similar
technology and methods on instrumented ranges. However, acoustic
detection, identification, localization, and tracking of individual
animals still requires a significant amount of research effort to be
considered a reliable method for marine mammal monitoring. The Navy
supports research efforts on acoustic monitoring and will continue to
investigate the feasibility of passive acoustics as a potential
mitigation and monitoring tool.
Overall, the Navy will continue to fund ongoing marine mammal
research, and is planning to coordinate long term monitoring/studies of
marine mammals on various established ranges and operating areas. The
Navy will continue to research and contribute to university/external
research to improve the state of the science regarding marine species
biology and acoustic effects. These efforts include mitigation and
monitoring programs; data sharing with NMFS and via the literature for
research and development efforts; and future research as described
previously.
Long-Term Prospective Study
Apart from this final rule, NMFS, with input and assistance from
the Navy and several other agencies and entities, will perform a
longitudinal observational study of marine mammal strandings to
systematically observe and record the types of pathologies and diseases
and investigate the relationship with potential causal factors (e.g.,
sonar, seismic, weather). The proposed rule contained an outline of the
proposed
[[Page 4855]]
study (73 FR 60754, pages 60790-60791). No changes have been made to
the longitudinal study as described in the proposed rule.
Monitoring
In order to issue an ITA for an activity, Section 101(a)(5)(A) 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 LOAs
must include the suggested means of accomplishing the necessary
monitoring and reporting that will result in increased knowledge of the
species and of the level of taking or impacts on populations of marine
mammals that are expected to be present.
Monitoring measures prescribed by NMFS should accomplish one or
more of the following general goals:
(a) An increase in the probability of detecting marine mammals,
both within the safety zone (thus allowing for more effective
implementation of the mitigation) and in general to generate more data
to contribute to the effects analyses.
(b) An increase in our understanding of how many marine mammals are
likely to be exposed to levels of MFAS/HFAS (or explosives or other
stimuli) that we associate with specific adverse effects, such as
behavioral harassment, TTS, or PTS.
(c) An increase in our understanding of how marine mammals respond
(behaviorally or physiologically) to MFAS/HFAS (at specific received
levels), explosives, or other stimuli expected to result in take and
how anticipated adverse effects on individuals (in different ways and
to varying degrees) may impact the population, species, or stock
(specifically through effects on annual rates of recruitment or
survival).
(d) An increased knowledge of the affected species.
(e) An increase in our understanding of the effectiveness of
certain mitigation and monitoring measures.
(f) A better understanding and record of the manner in which the
authorized entity complies with the incidental take authorization.
Proposed Monitoring Plan for AFAST Study Area
As NMFS indicated in the proposed rule, the Navy has (with input
from NMFS) fleshed out the details of and made improvements to the
AFAST Monitoring Plan. Additionally, NMFS and the Navy have
incorporated a recommendation from the public, which recommended the
Navy hold a workshop to discuss the Navy's Monitoring Plan (see
Monitoring Workshop section). The final AFAST Monitoring Plan, which is
summarized below, may be viewed at https://www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications. The Navy plans to implement all of the
components of the Monitoring Plan: however, only the marine mammal
components (not the sea turtle components) will be required by the MMPA
regulations and associated LOAs.
The Monitoring Plan for AFAST has been designed as a collection of
focused ``studies'' (described fully in the AFAST Monitoring Plan) to
gather data that will allow the Navy to address the following
questions:
(a) Are marine mammals exposed to MFAS, especially at levels
associated with adverse effects (i.e., based on NMFS'criteria for
behavioral harassment, TTS, or PTS)? If so, at what levels are they
exposed?
(b) If marine mammals are exposed to MFAS in the AFAST Study Area,
do they redistribute geographically as a result of continued exposure?
If so, how long does the redistribution last?
(c) If marine mammals are exposed to MFAS, what are their
behavioral responses to various received levels?
(d) Is the Navy's suite of mitigation measures for MFAS (e.g.,
measures agreed to by the Navy through permitting) effective at
avoiding TTS, injury, and mortality of marine mammals?
Data gathered in these studies will be collected by qualified,
professional marine mammal biologists that are experts in their field.
They will use a combination of the following methods to collect data:
Contracted vessel and aerial surveys.
Passive acoustics.
Marine mammal observers on Navy ships.
In the four proposed study designs (all of which cover multiple
years), the above methods will be used separately or in combination to
monitor marine mammals in different combinations before, during, and
after training activities utilizing MFAS/HFAS. Table 7 contains a
summary of the Monitoring effort that is planned for each study in each
year.
This monitoring plan has been designed to gather data on all
species of marine mammals that are observed in the AFAST study area.
The Plan recognizes that deep-diving and cryptic species of marine
mammals such as beaked whales have a low probability of detection
(Barlow and Gisiner, 2006). Therefore, methods will be utilized to
attempt to address this issue (e.g., passive acoustic monitoring).
North Atlantic right whales will also be given particular attention
during monitoring in the AFAST study area, although monitoring methods
will be the same for all species. Within the AFAST study area, the
Northwestern Atlantic provides unique breeding and calving habitat for
NARW, and as a result, critical habitat has been designated for one
calving ground (off Georgia and northern Florida) and two feeding areas
(Cape Cod Bay and the Great South Channel). Pursuant to the Monitoring
Plan, NARWs will be given particular attention in the form of focal
follows (e.g. collect behavioral data using the Big Eyes binoculars,
and observe the behavior of any animals that are seen) when observed.
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Monitoring Workshop
During the public comment period on the AFAST proposed rule (as
well as the Hawaii Range Complex and Southern California Range Complex
proposed rules), NMFS received a comment which, in consultation with
the Navy, we have chosen to incorporate into the final rule (in a
modified form). One commenter recommended that a workshop or panel be
convened to solicit input on the monitoring plan from researchers,
experts, and other interested parties. The AFAST proposed rule included
an adaptive management component and both NMFS and the Navy believe
that a workshop would provide a means for Navy and NMFS to consider
input from participants in determining whether or how to modify
monitoring techniques to more effectively accomplish the goals of
monitoring set forth earlier in the document. NMFS and the Navy believe
that this workshop concept is valuable in relation to all of the Range
Complexes and major training exercise rules and LOAs that NMFS is
working on with the Navy at this time, and consequently this single
Monitoring Workshop will be included as a component of all of the rules
and LOAs that NMFS will be processing for the Navy in the next year or
so.
The Navy, with guidance and support from NMFS, will convene a
Monitoring Workshop, including marine mammal and acoustic experts as
well as other interested parties, in 2011. The Monitoring Workshop
participants will review the monitoring results from the previous two
years of monitoring pursuant to the AFAST rule as well as monitoring
results from other Navy rules and LOAs (e.g., the Southern California
Range Complex (SOCAL), Hawaii Range Complex (HRC), and other rules).
The Monitoring Workshop participants would provide their individual
recommendations to the Navy and NMFS on the monitoring plan(s) after
also considering the current science (including Navy research and
development) and working within the framework of available resources
and feasibility of implementation. NMFS and the Navy would then analyze
the input from the Monitoring Workshop participants and determine the
best way forward from a national perspective. Subsequent to the
Monitoring
[[Page 4857]]
Workshop, modifications would be applied to monitoring plans as
appropriate.
Integrated Comprehensive Monitoring Program
In addition to the Monitoring Plan for AFAST, the Navy will
complete the Integrated Comprehensive Monitoring Program (ICMP) Plan by
the end of 2009. The ICMP will provide the overarching coordination
that will support compilation of data from project-specific monitoring
plans (e.g., AFAST Monitoring Plan) as well as Navy funded research and
development (R&D) studies. The ICMP will coordinate the monitoring
programs progress towards meeting its goals and develop a data
management plan. The ICMP will be evaluated annually to provide a
matrix for progress and goals for the following year, and will make
recommendations on adaptive management for refinement and analysis of
the monitoring methods.
The primary objectives of the ICMP are to:
Monitor and assess the effects of Navy activities on
protected species;
Ensure that data collected at multiple locations is
collected in a manner that allows comparison between and among
different geographic locations;
Assess the efficacy and practicality of the monitoring and
mitigation techniques;
Add to the overall knowledge-base of marine species and
the effects of Navy activities on marine species.
The ICMP will be used both as: (1) A planning tool to focus Navy
monitoring priorities (pursuant to ESA/MMPA requirements) across Navy
Range Complexes and Exercises; and (2) an adaptive management tool,
through the consolidation and analysis of the Navy's monitoring and
watchstander data, as well as new information from other Navy programs
(e.g., R&D), and other appropriate newly published information.
In combination with the 2011 Monitoring Workshop and the adaptive
management component of the AFAST rule and the other planned Navy rules
(e.g. SOCAL and HRC), the ICMP could potentially provide a framework
for restructuring the monitoring plans and allocating monitoring effort
based on the value of particular specific monitoring proposals (in
terms of the degree to which results would likely contribute to stated
monitoring goals, as well the likely technical success of the
monitoring based on a review of past monitoring results) that have been
developed through the ICMP framework, instead of allocating based on
maintaining an equal (or commensurate to effects) distribution of
monitoring effort across Range complexes. For example, if careful
prioritization and planning through the ICMP (which would include a
review of both past monitoring results and current scientific
developments) were to show that a large, intense monitoring effort in
Hawaii would likely provide extensive, robust and much-needed data that
could be used to understand the effects of sonar throughout different
geographical areas, it may be appropriate to have other Range Complexes
dedicate money, resources, or staff to the specific monitoring proposal
identified as ``high priority'' by the Navy and NMFS, in lieu of
focusing on smaller, lower priority projects divided throughout their
home Range Complexes.
The ICMP will identify:
A means by which NMFS and the Navy would jointly consider
prior years monitoring results and advancing science to determine if
modifications are needed in mitigation or monitoring measures to better
effect the goals laid out in the Mitigation and Monitoring sections of
the AFAST rule.
Guidelines for prioritizing monitoring projects.
If, as a result of the workshop and similar to the example
described in the paragraph above, the Navy and NMFS decide it is
appropriate to restructure the monitoring plans for multiple ranges
such that they are no longer evenly allocated (by rule), but rather
focused on priority monitoring projects that are not necessarily tied
to the geographic area addressed in the rule, the ICMP will be modified
to include a very clear and unclassified recordkeeping system that will
allow NMFS and the public to see how each Range Complex/project is
contributing to all of the ongoing monitoring (resources, effort,
money, etc.).
Past Monitoring in AFAST
The proposed rule contained a detailed review of the previous
marine mammal monitoring conducted in the AFAST Study Area, which was
conducted in compliance with the terms and conditions of multiple
biological opinions issued for MFAS training activities (73 FR 60754,
pages 60791-60798). No changes have been made to the discussion
contained in the proposed rule.
Adaptive Management
The final regulations governing the take of marine mammals
incidental to Navy's AFAST exercises contain an adaptive management
component. Our understanding of the effects of MFAS/HFAS and explosives
on marine mammals is still in its relative infancy, and yet the science
in this field continues to improve. These circumstances make the
inclusion of an adaptive management component both valuable and
necessary within the context of 5-year regulations for activities that
have been associated with marine mammal mortality in certain
circumstances and locations (though not off the Atlantic Coast of the
U.S.). The use of adaptive management will give NMFS the ability to
consider new data from different sources to determine (in coordination
with the Navy) on an annual basis if mitigation or monitoring measures
should be modified or added (or deleted) if new data suggests that such
modifications are appropriate (or are not appropriate) for subsequent
annual LOAs.
Following are some of the possible sources of applicable data:
Results from the Navy's monitoring from the previous year
(either from AFAST or other locations).
Findings of the Workshop that the Navy will convene in
2011 to analyze monitoring results to date, review current science, and
recommend modifications, as appropriate to the monitoring protocols to
increase monitoring effectiveness.
Compiled results of Navy funded research and development
(R&D) studies (presented pursuant to the ICMP, which is discussed
elsewhere in this document).
Results from specific stranding investigations (either
from AFAST or other locations, and involving coincident MFAS/HFAS of
explosives training or not involving coincident use).
Results from the Long Term Prospective Study described
above.
Results from general marine mammal and sound research
(funded by the Navy (described above) or otherwise).
Mitigation measures could be modified or added (or deleted) if new
data suggest that such modifications would have (or do not have) a
reasonable likelihood of accomplishing the goals of mitigation laid out
in this final rule and if the measures are practicable. NMFS would also
coordinate with the Navy to modify or add to (or delete) the existing
monitoring requirements if the new data suggest that the addition of
(or deletion of) a particular measure would more effectively accomplish
the goals of monitoring laid out in this final rule. The reporting
requirements associated with this rule are designed to provide
[[Page 4858]]
NMFS with monitoring data from the previous year to allow NMFS to
consider the data and issue annual LOAs. NMFS and the Navy will meet
annually, prior to LOA issuance, to discuss the monitoring reports,
Navy R&D developments, and current science and whether mitigation or
monitoring modifications are appropriate.
Reporting
In order to issue an ITA for an activity, Section 101(a)(5)(A) of
the MMPA states that NMFS must set forth ``requirements pertaining to
the monitoring and reporting of such taking''. Effective reporting is
critical to ensure compliance with the terms and conditions of a LOA,
and to provide NMFS and the Navy with data of the highest quality based
on the required monitoring.
As NMFS noted in its proposed rule, additional detail has been
added to the reporting requirements since they were outlined in the
proposed rule. The updated reporting requirements are all included
below. A subset of the information provided in the monitoring reports
may be classified and not releasable to the public.
NMFS will work with the Navy to develop tables that allow for
efficient submission of the information required below.
General Notification of Injured or Dead Marine Mammals
Navy personnel will ensure that NMFS (regional stranding
coordinator) is notified immediately (or as soon as operational
security allows) if an injured or dead marine mammal is found during or
shortly after, and in the vicinity of, any Navy training exercise
utilizing MFAS, HFAS, or underwater explosive detonations. The Navy
will provide NMFS with species or description of the animal(s), the
condition of the animal(s) (including carcass condition if the animal
is dead), location, time of first discovery, observed behaviors (if
alive), and photo or video (if available). The Stranding Response Plan
contains more specific reporting requirements for specific
circumstances.
Annual AFAST Monitoring Plan Report
The Navy shall submit a report annually on October 1 describing the
implementation and results (through August 1 of the same year) of the
AFAST Monitoring Plan, described above. Data collection methods will be
standardized across range complexes to allow for comparison in
different geographic locations. Although additional information will
also be gathered, the marine mammal observers (MMOs) collecting marine
mammal data pursuant to the AFAST Monitoring Plan shall, at a minimum,
provide the same marine mammal observation data required in the MFAS/
HFAS major Training Exercises section of the Annual AFAST Exercise
Report referenced below.
The AFAST Monitoring Plan Report may be provided to NMFS within a
larger report that includes the required Monitoring Plan Reports from
multiple Range Complexes.
Annual AFAST Exercise Report
The Navy will submit an Annual AFAST Exercise Report on October 1
of every year (covering data gathered through August 1). This report
shall contain the subsections and information indicated below.
MFAS/HFAS Major Training Exercises
This section shall contain the following information for the
following Coordinated and Strike Group exercises, which for simplicity
will be referred to as major training exercises for reporting (MTERs):
Southeastern ASW Integrated Training Initiative (SEASWITI), Integrated
ASW Course (IAC), Composite Training Unit Exercises (COMPTUEX), and
Joint Task Force Exercises (JTFEX) conducted in AFAST:
(a) Exercise Information (for each MTER):
(i) Exercise designator.
(ii) Date that exercise began and ended.
(iii) Location.
(iv) Number and types of active sources used in the exercise.
(v) Number and types of passive acoustic sources used in exercise.
(vi) Number and types of vessels, aircraft, etc., participating in
exercise.
(vii) Total hours of observation by watchstanders.
(viii) Total hours of all active sonar source operation.
(ix) Total hours of each active sonar source (along with
explanation of how hours are calculated for sources typically
quantified in alternate way (buoys, torpedoes, etc.)).
(x) Wave height (high, low, and average during exercise).
(b) Individual marine mammal sighting info (for each sighting in
each MTER):
(i) Location of sighting.
(ii) Species (if not possible--indication of whale/dolphin/
pinniped).
(iii) Number of individuals.
(iv) Calves observed (y/n).
(v) Initial Detection Sensor.
(vi) Indication of specific type of platform observation made from
(including, for example, what type of surface vessel, i.e., FFG, DDG,
or CG).
(vii) Length of time observers maintained visual contact with
marine mammal(s).
(viii) Wave height (in feet).
(ix) Visibility.
(x) Sonar source in use (y/n).
(xi) Indication of whether animal is <200yd, 200-500yd, 500-1000yd,
1000-2000yd, or >2000yd from sonar source in (x) above.
(xiii) Mitigation Implementation--Whether operation of sonar sensor
was delayed, or sonar was powered or shut down, and how long the delay
was.
(xiv) If source in use (x) is hullmounted, true bearing of animal
from ship, true direction of ship's travel, and estimation of animal's
motion relative to ship (opening, closing, parallel)
(xv) Observed behavior--Watchstanders shall report, in plain
language and without trying to categorize in any way, the observed
behavior of the animals (such as animal closing to bow ride,
paralleling course/speed, floating on surface and not swimming, etc.)
(c) An evaluation (based on data gathered during all of the MTERs)
of the effectiveness of mitigation measures designed to avoid exposing
marine mammals to MFAS. This evaluation shall identify the specific
observations that support any conclusions the Navy reaches about the
effectiveness of the mitigation.
ASW Summary
This section shall include the following information as summarized
from both MTERs and non-major training exercises:
(i) Total annual hours of each type of sonar source (along with
explanation of how hours are calculated for sources typically
quantified in alternate way (buoys, torpedoes, etc.))
(iv) Cumulative Impact Report--To the extent practicable, the Navy,
in coordination with NMFS, shall develop and implement a method of
annually reporting non-major (i.e., other than MTERs) training
exercises utilizing hull-mounted sonar. The report shall present an
annual (and seasonal, where practicable) depiction of non-major
training exercises geographically across the AFAST Study Area. To the
extent practicable, this report will also include the total number of
sonar hours (from helicopter dipping sonar and object detection
exercises) conducted within the southern NARW critical habitat plus 5
nm buffer area). The Navy shall include (in the AFAST annual report) a
brief annual progress update on the
[[Page 4859]]
status of the development of an effective and unclassified method to
report this information until an agreed-upon (with NMFS) method has
been developed and implemented.
Improved Extended Echo-Ranging System (IEER)/Advanced Extended Echo-
Ranging System (AEER) Summary
This section shall include an annual summary of the following IEER
and AEER information:
(i) Total number of IEER and AEER events conducted in AFAST Study
Area
(ii) Total expended/detonated rounds (buoys).
(iii) Total number of self-scuttled IEER rounds.
Sonar Exercise Notification
The Navy shall submit to the NMFS Office of Protected Resources
(specific contact information to be provided in LOA) either an
electronic (preferably) or verbal report within fifteen calendar days
after the completion of any MTER indicating:
(1) Location of the exercise.
(2) Beginning and end dates of the exercise.
(3) Type of exercise.
AFAST 5-Yr Comprehensive Report
The Navy shall submit to NMFS a draft report that analyzes and
summarizes all of the multi-year marine mammal information gathered
during ASW and IEER exercises for which annual reports are required
(Annual AFAST Exercise Reports and AFAST Monitoring Plan Reports). This
report will be submitted at the end of the fourth year of the rule
(November 2012), covering activities that have occurred through June 1,
2012.
Comprehensive National ASW Report
By June 2014, the Navy shall submit a draft National Report that
analyzes, compares, and summarizes the active sonar data gathered
(through January 1, 2014) from the watchstanders and pursuant to the
implementation of the Monitoring Plans for AFAST, SOCAL, the HRC, the
Mariana Islands Range Complex, the Northwest Training Range Complex,
the Gulf of Alaska, and the East Coast Undersea Warfare Training Range.
The Navy shall respond to NMFS comments and requests for additional
information or clarification on the AFAST Comprehensive Report, the
Comprehensive National ASW report, the Annual AFAST Exercise Report, or
the Annual AFAST Monitoring Plan Report (or the multi-Range Complex
Annual Monitoring Plan Report, if that is how the Navy chooses to
submit the information) if submitted within 3 months of receipt. These
reports will be considered final after the Navy has addressed NMFS'
comments or provided the requested information, or three months after
the submittal of the draft if NMFS does not comment by then.
Comments and Responses
On October 14, 2008 (73 FR 60754), NMFS published a proposed rule
in response to the Navy's request to take marine mammals incidental to
military readiness training, maintenance, and RDT&E activities in the
AFAST Study Area and requested comments, information and suggestions
concerning the request. During the 30-day public comment period, NMFS
received comments from 6 private citizens and Senator Benjamin Cardin,
comments from the Marine Mammal Commission (MMC), comments from the
Maine Department of Marine Resources and the Georgia Department of
Natural Resources, and three sets of comments from non-governmental
organizations, including, the Natural Resources Defense Council (NRDC)
(which commented on behalf of The Humane Society of the United States,
the International Fund for Animal Welfare, Whale and Dolphin
Conservation Society, Cetacean Society International, Pamlico Tar River
Foundation, North Carolinians for Responsible Use of Sonar, League for
Coastal Protection, and Ocean Futures Society and its founder Jean-
Michel Cousteau), the Cascadia Research Collective (CRC), and the Ocean
Mammal and Animal Welfare Institutes. The comments are summarized and
sorted into general topic areas and are addressed below. Full copies of
the comment letters may be accessed at https://www.regulations.gov.
NMFS worked with the Navy to develop MMPA rules and LOAs for the
AFAST activities, SOCAL Range Complex, and HRC Range Complex. Many of
the issues raised in the public comments for this rule were also raised
for SOCAL and the HRC and NMFS considered many of the broader issues in
the context of all three of these Navy actions when determining how to
address the comments. Responses to public comments on the HRC and SOCAL
rules (addressing similar issues identified in the AFAST final rule)
were also published in January 2009 and may provide the public with
additional detail, if needed.
North Atlantic Right Whales
Comment 1: Several commenters had the following general comments/
concerns regarding the way that NMFS' rule analyzed the potential
impacts to right whales from sonar:
(a) As the only known calving ground, the southern critical habitat
is very important to the survival of the species and commenters were
concerned about the level of Navy activity in critical habitat and how
it will affect right whales. Some suggested that NMFS should restrict
Navy activity within critical habitat.
(b) The specific impacts to and responses of newborn right whale
calves and their mothers are unknown and commenters are concerned about
the effects of MFAS on this segment of the population. One commenter
notes that NMFS has previously indicated that the ``loss of even a
single individual right whale may contribute to the extinction of the
species,'' and that ``preventing the mortality of one adult female
alters the projected outcome.'' 69 FR 30858.
(c) The waters off of Gulf of Maine: Cape Cod Bay, Great South
Channel, Bay of Fundy, and the Brown's Bank area are primary feeding
grounds for the North Atlantic right whale (and other large whale
species) and commenters are concerned about impacts. Some commenters
recommended minimizing activities in that area.
(d) One commenter stated that although the Navy's DEIS and NMFS'
Proposed Rule acknowledge that right whales are expected to occur in
the AFAST area, the agencies arbitrarily conclude that no right whales
will be injured by the thousands of hours of sonar training exercises
per year spanning the entire East Coast and Gulf of Mexico. One
commenter further asserts that right whales are hard to detect because
they spend the majority of their time below the surface and are often
found alone or in pairs, which, combined with rough weather reduces the
probability of detection. Also, female right whales with young calves
are less mobile than adult whales without young calves and may not be
able to avoid sonar sources.
(e) The commenters requested clarification regarding why NMFS
believes that ship strikes are unlikely. Commenters further state that
the Navy has been involved in ship strikes in the past (specifically, a
female NARW and her near-term calf in the mid-Atlantic in 2004.)
Response: Following is NMFS' response to the above comments:
(a) NMFS agrees that the southern critical habitat for the North
Atlantic right is very important to the survival of the species. The
Navy intends to limit sonar use to a relatively small amount in the
southern NARW critical habitat
[[Page 4860]]
(see response to comment (1)(e) below). As described in the proposed
rule, following are the details of the planned sonar usage in the
vicinity of the southern critical habitat:
[ssbox] The Navy anticipates conducting approximately 30 helicopter
dipping sonar maintenance events (< 1 hr) annually in the NARW critical
habitat (and approximately 84 helicopter training exercises in the
vicinity of the critical habitat but in deeper waters at least more
than 5 nm seaward of the critical habitat boundaries). This means that
only a subset of those 30 activities will occur in the critical habitat
between Nov 15 and April 15 (approximately 13 if one assumes they are
distributed equally throughout the year, for example) and only a subset
of the 84 helicopter training exercises would occur near the critical
habitat between Nov 15 and April 15 (approximately 34 if one assumes
they are distributed equally throughout the year, for example). Note
that the source level of a helicopter dipping sonar is approximately 18
dB less than that of a surface sonar source, which means that the
ensonified area is on the order of 65 times less (if spherical
spreading is assumed). Additionally, the mitigation measures require
that the Navy minimize helicopter dipping activities in the critical
habitat.
[ssbox] The Navy would conduct approximately 40 ship object
detection exercises (1-2 hours each) and 57 submarine object detection
exercises (1-2 hours each) annually while entering/exiting port (within
approximately 1 mile of shore). This means that only a subset of those
activities will occur between Nov 15 and April 15, approximately 41 if
one assumes they are distributed equally throughout the year, for
example. Additionally, mitigation measures indicate that the Navy shall
reduce the time spent conducting object detection exercises in the
critical habitat, contact FACSFACJAX to obtain latest whale sightings
in vicinity of critical habitat, and (to the extent operationally
feasible) avoid conducting training in vicinity of recently sighted
whales. Ships are required to maneuver to maintain at least 500 yds of
separation from any observed whale (consistent with safety of ship).
[ssbox] The Navy's model predicted that approximately 20 takes of
right whales by behavioral harassment would occur within the southern
NARW critical habitat (and no takes by injury or mortality).
Time and area restrictions are one of the most effective ways to
reduce impacts to protected species. By planning the limited sonar
exercises outlined above and implementing the specific mitigation
measures listed, the Navy has minimized, to the extent practicable, the
impacts to right whales in the southern critical habitat. NMFS
discusses the practicability and benefits of time and area restrictions
in the Mitigation EA.
(b) The potential impacts to mother-calf pairs from sonar are
specifically discussed in Potential Effects of Specified Activities on
Marine Mammals section of the proposed rule. However, as the commenter
suggests, the specific effects of MFAS on right whales and their calves
are not discussed because NMFS does not possess data to draw any
specific conclusions regarding effects. As the commenter suggests, the
loss of even one right whale would have serious effects on the
population; however, as discussed in the proposed rule and above, 20
instances of right whale harassment are expected to occur within the
southern right whale critical habitat (over the entire year, not just
from November to April) and none of these are modeled to be at
injurious levels. Additionally, this take estimate does not account for
the mitigation measures discussed in (a) above, which include not
approaching right whales within closer than 500 yds and not conducting
training within the vicinity of recently sighted whales, when feasible.
For these reasons and others (see Negligible Impact section of proposed
rule), NMFS was able to determine that the Navy's AFAST activities
would have a negligible impact on the species.
(c) The Navy does not plan to conduct any major ASW training
exercises using hull-mounted sonar in the Northeast. All of the
exercises in the Northeast will consist of smaller scale unit-level
exercises predominantly utilizing submarine sonar, active sonobuoys,
and torpedoes (see Table 3). In the Northeast, the submarine object
detection exercises would occur primarily in the near-shore submarine
transiting lanes exiting Groton, Connecticut and Norfolk, Virginia
(neither of which are near the important feeding areas the comment
refers to). As indicated in the rule, in the Northeast the Navy is
largely avoiding conducting any training in the NARW critical habitat,
with one exception: Torpedo exercises (a maximum of 32 MK-48 torpedo
runs at 15 minutes each or up to 24 lightweight MK-46 or MK-54
torpedoes) would occur in August through December (when right whales
are less likely to be present). However, the Navy included extensive
TORPEX mitigation measures that were worked out in a previous section 7
consultation with NMFS (see 216.244(a)(1)(xxviii)). Approximately 2000
sonobuoys (with 12 pings, spaced 30 seconds apart) would be used
annually. Time and area restrictions are one of the most effective ways
to reduce impacts to protected species. Based on the limited sonar
exercises outlined above and because of the specific mitigation
measures listed, NMFS believes that impacts to right whales and other
large whales feeding in important areas in the Northeast will be
minimal. NMFS discusses the practicability and benefits of time and
area restrictions in the Mitigation EA.
(d) NMFS' rationale for why right whales will not be injured is not
arbitrary. Although the Navy is proposing to conduct thousands of hours
(approximately 5,000 of hull-mounted) of MFAS operation (see Table 1),
several factors need to be considered. For example, the AFAST Study
Area comprises over 2,170,175 square nautical miles, the exercises are
spread out over the course of a year, and there are only approximately
350 right whales in the population (the number of whales is germane
because at the most basic level the potential for injury is directly
based on the likelihood that the ensonified area (above threshold)
around the MFAS sound sources will overlap with a right whale in space
and time--the fewer right whales there are, the less likely this is to
happen.) The model predicts 666 exposures to levels above NMFS'
acoustic threshold for behavioral harassment, but less than the level
associated with PTS (or injury). Acknowledging that right whales may be
somewhat harder to detect than other large whales, the Navy's modeled
takes, as discussed in the Negligible Impact Analysis section of the
proposed rule, do not take any mitigation measures or any likely marine
mammal avoidance into consideration. Navy lookouts are specifically
trained to detect anomalies in the water around the ship and both the
safety of Navy personnel and success in the training exercise depend on
the lookout being able to detect objects (or marine mammals)
effectively around the ship. The response to Comment 2, below, explains
more specifically why injury is not expected.
(e) Regarding ship strikes, the Navy's EIS concluded that based on
the implementation of Navy mitigation measures, especially during times
of anticipated NARW occurrence, and the relatively low density of Navy
ships in the Study Area, the likelihood that a vessel strike would
occur is very low (as NMFS indicated in the above comment, the low
abundance of NARWs also supports this prediction). In addition to
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the standard operating procedures to reduce the likelihood of
collisions, which include: (1) Use of lookouts trained to detect all
objects on the surface of the water (including marine mammals); (2)
reasonable and prudent actions to avoid the close interactions of Navy
assets and marine mammals; and (3) maneuvering to keep away from any
observed marine mammal, the Navy has issued extensive North Atlantic
right whale protective measures for all Fleet Forces training
activities (see 216.244(a)(3)). These measures, which were developed
with input from NMFS, include additional training requirements,