Taking and Importing Marine Mammals; Navy Training Activities Conducted Within the Northwest Training Range Complex, 69296-69326 [2010-27540]
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Federal Register / Vol. 75, No. 217 / Wednesday, November 10, 2010 / Rules and Regulations
Availability of Supporting Information
Extensive Supplementary Information
was provided in the proposed rule for
this activity, which was published in
the Federal Register on Monday, July
13, 2009 (74 FR 33828). 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.
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 218
[Docket No. 0906101030–0489–03]
RIN 0648–AX88
Taking and Importing Marine
Mammals; Navy Training Activities
Conducted Within the Northwest
Training Range Complex
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
NMFS, upon application from
the U.S. Navy (Navy), is issuing
regulations to govern the unintentional
taking of marine mammals incidental to
activities conducted in the Northwest
Training Range Complex (NWTRC), off
the coasts of Washington, Oregon, and
northern California, for the period of
October 2010 through October 2015.
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 effecting the least practicable
adverse impact on marine mammal
species or stocks and their habitat, as
well as requirements pertaining to the
monitoring and reporting of such taking.
DATES: Effective November 9, 2010
through November 9, 2015.
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:
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SUMMARY:
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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, notice of a
proposed authorization is provided to
the public for 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 National Defense Authorization
Act of 2004 (NDAA) (Pub. L. 108–136)
modified the MMPA by removing 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
In September 2008, NMFS received an
application from the Navy requesting
authorization for the take of individuals
of 26 species of marine mammals
incidental to upcoming Navy training
activities to be conducted within the
NWTRC, which extends west to 250
nautical miles (nm) (463 kilometers
[km]) beyond the coast of Northern
California, Oregon, and Washington and
east to Idaho and encompasses 122,400
nm2 (420,163 km2) of surface/subsurface
ocean operating areas. These training
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 NWTRC by
exposing them to sound from midfrequency or high-frequency active
sonar (MFAS/HFAS) or underwater
detonations. The Navy requested
authorization to take individuals of 26
species of marine mammals by Level B
Harassment and 13 individuals of 9
species by Level A Harassment. The
Navy’s model, which did not factor in
any potential benefits of mitigation
measures, predicted that 13 individual
marine mammals would be exposed to
levels of sound or pressure that would
result in injury; thus, NMFS is
authorizing the take of 13 individuals
per year by Level A Harassment.
However, NMFS and the Navy have
determined that injury can most likely
be avoided through the implementation
of the required mitigation measures. No
mortality of marine mammals is
authorized incidental to naval exercises
in the NWTRC.
Background of 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 (74 FR 33829).
Overview of the NWTRC
The proposed rule contains a
description of the NWTRC, including
both the Inshore and Offshore areas. The
description contained in the proposed
rule has not changed (74 FR 33829).
Description of 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
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related LOAs. The proposed rule
describes the nature and number of antisubmarine warfare (ASW) exercises,
anti-surface warfare (ASUW) exercises,
and mine warfare training (MIW)
exercises, involving both mid- and highfrequency active sonar (MFAS and
HFAS), as well as explosive
detonations. It also describes the sound
sources and explosive types used (74 FR
33828, pages 33829–33838). The
narrative description of the action
contained in the proposed rule has not
changed, with one exception and one
clarification indicated below. Tables 1,
2, and 3 list the types of sonar sources
and the estimated yearly use,
summarize the characteristics of the
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exercise types, and list the explosive
types used.
As a result of their Section 7
consultation with the U.S. Fish and
Wildlife Service, the Navy agreed to
make a small modification to their
activity. They agreed to not conduct
Explosive Ordnance Disposal (EOD)
underwater demolition training at the
Naval Magazine Indian Island site (1
event per year was previously included
in the proposed rule). Instead, that
training event will be conducted at the
Hood Canal training site, so there will
now be up to a total of two events per
year in Hood Canal (instead of 1). The
Navy further agreed that EOD will
utilize charge sizes of 1.5 lbs or less at
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the Hood Canal site, instead of the 2.5
lbs or less identified in the proposed
rule.
The Navy has carefully characterized
the training activities planned for the
NWTRC over the 5 years covered by
these regulations; however, evolving
real-world needs necessitate flexibility
in annual activities. NMFS has
attempted to bound this flexibility with
new language in the regulatory text (see
§ 218.110(c)) which allows for flexibility
in planned activities, provided it does
not affect the take estimates and
anticipated impacts in a manner that
changes our analysis.
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Description of Marine Mammals in the
Area of the Specified Activities
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Twenty-seven marine mammal
species have confirmed or possible
occurrence within the NWTRC,
including six species of baleen whales
(mysticetes), 16 species of toothed
whales (odontocetes), five species of
seals and sea lions (pinnipeds), and the
sea otter (mustelids). Sea otters are
under the jurisdiction of the Department
of the Interior and are not considered
further.) Table 4 summarizes their
abundance, Endangered Species Act
(ESA) status, population trends, and
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occurrence in the area. Seven of the
species are ESA-listed and considered
depleted under the MMPA: Blue whale;
fin whale; humpback whale; sei whale;
sperm whale; southern resident killer
whale; and Steller sea lion. The
proposed rule contains a discussion of
one species that is not considered
further in the analysis (the North Pacific
right whale) because of its rarity in the
NWTRC. The proposed rule also
contains a discussion of bottlenose
dolphins, but due to their
extralimitality, the impact analysis
concluded that this species will not be
taken by the Navy’s activity. The
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proposed rule also contains a discussion
of important areas, including southern
resident killer whale and Steller sea lion
critical habitat, and the gray whale
migration corridor. The proposed rule
also includes a discussion of marine
mammal vocalizations. Last, the
proposed rule includes a discussion of
the methods used to estimate marine
mammal density in the NWTRC. The
Description of Marine Mammals in the
Area of the Specified Activities section
has not changed from what was in the
proposed rule (74 FR 33828, pages
33838–33842).
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Brief Background on Sound
The proposed rule contains a section
that provides a brief background on the
principles of sound that are frequently
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referred to in this rulemaking (74 FR
33828, pages 33845–33846). 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
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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 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 NWTRC,
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 may potentially
affect marine mammals (some of which
NMFS would not classify as
harassment), as well as a discussion of
the potential effects of vessel movement
and collision (74 FR 33828, pages
33846–33862). 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 behaviorallymediated bubble growth) that have been
observed a limited number of times in
certain circumstances (the specific
events are also described) (74 FR 33828,
pages 33855–33860). The information
contained in Potential Effects of
Specified Activities on Marine
Mammals section from the proposed
rule has not changed.
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
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discussed here to the MMPA definitions
of Level A and Level B Harassment.
Mitigation
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 effecting the least
practicable adverse impact on such
species or stock and its habitat, paying
particular attention to rookeries, mating
grounds, and areas of similar
significance.’’ The NDAA of 2004
amended the MMPA as it relates to
military-readiness activities and the ITA
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
training activities described in the
NWTRC application are considered
military readiness activities.
NMFS reviewed the proposed
NWTRC activities and the proposed
NWTRC mitigation measures as
described in the Navy’s LOA
application to determine if they would
result in the least practicable adverse
effect on marine mammals, which
includes 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 effectiveness of the
‘‘military-readiness activity.’’ NMFS
determined that further discussion was
necessary regarding the use of MFAS/
HFAS for training in the Inshore Area
that contains the southern resident
killer whale critical habitat.
To address the concerns above, the
Navy clarified for NMFS that no training
utilizing MFAS/HFAS had occurred in
the Inshore Area of NWTRC for the last
six years, that it is not being conducted
now, and that there are no plans to
utilize MFAS/HFAS for training in the
Inshore Area (i.e., it is not part of the
Navy’s specified activity). This
information has been factored into
NMFS’ effects analysis. The Navy has
indicated that should their plans change
in the future they will request a new
LOA, which would likely require new
regulations, for the additional activities
within the NWTRC. The Navy further
explained that no explosive training
occurs in the Inshore Area other than
the annual detonation of four, up to 1.5–
2.5lb charges, which are not anticipated
to result in the take of marine mammals.
For these reasons, no take of killer
whales is anticipated to result from the
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Navy’s activities in the Inshore area and
none has been authorized.
NMFS’ proposed rule includes a list
of the Navy’s proposed mitigation
measures (74 FR 33828, pages 33863–
33867), which have been included in
the regulatory text of this document.
The following mitigation measure has
been added since the publication of the
proposed rule:
‘‘Naval vessels will maneuver to keep
at least 1,500 ft (500 yds) away from any
observed whale in the vessel’s path and
avoid approaching whales head-on.
These requirements do not apply if a
vessel’s safety is threatened, such as
when change of course will create an
imminent and serious threat to a person,
vessel, or aircraft, and to the extent
vessels are restricted in their ability to
maneuver. Restricted maneuverability
includes, but is not limited to, situations
when vessels are engaged in dredging,
submerged activities, launching and
recovering aircraft or landing craft,
minesweeping activities, replenishment
while underway and towing activities
that severely restrict a vessel’s ability to
deviate course. Vessels will take
reasonable steps to alert other vessels in
the vicinity of the whale. Given rapid
swimming speeds and maneuverability
of many dolphin species, naval vessels
would maintain normal course and
speed on sighting dolphins unless some
condition indicated a need for the vessel
to maneuver.’’
Based on our evaluation of the
proposed measures and other measures
considered by NMFS or recommended
by the public, NMFS has determined
that the required mitigation measures
(including the Adaptive Management
(see Adaptive Management below)
component) 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 proposed rule contains
further support for this finding in the
Mitigation Conclusion section (74 FR
33828, pages 33867–33868). During the
public comment period, a few
mitigation measures not previously
considered were recommended and
NMFS’ analysis of these measures is
included in the Response to Public
Comment section.
Research
The Navy provides a significant
amount of funding and support to
marine research. In the past five years
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the agency provided over $100 million
($26 million in FY08 alone) to
universities, research institutions,
federal laboratories, private companies,
and independent researchers around the
world to study marine mammals. The
U.S. Navy sponsors 70 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.
This research is directly applicable to
Fleet training activities, particularly
with respect to the investigations of the
potential effects of underwater noise
sources on marine mammals and other
protected species. Proposed training
activities employ active sonar and
underwater explosives, which introduce
sound into the marine environment.
The Marine Life Sciences Division of
the 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, which include the Marine
Resource Assessments and the Navy
OPAREA Density Estimates (NODE)
reports. 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
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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.
(tagging animals, measuring received
sounds, and evaluating behavior or
injuries) in the presence of activities
and non-activities will provide critical
information needed to further define the
impacts of active sonar training
exercises and other anthropogenic and
non-anthropogenic stressors. In
coordination with the Navy and other
Federal and non-federal partners, the
comparative study will be designed and
conducted for specific sites during
intervals of both the presence and
absence of anthropogenic activities such
as active sonar transmission or other
sound exposures to evaluate
demographics of morbidity and
mortality, presence of lesions, and cause
of death or stranding. Additional data
that will be collected and analyzed in an
effort to control potential confounding
factors includes factors such as average
sea temperature (or just season),
meteorological or other environmental
variables (e.g., seismic activity), fishing
activities, etc. All efforts will be made
to include appropriate controls (i.e., no
active sonar or no seismic);
environmental variables may, however,
complicate the interpretation of
‘‘control’’ measurements. The Navy and
NMFS along with other partners are
evaluating mechanisms for funding this
study.
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 for
and record the types of any pathologies
and diseases and investigate the
relationship with potential causal
factors (e.g., active sonar, seismic,
weather). The study will not be a true
‘‘cohort’’ study, because NMFS will be
unable to quantify or estimate specific
active sonar or other sound exposures
for individual animals that strand.
However, a cross-sectional or
correlational analyses, a method of
descriptive rather than analytical
epidemiology, can be conducted to
compare population characteristics, e.g.,
frequency of strandings and types of
specific pathologies between general
periods of various anthropogenic
activities and non-activities within a
prescribed geographic space. In the
long-term study, NMFS will more fully
and consistently collect and analyze
data on the demographics of strandings
in specific locations and consider
anthropogenic activities and physical,
chemical, and biological environmental
parameters. This approach in
conjunction with true cohort studies
Monitoring
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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.
Proposed Monitoring Plan for the
NWTRC
The Navy’s final Monitoring Plan for
the NWTRC may be viewed at NMFS’
web site: https://www.nmfs.noaa.gov/pr/
permits/incidental.htm#applications.
The Monitoring Plan for NWTRC has
been designed as a collection of focused
‘‘studies’’ (described fully in the NWTRC
draft Monitoring Plan) to gather data
that will allow the Navy to address the
following questions:
(a) Are marine mammals exposed to
MFAS/HFAS, especially at levels
associated with adverse effects (i.e.,
based on NMFS’ criteria for behavioral
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harassment, TTS, or PTS)? If so, at what
levels are they exposed?
(b) If marine mammals are exposed to
MFAS/HFAS in the NWTRC Range
Complex, 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/HFAS, what are their behavioral
responses to various levels?
(d) What are the behavioral responses
of marine mammals that are exposed to
explosives at specific levels?
(e) Is the Navy’s suite of mitigation
measures for MFAS/HFAS (e.g.,
measures agreed to by the Navy through
permitting) effective at preventing TTS,
injury, and mortality of marine
mammals?
The extent of the training utilizing
MFAS/HFAS in the NWTRC is
comparatively less than several of the
other training areas utilized by the Navy
and not every one of these original five
study questions will be addressed
within NWTRC. Rather, data collected
from NWTRC monitoring will be used to
supplement a consolidated range
complex marine mammal monitoring
report incorporating data from the
Navy’s Hawaii Range Complex,
Marianas Island Range Complex,
NWTRC, and Southern California Range
Complex. Monitoring methods proposed
for the NWTRC include a combination
of research elements designed to
support both Range Complex specific
monitoring, and contribute information
to a larger Navy-wide program. These
research elements include:
—Deployment of passive acoustic
monitoring (PAM) devices, and,
—Marine mammal tagging.
The monitoring techniques selected
for the NWTRC will be primarily
focused on providing additional data for
study questions (b), (c), and (d).
The amount of each type of
monitoring may vary from the summary
table or Monitoring Plan based on
annual discussions between NMFS and
the Navy regarding previous monitoring
results and effectiveness and in
accordance with the Adaptive
Management component of this rule,
however, the overall effort over the 5year period will remain approximately
equal to that laid out in the monitoring
plan.
This monitoring plan has been
designed to gather data on all species of
marine mammals that are observed in
the NWTRC; however, where
appropriate, priority will be given to
beaked whales, ESA-listed species,
killer whales, and harbor porpoises. The
Plan recognizes that deep-diving and
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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).
In addition to the Monitoring Plan for
MIRC, the Navy has completed an
Integrated Comprehensive Monitoring
Program (ICMP) Plan.
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. The Navy finalized a 2009
ICMP Plan outlining the program on
December 22, 2009, as required by the
2009 LOAs for the Hawaii Range
Complex (HRC), the Southern California
Range (SOCAL), and Atlantic Fleet
Active Sonar Training (AFAST). The
ICMP may be viewed at: https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm.
The ICMP is a developing program
that will be in place for the length of
this rule, and beyond, and NMFS and
Navy will evaluate it annually to
determine if it needs to be updated in
order to keep pace with advances in
science and technology and the
collection of new data. In the 2009
ICMP Plan, the Navy outlines three
areas of targeted development for 2010,
including:
1. Identifying more specific
monitoring sub-goals under the major
goals that have been identified.
2. Characterizing Navy Range
Complexes and Study Areas within the
context of the prioritization guidelines
described in the ICMP.
3. Continuing to Develop Data
Management, Organization and Access
Procedures.
The Navy shall comply with the 2009
ICMP Plan and continue to improve the
program in consultation with NMFS.
Changes and improvements to the
program made during 2010 (as
prescribed in the 2009 ICMP and
otherwise deemed appropriate by the
Navy and NMFS) will be described in
an updated 2010 ICMP and submitted to
NMFS by October 31, 2010 for review.
An updated 2010 ICMP will be finalized
by December 31, 2010. NMFS plans to
solicit public comments on the updated
ICMP in January, 2011 and the input
will be used to inform the 2011
Monitoring Workshop, the further
development of the ICMP, and,
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potentially, monitoring modifications in
the Navy’s 2012 monitoring plans.
Monitoring Workshop
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 monitoring pursuant to the
NWTRC rule as well as monitoring
results from other Navy rules and LOAs
(e.g., SOCAL, HRC, etc.). 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
Workshop, modifications would be
applied to monitoring plans as
appropriate.
Adaptive Management
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 is
evolving fairly quickly. 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
in the NWTRC in the Navy’s over 60
years of use of the area for testing and
training). NMFS has included an
adaptive management component in the
regulations, which will allow NMFS 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.
The following are some of the
possible sources of applicable data:
• Results from the Navy’s monitoring
from the previous year (either from
NWTRC 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
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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 NWTRC or
other locations, and involving
coincident MFAS/HFAS or 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 other
agencies or entities).
• Any information that reveals that
marine mammals may have been taken
in a manner, extent or number not
authorized by these regulations or
subsequent Letters of Authorization.
Mitigation measures could be
modified or added (or deleted) if new
data suggests 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 final rule are designed to
provide 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
both to compliance as well as ensuring
that the most value is obtained from the
required monitoring. The proposed rule
contains the reporting requirements for
the Navy (74 FR 33828, pages 33871–
33872), and these requirements remain
unchanged with the following
exception. The requirements as written
in the proposed rule include specific
due dates for each of the reports. NMFS
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and the Navy are coordinating a
workload plan to determine the best
times during every year to submit all of
the reports that the Navy is responsible
for under final rules for multiple Range
Complexes and training exercises.
Although the reports described will
always be submitted every year at a time
that allows for adequate analysis by
NMFS prior to the issuance of the
subsequent LOA, we want to allow
flexibility to change those dates yearly.
Therefore, the regulatory text below will
not specify the specific dates that the
reports are due, as the due dates will be
specified in the annual LOA.
Comments and Responses
On July 13, 2009 (74 FR 33828),
NMFS published a proposed rule in
response to the Navy’s request to take
marine mammals incidental to military
readiness training in the NWTRC and
requested comments, information and
suggestions concerning the proposed
rule. During the 30-day public comment
period, NMFS received comments from
the Marine Mammal Commission, the
Washington Department of Fish and
Wildlife, the Department of the Interior,
the Natural Resources Defense Council
(on behalf of the International Fund for
Animal Welfare, the Center for
Biological Diversity, Cetacean Society
International, Friends of the San Juans,
the Humane Society of the United
States, the Ocean Futures Society, the
Ocean Mammal Institute, People for
Puget sound, Davis Bain, and JeanMichel Cousteau), the Orca Network,
The Whale Museum, Turtle Island
Restoration Network (TIRN) and Center
for Biological Diversity (CBD), as well as
over two hundred members of the
public. The NRDC gained support for
their comments from over 54,000
members through form letters.
Introduction
As described elsewhere in this
document, 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
effecting the least practicable adverse
impact on such species or stock and its
habitat, paying particular attention to
rookeries, mating grounds, and areas of
similar significance.’’ NMFS’ decisions
regarding whether or not to require any
particular mitigation measure must
include a careful balancing of the likely
benefit of any particular measure to
marine mammals and the likely
effectiveness of the measure, with the
practicability of the measure, which (for
military readiness activities) includes
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consideration of the likely effect of that
measure on personnel safety,
practicality of implementation, and
impact on the effectiveness of the
‘‘military-readiness activity.’’
Because some of the comments
received reflect an incomplete or
inaccurate understanding of the nature
and scope of the Navy’s MFAS training
exercises, we will summarize and
clarify some issues up front that will
support multiple responses below. For
example, one commenter begins by
stating that the Navy contemplates
extensive sonar training. This is not the
case. In the NWTRC, the annual amount
of planned operation for the most
powerful surface hull-mounted MFAS
(which is responsible for the vast
majority of the takes) is 108 hours
annually. Comparatively, the annual
sonar use in other areas that the Navy
uses for training is far more extensive:
1670 hrs/yr in Hawaii, 2400 in the
Mariana Islands, 2470 in SOCAL, and
5110 off the Atlantic Coast. Another
significant difference is the fact that all
of the sonar exercises in the NWTRC are
approximately 1.5-hr exercises that
utilize a single surface hull-mounted
sonar, versus the major exercises within
other training areas, which may last for
several weeks, and use multiple
(sometimes 10 or more) surface hullmounted sonars simultaneously.
Another point that is germane to
several of the comments raised is the
typical way that the MFAS exercises
utilizing surface hull-mounted sonar
(TRACKEXs) are conducted, and the
areas in which they are typically
conducted. Approximately 10 percent of
the surface hull-mounted MFAS is
conducted in conjunction with the use
of the Portable Undersea Training Range
(PUTR), while the remaining 90 percent
is conducted primarily in-transit as the
vessel is moving from one point to
another, most often south through the
NWTRC towards the Southern
California Range Complex. The majority
of the in-transit MFAS use in the
NWTRC has taken place and is
projected to continue to take place at a
distance of 50 nm or greater from shore,
with infrequent training events
occurring between 12 and 50 nm from
shore. In-transit MFAS training is not
anticipated to occur inside of 12 nm.
The PUTR has been developed to
support ASW training in areas where
the ocean depth is between 300 ft and
12,000 ft and at least 3 nm from land.
The PUTR will not be utilized within
the Olympic Coast National Marine
Sanctuary (OCNMS).
In addition, the Navy provided
funding to NMFS’s Southwest Fisheries
Science Center (SWFSC) in the fall of
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2009, to update their newest spatial
predictive habitat model with composite
data from 1991 through 2008, the date
of the last U.S. West Coast marine
mammal survey. In the spring of 2010,
SWFSC completed this analysis which
provides finer scale (25-km) density
resolution for 12 of the most commonly
sighted species within the U.S. West
Coast EEZ including NWTRC. Results of
this effort will be published in a NMFS
Technical Report.
From 2009 through 2010, marine
mammal satellite tracking tag studies
funded by the Navy in Southern
California show that static plots of
marine mammal occurrence do not
provide the entire story on marine
mammal life history. Tagged baleen
whales and dolphins within Southern
California quite frequently move
significant distances. As part of the
Navy’s NWTRC Monitoring Plan,
presence\absence data will be collected
via offshore long-term passive acoustic
monitoring devices from Scripps
Institute of Oceanography, as well as
marine mammal satellite tagging.
In summary, the Navy, as part of its
NWTRC Monitoring Plan will continue
to contribute valuable scientific data in
collaborating with regional and national
scientific academic partners as to
marine mammal distributions within
the NWTRC.
Last, for the second year in a row, the
Navy is convening a workshop in
October to which marine mammal
experts have been invited. The Navy
will review its monitoring results from
the previous year and solicit
recommendations on future plans. More
formally, the Navy has been required by
multiple LOAs to hold a Monitoring
Workshop in 2011 that will include
both marine mammal experts and nongovernmental organizations. Here,
again, the Navy will provide a review of
previous monitoring results from
multiple range complexes and solicit
input. The goal of the 2011 workshop,
as laid out in the Integrated
Comprehensive Monitoring Program
Plan, is to comprehensively consider the
resources available in different ranges,
the data needs, and the species and
conditions present in different ranges in
order to identify the most appropriate
monitoring across range complexes that
will provide the most efficient
methodology and best results.
Additional Mitigation
Recommendations
Comment 1: NRDC and other
commenters recommended the
establishment of a panel of marine
mammal and oceanographic experts
with regional expertise on marine
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mammal distribution, abundance,
habitat, or population structure and
ecology, or habitat suitability modeling
to identify high-value habitat by
reviewing and analyzing the published
literature, survey data, and predictive
models. The use of sonar in such habitat
would be prohibited or subject to
additional operational measures to
ensure the greatest protection of animals
in the area.
Response: In January 2009, the
Administrator of the National Oceanic
and Atmospheric Administration
committed, in a letter to the Council on
Environmental Quality, to convene a
panel to identify important marine
mammal habitat, as described above.
This process has begun. Once the results
of that effort are available (anticipated
in 2011), NMFS will use them to inform
decisions related to geographic
mitigation requirements, both in
upcoming rules, as well as in rules that
have already been issued, through the
adaptive management provision
(described in the Adaptive Management
section above).
Comment 2: NRDC and several other
commenters recommended that NMFS
establish a protection area for northwest
harbor porpoise populations landward
of the 100-m isobath. Further, they
recommended that NMFS establish an
adjacent buffer zone to ensure that
exposure levels do not exceed 120dB
within the 100-m isobath. NMFS should
ask the Navy to prepare a nominal
propogation analysis for the coast to
determine what stand-off distances are
necessary to reduce exposures below the
120dB threshold. The NRDC further
notes that the vast majority of the takes
in the NWTRC are harbor porpoises.
Response: The Navy conducts about
99 percent of their MFAS activities in
the W–237 area, which extends out
approximately 200 nm from the coast of
the northern half of Washington state
(see page 2–5 of the Navy’s NWTRC
FEIS). Within the W–237, the 100-m
isobath extends out from the coast
approximately 40 nm at some points,
and up to 80 nm in the northern portion
near the Strait of Juan de Fuca. As noted
above in the introduction to this section,
the Navy has conducted, and plans to
conduct, the majority of their in-transit
MFAS activities beyond 50 nm from
shore, and has operated MFAS between
12 and 50 nm from shore infrequently
in the past. As mentioned above, the
PUTR (with which approximately 10
percent of the MFAS activities are
associated) is designed to be used in
depths of 300–1200 ft, so it is unlikely
that it will be used within the 100-m
isobath. Based on this general
operational plan, there is only a
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69307
relatively small area within the 100-m
isobath in which the Navy would
potentially operate MFAS, and this is
only a very small percentage of the
entire W–237 area that is available and
in which the Navy typically operates
MFAS. In order to adequately train,
however, the Navy needs to train within
a wide range of bathymetric conditions,
environmental conditions, and
operational conditions (i.e., proximity to
certain resources such as airfields), so it
is unlikely that they would completely
avoid the 100-m isobath.
In short, based on their general
operating plans, the overall size of the
area available for training and the fact
that they only plan to operate 108 hours
of surface hull-mounted sonar total
annually (but need to operate in a
variety of conditions, including depths
other than within the 100-m isobath), it
is likely that only a relatively small
subset of the 108 hours of MFAS will be
operated within the 100-m isobath, but
these hours are needed for operational
flexibility.
Regarding the establishment of an
additional buffer to ensure that the area
within the 100-m isobath is not
ensonified above 120 dB, the Navy has
done a propagation analysis and the
distance at which sound from a surface
hull-mounted sonar attenuates to 120
dB in the NWTRC is approximately 70
nm. A buffer of this nature would
extend out approximately 110–150 nm
from shore, rendering about 60–70
percent of the available MFAS training
area inaccessible and reducing access to
the vast majority of the bathymetric
relief that is necessary for effective
training. (NMFS notes that 120 dB is the
minimum received level at which we
have estimated that harbor porpoises
may be taken by behavioral (Level B)
harassment, and avoiding exposure
above this level is akin to avoiding take
completely, which would negate the
need for an incidental take
authorization.)
Last, NRDC notes that the vast
majority of the total takes in the NWTRC
are of harbor porpoises. This is correct;
of the approximately 130,000 total
annual authorized takes in the NWTRC,
119,000 are of harbor porpoises. This is
because harbor porpoises are considered
more sensitive to sound than many
other marine mammals and any
exposure above a received level of 120
dB is considered a take. However, of the
total harbor porpoise takes,
approximately 85 percent are
anticipated to occur at a received level
between 120 and 140 dB, from which
we would expect a comparatively less
severe response. Additionally, only
approximately 0.5 percent of these takes
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would result from exposures above a
received level of 160 dB, which is still
far below received levels associated
with injurious takes. In short, there are
more takes of harbor porpoises because
they are more sensitive to sound.
However, because we use a step
function to define their predicted
response, instead of a dose curve as we
do for other marine mammal species, a
large portion of the takes will likely
consist of the minimum response that
we would still consider a take.
Comment 3: NRDC and several other
commenters recommended that NMFS
provide additional protection for marine
mammals from the use of sonar within
the OCNMS, by specifically prohibiting
sonar usage in the OCNMS, or at a
minimum, limiting the exercises taking
place with the OCNMS by requiring
final approval from the Pacific Fleet
command, or using other means to
minimize sonar use. In support of this
recommendation, NRDC notes the
seasonal use of the area by migrating
gray whales, summer resident gray
whales that use the area for feeding, and
Southern Resident killer whales (SRKW)
that use the area for part of the year.
Response: The OCNMS is contained
within the NWTRC and the delineation
of the edge of the OCNMS essentially
follows the 100-m isobath. The Navy
will not deploy the PUTR within the
OCNMS. Otherwise, please see NMFS’
response to comment 2, above. Of
additional note, because of the seasonal
nature of the use of the area by some of
the species that the commenters
mention, those species’ potential
exposure to MFAS is likely an even
smaller proportion of the total hours, as
some of the hours of operation will
occur in months that they are not
present.
Although the comment addressed
here mentions only sonar training, it is
worth noting that the Navy does not do
any live bombing in the OCNMS waters
(i.e., BOMBEX and SINKEXs are
conducted outside the limits of the
OCNMS). Additionally, in their DEIS,
the Navy indicated their intent to create
a small underwater minefield training
range. Although they did not specify it
in the DEIS, they have since clarified
the fact that this small range will not be
in OCNMS waters.
Comment 4: NRDC and several other
commenters recommended that NMFS
identify the Greater Puget Sound as a
protection area (except for activities
occurring as part of the Keyport EIS) as
a condition of the proposed rule. They
further recommended that if Puget
Sound is not designated as a protected
area, NMFS should make the following
clarifications in its final rule:
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Æ That any use of MFA sonar for
training or maintenance in the Greater
Puget Sound would first require the
Navy to obtain an incidental take permit
given the potential for serious injury or
mortality to marine mammals in the
area;
Æ That the Navy has agreed to
conduct neither sonar training nor
maintenance activities in the Greater
Puget Sound without MMPA
authorization;
Æ That the Navy has internal checks,
in addition to the MMPA requirement,
on non-RDT&E sonar use in the Greater
Puget Sound (e.g., requiring approval
from Fleet Command).
Response: The Navy’s action does not
include the use of MFAS for training or
in-transit maintenance in the Greater
Puget Sound area, so it is not necessary
to designate the Greater Puget Sound
area as a Protection Area. The Navy
does not currently plan to use MFAS for
training or in-transit maintenance in the
Greater Puget Sound area, and they have
committed to obtaining a separate LOA
(which would require a new
rulemaking) if they plan to conduct
those activities in the Greater Puget
Sound area.
Additionally, the Navy has in place,
and has since June 2003, an internal
requirement wherein they must obtain
permission from the Commander Pacific
Fleet (CPF) before they may operate
MFAS for training, maintenance or
testing in Puget Sound. Since 2003, it
has been CPF policy to not approve
training, maintenance or testing use of
sonar systems for vessels underway
within Puget Sound. Pierside
maintenance/testing of sonar systems
within Puget Sound still requires CPF
approval, and may be approved by CPF
if it is not practical or feasible to
conduct alternate maintenance/testing
outside of Puget Sound. Since this
requirement was put into place, every
request to use MFAS underway for
training, maintenance, or testing in
Puget Sound has been denied, except on
the Nanoose Range.
Separately, pier-side maintenance was
not included as part of the proposed
action, either for the MMPA
authorization, or in the Navy’s EIS.
Pierside maintenance and testing of
sonars rarely involves emission of
sound. Most often the source is out of
the water and might emit only one or a
few low amplitude pings. The Navy is
currently compiling detailed
information on all pierside testing
activity nationwide and that
information will be included in the next
phase of environmental assessments in
2014. At this time the Navy does not
anticipate that there will be any
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additional risk to marine mammals from
pierside testing due to the infrequency
of sound emissions and the relative
rarity of marine mammals in the vicinity
of these sites.
Comment 5: NRDC and several other
commenters recommended that NMFS
establish a seasonal protection area in
certain canyons and banks on the
NWTRC that represent important
foraging habitat, particularly for
humpback whales. NRDC recommends
seasonal protection areas for the
‘‘Prairie,’’ Juan de Fuca Canyon,
Swiftsure Bank, Barkley and Nitinat
Canyons, and Heceta Bank, during the
main humpback whale feeding season
from June to October.
Response: With respect to some of
these specific areas, the Swiftsure Bank
is well within 50 nm of shore, and as
described above, it is unlikely that the
Navy will utilize in-transit MFAS there.
Additionally, Swiftsure Bank is within
the 100-m isobaths, which is not where
the PUTR is designed to be used, and
partially within the OCNMS, where the
PUTR will not be used. Heceta Bank is
located off the shore of Oregon, and 99
percent of the Navy’s MFAS use in the
NWTRC is conducted within the W–237
area, which is located off the coast of
Washington, so MFAS use is not likely
to occur there. Additionally, the Prairie
is an area that is less than 100 m deep,
so the PUTR is not likely to be deployed
there.
The Navy plans to conduct
approximately 108 hours of surface
hull-mounted MFAS use in the NWTRC
annually. Allowing for the fact that it is
not all planned in the months of JuneOctober, and not all planned in any one
of the specific areas noted in the
comment, only a small number of hours
of sonar is likely to occur in any of the
specific areas recommended for
protection by the commentors.
Generally speaking, because of the
small number of hours that the Navy
may be conducting MFAS sonar
training, the short duration of the
exercises, the use of only one single
hull-mounted sonar vessel, and the huge
area over which training is conducted,
the impracticability of designating
additional protective areas identified by
the commentors outweighs the likely
benefits. It requires a considerable
amount of planning, education, and
subsequent attention by the Navy to
establish and implement protective
areas. Furthermore, the Navy only
anticipates taking a small number of the
species for which the protected areas
would be established, by Level B
Harassment (15 humpback whales, 14
killer whales, and 4 gray whales), with
the exception of harbor porpoises
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(discussed in comment response 2).
Considering the density of marine
mammals and the likelihood of
encountering them in any location
during the course of a 1.5 hour period,
we cannot predict with sufficient
certainty that avoiding these areas
would necessarily result in a decrease of
takes.
In addition, as mentioned previously,
the Navy’s NWTRC Monitoring Plan
entails deploying long-term passive
acoustic monitoring devices at two
locations within the offshore NWTRC.
One such Navy funded device has been
in operation near Quinault Canyon
since 2004. This will be supplemented
with a second device which is currently
forecast for deployment near the Juan de
Fuca Canyon. Information from both
passive acoustic devices will provide
valuable scientific data on marine
mammal vocalizations and
anthropogenic sounds including
commercial ship noise or transitory
MFAS at these two locations. This
analytical approach continues to be
refined based on lessons learned from
similar deployments and data review in
Hawaii and Southern California.
Summary data from these devices will
be provided to NMFS and the public via
annual Navy monitoring reports.
Comment 6: The NRDC and several
other commenters recommended that
NMFS require avoidance of, or a
reduction of training activity within,
areas between 500 and 2,000 meters
depth with unusual bottom topography
(such as canyons), to provide additional
protection to beaked whales.
Response: The NRDC notes in their
comments that there are no particular
areas of known concentration for beaked
whales in the NWTRC, but that most
species appear to have a preference for
areas of the lower continental slope.
They may also be found in a wider
range of conditions, from slopes to
abyssal plain. First, NMFS may consider
requiring a geographic limitation on an
activity in a specific area of known
concentration of particular species of
animals, if the practicability analysis
(which includes consideration of the
nature of the activity, the likely benefits
to the species, and the practicability of
the measure) suggests that it will
accomplish the least practicable adverse
impact. However, we are less likely to
recommend the avoidance of all of a
type of area that an animal has a general
preference for, especially in a case like
this where the activity is comparatively
limited, because it is unclear whether
avoidance of all of the areas of this type
will result in the reduction of impacts
to the animals.
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More specifically, in the case of
beaked whales, we are only authorizing
the Level B take of 38 animals, so there
is only a very limited potential benefit
to making a huge tract of area
unavailable for training. Further, as
noted above, beaked whales may prefer
a wider variety of areas than previously
thought. In summary, only a portion of
the already few hours of planned MFAS
use will occur in this habitat, and it is
impracticable to completely prohibit the
Navy’s access to this particular depth
when they need to train in a wide
variety of circumstances.
Comment 7: The MMC recommended
that the rule require suspension of the
Navy’s activities if a marine mammal is
seriously injured or killed and the
injury or death could be associated with
those activities. The injury or death
should be investigated to determine the
cause, assess the full impact of the
activity or activities and determine how
activities should be modified to avoid
future injuries or deaths.
Response: NMFS’ regulations include
a provision for ‘‘General notification of
injured or dead marine mammals,’’
under which Navy personnel shall
ensure that NMFS is notified
immediately (or as soon as clearance
procedures allow) if an injured,
stranded, 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 provision
further requires the Navy to 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 of the animals (if
available).
It can take months to years to
complete the necessary tests and
analyses required to determine, with a
reasonable amount of certainty, the
cause of a marine mammal death—and
sometimes it is not possible to
determine it. All but one of the small
number of strandings that have occurred
around the world associated with MFAS
exercises have occurred concurrent to
exercises that would be considered
‘‘major’’, which typically involve
multiple surface vessels and last for a
much longer duration than the nonmajor exercises that occur in the
NWTRC (as described above in the
Introduction to this section). Hence,
NMFS (with input from the Navy)
determined that it was beneficial and
practicable to preemptively outline an
explicit plan (that includes a shutdown
requirement in certain circumstances)
for how to deal with a stranding that
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occurs during a major exercise, and
therefore Stranding Response Plans
were developed for all of the areas in
which major exercises are conducted.
Alternatively, for non-major exercises
(including all of the exercises in the
NWTRC), the general notification
provisions apply, which means that the
Navy would contact NMFS as soon as
clearance procedures allow and we
would determine how best to proceed at
that time.
Because so few strandings have been
definitively associated with MFAS
training in the 60+ years that the U.S.
and other countries that share
information have been conducting
MFAS training; the exercises conducted
in the NWTRC are of short duration and
involve only one surface hull-mounted
sonar; and investigations take a long
time and are not always conclusive, it
is not reasonable or practicable to
require the Navy to shut down every
time an injured or dead animal is found
in the vicinity pending the results of an
investigation that could take years to
conduct.
Comment 8: One commenter
recommended that MFAS not be
utilized off the coast of California from
June through October to protect seasonal
migration of blue and humpback
whales.
Response: The Navy plans to conduct
99 percent of their MFAS operation
(which consists of 108 hours of surface
hull-mounted sonar) within the W–237
area, which is located off the coast of
Washington. This means that MFAS
would be operated for only a few hours
annually off the coast of California, at
most.
Comment 9: One commenter
recommended that the Navy avoid
operating MFAS within 300 nm of the
OCNMS.
Response: A three hundred mile
buffer around the OCNMS would
entirely encompass the NWTRC, thereby
preventing the Navy from conducting
the proposed activity, which is not a
practicable option under the MMPA.
Comment 10: One commenter noted
that there is no reference to the Navy
going to the aid of stranded animals.
Response: NMFS, as the agency with
authority over marine mammal health
and stranding, does not want Navy
personnel or other untrained and
unpermitted individuals going to the aid
of stranded animals. Rather, as
described in the response to comment 7,
above, the Navy is required to notify
NMFS if they encounter an injured,
stranded, or dead animal, and NMFS
will respond as appropriate.
Comment 11: One commenter
recommended that we correct the
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statement ‘‘Southern resident killer
whales spend the majority of their time
in the Inshore Area from May/June
through October/November, although
they do make multi-day trips to the
outer coast,’’ to say ‘‘mid-June through
September.’’ The commenter further
recommended that the Navy’s sonar
activity be limited to the summer period
and when SRKWs have been located
well within the Inshore Area (e.g.
greater than ∼30 nautical miles east of
Cape Flattery for sonar activities lasting
less than 6 hours) by the listening
network (Salish Sea hydrophone
network—https://orcasound.net) and/or
sighting networks (The Whale Museum,
whale watch operators, Orca Network,
Center for Whale Research, etc.).
Response: The months originally
indicated are taken from NMFS’
Southern Resident Killer Whale
Recovery Plan. The commenter did not
offer a citation to support the alternate
months suggested and, therefore, NMFS
declines to make the suggested change.
Killer whales are rarely seen outside of
Puget Sound, and the Navy’s model
predicts that only 14 whales will be
taken by Level B Harassment annually.
Further, killer whales have a
comparatively high probability of
detection (Barlow, 2003a; Forney et al.,
1995) and there is little doubt that they
will be detected and MFAS shutdown
before they can be exposed to received
levels that might be associated with
more severe behavioral responses or
hearing sensitivity loss.
Considering the low likelihood of
impacts to killer whales from sonar in
the absence of the additional limitations
recommended by the commenter,
combined with the resources and effort
that would be necessary to maintain a
running knowledge of the location of
the killer whale pods, NMFS is not
requiring that the Navy implement the
recommended measure.
Comment 12: One commenter
believes that the Navy should restrict its
training operations to instrumented
ranges with acoustic systems that allow
real-time monitoring and mitigation for
marine mammals, such as the one it
operates off southern California.
Acoustic ranges apparently work well
for detecting baleen whales and may be
the only effective way to detect and
monitor beaked whales, but may not be
as effective for species (e.g., some
porpoises) that vocalize at very high
frequencies. The Navy should consider
developing such a range in the Pacific
Northwest.
Response: The Navy has several
instrumented ranges (Bahamas,
Southern California, and Hawaii) and
plans to install another off of
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Jacksonville, Florida. These ranges are
used regularly in Navy marine mammal
research and monitoring, and have
greatly contributed to marine mammal
distribution and abundance data in
these areas, as well as our
understanding of behavioral responses
to MFAS. However, they are not used
for real-time implementation of
mitigation (see Navy DEIS at 5–29).
Because of the need to train in a
variety of operational situations (i.e.,
proximity to different Navy resources)
and bathymetric/oceanographic
conditions, as well as the need to
conduct a large volume of training, the
Navy cannot limit its training to areas
with instrumented ranges. Additionally,
the conservation value of such a
limitation is unclear, as it would focus
a greater volume of MFAS use in areas
that also have high densities of marine
mammals and in some cases near areas
considered particularly important to
marine mammals.
Last, MFAS training occurs in
relatively low amounts annually in the
NWTRC and an instrumented range is
not currently needed or being
considered.
Comment 13: One commenter
questioned why dolphins or porpoises
that ‘‘deliberately’’ ride Navy ships’ bow
waves are not entitled to any
protections.
Response: The mitigation measure
indicates that ‘‘[i]f, after conducting an
initial maneuver to avoid close quarters
with dolphins or porpoises, the OOD
concludes that dolphins or porpoises
are deliberately closing to ride the
vessel’s bow wave, no further mitigation
actions are necessary while the dolphins
or porpoises continue to exhibit bow
wave riding behavior.’’ Navy personnel
first try and avoid the bow-riding
dolphins, and if that does not work,
they may continue without further
mitigation. Bow-riding is a common
occurrence with certain species, and
shutting down MFAS as frequently as
these animals are encountered would
seriously impact the Navy’s mission
effectiveness. The proposed rule
described the potential impacts from
this difference in mitigation (74 FR
33868), which is primarily that a
temporary loss of hearing sensitivity is
more likely to be incurred by these
species than others, but still of a
relatively brief and mild nature, and
NMFS was still able to make its
negligible impact determination for
these species.
Comment 14: One commenter
recommended that NOAA ensure that as
noise levels are ramped up, cetaceans
are not herded by the noise into
progressively shallower and shallower
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water where they may strand as beaked
whales did in the Bahamas (2000)
during Navy exercises.
Response: Although the Navy does
not utilize a ramp-up strategy for their
sound sources, there is no scenario in
the Navy’s action under which animals
would be herded into shallower water.
The Navy is not conducting any MFAS
training within the Greater Puget Sound
area and MFAS use of the Washington
Coast is primarily farther than 50 nm
from shore, with infrequent occurrences
between 12 and 50 nm from shore.
Mitigation Effectiveness
Comment 15: The MMC and several
other commenters recommended that
NMFS require the Navy to develop and
implement a plan to validate the
effectiveness of monitoring and
mitigation measures before beginning,
or in conjunction with, the proposed
military readiness training operations.
The MMC further notes that NMFS
appears to have concurred with the
Navy that the Navy’s mitigation efforts
will reduce Level A takes to 0 and that
the proposed mitigation measures are
sufficient.
Response: First, in response to the
second sentence above, the Navy has
estimated, through their modeling
efforts, the numbers of animals that will
be exposed to levels of sound or
pressure that would be thought to result
in Level A take (either through a
permanent loss of hearing sensitivity
from noise exposure, or tissue damage
from exposure to explosives) in the
absence of any mitigation. Those are the
numbers of Level A takes that they have
requested and NMFS is authorizing.
Hence, although NMFS believes that the
Navy’s mitigation will most likely be
effective at avoiding exposure to these
levels (which, in the case of MFAS
occur within 10m of the vessel), and
that many animals will avoid noises at
the levels necessary to incur a
permanent hearing sensitivity loss, we
are still authorizing the Level A take of
13 individuals of 9 species.
Marine mammal researchers have
developed detection probabilities that
estimate the likelihood of detecting
individuals of different species of
marine mammals from different
platforms, in different environmental
conditions, and at different distances.
As part of their Monitoring Plans in
other areas where training occurs, the
Navy has developed studies to
determine how well their watchstanders
detect marine mammals as compared to
experienced marine mammal observers.
Four of these comparison studies have
been conducted by the Navy this year
pursuant to the requirements of their
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LOAs for HRC, SOCAL, and AFAST and
when the results of these studies have
been fully analyzed, they will be
included in NMFS analysis of the
likelihood of Level A takes occurring. In
the meantime, we have conservatively
assumed that the mitigation is not
effective and that animals will be taken
by Level A Harassment as predicted by
the model, which assumes that animals
do not move away from a strong sound
source and that exposure at a high level
will never be avoided through detection
and implementation of a shutdown (or
non-startup).
If there are other studies that the
MMC has in mind to quantify mitigation
and monitoring effectiveness, we would
welcome specific recommendations.
Additionally, the Navy is required to
hold a Monitoring Workshop in 2011 (at
which MMC representatives will
hopefully be present) and the
discussions at that workshop are
intended to inform potential
modifications to the Navy’s existing
monitoring plans, if appropriate, as they
pursue a more comprehensive plan that
best utilizes the resources in each area
to gather the data that is most needed
and can most effectively be gathered in
a particular geographic area.
Comment 16: Several commenters
suggested that the Navy’s primary
method of reducing harm to marine
mammals, powering down or securing
sonar, is not effective. They indicated
that it is hard to sight whales on fastmoving ships, especially beaked whales,
and especially in certain conditions).
They further suggested that time/area
closures are a more effective form of
mitigation.
Response: While few mitigation
measures are 100 percent effective, the
Navy’s powerdown and shutdown
strategy is likely effective at avoiding
exposure to injurious levels of sound,
and does succeed in reducing exposures
of marine mammals (to varying degrees,
depending on the species and
environmental conditions) to higher
levels of sound that might be associated
with more severe behavioral responses.
The Mitigation Conclusion section of
the proposed rule describes our least
practicable adverse impact analysis (74
FR 33867).
NMFS agrees that geographic
mitigation can be an effective tool for
reducing impacts to marine mammals in
certain circumstances. However, we
have evaluated the potential areas
recommended for marine mammal
protection in the NWTRC and the
impracticability of the recommended
measures outweighed the likely benefit
to the species.
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Comment 17: To protect the Southern
Residents, NOAA should insist that the
Navy not operate SONARs or set off
explosions for any purposes short of
war, unless they know that orcas are not
within a distance where they would be
killed, injured or caused to panic.
Response: The Navy is currently
required to implement MFAS and
explosive powerdown and shutdown
requirements, which, considering the
high probability of detection of killer
whales, should ensure that killer whales
do not approach within a distance
where they would be injured or killed.
It is hard to know exactly what might
cause a killer whale to panic, but the
circumstances in which this behavior
has previously been observed in killer
whales in response to MFAS in this area
are no longer likely to occur in the
NWTRC, as no MFAS is operated within
the Greater Puget Sound area and sonar
is predominantly operated over 50 nm
off-shore.
Comment 18: NOAA should initiate
studies independent of the Navy in
order to determine if mitigation
measures in other range complexes are
working. If the measures are not
working no future permits should be
allowed until such time as alternative
mitigation measures are proposed and
tested. NOAA should also prepare to
conduct studies, independent of Navy
influence, in all Navy range complexes
prior to issuing a permit for NWTRC.
Response: NOAA has a duty to use
the best available data to conduct our
analyses and make our determinations.
To assess the likely success of
monitoring and mitigation measures, we
consider available literature and
examples of previous mitigation
implementation and monitoring reports.
We also require that the Navy submit
multiple monitoring and reporting
results annually for each range complex
and that the Navy compile this
information in a comprehensive manner
for an annual adaptive management
meeting. This meeting is used in
coordination with the adaptive
management components of the Navy
rules, which provide a mechanism for
mitigation or monitoring measures to be
modified, as appropriate, based on new
information.
The MMPA does not require that
NOAA initiate independent studies to
determine if different mitigation
measures are effective, nor do we
always have the resources to do so, and
nor is it necessary when information is
available through other means.
However, NOAA supports these efforts
when feasible, and as noted in the
introduction, in January 2009, NOAA
committed to convene a workshop to
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identify cetacean hotspots and the
information generated from that
workshop will be used to inform
management decisions, such as the
development of geographic mitigation
measures.
Finally, most of the Navy funded
range complex monitoring is conducted
by qualified academic and scientific
organizations. Information from these
researchers is presented to NMFS and
the public in annual monitoring reports,
and these researchers have a long
history of unbiased, successful scientific
publication based on these studies. This
kind of peer-review presentation of
scientific results will continue based on
monitoring efforts in the NWTRC and
other Navy range complexes.
Impact Assessment
Comment 19: The MMC
recommended that NMFS require the
Navy to conduct an external peer review
of its marine mammal density estimates,
the data upon which those estimates are
based, and the manner in which those
data are being used.
Response: Both NMFS and the Navy
use peer-reviewed science whenever it
is available and applicable, and NMFS
has encouraged the Navy to get the
models they use and data they gather
peer-reviewed. However, neither the
NEPA, the MMPA, nor the ESA require
that data or calculations used in the
analyses pursuant to these statutes be
peer-reviewed prior to making a
decision. Rather, NMFS and the Navy
are required to use the best available
science to inform our analyses.
In the context of the Navy’s NWTRC
EIS/OEIS and LOA application, the
marine mammal densities used in the
Navy’s impact analysis were derived
from estimates directly provided by
NMFS’s Southwest Fisheries Science
Center (SWFSC). As mentioned in a
previous comment response, SWFWC
continues to refine and improve this
density estimation process.
Also, while it is not the same as a peer
review, both the NEPA and MMPA
processes include a comment period in
which the public can specifically
recommend better ways to use the data
to estimate density, and which the Navy
and NMFS would need to address.
Further, the Navy is developing a new
systematic framework (that includes a
hierarchy of preferred methodologies
based on the data available in an area)
to estimate density in the analyses for
the rule renewals that will follow the
expiration of the MMPA rules for Navy
training issued in 2009, 2010, and 2011
(i.e., rules that would, if appropriate, be
issued in 2014 and later). The Navy has
indicated that they may pursue a peer
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review of this framework and NMFS has
encouraged them to do so.
Comment 20: NRDC included a copy
of their comments on the Navy’s EIS
and suggested that some of those
comments also pertained to the MMPA
authorization. Other commenters
mirrored several of the
recommendations that NRDC made in
these comments.
Response: NMFS has addressed the
issues that apply to our issuance of the
MMPA authorization below:
(1) Additional Mitigation—NRDC
recommends a suite of additional
mitigation measures for the Navy to
consider to protect various resources,
including marine mammals. NMFS and
the Navy have previously discussed
either the specific measures listed in
NRDC’s comments on the Navy’s EIS, or
the general class of mitigation
contemplated and have developed a
section for the EIS that discusses the
benefits of the proposed measure to
marine mammals, the likely
effectiveness of the measure, and the
practicability of the measure for Navy
implementation. Section 5.2.1.5 (begin
page 5–23) of the NWTRC EIS, entitled
Alternative Mitigation Measures
Considered But Eliminated, explains
why these measures are not included in
NMFS MMPA regulations and NMFS
refers readers to that document.
(2) Dr. Bain’s Critique of Risk
Function—NRDC includes a
comprehensive critique of the risk
function that the Navy (and NMFS) uses
to calculate takes. NMFS responded to
Dr. Bain’s comments in the Atlantic
Fleet Active Sonar Training final rule
(74 FR 4865) and refers readers to that
document.
Comment 21: One commenter
suggests that it would be premature for
NMFS to issue a take permit to the Navy
until NOAA conducts an independent
review of the adequacy of the Navy’s
proposed mitigation for the use of sonar.
Response: Pursuant to Section
101(a)(5)(A) of the MMPA, NMFS has
the responsibility of ensuring that any
incidental take authorization regulations
set forth the means of effecting the least
practicable impact, which requires a
review of the proposed mitigation
measures in the context of the benefit to
the species, the likely effectiveness of
the measure, and the practicability of
the measure for implementation. The
rationale behind our finding of least
practicable adverse impact was spelled
out in the Mitigation Conclusion section
of the proposed rule (74 FR 33868). The
MMPA does not require that NOAA
conduct an independent review.
However, NMFS continues to monitor
the Navy’s mitigation and monitoring
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effectiveness by reviewing annual
reports and using the adaptive
management mechanism in the rule to
inform decisions regarding whether
mitigation or monitoring should be
modified to increase their effectiveness.
Comment 22: One commenter
questioned why the Navy was not
required to have incidental take
authorization for explosive ordinance
activities in the in-shore region.
Response: As described in the
proposed rule, (74 FR 33837), because of
the more easily monitored inland
location of the explosive ordnance
disposal (EOD) ranges, the very limited
use of explosives (4 individual
explosions between 1.5 and 2.5 pounds)
proposed annually for these Mine
Countermeasure exercises, and the
likely effectiveness of the mitigation
(e.g., marine mammal take would only
be expected if a marine mammal were
exposed within less than 200 m of the
detonation, and the Navy does not
detonate explosives if a marine mammal
is seen within 700 m), take of marine
mammals is not anticipated or
authorized.
Comment 23: A few commenters
noted that NMFS should conduct
additional analysis and provide stronger
protection for marine mammals from
Navy training vessel operations
including collisions, discharges of
wastewater and garbage, and emissions
of air pollution and greenhouse gases.
Some commenters also objected to the
Navy’s use of depleted uranium in some
of their ordnance.
Response: NMFS did analyze (74 FR
33862) the potential impacts from vessel
strike in the proposed rule and added a
mitigation measure in the final rule to
minimize the likelihood of a strike (see
§ 218.114(a)(1)(ii)(I). Because of the
relatively low density of Navy traffic in
the NWTRC and the mitigation
measures (and the fact that the Navy has
not struck a whale there previously),
NMFS does not believe that the vessel
strike of a marine mammal is likely in
the NWTRC.
The Effects on Marine Mammal
Habitat section of the proposed rule
considered the impacts of expendable
materials and some of the chemicals
associated with Navy training activities
on marine mammal habitat (74 FR
33885) and determined that there would
be no significant impacts to marine
mammal habitat. Additionally, NMFS’
Biological Opinion (page 192–195)
covering the Navy’s training activities in
the NWTRC, as well as NMFS’ issuance
of an MMPA authorization, analyzed the
effects of the chemicals expended by the
Navy’s ordnance and projectiles and
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found they were unlikely to adversely
impact ESA-listed marine mammals.
The Navy’s NWTRC EIS addresses
discharges and emissions resulting from
the Navy’s training activities. The Navy
complies with all state and Federal
requirements related to water and air
quality. Based on the Navy’s analysis,
NMFS does not believe that wastewater
or garbage discharge or emissions will
result in the take of marine mammals or
significantly impact marine mammal
habitat adversely.
Separately, none of the surface
combatant ships stationed in the Pacific
Northwest, which are the ships that do
the preponderance of training at sea in
the Pacific Northwest, have depleted
uranium rounds onboard. Subsequent to
public release of the Draft EIS/OEIS,
Commander Pacific Fleet directed that
all Pacific Fleet ships offload all
depleted uranium rounds at the earliest
opportunity. This change is reflected in
the Final EIS/OEIS in Section 2.4.1.1,
which indicates that depleted uranium
use is no longer included in the Navy’s
Proposed Action.
Comment 24: One commenter
suggested that the mitigation measures
with regard to Navy vessels operating at
‘‘safe speeds’’ to avoid collisions with
marine mammals are unrealistic. There
is no such thing as a safe speed due to
the fact that Navy vessels do not stop,
turn or slow down like small speed
boats or automobiles. Thus, avoiding a
collision would be impossible because it
takes thousands of yards to turn a vessel
or slow it down. Marine mammals
surface to breathe sporadically and are
not seen on the surface often enough to
give enough warning time to avoid
collisions.
Response: Avoiding collisions is
difficult for large ships. However, some
Navy vessels are fairly maneuverable,
even at speed, and the more vigilant the
watchstanders are (i.e., the earlier a
whale is sighted), the more likely a
collision can be avoided. Mitigation
measures are intended to reduce the
likelihood of ship strikes to the lowest
level possible. In the case of the
NWTRC, which has comparatively low
Navy traffic and in which a Navy vessel
has not previously struck a whale,
NMFS believes that vessel strike is
unlikely.
Comment 25: One commenter
suggests that the Navy’s assumption of
a ‘‘uniform and stationary distribution of
marine mammals,’’ would result in gross
underestimation of potential exposures
in all areas, seasons, or circumstances
involving aggregations of animals
engaged in mating, birthing, feeding,
migrating, and other common activities
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that often concentrate large numbers of
animals in one area.
Response: This statement is incorrect.
Given the same total number of animals
in an area (and the Navy used the best
available survey information to inform
their density estimates), over a long
amount of time, you would encounter
the same number of animals if they were
evenly distributed as if they were
clumped (unless you were selectively
going to the places that they were
clumped, which will not occur here).
With a uniform distribution you would
encounter marine mammals more often,
but only one at a time, whereas with a
clumped distribution, you would
encounter them far less frequently, but
in higher numbers at one time. Given a
short amount of time (for example, the
short duration of the MFAS activities in
the NWTRC), a uniform distribution
might be more likely to overestimate
takes, because with a clumped
distribution, you are far less likely to
encounter groups of animals during the
short duration of the actual exercises.
Comment 26: One commenter states
that the proposed rule assumes that
because effects were not detected over
the last 60 years, they never occurred,
while at the same time, the proposed
rule acknowledges that no monitoring
has occurred during this period.
Response: NMFS does not make this
assumption (see 74 FR 33887–33888).
The Navy has been conducting MFAS/
HFAS training exercises in the NWTRC
Range Complex for over 60 years.
Although the Navy has not conducted
monitoring specifically in conjunction
with training exercises in the past,
people have been collecting stranding
data in the NWTRC Range Complex for
approximately 30 years. We further state
that although 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 marine
mammals were being harmed by the
Navy training exercises with any
regularity, more evidence would have
been detected over the 30-yr period.
Comment 27: If the whales do not
reach Alaska because they are all
disoriented from sonar, bombings, etc.,
does this not affect the traditional
Alaskan Native hunting grounds?
Response: None of the species (or
populations) of whales that Alaska
natives currently hunt are present in the
NWTRC (bowhead or beluga whales).
Comment 28: One commenter had the
following comment: Mooney, et al.
(2009) have just demonstrated hearing
loss in porpoises exposed to U.S. Navy
MFA sonar ping recordings. Loss of
auditory sensitivity could be as
catastrophic for SRKWs (porpoises) as
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stranding. Because Navy underwater
noise pollution could—in a worst case
scenario—exacerbate difficulties the
SRKWs may already be experiencing
hearing the echolocation reflections
from their rare salmonid prey (Au, 2004)
due to vessel noise, the commenter has
serious concerns about the proposed
rule, and particularly the Killer Whale
section on page 33890.
Response: The proposed rule
discusses both the likelihood of TTS
occurring as a result of MFAS exposure
(unlikely due to how close an animal
would need to be to the source, the
tendency of many marine mammals to
avoid loud sounds at some distance, and
the likely success of mitigation
measures, especially for highly visible
killer whales) and the likely overall
impact of TTS if it should occur in these
circumstances (minimal, short in
duration and severity because of the
short duration that an animal would
likely be able to remain in close
proximity to the source given the
moving vessel and the continued
likelihood of mitigation detection).
Additionally, the Navy estimated that
only 14 killer whales would be exposed
to levels associated with Level B
Harassment and that 0 would be
exposed to levels associated with TTS,
assuming no mitigation. In short,
because of the low hours of total MFAS
use, the short duration of each exercise,
the fact that it is far from shore and does
not take place in Puget Sound (where
killer whales are known to concentrate
in certain parts of the year, and where
there are bathymetric conditions that
have been associated with more severe
responses to MFAS), killer whales are
highly unlikely to incur TTS from the
MFAS exercises in the NWTRC.
Comment 29: One commenter
suggested that NMFS made an incorrect
statement in the proposed rule:
‘‘Southern resident killer whales are
very vocal, making calls during all types
of behavioral states.’’ They indicated
that, on the contrary, it is well known
that entire pods of SRKWs remain
completely silent during the resting
behavioral state.
Response: This is a valid correction.
NMFS did not mean to imply that killer
whales vocalized while they are resting.
A corrected sentence would read
‘‘Southern resident killer whales are
very vocal, making calls during almost
all types of behavioral states.’’
Comment 30: Several comments made
comments related to the analysis of
cumulative impacts. One commenter
specifically suggested that NMFS
consider the cumulative impacts of
several specific military activities that
would likely occur in the area of the
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NWTRC (e.g., the Keyport expansion,
and the explosives handling wharf at
Naval Base Kitsap Bangor). Other
commenters suggested that the Navy
fails to consider the cumulative impacts
of toxic chemicals on marine mammals.
Another commenter suggested that the
Navy has not considered the cumulative
and synergistic impacts of ‘‘taking’’
marine mammals by exposure to MFAS
from all of the Navy’s range complexes.
Another commenter suggests that NMFS
and the Navy assume that the entire
batch of proposed Navy actions will
take place in a pristine environment and
do not take into account their
contributions to or exacerbation of
existing conditions such as global
climate change, acidification of the
oceans, rising ocean levels, global ocean
and atmospheric pollution, warming
ocean waters, increased storm activities,
global extinctions, and other disasters.
Response: NMFS participated as a
cooperating agency in the development
of the Navy’s NWTRC EIS and has
adopted it to support our issuance of
incidental take regulations and LOAs.
NMFS discussed with the Navy the
specific examples the commenter raised
of activities that should be included in
the cumulative impact analysis and they
are included, as appropriate (i.e.,
considering the location of the activity
and the anticipated impacts) in the
FEIS. The FEIS contains a thorough
analysis of potential cumulative effects,
including pollutants and toxic
chemicals. 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
implementation of our statutory
authorities (Endangered Species Act
(ESA), NEPA, Magnuson-Stevens
Fishery Conservation and Management
Act, Coastal Zone Management Act, etc.)
and more directly through policy and
other actions, 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.
Regarding the consideration of the
cumulative or synergistic effects of
sonar conducted in all of the Navy’s
major range complexes the Navy has
considered the cumulative impacts of
sonar from different range complexes if
they are adjacent or nearby. However,
generally speaking (on the West Coast
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especially), Navy range complexes are
not in close proximity to one another
and therefore the Navy has not
considered the cumulative impacts of
sonar use. Additionally, the vast
majority of the impacts to marine
mammals expected from sonar exposure
are behavioral in nature, comparatively
short in duration, and not of the type or
severity that would be expected to be
additive for the portion of marine
mammals that might travel between
range complexes.
Last, NMFS and the Navy have
considered how the Navy’s action
interacts with global conditions, such as
climate change. The NWTRC FEIS notes
that recent observed changes due to
global warming include shrinking
glaciers, thawing permafrost, a
lengthened growing season, and shifts
in plant and animal ranges
(Intergovernmental Panel on Climate
Change 2007). Also, predictions of longterm environmental impacts due to
global warming include sea level rise,
changing weather patterns with
increases in the severity of storms and
droughts, changes to local and regional
ecosystems including the potential loss
of species, and a significant reduction in
winter snow pack. The Cumulative
Impacts chapter of the NWTRC FEIS
includes a discussion of climate change,
greenhouse gases and other pollutants,
and how the Navy’s action will
contribute to these global issues. The
FEIS also highlights several goals that
the Secretary of the Navy has
established for reducing the Navy’s
consumption of fossil fuels, including:
• Mandate that energy usage,
efficiency, life-cycle costs and other
such factors be part of the Navy’s
decision when acquiring new
equipment or systems, as well as
vendors’ efficiency or energy policies.
• Cut petroleum use by half in the
Navy’s fleet of commercial vehicles by
2015, by phasing in new hybrid trucks
to replace older ones.
• Procure half the power at Navy
shore installations from alternative
energy sources—including wind or
solar—by 2020, and where possible,
supply energy back to the grid, as the
Navy does today at Naval Air Weapons
Station China Lake, California.
• Reach the point that half the energy
used throughout the Navy Department,
including in ships, aircraft, vehicles and
shore stations, comes from alternative
fuel or alternative sources by 2020.
Today that percentage is about 17
percent.
Monitoring and Reporting
Comment 31: One commenter
suggested that it would be premature for
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NMFS to issue a take permit to the Navy
until the public has had a chance to
review the Monitoring Plan proposed
for the NWTRC.
Response: NMFS made the draft
Monitoring Plan available on its
webpage for the public to review during
the public comment period.
Comment 32: One commenter
suggests that the Navy should assist in
extending underwater monitoring for
marine mammal sounds to the outer
coast of Washington state.
Response: The Navy’s Monitoring
Plan (https://www.nmfs.noaa.gov/pr/
permits/incidental.htm#applications)
includes the deployment, and
subsequent monitoring, of two passive
acoustic devises on the outer coast of
Washington.
Comment 33: One commenter
suggested that the Navy training DVD is
inadequate for Navy observers.
Response: The primary duty of the
watchstanders on Navy vessels is to
detect objects in the water, estimate
their distance from the ship, and
identify them as any of a number of
inanimate or animate objects that are
significant to a Navy exercise or as a
marine mammal so that the mitigation
can be implemented. Navy
watchstanders go through extensive
training to learn these skills, and the
Marine Species Awareness Training is
used to augment it with some marine
mammal specific information that will
make them aware of some cues that they
may not otherwise have learned and
may contribute to their collection of
slightly more accurate and descriptive
information in their reports. However,
watchstanders are not expected to
identify marine mammals to species and
they are not expected to provide indepth behavioral or status information
on marine mammals.
Alternatively, for the Monitoring
Plans that the Navy develops and
implements, professional biologists and
scientists, with extensive marine
mammal field experience, develop and
conduct the data collection, and do the
subsequent analysis.
Comment 34: NMFS has prioritized
beaked whales in the Navy’s proposed
Monitoring Plan for the area (74 FR
33870). This prioritization should
include a firm, multi-year commitment
to sponsor fine-scale surveys with the
aim of identifying important beaked
whale habitat for avoidance.
Response: The Navy’s current
monitoring commitment includes the
deployment of passive acoustic
monitoring hydrophones off shore of
Washington as well as tagging studies,
both of which allow for a focus on
beaked whales and will likely collect
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valuable information. In 2011, the Navy
will hold a Monitoring Workshop, in
which (with expert and public input)
they will be comprehensively reevaluating their monitoring priorities
and plans (see Introduction to
Monitoring section, above), and may
modify this plan, as appropriate.
Comments 35: We recommend that
NMFS increase its reporting
requirements for the Navy to provide
information on (1) its use of midfrequency sonar (e.g., times, locations),
which would greatly assist in analyzing
and understanding the impacts of this
sonar on marine mammals, and (2) the
locations of southern resident killer
whales and other marine mammals
detected during its various monitoring
efforts along the west coast.
Response: For major MFAS training
exercises (which do not occur in the
NWTRC), the Navy is required to
provide the times and locations of their
MFAS use and the locations of the
individual animals detected by their
watchstanders. For non-major MFAS
exercises (like those in the NWTRC), the
Navy watchstanders implement the
mitigation measures, but are not
required to keep a written record of each
animal seen because it is logistically
difficult given the existing resources.
Also for non-major exercises, the Navy
is required to, to the extent practicable,
develop and implement a method of
annually reporting non-major training
utilizing hull-mounted sonar that
presents an annual (and seasonal, where
practicable) depiction of non-major
training exercises geographically across
NWTRC.
The Navy also has a monitoring plan
that includes the use of hydrophones to
detect whale calls, and which will also
utilize animal tagging. The results of the
Navy’s monitoring plan will be made
available annually.
Other
Comment 36: Multiple commenters
requested an extension on the 30-day
public comment period on the MMPA
proposed rule for the NWTRC. Another
commenter suggested that in the future,
NMFS allow 60 days for public
comment on Navy training rules.
Response: NMFS extended the public
comment period by 7 days. Of note, the
public comment period for the Navy’s
NWTRC DEIS was extended three times
and the total comment period was 105
days. NMFS is currently working with
the Navy to develop scheduling plans
for the next round of training activities
for which the Navy plans to request
incidental take authorization. NMFS
intends to include 60 days for public
comment on these proposed rules.
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Comment 37: NMFS should hold back
on approving marine mammal takes
under the proposed MMPA rule for the
NWTRC until the Presidential Ocean
Policy Task Force process is complete.
Response: NOAA is committed to the
goals of the Ocean Policy Task Force.
However, the intent is not to cease
conducting our required regulatory
actions while the details of
implementation are being worked out.
Additionally, the Ocean Policy Task
Force strategy does not yet contain a
level of detailed information that could
be applied to this specific action. The
MMPA mandates that NOAA ‘‘shall
issue’’ the incidental take authorization
if we are able to make the necessary
findings. When the Task Force has
produced a plan containing a level of
detail that is applicable to MMPA
authorizations under 101(a)(5)(A), it
will be applied to this program. In the
interim, NOAA will continue to comply
with the MMPA requirements in a
timely manner.
Comment 38: Many commenters
expressed general opposition to Navy
activities and NMFS’ issuance of an
MMPA authorization, citing general
concerns about the health and welfare of
marine mammals.
Response: NMFS appreciates the
commenters’ concern for the marine
mammals that live in the area of the
Navy’s training activities. The MMPA
directs NMFS to issue an incidental take
authorization if certain findings can be
made. NMFS has determined that the
Navy’s NWTRC training activities will
have a negligible impact on the affected
species or stocks. Additionally, NMFS
has worked with the Navy to develop
mitigation measures that help minimize
the impacts to marine mammals and a
monitoring plan that will increase our
understanding of the marine mammals
in the area and their responses in the
presence of marine mammals.
Therefore, we are issuing the necessary
governing regulations and plan to issue
the requested MMPA authorization.
Comment 39: Several commenters
recommended that the Navy share more
of the information that they have access
to with the public, for example:
• The Navy could make a significant
contribution to the public’s
understanding of the whereabouts of
killer whales by providing sighting data
from their bases and ships as well as
including hydrophones on the
oceanographic buoys and tidal energy
projects they are employing in the
Sound.
• The Navy could utilize their
existing infrastructure to provide the
public (or at least independent
scientists) with the ability to listen to
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the underwater soundscape on the outer
coast of Washington.
• The Navy could share information
about the locations of orcas with
civilian agencies and organizations that
seek to track the location of the orcas.
Response: Following are responses to
the specific bullets above:
• The reporting of killer whale
sightings from transitory Navy ships
would be of little value, given the vast
tracts of ocean traversed in which
sightings would not be obtained, the
logistic difficulties of getting such
reports in a useable and timely manner
from the ships to outside Navy
organizations, and the lack of useable
scientific detail in a generic report of
‘‘killer whale’’ (no way to know if
inshore or other killer whale stock). The
shore based infrastructure is not part the
Navy’s LOA authorization for the
NWTRC, nor is the Navy seeking MMPA
authorization within inshore
Washington State waters. The Navy’s
offshore monitoring program which
includes passive acoustic monitoring
will provide more scientifically robust
information as to specific killer whale
stocks detected and the periodicity of
those detections, a far stronger and more
useful approach than individual ship
sightings.
• The Navy has no real-time
infrastructure in-place for offshore
passive acoustic ‘‘listening’’. Under the
NWTRC Monitoring Plan, the Navy is
proposing to deploy two of Scripps
Institute of Oceanography Highfrequency acoustic recording packages
(HARP) within this area (https://
cetus.ucsd.edu/). Given the distance
from shore, depths of deployment (800–
1000 m), and current technology
limitations, there is no real-time
listening available. Scripps services
these devices approximately every 4–5
months to retrieve hard drives. New
hard drives are inserted and the HARP
re-deployed back into the ocean. The
retrieved hard drive is then returned to
the laboratory for analysis which can
take some time to complete. Results
from these deployments will however
be provided to the NMFS and the public
in the Navy’s annual monitoring report
for the NWTRC.
• All of the Navy monitoring results
and summaries for the NWTRC will be
made available to the NMFS and the
public via annual monitoring reports. If
detected, presence/absence
vocalizations from offshore stocks and
inshore resident stocks of killer whales
will be reported. As described in the
Navy’s draft Monitoring Plan for the
NWTRC, some results from the Quinault
HARP do contain killer whale
detections (see Oleson, E.M., J.
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Calambokidis, Erin Falcone, and Greg
Schorr and J.A. Hildebrand. 2009.
Acoustic and visual monitoring for
cetaceans along the outer Washington
coast-Technical Report, July 2004–
September 2008. Prepared for U.S.
Navy. Naval Postgraduate School,
Monterey, CA. NPS–OC–09–001. 45 pp.)
Comment 40: In considering the U.S.
Navy’s plans to use loud sonars and to
set off underwater explosions, it is
imperative that NOAA be just as careful
with the Navy with its fleets of
generators of potentially lethal noises as
NOAA is being with respect to whale
watch boats and kayaks.
Response: The Navy requested
(pursuant to the MMPA) authorization
to take marine mammals during their
training exercises, which utilize sonar
and explosives. In order to issue the
authorization and comply with section
101(a)(5)(A) of the MMPA, NOAA must
make certain findings and set forth
appropriate mitigation and monitoring
measures, which we have done.
Additionally, where ESA-listed species
are affected, and where NOAA proposes
to authorize take, NOAA must evaluate
those impacts pursuant to the ESA in a
formal consultation, make certain
findings, and issue an incidental take
statement, which we have done.
Alternately, in the case of whale
watching boats and kayaks, those
entities have not engaged in formal
consultation under the ESA, nor do they
have authorization under the MMPA to
take marine mammals. Rather, NOAA
has developed regional guidance
regarding avoidance distances that are
intended to completely avoid the take of
killer whales. Consequently (and
because the activities are completely
different), the protective measures are
different—the Navy is allowed to take
marine mammals, but still has
minimizing measures, whereas
whalewatchers and kayakers have
required measures to ensure that they
do not take killer whales at all.
Comment 41: Some comments
addressed the protection of resources
other than marine mammals (e.g.,
turtles) or addressed activities other
than the take authorization (e.g., the
designation of critical habitat). Some
comments misrepresented the
information contained in the proposed
rule (e.g., ‘‘NMFS should not allow the
death of millions of marine mammals’’).
Response: NMFS considered these
types of comments inapplicable and
does not address them further here.
Estimated Take of Marine Mammals
As mentioned previously, one of the
main purposes of NMFS’ effects
assessments is to identify the
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permissible methods of taking, meaning:
The nature of the take (e.g., resulting
from anthropogenic noise vs. from ship
strike, etc.); the regulatory level of take
(i.e., mortality vs. Level A or Level B
Harassment) and the amount of take. In
the Potential Effects of Exposure of
Marine Mammals to MFAS/HFAS and
Underwater Detonations section, NMFS
identified the lethal responses, physical
trauma, sensory impairment (permanent
and temporary threshold shifts and
acoustic masking), physiological
responses (particular stress responses),
and behavioral responses that could
potentially result from exposure to
MFAS/HFAS or underwater explosive
detonations. In this section, we will
relate the potential effects to marine
mammals from MFAS/HFAS and
underwater detonation of explosives to
the MMPA statutory definitions of Level
A and Level B Harassment and attempt
to quantify the effects that might occur
from the specific training activities that
the Navy is proposing in the NWTRC.
In the Estimated Take of Marine
Mammals section of the proposed rule,
NMFS relates the potential effects to
marine mammals from MFAS/HFAS
and underwater detonations (discussed
in the 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
that analysis are discussed individually
below.
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Definition of Harassment
The Definition of Harassment section
of the proposed rule contains the
definitions of Level A and Level B
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Harassment, 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 74 FR 33828,
pages 33872–33873. 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 (74 FR 33828,
pages 33873–33880). No changes have
been made to the discussion contained
in this section of the proposed rule.
Estimates of Potential Marine Mammal
Exposure
The proposed rule describes in detail
how the Navy estimated the take that
will result from their proposed activities
(74 FR 33828, pages 33880–33881),
which entails the following three
general steps: (1) A propagation model
estimates animals exposed to sources at
different levels; (2) further modeling
determines the number of exposures to
levels indicated in criteria above (i.e.,
number of takes); and (3) post-modeling
corrections refine estimates to make
them more accurate. More information
regarding the models used, the
assumptions used in the models, and
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the process of estimating take is
available in Appendix D of the Navy’s
DEIS for NWTRC.
Table 5, which is identical to the
Table 8 in the proposed rule with a few
minor corrections (including the
reduction from 1 to 0 of Level A
Harassment takes of blue whales and
Steller sea lions), indicates the number
of takes that were modeled and that are
being authorized yearly incidental to the
Navy’s activities, with the following
allowances. The Navy has carefully
characterized the training activities
planned for the NWTRC over the 5 years
covered by these regulations; however,
evolving real-world needs necessitate
flexibility in annual activities, which in
turn is reflected in annual variation in
the potential take of marine mammals.
Where it was mentioned more generally
in the proposed rule, NMFS has now
included language bounding this
flexibility in the regulatory text (see
§ 218.112(c)). These potential annual
variations were considered in the
negligible impact analysis and the
analysis in the proposed rule remains
applicable. The new language indicates
that after-action modeled annual takes
(i.e., based on the activities that were
actually conducted and which must be
provided with annual LOA
applications) of any individual species
may vary but will not ultimately exceed
the indicated 5-year total for that
species by more than 10 percent and
will not exceed the indicated annual
total by more than 25 percent in any
given year; and that modeled total
yearly take of all species combined may
vary but may not exceed the combined
amount indicated below in any given
year by more than 10 percent.
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Therefore, NMFS is not authorizing
mortality.
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Mortality
Evidence from five beaked whale
strandings, all of which have taken
place outside the NWTRC and 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
active sonar, steep bathymetry,
constricted channels, strong surface
ducts, etc.) may result in strandings,
potentially leading to mortality.
Although these physical factors believed
to have contributed to the likelihood of
beaked whale strandings are not
present, in their aggregate, in the
NWTRC, scientific uncertainty exists
regarding what other factors, or
combination of factors, may contribute
to beaked whale strandings. However,
because none of the MFAS/HFAS ASW
exercises conducted in the NWTRC are
major exercises employing multiple
surface vessels, the exercises last 1.5
hours or less, and only 65 exercises are
planned (for a total of about 100 hours
of surface vessel sonar operation),
NMFS and the Navy believe it is highly
unlikely that marine mammals would
respond to these exercises in a manner
that would result in a stranding.
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Effects on Marine Mammal Habitat
NMFS’ proposed rule includes a
section that addresses the effects of the
Navy’s activities on Marine Mammal
Habitat (74 FR 33828, pages 33883–
33884). 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 and NMFS
has concluded there would be minimal
effects on marine mammal habitat.
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 affected species or stock. Level B
(behavioral) Harassment occurs at the
level of the individual(s) and does not
assume any resulting population-level
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consequences, though there are known
avenues through which behavioral
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.), 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
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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 preliminarily determine that Navy
training will have a negligible impact on
the marine mammal species and stocks
present in NWTRC. No changes have
been made to the discussion contained
in this section of the proposed rule (74
FR 33828, pages 33884–33892), with the
following exception.
As mentioned previously in the
Estimated Take section, NMFS has
added language bounding the flexibility
in annual variation of potential take of
individual marine mammal species into
the regulatory text (see § 218.112(c)).
The new language indicates that
modeled annual takes (which must be
provided with the annual LOA
application) of any individual species
may vary but will not ultimately exceed
the indicated 5-year total for that
species (indicated by Table 6) by more
than 10 percent and will not exceed the
indicated annual total by more than 25
percent in any given year; and that
modeled total yearly take of all species
combined may vary but may not exceed
the combined amount indicated below
in any given year by more than 10
percent. NMFS has considered these
limitations in our negligible impact
determination and the findings
described in the proposed rule remain
applicable.
jlentini on DSKJ8SOYB1PROD with RULES2
Determination
Negligible Impact
Based on the analysis contained here
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 and monitoring measures,
NMFS finds that the total taking from
Navy training exercises utilizing MFAS/
HFAS and underwater explosives in the
NWTRC will have a negligible impact
on the affected species or stocks. NMFS
is issuing regulations for these exercises
that prescribe the means of effecting the
least practicable adverse impact on
marine mammals and their habitat and
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set forth requirements pertaining to the
monitoring and reporting of that taking.
Subsistence Harvest of Marine
Mammals
NMFS has determined that the
issuance of 5-year regulations and
subsequent LOAs for Navy training
exercises in the NWTRC would not have
an unmitigable adverse impact on the
availability of the affected species or
stocks for subsistence use for any Alaska
Natives or tribal member in the
Northwest (e.g., Oregon, Washington,
and northern California). Specifically,
the Navy’s exercises would not affect
any Alaskan Native because the
activities will be limited to waters off
the coast of Washington, Oregon, and
northern California, areas outside of
traditional Alaskan Native hunting
grounds. Moreover, there are no
cooperative agreements in force under
the MMPA or Whaling Convention Act
that would allow for the subsistence
harvest of marine mammals in waters
off the Northwest coast. Consequently,
this action would not result in an
unmitigable adverse impact on the
availability of the affected species or
stocks for taking for subsistence uses in
the Northwest.
ESA
There are seven marine mammal
species and one sea turtle species that
are listed as endangered under the ESA
with confirmed or possible occurrence
in the study area: Humpback whale, sei
whale, fin whale, blue whale, sperm
whale, southern resident killer whale,
Steller sea lion, and the leatherback 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) issued on June 15, 2010, NMFS
concluded that the Navy’s activities in
the NWTRC 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 annual 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 than the takes requested by the
applicant (and analyzed for
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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
appropriate number of takes are
authorized. For the Navy’s proposed
NWTRC 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 were requested by the
applicant (because NMFS’ ESA 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. 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 2010 LOA (and
subsequent LOAs in 2011, 2012, 2013,
and 2014). With respect to listed marine
mammals, the terms and conditions of
the ITSs will be incorporated into the
LOAs.
NEPA
NMFS has participated as a
cooperating agency on the Navy’s Draft
Environmental Impact Statement (DEIS)
for the NWTRC, which was published
on December 29, 2008. A Notice of
Availability for the FEIS was published
on September 10, 2010. NMFS
subsequently adopted the Navy’s EIS for
the purpose of complying with the
MMPA.
Classification
This action does not contain any
collection of information requirements
for purposes of the Paperwork
Reduction Act.
The Office of Management and Budget
has determined that this final rule is not
significant for purposes of Executive
Order 12866.
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
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
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whenever the agency is required to
publish a notice of proposed
rulemaking. However, a Federal agency
may certify, pursuant to 5 U.S.C. 605
(b), that the action will not have a
significant economic impact on a
substantial number of small entities.
The Navy is the sole 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 (RFA). 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. NMFS does
not expect the issuance of these
regulations or the associated LOAs to
result in any impacts to small entities
pursuant to the RFA. Because this
action, if adopted, would directly affect
the Navy and not a small entity, this
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. Navy, as the authorized entity, has
informed NMFS that any delay of
enacting the final rule would result in
either: (1) A suspension of ongoing or
planned naval training, which would
disrupt vital training essential to
national security; or (2) the Navy’s
procedural non-compliance with the
MMPA (should the Navy conduct
training without an LOA), thereby
resulting in the potential for
unauthorized takes of marine mammals.
Moreover, the Navy is ready to
implement the rule immediately.
Therefore, these measures will become
effective upon publication.
List of Subjects in 50 CFR Part 218
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Exports, Fish, Imports, Incidental
take, Indians, Labeling, Marine
mammals, Navy, Penalties, Reporting
and recordkeeping requirements,
Seafood, Sonar, Transportation.
Dated: October 25, 2010.
John Oliver,
Deputy Assistant Administrator for
Operations, National Marine Fisheries
Service.
For reasons set forth in the preamble,
50 CFR part 218 is amended as follows:
■
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PART 218—REGULATIONS
GOVERNING THE TAKING AND
IMPORTING OF MARINE MAMMALS
1. The authority citation for part 218
continues to read as follows:
■
Authority: 16 U.S.C. 1361 et seq.
2. Subpart M is added to part 218 to
read as follows:
■
Subpart M—Taking and Importing Marine
Mammals; U.S. Navy’s Northwest Training
Range Complex (NWTRC)
Sec.
218.110 Specified activity and specified
geographical area.
218.111 Effective dates.
218.112 Permissible methods of taking.
218.113 Prohibitions.
218.114 Mitigation.
218.115 Requirements for monitoring and
reporting.
218.116 Applications for Letters of
Authorization.
218.117 Letters of Authorization.
218.118 Renewal of Letters of
Authorization and adaptive
management.
218.119 Modifications to Letters of
Authorization.
Subpart M—Taking and Importing
Marine Mammals; U.S. Navy’s
Northwest Training Range Complex
(NWTRC)
§ 218.110 Specified activity and specified
geographical area.
(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 occur incidental to the
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 Offshore area of the
Northwest Training Range Complex
(NWTRC) (as depicted in Figure ES–1 in
the Navy’s Draft Environmental Impact
Statement for NWTRC), which is
bounded by 48°30′ N. lat.; 130°00′ W.
long.; 40°00′ N. lat.; and on the east by
124°00′ W. long or by the shoreline
where the shoreline extends west of
124°00′ W. long (excluding the Strait of
Juan de Fuca (east of 124°40′ W. long),
which is not included in the Offshore
area).
(c) The taking of marine mammals by
the Navy is only authorized if it occurs
incidental to the following activities
within the designated amounts of use:
(1) The use of the following midfrequency active sonar (MFAS) sources,
high frequency active sonar (HFAS)
sources for U.S. Navy anti-submarine
warfare (ASW) and mine warfare (MIW)
training, in the amounts indicated
below:
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(i) AN/SQS–53 (hull-mounted active
sonar)—up to 215 hours over the course
of 5 years (an average of 43 hours per
year);
(ii) AN/SQS–56 (hull-mounted active
sonar)—up to 325 hours over the course
of 5 years (an average of 65 hours per
year);
(iii) SSQ–62 (Directional Command
Activated Sonobuoy System (DICASS)
sonobuoys)—up to 4430 sonobuoys over
the course of 5 years (an average of 886
sonobuoys per year)
(iv) MK–48 (heavyweight
torpedoes)—up to 10 torpedoes over the
course of 5 years (an average of 2
torpedoes per year);
(v) AN/BQS–15 (mine detection and
submarine navigational sonar)—up to
210 hours over the course of 5 years (an
average of 42 hours per year);
(vi) AN/SSQ–125 (AEER)—up to 745
buoys deployed over the course of 5
years (total combined with the AN/
SSQ–110A (IEER)) (an average of 149
per year);
(vii) Range Pingers—up to 900 hours
over the course of 5 years (an average of
180 hours per year); and
(viii) PUTR Uplink—up to 750 hours
over the course of 5 years (an average of
150 hours per year).
(2) The detonation of the underwater
explosives indicated in paragraph
(c)(2)(i) conducted as part of the training
events indicated in paragraph (c)(2)(ii):
(i) Underwater Explosives:
(A) 5″ Naval Gunfire (9.5 lbs);
(B) 76 mm rounds (1.6 lbs);
(C) Maverick (78.5 lbs);
(D) Harpoon (448 lbs);
(E) MK–82 (238 lbs);
(F) MK–48 (851 lbs);
(G) Demolition Charges (2.5 lbs);
(H) AN/SSQ–110A (IEER explosive
sonobuoy—5 lbs);
(I) HARM;
(J) Hellfire;
(K) SLAM; and
(L) GBU 10, 12, and 16.
(ii) Training Events:
(A) Surface-to-surface Gunnery
Exercises (S–S GUNEX)—up to 1700
exercises over the course of 5 years (an
average of 340 per year).
(B) Bombing Exercises (BOMBEX)—
up to 150 exercises over the course of
5 years (an average of 30 per year).
(C) Sinking Exercises (SINKEX)—up
to 10 exercises over the course of 5 years
(an average of 2 per year).
(D) Extended Echo Ranging and
Improved Extended Echo Ranging (EER/
IEER) Systems—up to 60 exercises (total
combined with the AN/SSQ–125A
(AEER)) over the course of 5 years (an
average of 12 per year).
(3) The taking of marine mammals
may also be authorized in an LOA for
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the activities and sources listed in
§ 218.110(c)(1) should the amounts (i.e.,
hours, dips, number of exercises) vary
from those estimated in § 218.110(c)(2),
provided that the variation does not
result in exceeding the amount of take
indicated in § 218.112(c).
§ 218.111
Effective dates.
Regulations are effective November 9,
2010 through November 9, 2015.
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§ 218.112
Permissible methods of taking.
(a) Under Letters of Authorization
issued pursuant to §§ 216.106 and
218.117 of this chapter, the Holder of
the Letter of Authorization (hereinafter
‘‘Navy’’) may incidentally, but not
intentionally, take marine mammals
within the area described in
§ 218.110(b), provided the activity is in
compliance with all terms, conditions,
and requirements of these regulations
and the appropriate Letter of
Authorization.
(b) [Reserved]
(c) The incidental take of marine
mammals under the activities identified
in § 218.110(c) is limited to the species
listed in paragraphs (c)(4) and (5) of this
section by the indicated method of take
and the indicated number of times
(estimated based on the authorized
amounts of sound source operation), but
with the following allowances for
annual variation in sonar activities:
(1) In any given year, annual take, by
harassment, of any species of marine
mammal may not exceed the amount
indentified in paragraph (c)(4) and (5) of
this section, for that species by more
than 25 percent (a post-calculation/
estimation of which must be provided
in the annual LOA application);
(2) In any given year, annual take by
harassment of all marine mammal
species combined may not exceed the
estimated total of all species combined,
indicated in paragraphs (c)(4) and (5),
by more than 10 percent; and
(3) Over the course of the effective
period of this subpart, total take, by
harassment, of any species may not
exceed the 5-year amounts indicated in
paragraphs (c)(4) and (5) by more than
10 percent. A running calculation/
estimation of takes of each species over
the course of the years covered by the
rule must be maintained.
(4) Level B Harassment:
(i) Mysticetes:
(A) Humpback whale (Megaptera
novaeangliae)—75 (an average of 15
annually);
(B) Fin whale (Balaenoptera
physalus)—720 (an average of 144
annually);
(C) Blue whale (Balaenoptera
musculus)—95 (an average of 19
annually);
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(D) Sei whale (Balaenoptera
borealis)—5 (an average of 1 annually);
(E) Minke whale (Balaenoptera
acutorostrata)—45 (an average of 9
annually); and
(F) Gray whale (Eschrichtius
robustus)—20 (an average of 4
annually).
(ii) Odontocetes:
(A) Sperm whales (Physeter
macrocephalus)—635 (an average of 127
annually);
(B) Killer whale (Orcinus orca)—70
(an average of 14 annually);
(C) Pygmy or dwarf sperm whales
(Kogia breviceps or Kogia sima)—20 (an
average of 4 annually);
(D) Mesoplodont beaked whales—75
(an average of 15 annually);
(E) Cuvier’s beaked whales (Ziphius
cavirostris)—70 (an average of 14
annually);
(F) Baird’s beaked whales (Berardius
bairdii)—65 (an average of 13 annually);
(G) Short-finned pilot whale
(Globicephala macrorynchus)—10 (an
average of 2 annually);
(H) Striped dolphin (Stenella
coeruleoalba)—200 (an average of 40
annually);
(I) Short-beaked common dolphin
(Globicephala macrorhynchus)—6280
(an average of 1256 annually);
(J) Risso’s dolphin (Grampus
griseus)—500 (an average of 100
annually);
(K) Northern right whale dolphin
(Lissodelphis borealis)—3705 (an
average of 741 annually);
(L) Pacific white-sided dolphin
(Lagenorhynchus obliquidens)—2855
(an average of 571 annually);
(M) Dall’s porpoise (Phocoenoides
dalli)—23760 (an average of 4752
annually); and
(N) Harbor Porpoise (Phocoena
phocoena)—596370 (an average of
119274 annually).
(ii) Pinnipeds:
(A) Northern elephant seal (Mirounga
angustirostris)—1890 (an average of 378
annually);
(B) Pacific harbor seal (Phoca
vitulina)—2930 (an average of 586
annually);
(C) California sea lion (Zalophus
californianus)—1430 (an average of 286
annually);
(D) Northern fur seal (Callorhinus
ursinus)—6825 (an average of 1365
annually); and
(E) Steller sea lion (Eumetopias
jubatus)—600 (an average of 120
annually).
(5) Level A Harassment:
(i) Fin whale—5 (an average of 1
annually);
(ii) Sperm whale—5 (an average of 1
annually);
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(iii) Dall’s Porpoise—15 (an average of
3 annually);
(iv) Harbor Porpoise—5 (an average of
1 annually);
(v) Northern right whale dolphin—5
(an average of 1 annually);
(vi) Short-beaked common dolphin—
10 (an average of 2 annually);
(vii) Northern elephant seal—10 (an
average of 2 annually);
(viii) Pacific harbor seal—5 (an
average of 1 annually); and
(ix) Northern fur seal—5 (an average
of 1 annually).
§ 218.113
Prohibitions.
No person in connection with the
activities described in § 218.110 may:
(a) Take any marine mammal not
specified in § 218.112(c);
(b) Take any marine mammal
specified in § 218.112(c) other than by
incidental take as specified in
§§ 218.112(c)(1) and (c)(2);
(c) Take a marine mammal specified
in § 218.112(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 218.117 of this chapter.
§ 218.114
Mitigation.
(a) When conducting training and
utilizing the sound sources or
explosives identified in § 218.110(c), the
mitigation measures contained in the
Letter of Authorization issued under
§§ 216.106 and 218.117 of this chapter
must be implemented. These mitigation
measures include, but are not limited to:
(1) Navy’s General Maritime Measures
for All Training at Sea:
(i) Personnel Training (for all Training
Types):
(A) All commanding officers (COs),
executive officers (XOs), lookouts,
Officers of the Deck (OODs), junior
OODs (JOODs), maritime patrol aircraft
aircrews, and Anti-submarine Warfare
(ASW)/Mine Warfare (MIW) helicopter
crews shall complete the NMFSapproved Marine Species Awareness
Training (MSAT) by viewing the U.S.
Navy MSAT digital versatile disk (DVD).
All bridge lookouts shall complete both
parts one and two of the MSAT; part
two is optional for other personnel.
(B) Navy lookouts shall undertake
extensive training in order to qualify as
a watchstander in accordance with the
Lookout Training Handbook (Naval
Education and Training Command
[NAVEDTRA] 12968–D) available at
https://portal.navfac.navy.mil/go/
navytraining-env-docs.
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(C) Lookout training shall include onthe-job instruction under the
supervision of a qualified, experienced
lookout. 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). Personnel being
trained as lookouts can be counted
among required lookouts as long as
supervisors monitor their progress and
performance.
(D) 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 protective measures
if marine species are spotted.
(ii) Operating Procedures and
Collision Avoidance:
(A) Prior to major exercises, a Letter
of Instruction, Mitigation Measures
Message or Environmental Annex to the
Operational Order shall be issued to
further disseminate the personnel
training requirement and general marine
species protective measures.
(B) COs shall make use of marine
species detection cues and information
to limit interaction with marine species
to the maximum extent possible
consistent with safety of the ship.
(C) While underway, surface vessels
shall have at least two lookouts with
binoculars; surfaced submarines shall
have at least one lookout with
binoculars. Lookouts already posted for
safety of navigation and man-overboard
precautions may be used to fill this
requirement. As part of their regular
duties, lookouts will watch for and
report to the OOD the presence of
marine mammals.
(D) On surface vessels equipped with
a multi-function active sensor, pedestal
mounted ‘‘Big Eye’’ (20x110) binoculars
shall be properly installed and in good
working order to assist in the detection
of marine mammals in the vicinity of
the vessel.
(E) Personnel on lookout shall employ
visual search procedures employing a
scanning methodology in accordance
with the Lookout Training Handbook
(NAVEDTRA 12968–D).
(F) After sunset and prior to sunrise,
lookouts shall employ Night Lookouts
Techniques in accordance with the
Lookout Training Handbook.
(NAVEDTRA 12968–D).
(G) While in transit, naval vessels
shall be alert at all times, use extreme
caution, and proceed at a ‘‘safe speed’’ so
that the vessel can take proper and
effective action to avoid a collision with
any marine animal and can be stopped
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within a distance appropriate to the
prevailing circumstances and
conditions.
(H) When marine mammals have been
sighted in the area, Navy vessels shall
increase vigilance and take reasonable
and practicable actions to avoid
collisions and activities that might
result in close interaction of naval assets
and marine mammals. Actions may
include changing speed and/or direction
and are dictated by environmental and
other conditions (e.g., safety, weather).
(I) Naval vessels shall maneuver to
keep at least 1,500 ft (500 yds) away
from any observed whale in the vessel’s
path and avoid approaching whales
head-on. These requirements do not
apply if a vessel’s safety is threatened,
such as when change of course will
create an imminent and serious threat to
a person, vessel, or aircraft, and to the
extent vessels are restricted in their
ability to maneuver. Restricted
maneuverability includes, but is not
limited to, situations when vessels are
engaged in dredging, submerged
activities, launching and recovering
aircraft or landing craft, minesweeping
activities, replenishment while
underway and towing activities that
severely restrict a vessel’s ability to
deviate course. Vessels will take
reasonable steps to alert other vessels in
the vicinity of the whale. Given rapid
swimming speeds and maneuverability
of many dolphin species, naval vessels
would maintain normal course and
speed on sighting dolphins unless some
condition indicated a need for the vessel
to maneuver.
(J) 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. Marine mammal detections shall
be immediately reported to assigned
Aircraft Control Unit for further
dissemination to ships in the vicinity of
the marine species as appropriate when
it is reasonable to conclude that the
course of the ship will likely result in
a closing of the distance to the detected
marine mammal.
(K) All vessels shall maintain logs and
records documenting training
operations should they be required for
event reconstruction purposes. Logs and
records will be kept for a period of 30
days following completion of a major
training exercise.
(2) Navy’s Measures for MFAS
Operations:
(i) Personnel Training (for MFAS
Operations):
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(A) All lookouts onboard platforms
involved in ASW training events shall
review the NMFS-approved Marine
Species Awareness Training material
prior to use of mid-frequency active
sonar.
(B) All COs, XOs, and officers
standing watch on the bridge shall have
reviewed the Marine Species Awareness
Training material prior to a training
event employing the use of midfrequency active sonar.
(C) Navy lookouts shall undertake
extensive training in order to qualify as
a watchstander in accordance with the
Lookout Training Handbook (Naval
Educational Training [NAVEDTRA],
12968–D).
(D) 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). This does not forbid
personnel being trained as lookouts
from being counted as those listed in
previous measures so long as
supervisors monitor their progress and
performance.
(E) 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 species are spotted.
(ii) Lookout and Watchstander
Responsibilities:
(A) 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.
(B) All surface ships participating in
ASW training events 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 marine mammal
lookouts.
(C) 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.
(D) On surface vessels equipped with
mid-frequency active sonar, pedestal
mounted ‘‘Big Eye’’ (20x110) binoculars
shall be present and in good working
order to assist in the detection of marine
mammals in the vicinity of the vessel.
(E) Personnel on lookout shall employ
visual search procedures employing a
scanning methodology in accordance
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with the Lookout Training Handbook
(NAVEDTRA 12968–D).
(F) After sunset and prior to sunrise,
lookouts shall employ Night Lookouts
Techniques in accordance with the
Lookout Training Handbook.
(G) Personnel on lookout shall be
responsible for reporting 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.
(iii) Operating Procedures (for MFAS
Operations):
(A) Navy will distribute final
mitigation measures contained in the
LOA and the Incidental take statement
of NMFS’ biological opinion to the
Fleet.
(B) COs shall make use of marine
species detection cues and information
to limit interaction with marine species
to the maximum extent possible
consistent with safety of the ship.
(C) 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.
(D) During mid-frequency active sonar
operations, personnel shall utilize all
available sensor and optical systems
(such as night vision goggles) to aid in
the detection of marine mammals.
(E) Navy aircraft participating in
exercises at sea shall conduct and
maintain, when operationally feasible
and safe, surveillance for marine species
of concern as long as it does not violate
safety constraints or interfere with the
accomplishment of primary operational
duties.
(F) Aircraft with deployed sonobuoys
shall use only the passive capability of
sonobuoys when marine mammals are
detected within 200 yds (183 m) of the
sonobuoy.
(G) Marine mammal detections shall
be immediately reported to assigned
Aircraft Control Unit for further
dissemination to ships in the vicinity of
the marine species as appropriate where
it is reasonable to conclude that the
course of the ship will likely result in
a closing of the distance to the detected
marine mammal.
(H) Safety Zones—When marine
mammals are detected by any means
(aircraft, shipboard lookout, or
acoustically) the Navy shall ensure that
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sonar transmission levels are limited to
at least 6 dB below normal operating
levels if any detected marine mammals
are within 1,000 yards (914 m) of the
sonar dome (the bow).
(1) Ships and submarines shall
continue to limit maximum
transmission levels by this 6-dB factor
until the animal has been seen to leave
the 1,000-yd safety zone, has not been
detected for 30 minutes, or the vessel
has transited more than 2,000 yds (1829
m) beyond the location of the last
detection.
(2). 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 10 dB below normal operating
levels if any detected marine mammals
are within 500 yards (497 m) of the
sonar dome (the bow). Ships and
submarines shall continue to limit
maximum ping levels by this 10-dB
factor until the animal has been seen to
leave the 500-yd safety zone, has not
been detected for 30 minutes, or the
vessel has transited more than 2,000 yds
(1829 m) beyond the location of the last
detection.
(3). When marine mammals are
detected by any means (aircraft,
shipboard lookout, or acoustically) the
Navy shall ensure that sonar
transmission ceases if any detected
marine mammals are within 200 yards
(183 m) of the sonar dome (the bow).
Sonar shall not resume until the animal
has been seen to leave the the 200-yd
safety zone, has not been detected for 30
minutes, or the vessel has transited
more than 2,000 yds (1829 m) beyond
the location of the last detection.
(4) Special conditions applicable for
dolphins and porpoises only: If, after
conducting an initial maneuver to avoid
close quarters with dolphins or
porpoises, the OOD concludes that
dolphins or porpoises are deliberately
closing to ride the vessel’s bow wave, no
further mitigation actions are necessary
while the dolphins or porpoises
continue to exhibit bow wave riding
behavior.
(5) If the need for power-down should
arise as detailed in ‘‘Safety Zones’’
above, the Navy shall follow the
requirements as though they were
operating at 235 dB—the normal
operating level (i.e., the first powerdown will be to 229 dB, regardless of at
what level above 235 dB active sonar
was being operated).
(I) Prior to start up or restart of active
sonar, operators will check that the
Safety Zone radius around the sound
source is clear of marine mammals.
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(J) Active sonar levels (generally)—
Navy shall operate active sonar at the
lowest practicable level, not to exceed
235 dB, except as required to meet
tactical training objectives.
(K) Helicopters shall observe/survey
the vicinity of an ASW training event
for 10 minutes before the first
deployment of active (dipping) sonar in
the water.
(L) Helicopters shall not dip their
active sonar within 200 yds (183 m) of
a marine mammal and shall cease
pinging if a marine mammal closes
within 200 yds of the sound source (183
m) after pinging has begun.
(M) Submarine sonar operators shall
review detection indicators of closeaboard marine mammals prior to the
commencement of ASW training events
involving active mid-frequency sonar.
(N) Night vision goggles shall be
available to all ships and air crews, for
use as appropriate.
(3) Navy’s Measures for Underwater
Detonations:
(i) Surface-to-Surface Gunnery (nonexplosive rounds)
(A) A 200-yd (183 m) radius buffer
zone shall be established around the
intended target.
(B) From the intended firing position,
trained lookouts shall survey the buffer
zone for marine mammals prior to
commencement and during the exercise
as long as practicable.
(C) If applicable, target towing vessels
shall maintain a lookout. If a marine
mammal is sighted in the vicinity of the
exercise, the tow vessel shall
immediately notify the firing vessel in
order to secure gunnery firing until the
area is clear.
(D) The exercise shall be conducted
only when the buffer zone is visible and
marine mammals are not detected
within the target area and the buffer
zone.
(ii) Surface-to-Air Gunnery (explosive
and non-explosive rounds)
(A) Vessels shall orient the geometry
of gunnery exercises in order to prevent
debris from falling in the area of sighted
marine mammals.
(B) Vessels will attempt to recover any
parachute deploying aerial targets to the
extent practicable (and their parachutes
if feasible) to reduce the potential for
entanglement of marine mammals.
(C) For exercises using targets towed
by a vessel or aircraft, target towing
vessel/aircraft shall maintain a lookout.
If a marine mammal is sighted in the
vicinity of the exercise, the tow aircraft
shall immediately notify the firing
vessel in order to secure gunnery firing
until the area is clear.
(iii) Air-to-Surface At-sea Bombing
Exercises (explosive and non-explosive):
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(A) If surface vessels are involved,
trained lookouts shall survey for floating
kelp and marine mammals. Ordnance
shall not be targeted to impact within
1,000 yds (914 m) of known or observed
floating kelp or marine mammals.
(B) A 1,000 yd (914 m) radius buffer
zone shall be established around the
intended target.
(C) Aircraft shall visually survey the
target and buffer zone for marine
mammals prior to and during the
exercise. The survey of the impact area
shall be made by flying at 1,500 ft (457
m) or lower, if safe to do so, and at the
slowest safe speed. Release of ordnance
through cloud cover is prohibited:
aircraft must be able to actually see
ordnance impact areas. Survey aircraft
should employ most effective search
tactics and capabilities.
(D) The exercise will be conducted
only if marine mammals are not visible
within the buffer zone.
(iv) Air-to-Surface Missile Exercises
(explosive and non-explosive):
(A) Ordnance shall not be targeted to
impact within 1,800 yds (1646 m) of
known or observed floating kelp.
(B) Aircraft shall visually survey the
target area for marine mammals. Visual
inspection of the target area shall be
made by flying at 1,500 ft (457 m) or
lower, if safe to do so, and at slowest
safe speed. Firing or range clearance
aircraft must be able to actually see
ordnance impact areas. Explosive
ordnance shall not be targeted to impact
within 1,800 yds (1646 m) of sighted
marine mammals.
(v) Demolitions, Mine Warfare, and
Mine Countermeasures (up to a 2.5-lb
charge):
(A) Exclusion Zones—All Mine
Warfare and Mine Countermeasures
Operations involving the use of
explosive charges must include
exclusion zones for marine mammals to
prevent physical and/or acoustic effects
to those species. These exclusion zones
shall extend in a 700-yard arc radius
around the detonation site.
(B) Pre-Exercise Surveys—For
Demolition and Ship Mine
Countermeasures Operations, preexercise surveys shall be conducted
within 30 minutes prior to the
commencement of the scheduled
explosive event. The survey may be
conducted from the surface, by divers,
and/or from the air, and personnel shall
be alert to the presence of any marine
mammal. Should such an animal be
present within the survey area, the
explosive event shall not be started until
the animal voluntarily leaves the area.
The Navy will ensure the area is clear
of marine mammals for a full 30
minutes prior to initiating the explosive
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event. Personnel will record any marine
mammal observations during the
exercise as well as measures taken if
species are detected within the
exclusion zone.
(C) Post-Exercise Surveys—Surveys
within the same radius shall also be
conducted within 30 minutes after the
completion of the explosive event.
(D) Reporting—If there is evidence
that a marine mammal may have been
stranded, injured or killed by the action,
Navy training activities shall be
immediately suspended and the
situation immediately reported by the
participating unit to the Officer in
Charge of the Exercise (OCE), who will
follow Navy procedures for reporting
the incident to Commander, Pacific
Fleet, Commander, Navy Region
Northwest, Environmental Director, and
the chain-of-command. The situation
shall also be reported to NMFS (see
Stranding Plan for details).
(vi) Sink Exercise:
(A) All weapons firing shall be
conducted during the period 1 hour
after official sunrise to 30 minutes
before official sunset.
(B) An exclusion zone with a radius
of 1.5 nm shall be established around
each target. This 1.5 nm zone includes
a buffer of 0.5 nm to account for errors,
target drift, and animal movement. In
addition to the 1.5 nm exclusion zone,
a further safety zone, which extends
from the exclusion zone at 1.5 nm out
an additional 0.5 nm, shall be surveyed.
Together, the zones extend out 2 nm
(3.7 km) from the target.
(C) A series of surveillance overflights shall be conducted within the 2nm zone around the target, prior to and
during the exercise, when feasible.
Survey protocol shall be as follows:
(1) Overflights within the 2-nm zone
around the target shall be conducted in
a manner that optimizes the surface area
of the water observed. This may be
accomplished through the use of the
Navy’s Search and Rescue Tactical Aid,
which provides the best search altitude,
ground speed, and track spacing for the
discovery of small, possibly dark objects
in the water based on the environmental
conditions of the day. These
environmental conditions include the
angle of sun inclination, amount of
daylight, cloud cover, visibility, and sea
state.
(2) All visual surveillance activities
shall be conducted by Navy personnel
trained in visual surveillance. At least
one member of the mitigation team is
required to have completed the Navy’s
marine mammal training program for
lookouts.
(3) In addition to the overflights, the
2-nm zone around the target shall be
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69323
monitored by passive acoustic means,
when assets are available. This passive
acoustic monitoring would be
maintained throughout the exercise.
Potential assets include sonobuoys,
which can be utilized to detect any
vocalizing marine mammals
(particularly sperm whales) in the
vicinity of the exercise. The sonobuoys
shall be re-seeded as necessary
throughout the exercise. Additionally, if
submarines are present, passive sonar
onboard shall be utilized to detect any
vocalizing marine mammals in the area.
The OCE would be informed of any
aural detection of marine mammals and
would include this information in the
determination of when it is safe to
commence the exercise.
(4) On each day of the exercise, aerial
surveillance of the 2-nm zone around
the target shall commence 2 hours prior
to the first firing.
(5) The results of all visual, aerial, and
acoustic searches shall be reported
immediately to the OCE. No weapons
launches or firing may commence until
the OCE declares the 2-nm zone around
the target free of marine mammals.
(6) If a marine mammal observed
within the 2-nm zone around the target
is diving, firing would be delayed until
the animal is re-sighted outside the
2-nm zone around the target, or 30
minutes have elapsed. After 30 minutes,
if the animal has not been re-sighted it
would be assumed to have left the
exclusion zone. The OCE would
determine if the identified marine
mammal is in danger of being adversely
affected by commencement of the
exercise.
(7) During breaks in the exercise of 30
minutes or more, the 2-nm zone around
the target shall again be surveyed for
any marine mammal. If marine
mammals are sighted within 2-nm zone
around the target, the OCE shall be
notified, and the procedure described in
(vi)(c)(1)–(6) would be followed.
(8) Upon sinking of the vessel, a final
surveillance of the 2-nm zone around
the target shall be monitored for 2
hours, or until sunset, to verify that no
marine mammals were injured.
(D) Aerial surveillance shall be
conducted using helicopters or other
aircraft based on necessity and
availability.
(E) Where practicable, the Navy shall
conduct the exercise in sea states that
are ideal for marine mammal sighting,
i.e., Beaufort Sea State 3 or less. In the
event of a Beaufort Sea State 4 or above,
survey efforts shall be increased within
the 2-nm zone around the target. This
shall be accomplished through the use
of an additional aircraft, if available,
and conducting tight search patterns.
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(F) The sink exercise shall not be
conducted unless the 2-nm zone around
the target could be adequately
monitored visually.
(G) In the event that any marine
mammals are observed to be harmed in
the area, NMFS shall be notified as soon
as feasible following the stranding
communication protocol. A detailed
description of the animal shall be taken,
the location noted, and if possible,
photos taken. This information shall be
provided to NMFS as soon as
practicable via the Navy’s regional
environmental coordinator for purposes
of identification.
(H) An after action report detailing the
exercise’s time line, the time the surveys
commenced and terminated, amount,
and types of all ordnance expended, and
the results of survey efforts for each
event shall be submitted to NMFS.
(vii) Extended Echo Ranging/
Improved Extended Echo Ranging (EER/
IEER):
(A) Crews shall conduct visual
reconnaissance of the drop area prior to
laying their intended sonobuoy pattern.
This search shall be conducted at an
altitude below 457 m (500 yd) at a slow
speed, if operationally feasible and
weather conditions permit. In dual
aircraft operations, crews are allowed to
conduct area clearances utilizing more
than one aircraft.
(B) For IEER (AN/SSQ–110A), crews
shall conduct a minimum of 30 minutes
of visual and aural monitoring of the
search area prior to commanding the
first post detonation. This 30-minute
observation period may include pattern
deployment time.
(C) For any part of the intended
sonobuoy pattern where a post (source/
receiver sonobuoy pair) will be
deployed within 914 m (1,000 yd) of
observed marine mammal activity, the
Navy shall deploy the receiver ONLY
(i.e., not the source) and monitor while
conducting a visual search. When
marine mammals are no longer detected
within 914 m (1,000 yd) of the intended
post position, the source sonobuoy (AN/
SSQ–110A/SSQ–125) will be co-located
with the receiver.
(D) When operationally feasible, Navy
crews shall conduct continuous visual
and aural monitoring of marine mammal
activity. This shall include monitoring
of aircraft sensors from the time of the
first sensor placement until the aircraft
have left the area and are out of RF
range of these sensors.
(E) Aural Detection—If the presence
of marine mammals is detected aurally,
then that shall cue the Navy aircrew to
increase the vigilance of their visual
surveillance. Subsequently, if no marine
mammals are visually detected, then the
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crew may continue multi-static active
search.
(F) Visual Detection—If marine
mammals are visually detected within
914 m (1,000 yd) of the explosive source
sonobuoy (AN/SSQ–110A) intended for
use, then that payload shall not be
detonated. 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 914
m (1,000 yd) safety buffer. Aircrews may
shift their multi-static active search to
another post, where marine mammals
are outside the 914 m (1,000 yd) safety
buffer.
(G) For IEER (AN/SSQ–110A),
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 will ensure that a 914 m (1,000
yd) safety buffer, visually clear of
marine mammals, is maintained around
each post as is done during active
search operations.
(H) 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, or in-flight
emergencies. In these cases, the
sonobuoy will self-scuttle using the
secondary or tertiary method.
(I) 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.
(J) Mammal monitoring shall continue
until out of own-aircraft sensor range.
(b) [Reserved]
§ 218.115 Requirements for monitoring
and reporting.
(a) General Notification of Injured or
Dead Marine Mammals—Navy
personnel shall ensure that NMFS is
notified immediately ((see
Communication Plan) or as soon as
clearance procedures allow) if an
injured, stranded, 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 the
name of species or description of the
animal(s), the condition of the animal(s)
(including carcass condition if the
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animal is dead), location, time of first
discovery, observed behaviors (if alive),
and photo or video (if available). In the
event that an injured, stranded, or dead
marine mammal is found by the Navy
that is not in the vicinity of, or during
or shortly after, MFAS, HFAS, or
underwater explosive detonations, the
Navy will report the same information
as listed above as soon as operationally
feasible and clearance procedures allow.
(b) General Notification of Ship
Strike—In the event of a ship strike by
any Navy vessel, at any time or place,
the Navy shall do the following:
(1) Immediately report to NMFS the
species identification (if known),
location (lat/long) of the animal (or the
strike if the animal has disappeared),
and whether the animal is alive or dead
(or unknown).
(2) Report to NMFS as soon as
operationally feasible the size and
length of animal, an estimate of the
injury status (ex., dead, injured but
alive, injured and moving, unknown,
etc.), vessel class/type and operational
status.
(3) Report to NMFS the vessel length,
speed, and heading as soon as feasible.
(4) Provide NMFS a photo or video, if
equipment is available.
(c) Event Communication Plan—The
Navy shall develop a communication
plan that will include all of the
communication protocols (phone trees,
etc.) and associated contact information
required for NMFS and the Navy to
carry out the necessary expeditious
communication required in the event of
a stranding or ship strike, including as
described in the proposed notification
measures above.
(d) The Navy must conduct all
monitoring and/or research required
under the Letter of Authorization,
including abiding by the annual
NWTRC Monitoring Plan. (https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications)
(e) The Navy shall comply with the
2009 Integrated Comprehensive
Monitoring Program (ICMP) Plan and
continue to improve the program in
consultation with NMFS. Changes and
improvements to the program made
during 2010 (as prescribed in the 2009
ICMP and otherwise deemed
appropriate by the Navy and NMFS)
will be described in an updated 2010
ICMP and submitted to NMFS by
October 31, 2010 for review. An
updated 2010 ICMP will be finalized by
December 31, 2010.
(f) Report on Monitoring required in
paragraph (e) of this section—The Navy
shall submit a report annually
describing the implementation and
results of the monitoring required in
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paragraph (d) of this section. The
required submission date will be
identified each year in the LOA. The
Navy will standardize data collection
methods across ranges to allow for
comparison in different geographic
locations.
(g) Annual NWTRC Report—The Navy
will submit an Annual NWTRC Report
every year. The required submission
date will be identified each year in the
LOA. This report shall contain the
subsections and information indicated
below.
(1) ASW Summary—This section
shall include the following information
as summarized from non-major training
exercises (unit-level exercises, such as
TRACKEXs and MIW):
(i) Total Hours—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 Impacts—To the
extent practicable, the Navy, in
coordination with NMFS, shall develop
and implement a method of annually
reporting non-major training (i.e., ULT)
utilizing hull-mounted sonar. The report
shall present an annual (and seasonal,
where practicable) depiction of nonmajor training exercises geographically
across NWTRC. The Navy shall include
(in the NWTRC 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.
(2) [Reserved]
(h) Sinking Exercises (SINKEXs)—
This section shall include the following
information for each SINKEX completed
that year:
(1) Exercise Info:
(i) Location;
(ii) Date and time exercise began and
ended;
(iii) Total hours of observation by
watchstanders before, during, and after
exercise;
(iv) Total number and types of rounds
expended/explosives detonated;
(v) Number and types of passive
acoustic sources used in exercise;
(vi) Total hours of passive acoustic
search time;
(vii) Number and types of vessels,
aircraft, etc., participating in exercise;
(viii) Wave height in feet (high, low
and average during exercise); and
(ix) Narrative description of sensors
and platforms utilized for marine
mammal detection and timeline
illustrating how marine mammal
detection was conducted.
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(2) Individual marine mammal
observation during SINKEX (by Navy
lookouts) information:
(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) Length of time observers
maintained visual contact with marine
mammal;
(vii) Wave height;
(viii) Visibility;
(ix) Whether sighting was before,
during, or after detonations/exercise,
and how many minutes before or after;
(x) Distance of marine mammal from
actual detonations (or target spot if not
yet detonated)—use four categories to
define distance:
(A) the modeled injury threshold
radius for the largest explosive used in
that exercise type in that OPAREA (662
m for SINKEX in NWTRC);
(B) the required exclusion zone (1 nm
for SINKEX in NWTRC);
(C) the required observation distance
(if different than the exclusion zone (2
nm for SINKEX in NWTRC)); and
(D) greater than the required observed
distance. For example, in this case, the
observer would indicate if < 662 m, from
738 m–1 nm, from 1 nm–2 nm, and
> 2 nm.
(xi) Observed behavior—
Watchstanders will 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.), including speed and
direction.
(xii) Resulting mitigation
implementation—Indicate whether
explosive detonations were delayed,
ceased, modified, or not modified due to
marine mammal presence and for how
long.
(xiii) If observation occurs while
explosives are detonating in the water,
indicate munitions type in use at time
of marine mammal detection.
(i) Improved Extended Echo-Ranging
System (IEER) Summary
(1) Total number of IEER events
conducted in NWTRC;
(2) Total expended/detonated rounds
(buoys); and
(3) Total number of self-scuttled IEER
rounds.
(j) Explosives Summary—The Navy is
in the process of improving the methods
used to track explosive use to provide
increased granularity. To the extent
practicable, the Navy shall provide the
information described below for all of
their explosive exercises. Until the Navy
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Sfmt 4700
69325
is able to report in full the information
below, they will provide an annual
update on the Navy’s explosive tracking
methods, including improvements from
the previous year.
(k) Total annual number of each type
of explosive exercise (of those identified
as part of the ‘‘specified activity’’ in this
final rule) conducted in NWTRC; and
(2) Total annual expended/detonated
rounds (missiles, bombs, etc.) for each
explosive type.
(l) NWTRC 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 explosive exercises for which
annual reports are required (Annual
NWTRC Exercise Reports and NWTRC
Monitoring Plan Reports). This report
will be submitted at the end of the
fourth year of the rule (July 2014),
covering activities that have occurred
through February 1, 2014.
(m) 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 the Northwest
Training Range Complex, the Southern
California Range Complex, the Atlantic
Fleet Active Sonar Training, the Hawaii
Range Complex, the Marianas Islands
Range Complex, and the Gulf of Alaska.
(n) The Navy shall respond to NMFS
comments and requests for additional
information or clarification on the
NWTRC Comprehensive Report, the
Comprehensive National ASW report,
the Annual NWTRC Exercise Report, or
the Annual NWTRC 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.
(o) 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.
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Federal Register / Vol. 75, No. 217 / Wednesday, November 10, 2010 / Rules and Regulations
§ 218.116 Applications for Letters of
Authorization.
To incidentally take marine mammals
pursuant to these regulations, the U.S.
Citizen (as defined by § 216.103)
conducting the activity identified in
§ 218.110(c) (i.e., the Navy) must apply
for and obtain either an initial Letter of
Authorization in accordance with
§ 218.117 or a renewal under § 218.118.
§ 218.117
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 § 218.118.
(b) Each Letter of Authorization shall
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 shall 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).
§ 218.118 Renewal of Letters of
Authorization and adaptive management.
jlentini on DSKJ8SOYB1PROD with RULES2
(a) A Letter of Authorization issued
under § 216.106 and § 218.117 of this
chapter for the activity identified in
§ 218.110(c) will be renewed annually
upon:
(1) Notification to NMFS that the
activity described in the application
submitted under § 218.116 will be
undertaken and that there will not be a
substantial modification to the
described work, mitigation or
monitoring undertaken during the
upcoming 12 months;
VerDate Mar<15>2010
17:55 Nov 09, 2010
Jkt 223001
(2) Receipt of the monitoring reports
and notifications within the timeframes
indicated in the previous LOA; and
(3) A determination by the NMFS that
the mitigation, monitoring and reporting
measures required under § 218.114 and
the Letter of Authorization issued under
§§ 216.106 and 218.117 of this chapter,
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 216.118 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.
(c) A notice of issuance or denial of
a renewal of a Letter of Authorization
will be published in the Federal
Register.
(d) Adaptive Management—NMFS
may modify or augment the existing
mitigation or monitoring measures (after
consulting with the Navy regarding the
practicability of the modifications) 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 the NWTRC Study Area or
other locations).
(2) Findings of the Monitoring
Workshop that the Navy will convene in
2011.
(3) Compiled results of Navy funded
research and development (R&D) studies
(presented pursuant to the Integrated
Comprehensive Monitoring Plan).
(4) Results from specific stranding
investigations (either from the NWTRC
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Fmt 4701
Sfmt 9990
Study Area or other locations, and
involving coincident MFAS/HFAS or
explosives training or not involving
coincident use).
(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 or otherwise).
(7) Any information which reveals
that marine mammals may have been
taken in a manner, extent or number not
authorized by these regulations or
subsequent Letters of Authorization.
§ 218.119 Modifications to Letters of
Authorization.
(a) Except as provided in paragraph
(b) of this section, no substantive
modification (including withdrawal or
suspension) to the Letter of
Authorization by NMFS, issued
pursuant to §§ 216.106 and 218.117 of
this chapter 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 § 218.118, without
modification (except for the period of
validity), is not considered a substantive
modification.
(b) If the Assistant Administrator
determines that an emergency exists
that poses a significant risk to the wellbeing of the species or stocks of marine
mammals specified in § 218.112(c), a
Letter of Authorization issued pursuant
to §§ 216.106 and 218.117 of this
chapter 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. 2010–27540 Filed 11–9–10; 8:45 am]
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Agencies
[Federal Register Volume 75, Number 217 (Wednesday, November 10, 2010)]
[Rules and Regulations]
[Pages 69296-69326]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-27540]
[[Page 69295]]
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Part IV
Department of Commerce
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National Oceanic and Atmospheric Administration
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50 CFR Part 218
Taking and Importing Marine Mammals; Navy Training Activities Conducted
Within the Northwest Training Range Complex; Final Rule
Federal Register / Vol. 75 , No. 217 / Wednesday, November 10, 2010 /
Rules and Regulations
[[Page 69296]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 218
[Docket No. 0906101030-0489-03]
RIN 0648-AX88
Taking and Importing Marine Mammals; Navy Training Activities
Conducted Within the Northwest Training Range Complex
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
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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 in the Northwest Training Range
Complex (NWTRC), off the coasts of Washington, Oregon, and northern
California, for the period of October 2010 through October 2015. 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 effecting the least
practicable adverse impact on marine mammal species or stocks and their
habitat, as well as requirements pertaining to the monitoring and
reporting of such taking.
DATES: Effective November 9, 2010 through November 9, 2015.
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:
Availability of Supporting Information
Extensive Supplementary Information was provided in the proposed
rule for this activity, which was published in the Federal Register on
Monday, July 13, 2009 (74 FR 33828). 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.
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, notice of a proposed authorization is
provided to the public for 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 National Defense Authorization Act of 2004 (NDAA) (Pub. L. 108-
136) modified the MMPA by removing 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
In September 2008, NMFS received an application from the Navy
requesting authorization for the take of individuals of 26 species of
marine mammals incidental to upcoming Navy training activities to be
conducted within the NWTRC, which extends west to 250 nautical miles
(nm) (463 kilometers [km]) beyond the coast of Northern California,
Oregon, and Washington and east to Idaho and encompasses 122,400 nm\2\
(420,163 km\2\) of surface/subsurface ocean operating areas. These
training 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 NWTRC by exposing them to sound from mid-frequency
or high-frequency active sonar (MFAS/HFAS) or underwater detonations.
The Navy requested authorization to take individuals of 26 species of
marine mammals by Level B Harassment and 13 individuals of 9 species by
Level A Harassment. The Navy's model, which did not factor in any
potential benefits of mitigation measures, predicted that 13 individual
marine mammals would be exposed to levels of sound or pressure that
would result in injury; thus, NMFS is authorizing the take of 13
individuals per year by Level A Harassment. However, NMFS and the Navy
have determined that injury can most likely be avoided through the
implementation of the required mitigation measures. No mortality of
marine mammals is authorized incidental to naval exercises in the
NWTRC.
Background of 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 (74 FR 33829).
Overview of the NWTRC
The proposed rule contains a description of the NWTRC, including
both the Inshore and Offshore areas. The description contained in the
proposed rule has not changed (74 FR 33829).
Description of 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
[[Page 69297]]
related LOAs. The proposed rule describes the nature and number of
anti-submarine warfare (ASW) exercises, anti-surface warfare (ASUW)
exercises, and mine warfare training (MIW) exercises, involving both
mid- and high-frequency active sonar (MFAS and HFAS), as well as
explosive detonations. It also describes the sound sources and
explosive types used (74 FR 33828, pages 33829-33838). The narrative
description of the action contained in the proposed rule has not
changed, with one exception and one clarification indicated below.
Tables 1, 2, and 3 list the types of sonar sources and the estimated
yearly use, summarize the characteristics of the exercise types, and
list the explosive types used.
As a result of their Section 7 consultation with the U.S. Fish and
Wildlife Service, the Navy agreed to make a small modification to their
activity. They agreed to not conduct Explosive Ordnance Disposal (EOD)
underwater demolition training at the Naval Magazine Indian Island site
(1 event per year was previously included in the proposed rule).
Instead, that training event will be conducted at the Hood Canal
training site, so there will now be up to a total of two events per
year in Hood Canal (instead of 1). The Navy further agreed that EOD
will utilize charge sizes of 1.5 lbs or less at the Hood Canal site,
instead of the 2.5 lbs or less identified in the proposed rule.
The Navy has carefully characterized the training activities
planned for the NWTRC over the 5 years covered by these regulations;
however, evolving real-world needs necessitate flexibility in annual
activities. NMFS has attempted to bound this flexibility with new
language in the regulatory text (see Sec. 218.110(c)) which allows for
flexibility in planned activities, provided it does not affect the take
estimates and anticipated impacts in a manner that changes our
analysis.
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[[Page 69301]]
Description of Marine Mammals in the Area of the Specified Activities
Twenty-seven marine mammal species have confirmed or possible
occurrence within the NWTRC, including six species of baleen whales
(mysticetes), 16 species of toothed whales (odontocetes), five species
of seals and sea lions (pinnipeds), and the sea otter (mustelids). Sea
otters are under the jurisdiction of the Department of the Interior and
are not considered further.) Table 4 summarizes their abundance,
Endangered Species Act (ESA) status, population trends, and occurrence
in the area. Seven of the species are ESA-listed and considered
depleted under the MMPA: Blue whale; fin whale; humpback whale; sei
whale; sperm whale; southern resident killer whale; and Steller sea
lion. The proposed rule contains a discussion of one species that is
not considered further in the analysis (the North Pacific right whale)
because of its rarity in the NWTRC. The proposed rule also contains a
discussion of bottlenose dolphins, but due to their extralimitality,
the impact analysis concluded that this species will not be taken by
the Navy's activity. The proposed rule also contains a discussion of
important areas, including southern resident killer whale and Steller
sea lion critical habitat, and the gray whale migration corridor. The
proposed rule also includes a discussion of marine mammal
vocalizations. Last, the proposed rule includes a discussion of the
methods used to estimate marine mammal density in the NWTRC. The
Description of Marine Mammals in the Area of the Specified Activities
section has not changed from what was in the proposed rule (74 FR
33828, pages 33838-33842).
[[Page 69302]]
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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 (74 FR 33828, pages 33845-33846). 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.
[[Page 69303]]
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 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 NWTRC, 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
may potentially affect marine mammals (some of which NMFS would not
classify as harassment), as well as a discussion of the potential
effects of vessel movement and collision (74 FR 33828, pages 33846-
33862). 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 have been observed a
limited number of times in certain circumstances (the specific events
are also described) (74 FR 33828, pages 33855-33860). The information
contained in Potential Effects of Specified Activities on Marine
Mammals section from the proposed rule has not changed.
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.
Mitigation
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
effecting the least practicable adverse impact on such species or stock
and its habitat, paying particular attention to rookeries, mating
grounds, and areas of similar significance.'' The NDAA of 2004 amended
the MMPA as it relates to military-readiness activities and the ITA
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
training activities described in the NWTRC application are considered
military readiness activities.
NMFS reviewed the proposed NWTRC activities and the proposed NWTRC
mitigation measures as described in the Navy's LOA application to
determine if they would result in the least practicable adverse effect
on marine mammals, which includes 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 effectiveness of the ``military-
readiness activity.'' NMFS determined that further discussion was
necessary regarding the use of MFAS/HFAS for training in the Inshore
Area that contains the southern resident killer whale critical habitat.
To address the concerns above, the Navy clarified for NMFS that no
training utilizing MFAS/HFAS had occurred in the Inshore Area of NWTRC
for the last six years, that it is not being conducted now, and that
there are no plans to utilize MFAS/HFAS for training in the Inshore
Area (i.e., it is not part of the Navy's specified activity). This
information has been factored into NMFS' effects analysis. The Navy has
indicated that should their plans change in the future they will
request a new LOA, which would likely require new regulations, for the
additional activities within the NWTRC. The Navy further explained that
no explosive training occurs in the Inshore Area other than the annual
detonation of four, up to 1.5-2.5lb charges, which are not anticipated
to result in the take of marine mammals. For these reasons, no take of
killer whales is anticipated to result from the Navy's activities in
the Inshore area and none has been authorized.
NMFS' proposed rule includes a list of the Navy's proposed
mitigation measures (74 FR 33828, pages 33863-33867), which have been
included in the regulatory text of this document. The following
mitigation measure has been added since the publication of the proposed
rule:
``Naval vessels will maneuver to keep at least 1,500 ft (500 yds)
away from any observed whale in the vessel's path and avoid approaching
whales head-on. These requirements do not apply if a vessel's safety is
threatened, such as when change of course will create an imminent and
serious threat to a person, vessel, or aircraft, and to the extent
vessels are restricted in their ability to maneuver. Restricted
maneuverability includes, but is not limited to, situations when
vessels are engaged in dredging, submerged activities, launching and
recovering aircraft or landing craft, minesweeping activities,
replenishment while underway and towing activities that severely
restrict a vessel's ability to deviate course. Vessels will take
reasonable steps to alert other vessels in the vicinity of the whale.
Given rapid swimming speeds and maneuverability of many dolphin
species, naval vessels would maintain normal course and speed on
sighting dolphins unless some condition indicated a need for the vessel
to maneuver.''
Based on our evaluation of the proposed measures and other measures
considered by NMFS or recommended by the public, NMFS has determined
that the required mitigation measures (including the Adaptive
Management (see Adaptive Management below) component) 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
proposed rule contains further support for this finding in the
Mitigation Conclusion section (74 FR 33828, pages 33867-33868). During
the public comment period, a few mitigation measures not previously
considered were recommended and NMFS' analysis of these measures is
included in the Response to Public Comment section.
Research
The Navy provides a significant amount of funding and support to
marine research. In the past five years
[[Page 69304]]
the agency provided over $100 million ($26 million in FY08 alone) to
universities, research institutions, federal laboratories, private
companies, and independent researchers around the world to study marine
mammals. The U.S. Navy sponsors 70 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.
This research is directly applicable to Fleet training activities,
particularly with respect to the investigations of the potential
effects of underwater noise sources on marine mammals and other
protected species. Proposed training activities employ active sonar and
underwater explosives, which introduce sound into the marine
environment.
The Marine Life Sciences Division of the 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, which include the Marine Resource Assessments and the
Navy OPAREA Density Estimates (NODE) reports. 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 for and record the types of any pathologies and
diseases and investigate the relationship with potential causal factors
(e.g., active sonar, seismic, weather). The study will not be a true
``cohort'' study, because NMFS will be unable to quantify or estimate
specific active sonar or other sound exposures for individual animals
that strand. However, a cross-sectional or correlational analyses, a
method of descriptive rather than analytical epidemiology, can be
conducted to compare population characteristics, e.g., frequency of
strandings and types of specific pathologies between general periods of
various anthropogenic activities and non-activities within a prescribed
geographic space. In the long-term study, NMFS will more fully and
consistently collect and analyze data on the demographics of strandings
in specific locations and consider anthropogenic activities and
physical, chemical, and biological environmental parameters. This
approach in conjunction with true cohort studies (tagging animals,
measuring received sounds, and evaluating behavior or injuries) in the
presence of activities and non-activities will provide critical
information needed to further define the impacts of active sonar
training exercises and other anthropogenic and non-anthropogenic
stressors. In coordination with the Navy and other Federal and non-
federal partners, the comparative study will be designed and conducted
for specific sites during intervals of both the presence and absence of
anthropogenic activities such as active sonar transmission or other
sound exposures to evaluate demographics of morbidity and mortality,
presence of lesions, and cause of death or stranding. Additional data
that will be collected and analyzed in an effort to control potential
confounding factors includes factors such as average sea temperature
(or just season), meteorological or other environmental variables
(e.g., seismic activity), fishing activities, etc. All efforts will be
made to include appropriate controls (i.e., no active sonar or no
seismic); environmental variables may, however, complicate the
interpretation of ``control'' measurements. The Navy and NMFS along
with other partners are evaluating mechanisms for funding this study.
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.
Proposed Monitoring Plan for the NWTRC
The Navy's final Monitoring Plan for the NWTRC may be viewed at
NMFS' web site: https://www.nmfs.noaa.gov/pr/permits/incidental.htm#applications. The Monitoring Plan for NWTRC has been
designed as a collection of focused ``studies'' (described fully in the
NWTRC draft Monitoring Plan) to gather data that will allow the Navy to
address the following questions:
(a) Are marine mammals exposed to MFAS/HFAS, especially at levels
associated with adverse effects (i.e., based on NMFS' criteria for
behavioral
[[Page 69305]]
harassment, TTS, or PTS)? If so, at what levels are they exposed?
(b) If marine mammals are exposed to MFAS/HFAS in the NWTRC Range
Complex, 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/HFAS, what are their
behavioral responses to various levels?
(d) What are the behavioral responses of marine mammals that are
exposed to explosives at specific levels?
(e) Is the Navy's suite of mitigation measures for MFAS/HFAS (e.g.,
measures agreed to by the Navy through permitting) effective at
preventing TTS, injury, and mortality of marine mammals?
The extent of the training utilizing MFAS/HFAS in the NWTRC is
comparatively less than several of the other training areas utilized by
the Navy and not every one of these original five study questions will
be addressed within NWTRC. Rather, data collected from NWTRC monitoring
will be used to supplement a consolidated range complex marine mammal
monitoring report incorporating data from the Navy's Hawaii Range
Complex, Marianas Island Range Complex, NWTRC, and Southern California
Range Complex. Monitoring methods proposed for the NWTRC include a
combination of research elements designed to support both Range Complex
specific monitoring, and contribute information to a larger Navy-wide
program. These research elements include:
--Deployment of passive acoustic monitoring (PAM) devices, and,
--Marine mammal tagging.
The monitoring techniques selected for the NWTRC will be primarily
focused on providing additional data for study questions (b), (c), and
(d).
The amount of each type of monitoring may vary from the summary
table or Monitoring Plan based on annual discussions between NMFS and
the Navy regarding previous monitoring results and effectiveness and in
accordance with the Adaptive Management component of this rule,
however, the overall effort over the 5-year period will remain
approximately equal to that laid out in the monitoring plan.
This monitoring plan has been designed to gather data on all
species of marine mammals that are observed in the NWTRC; however,
where appropriate, priority will be given to beaked whales, ESA-listed
species, killer whales, and harbor porpoises. 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).
In addition to the Monitoring Plan for MIRC, the Navy has completed
an Integrated Comprehensive Monitoring Program (ICMP) Plan.
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. The
Navy finalized a 2009 ICMP Plan outlining the program on December 22,
2009, as required by the 2009 LOAs for the Hawaii Range Complex (HRC),
the Southern California Range (SOCAL), and Atlantic Fleet Active Sonar
Training (AFAST). The ICMP may be viewed at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm.
The ICMP is a developing program that will be in place for the
length of this rule, and beyond, and NMFS and Navy will evaluate it
annually to determine if it needs to be updated in order to keep pace
with advances in science and technology and the collection of new data.
In the 2009 ICMP Plan, the Navy outlines three areas of targeted
development for 2010, including:
1. Identifying more specific monitoring sub-goals under the major
goals that have been identified.
2. Characterizing Navy Range Complexes and Study Areas within the
context of the prioritization guidelines described in the ICMP.
3. Continuing to Develop Data Management, Organization and Access
Procedures.
The Navy shall comply with the 2009 ICMP Plan and continue to
improve the program in consultation with NMFS. Changes and improvements
to the program made during 2010 (as prescribed in the 2009 ICMP and
otherwise deemed appropriate by the Navy and NMFS) will be described in
an updated 2010 ICMP and submitted to NMFS by October 31, 2010 for
review. An updated 2010 ICMP will be finalized by December 31, 2010.
NMFS plans to solicit public comments on the updated ICMP in January,
2011 and the input will be used to inform the 2011 Monitoring Workshop,
the further development of the ICMP, and, potentially, monitoring
modifications in the Navy's 2012 monitoring plans.
Monitoring Workshop
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
monitoring pursuant to the NWTRC rule as well as monitoring results
from other Navy rules and LOAs (e.g., SOCAL, HRC, etc.). 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 Workshop,
modifications would be applied to monitoring plans as appropriate.
Adaptive Management
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 is evolving fairly quickly. 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 in the NWTRC in the Navy's over
60 years of use of the area for testing and training). NMFS has
included an adaptive management component in the regulations, which
will allow NMFS 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.
The following are some of the possible sources of applicable data:
Results from the Navy's monitoring from the previous year
(either from NWTRC 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
[[Page 69306]]
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 NWTRC or other locations, and involving coincident MFAS/HFAS or
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 other agencies or entities).
Any information that reveals that marine mammals may have
been taken in a manner, extent or number not authorized by these
regulations or subsequent Letters of Authorization.
Mitigation measures could be modified or added (or deleted) if new
data suggests 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 final rule are designed to provide
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 both to compliance as well as ensuring that the most value is
obtained from the required monitoring. The proposed rule contains the
reporting requirements for the Navy (74 FR 33828, pages 33871-33872),
and these requirements remain unchanged with the following exception.
The requirements as written in the proposed rule include specific due
dates for each of the reports. NMFS and the Navy are coordinating a
workload plan to determine the best times during every year to submit
all of the reports that the Navy is responsible for under final rules
for multiple Range Complexes and training exercises. Although the
reports described will always be submitted every year at a time that
allows for adequate analysis by NMFS prior to the issuance of the
subsequent LOA, we want to allow flexibility to change those dates
yearly. Therefore, the regulatory text below will not specify the
specific dates that the reports are due, as the due dates will be
specified in the annual LOA.
Comments and Responses
On July 13, 2009 (74 FR 33828), NMFS published a proposed rule in
response to the Navy's request to take marine mammals incidental to
military readiness training in the NWTRC and requested comments,
information and suggestions concerning the proposed rule. During the
30-day public comment period, NMFS received comments from the Marine
Mammal Commission, the Washington Department of Fish and Wildlife, the
Department of the Interior, the Natural Resources Defense Council (on
behalf of the International Fund for Animal Welfare, the Center for
Biological Diversity, Cetacean Society International, Friends of the
San Juans, the Humane Society of the United States, the Ocean Futures
Society, the Ocean Mammal Institute, People for Puget sound, Davis
Bain, and Jean-Michel Cousteau), the Orca Network, The Whale Museum,
Turtle Island Restoration Network (TIRN) and Center for Biological
Diversity (CBD), as well as over two hundred members of the public. The
NRDC gained support for their comments from over 54,000 members through
form letters.
Introduction
As described elsewhere in this document, 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 effecting the least practicable
adverse impact on such species or stock and its habitat, paying
particular attention to rookeries, mating grounds, and areas of similar
significance.'' NMFS' decisions regarding whether or not to require any
particular mitigation measure must include a careful balancing of the
likely benefit of any particular measure to marine mammals and the
likely effectiveness of the measure, with the practicability of the
measure, which (for military readiness activities) includes
consideration of the likely effect of that measure on personnel safety,
practicality of implementation, and impact on the effectiveness of the
``military-readiness activity.''
Because some of the comments received reflect an incomplete or
inaccurate understanding of the nature and scope of the Navy's MFAS
training exercises, we will summarize and clarify some issues up front
that will support multiple responses below. For example, one commenter
begins by stating that the Navy contemplates extensive sonar training.
This is not the case. In the NWTRC, the annual amount of planned
operation for the most powerful surface hull-mounted MFAS (which is
responsible for the vast majority of the takes) is 108 hours annually.
Comparatively, the annual sonar use in other areas that the Navy uses
for training is far more extensive: 1670 hrs/yr in Hawaii, 2400 in the
Mariana Islands, 2470 in SOCAL, and 5110 off the Atlantic Coast.
Another significant difference is the fact that all of the sonar
exercises in the NWTRC are approximately 1.5-hr exercises that utilize
a single surface hull-mounted sonar, versus the major exercises within
other training areas, which may last for several weeks, and use
multiple (sometimes 10 or more) surface hull-mounted sonars
simultaneously.
Another point that is germane to several of the comments raised is
the typical way that the MFAS exercises utilizing surface hull-mounted
sonar (TRACKEXs) are conducted, and the areas in which they are
typically conducted. Approximately 10 percent of the surface hull-
mounted MFAS is conducted in conjunction with the use of the Portable
Undersea Training Range (PUTR), while the remaining 90 percent is
conducted primarily in-transit as the vessel is moving from one point
to another, most often south through the NWTRC towards the Southern
California Range Complex. The majority of the in-transit MFAS use in
the NWTRC has taken place and is projected to continue to take place at
a distance of 50 nm or greater from shore, with infrequent training
events occurring between 12 and 50 nm from shore. In-transit MFAS
training is not anticipated to occur inside of 12 nm.
The PUTR has been developed to support ASW training in areas where
the ocean depth is between 300 ft and 12,000 ft and at least 3 nm from
land. The PUTR will not be utilized within the Olympic Coast National
Marine Sanctuary (OCNMS).
In addition, the Navy provided funding to NMFS's Southwest
Fisheries Science Center (SWFSC) in the fall of
[[Page 69307]]
2009, to update their newest spatial predictive habitat model with
composite data from 1991 through 2008, the date of the last U.S. West
Coast marine mammal survey. In the spring of 2010, SWFSC completed this
analysis which provides finer scale (25-km) density resolution for 12
of the most commonly sighted species within the U.S. West Coast EEZ
including NWTRC. Results of this effort will be published in a NMFS
Technical Report.
From 2009 through 2010, marine mammal satellite tracking tag
studies funded by the Navy in Southern California show that static
plots of marine mammal occurrence do not provide the entire story on
marine mammal life history. Tagged baleen whales and dolphins within
Southern California quite frequently move significant distances. As
part of the Navy's NWTRC Monitoring Plan, presence\absence data will be
collected via offshore long-term passive acoustic monitoring devices
from Scripps Institute of Oceanography, as well as marine mammal
satellite tagging.
In summary, the Navy, as part of its NWTRC Monitoring Plan will
continue to contribute valuable scientific data in collaborating with
regional and national scientific academic partners as to marine mammal
distributions within the NWTRC.
Last, for the second year in a row, the Navy is convening a
workshop in October to which marine mammal experts have been invited.
The Navy will review its monitoring results from the previous year and
solicit recommendations on future plans. More formally, the Navy has
been required by multiple LOAs to hold a Monitoring Workshop in 2011
that will include both marine mammal experts and non-governmental
organizations. Here, again, the Navy will provide a review of previous
monitoring results from multiple range complexes and solicit input. The
goal of the 2011 workshop, as laid out in the Integrated Comprehensive
Monitoring Program Plan, is to comprehensively consider the resources
available in different ranges, the data needs, and the species and
conditions present in different ranges in order to identify the most
appropriate monitoring across range complexes that will provide the
most efficient methodology and best results.
Additional Mitigation Recommendations
Comment 1: NRDC and other commenters recommended the establishment
of a panel of marine mammal and oceanographic experts with regional
expertise on marine mammal distribution, abundance, habitat, or
population structure and ecology, or habitat suitability modeling to
identify high-value habitat by reviewing and analyzing the published
literature, survey data, and predictive models. The use of sonar in
such habitat would be prohibited or subject to additional operational
measures to ensure the greatest protection of animals in the area.
Response: In January 2009, the Administrator of the National
Oceanic and Atmospheric Administration committed, in a letter to the
Council on Environmental Quality, to convene a panel to identify
important marine mammal habitat, as described above. This process has
begun. Once the results of that effort are available (anticipated in
2011), NMFS will use them to inform decisions related to geographic
mitigation requirements, both in upcoming rules, as well as in rules
that have already been issued, through the adaptive management
provision (described in the Adaptive Management section above).
Comment 2: NRDC and several other commenters recommended that NMFS
establish a protection area for northwest harbor porpoise populations
landward of the 100-m isobath. Further, they recommended that NMFS
establish an adjacent buffer zone to ensure that exposure levels do not
exceed 120dB within the 100-m isobath. NMFS should ask the Navy to
prepare a nominal propogation analysis for the coast to determine what
stand-off distances are necessary to reduce exposures below the 120dB
threshold. The NRDC further notes that the vast majority of the takes
in the NWTRC are harbor porpoises.
Response: The Navy conducts about 99 percent of their MFAS
activities in the W-237 area, which extends out approximately 200 nm
from the coast of the northern half of Washington state (see page 2-5
of the Navy's NWTRC FEIS). Within the W-237, the 100-m isobath extends
out from the coast approximately 40 nm at some points, and up to 80 nm
in the northern portion near the Strait of Juan de Fuca. As noted above
in the introduction to this section, the Navy has conducted, and plans
to conduct, the majority of their in-transit MFAS activities beyond 50
nm from shore, and has operated MFAS between 12 and 50 nm from shore
infrequently in the past. As mentioned above, the PUTR (with which
approximately 10 percent of the MFAS activities are associated) is
designed to be used in depths of 300-1200 ft, so it is unlikely that it
will be used within the 100-m isobath. Based on this general
operational plan, there is only a relatively small area within the 100-
m isobath in which the Navy would potentially operate MFAS, and this is
only a very small percentage of the entire W-237 area that is available
and in which the Navy typically operates MFAS. In order to adequately
train, however, the Navy needs to train within a wide range of
bathymetric conditions, environmental conditions, and operational
conditions (i.e., proximity to certain resources such as airfields), so
it is unlikely that they would completely avoid the 100-m isobath.
In short, based on their general operating plans, the overall size
of the area available for training and the fact that they only plan to
operate 108 hours of surface hull-mounted sonar total annually (but
need to operate in a variety of conditions, including depths other than
within the 100-m isobath), it is likely that only a relatively small
subset of the 108 hours of MFAS will be operated within the 100-m
isobath, but these hours are needed for operational flexibility.
Regarding the establishment of an additional buffer to ensure that
the area within the 100-m isobath is not ensonified above 120 dB, the
Navy has done a propagation analysis and the distance at which sound
from a surface hull-mounted sonar attenuates to 120 dB in the NWTRC is
approximately 70 nm. A buffer of this nature would extend out
approximately 110-150 nm from shore, rendering about 60-70 percent of
the available MFAS training area inaccessible and reducing access to
the vast majority of the bathymetric relief that is necessary for
effective training. (NMFS notes that 120 dB is the minimum received
level at which we have estimated that harbor porpoises may be taken by
behavioral (Level B) harassment, and avoiding exposure above this level
is akin to avoiding take completely, which would negate the need for an
incidental take authorization.)
Last, NRDC notes that the vast majority of the total takes in the
NWTRC are of harbor porpoises. This is correct; of the approximately
130,000 total annual authorized takes in the NWTRC, 119,000 are of
harbor porpoises. This is because harbor porpoises are considered more
sensitive to sound than many other marine mammals and any exposure
above a received level of 120 dB is considered a take. However, of the
total harbor porpoise takes, approximately 85 percent are anticipated
to occur at a received level between 120 and 140 dB, from which we
would expect a comparatively less severe response. Additionally, only
approximately 0.5 percent of these takes
[[Page 69308]]
would result from exposures above a received level of 160 dB, which is
still far below received levels associated with injurious takes. In
short, there are more takes of harbor porpoises because they are more
sensitive to sound. However, because we use a step function to define
their predicted response, instead of a dose curve as we do for other
marine mammal species, a large portion of the takes will likely consist
of the minimum response that we would still consider a take.
Comment 3: NRDC and several other commenters recommended that NMFS
provide additional protection for marine mammals from the use of sonar
within the OCNMS, by specifically prohibiting sonar usage in the OCNMS,
or at a minimum, limiting the exercises taking place with the OCNMS by
requiring final approval from the Pacific Fleet command, or using other
means to minimize sonar use. In support of this recommendation, NRDC
notes the seasonal use of the area by migrating gray whales, summer
resident gray whales that use the area for feeding, and Southern
Resident killer whales (SRKW) that use the area for part of the year.
Response: The OCNMS is contained within the NWTRC and the
delineation of the edge of the OCNMS essentially follows the 100-m
isobath. The Navy will not deploy the PUTR within the OCNMS. Otherwise,
please see NMFS' response to comment 2, above. Of additional note,
because of the seasonal nature of the use of the area by some of the
species that the commenters mention, those species' potential exposure
to MFAS is likely an even smaller proportion of the total hours, as
some of the hours of operation will occur in months that they are not
present.
Although the comment addressed here mentions only sonar training,
it is worth noting that the Navy does not do any live bombing in the
OCNMS waters (i.e., BOMBEX and SINKEXs are conducted outside the limits
of the OCNMS). Additionally, in their DEIS, the Navy indicated their
intent to create a small underwater minefield training range. Although
they did not specify it in the DEIS, they have since clarified the fact
that this small range will not be in OCNMS waters.
Comment 4: NRDC and several other commenters recommended that NMFS
identify the Greater Puget Sound as a protection area (except for
activities occurring as part of the Keyport EIS) as a condition of the
proposed rule. They further recommended that if Puget Sound is not
designated as a protected area, NMFS should make the following
clarifications in its final rule:
[cir] That any use of MFA sonar for training or maintenance in the
Greater Puget Sound would first require the Navy to obtain an
incidental take permit given the potential for serious injury or
mortality to marine mammals in the area;
[cir] That the Navy has agreed to conduct neither sonar training
nor maintenance activities in the Greater Puget Sound without MMPA
authorization;
[cir] That the Navy has internal checks, in addition to the MMPA
requirement, on non-RDT&E sonar use in the Greater Puget Sound (e.g.,
requiring approval from Fleet Command).
Response: The Navy's action does not include the use of MFAS for
training or in-transit maintenance in the Greater Puget Sound area, so
it is not necessary to designate the Greater Puget Sound area as a
Protection Area. The Navy does not currently plan to use MFAS for
training or in-transit maintenance in the Greater Puget Sound area, and
they have committed to obtaining a separate LOA (which would require a
new rulemaking) if they plan to conduct those activities in the Greater
Puget Sound area.
Additionally, the Navy has in place, and has since June 2003, an
internal requirement wherein they must obtain permission from the
Commander Pacific Fleet (CPF) before they may operate MFAS for
training, maintenance or testing in Puget Sound. Since 2003, it has
been CPF policy to not approve training, maintenance or testing use of
sonar systems for vessels underway within Puget Sound. Pierside
maintenance/testing of sonar systems within Puget Sound still requires
CPF approval, and may be approved by CPF if it is not practical or
feasible to conduct alternate maintenance/testing outside of Puget
Sound. Since this requirement was put into place, every request to use
MFAS underway for training, maintenance, or testing in Puget Sound has
been denied, except on the Nanoose Range.
Separately, pier-side maintenance was not included as part of the
proposed action, either for the MMPA authorization, or in the Navy's
EIS. Pierside maintenance and testing of sonars rarely involves
emission of sound. Most often the source is out of the water and might
emit only one or a few low amplitude pings. The Navy is currently
compiling detailed information on all pierside testing activity
nationwide and that information will be included in the next phase of
environmental assessments in 2014. At this time the Navy does not
anticipate that there will be any additional risk to marine mammals
from pierside testing due to the infrequency of sound emissions and the
relative rarity of marine mammals in the vicinity of these sites.
Comment 5: NRDC and several other commenters recommended that NMFS
establish a seasonal protection area in certain canyons and banks on
the NWTRC that represent important foraging habitat, particularly for
humpback whales. NRDC recommends seasonal protection areas for the
``Prairie,'' Juan de Fuca Canyon, Swiftsure Bank, Barkley and Nitinat
Canyons, and Heceta Bank, during the main humpback whale feeding season
from June to October.
Response: With respect to some of these specific areas, the
Swiftsure Bank is well within 50 nm of shore, and as described above,
it is unlikely that the Navy will utilize in-transit MFAS there.
Additionally, Swiftsure Bank is within the 100-m isobaths, which is not
where the PUTR is designed to be used, and partially within the OCNMS,
where the PUTR will not be used. Heceta Bank is located off the shore
of Oregon, and 99 percent of the Navy's MFAS use in the NWTRC is
conducted within the W-237 area, which is located off the coast of
Washington, so MFAS use is not likely to occur there. Additionally, the
Prairie is an area that is less than 100 m deep, so the PUTR is not
likely to be deployed there.
The Navy plans to conduct approximately 108 hours of surface hull-
mounted MFAS use in the NWTRC annually. Allowing for the fact that it
is not all planned in the months of June-October, and not all planned
in any one of the specific areas noted in the comment, only a small
number of hours of sonar is likely to occur in any of the specific
areas recommended for protection by the commentors.
Generally speaking, because of the small number of hours that the
Navy may be conducting MFAS sonar training, the short duration of the
exercises, the use of only one single hull-mounted sonar vessel, and
the huge area over which training is conducted, the impracticability of
designating additional protective areas identified by the commentors
outweighs the likely benefits. It requires a considerable amount of
planning, education, and subsequent attention by the Navy to establish
and implement protective areas. Furthermore, the Navy only anticipates
taking a small number of the species for which the protected areas
would be established, by Level B Harassment (15 humpback whales, 14
killer whales, and 4 gray whales), with the exception of harbor
porpoises
[[Page 69309]]
(discussed in comment response 2). Considering the density of marine
mammals and the likelihood of encountering them in any location during
the course of a 1.5 hour period, we cannot predict with sufficient
certainty that avoiding these areas would necessarily result in a
decrease of takes.
In addition, as mentioned previously, the Navy's NWTRC Monitoring
Plan entails deploying long-term passive acoustic monitoring devices at
two locations within the offshore NWTRC. One such Navy funded device
has been in operation near Quinault Canyon since 2004. This will be
supplemented with a second device which is currently forecast for
deployment near the Juan de Fuca Canyon. Information from both passive
acoustic devices will provide valuable scientific data on marine mammal
vocalizations and anthropogenic sounds including commercial ship noise
or transitory MFAS at these two locations. This analytical approach
continues to be refined based on lessons learned from similar
deployments and data review in Hawaii and Southern California. Summary
data from these devices will be provided to NMFS and the public via
annual Navy monitoring reports.
Comment 6: The NRDC and several other commenters recommended that
NMFS require avoidance of, or a reduction of training activity within,
areas between 500 and 2,000 meters depth with unusual bottom topography
(such as canyons), to provide additional protection to beaked whales.
Response: The NRDC notes in their comments that there are no
particular areas of known concentration for beaked whales in the NWTRC,
but that most species appear to have a preference for areas of the
lower continental slope. They may also be found in a wider range of
conditions, from slopes to abyssal plain. First, NMFS may consider
requiring a geographic limitation on an activity in a specific area of
known concentration of particular species of animals, if the
practicability analysis (which includes consideration of the nature of
the activity, the likely benefits to the species, and the
practicability of the measure) suggests that it will accomplish the
least practicable adverse impact. However, we are less likely to
recommend the avoidance of all of a type of area that an animal has a
general preference for, especially in a case like this where the
activity is comparatively limited, because it is unclear whether
avoidance of all of the areas of this type will result in the reduction
of impacts to the animals.
More specifically, in the case of beaked whales, we are only
authorizing the Level B take of 38 animals, so there is only a very
limited potential benefit to making a huge tract of area unavailable
for training. Further, as noted above, beaked whales may prefer a wider
variety of areas than previously thought. In summary, only a portion of
the already few hours of planned MFAS use will occur in this habitat,
and it is impracticable to completely prohibit the Navy's access to
this particular depth when they need to train in a wide variety of
circumstances.
Comment 7: The MMC recommended that the rule require suspension of
the Navy's activities if a marine mammal is seriously injured or killed
and the injury or death could be associated with those activities. The
injury or death should be investigated to determine the cause, assess
the full impact of the activity or activities and determine how
activities should be modified to avoid future injuries or deaths.
Response: NMFS' regulations include a provision for ``General
notification of injured or dead marine mammals,'' under which Navy
personnel shall ensure that NMFS is notified immediately (or as soon as
clearance procedures allow) if an injured, stranded, 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 provision further requires the Navy to 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 of the animals (if available).
It can take months to years to complete the necessary tests and
analyses required to determine, with a reasonable amount of certainty,
the cause of a marine mammal death--and sometimes it is not possible to
determine it. All but one of the small number of strandings that have
occurred around the world associated with MFAS exercises have occurred
concurrent to exercises that would be considered ``major'', which
typically involve multiple surface vessels and last for a much longer
duration than the non-major exercises that occur in the NWTRC (as
described above in the Introduction to this section). Hence, NMFS (with
input from the Navy) determined that it was beneficial and practicable
to preemptively outline an explicit plan (that includes a shutdown
requirement in certain circumstances) for how to deal with a stranding
that occurs during a major exercise, and therefore Stranding Response
Plans were developed for all of the areas in which major exercises are
conducted. Alternatively, for non-major exercises (including all of the
exercises in the NWTRC), the general notification provisions apply,
which means that the Navy would contact NMFS as soon as clearance
procedures allow and we would determine how best to proceed at that
time.
Because so few strandings have been definitively associated with
MFAS training in the 60+ years that the U.S. and other countries that
share information have been conducting MFAS training; the exercises
conducted in the NWTRC are of short duration and involve only one
surface hull-mounted sonar; and investigations take a long time and are
not always conclusive, it is not reasonable or practicable to require
the Navy to shut down every time an injured or dead animal is found in
the vicinity pending the results of an investigation that could take
years to conduct.
Comment 8: One commenter recommended that MFAS not be utilized off
the coast of California from June through October to protect seasonal
migration of blue and humpback whales.
Response: The Navy plans to conduct 99 percent of their MFAS
operation (which consists of 108 hours of surface hull-mounted sonar)
within the W-237 area, which is located off the coast of Washington.
This means that MFAS would be operated for only a few hours annually
off the coast of California, at most.
Comment 9: One commenter recommended that the Navy avoid operating
MFAS within 300 nm of the OCNMS.
Response: A three hundred mile buffer around the OCNMS would
entirely encompass the NWTRC, thereby preventing the Navy from
conducting the proposed activity, which is not a practicable option
under the MMPA.
Comment 10: One commenter noted that there is no reference to the
Navy going to the aid of stranded animals.
Response: NMFS, as the agency with authority over marine mammal
health and stranding, does not want Navy personnel or other untrained
and unpermitted individuals going to the aid of stranded animals.
Rather, as described in the response to comment 7, above, the Navy is
required to notify NMFS if they encounter an injured, stranded, or dead
animal, and NMFS will respond as appropriate.
Comment 11: One commenter recommended that we correct the
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statement ``Southern resident killer whales spend the majority of their
time in the Inshore Area from May/June through October/November,
although they do make multi-day trips to the outer coast,'' to say
``mid-June through September.'' The commenter further recommended that
the Navy's sonar activity be limited to the summer period and when
SRKWs have been located well within the Inshore Area (e.g. greater than
~30 nautical miles east of Cape Flattery for sonar activities lasting
less than 6 hours) by the listening network (Salish Sea hydrophone
network--https://orcasound.net) and/or sighting networks (The Whale
Museum, whale watch operators, Orca Network, Center for Whale Research,
etc.).
Response: The months originally indicated are taken