Taking and Importing Marine Mammals; U.S. Navy Training in the Hawaii Range Complex, 1456-1491 [E9-37]
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rather, all sections from the proposed
rule will be represented herein and will
contain either a summary of the material
presented in the proposed rule or a note
referencing the page(s) in the proposed
rule where the information may be
found. Any information that has
changed since the proposed rule was
published will be addressed herein.
Additionally, this final rule contains a
section that responds to the comments
received during the public comment
period.
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 216
[Docket No. 080519680–81530–02]
RIN 0648–AW86
Taking and Importing Marine
Mammals; U.S. Navy Training in the
Hawaii Range Complex
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AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
SUMMARY: NMFS, upon application from
the U.S. Navy (Navy), is issuing
regulations to govern the unintentional
taking of marine mammals incidental to
training activities conducted within the
Hawaii Range Complex (HRC) for the
period of January 2009 through January
2014. The Navy’s training activities are
considered military readiness activities
pursuant to the Marine Mammal
Protection Act (MMPA), as amended by
the National Defense Authorization Act
of 2004 (NDAA). These regulations,
which allow for the issuance of ‘‘Letters
of Authorization’’ (LOAs) for the
incidental take of marine mammals
during the described activities and
specified timeframes, prescribe the
permissible methods of taking and other
means of affecting the least practicable
adverse impact on marine mammal
species and their habitat, as well as
requirements pertaining to the
monitoring and reporting of such taking.
DATES: Effective January 5, 2009 through
January 5, 2014.
ADDRESSES: A copy of the Navy’s
application, which contains a list of the
references used in this document,
NMFS’ Record of Decision (ROD), and
other documents cited herein, may be
obtained by writing to Michael Payne,
Chief, Permits, Conservation and
Education Division, Office of Protected
Resources, National Marine Fisheries
Service, 1315 East-West Highway, Silver
Spring, MD 20910–3225 or by telephone
via the contact listed here.
FOR FURTHER INFORMATION CONTACT: Jolie
Harrison, Office of Protected Resources,
NMFS, (301) 713–2289, ext. 166.
SUPPLEMENTARY INFORMATION: Extensive
supplementary information was
provided in the proposed rule for this
activity, which was published in the
Federal Register on Monday, June 23,
2008 (73 FR 35510). This information
will not be reprinted here in its entirety;
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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 and of no more
than 1 year, the Secretary shall issue a
notice of proposed authorization for
public review.
Authorization shall be granted if
NMFS finds that the taking will have a
negligible impact on the species or
stock(s), will not have an unmitigable
adverse impact on the availability of the
species or stock(s) for subsistence uses,
and if the permissible methods of taking
and requirements pertaining to the
mitigation, monitoring and reporting of
such taking are set forth.
NMFS has defined ‘‘negligible
impact’’ in 50 CFR 216.103 as:
an impact resulting from the specified
activity that cannot be reasonably expected
to, and is not reasonably likely to, adversely
affect the species or stock through effects on
annual rates of recruitment or survival.
The NDAA (Pub. L. 108–136)
removed the ‘‘small numbers’’ and
‘‘specified geographical region’’
limitations and amended the definition
of ‘‘harassment’’ as it applies to a
‘‘military readiness activity’’ to read as
follows (Section 3(18)(B) of the MMPA):
(i) Any act that injures or has the
significant potential to injure a marine
mammal or marine mammal stock in the wild
[Level A Harassment]; or
(ii) any act that disturbs or is likely to
disturb a marine mammal or marine mammal
stock in the wild by causing disruption of
natural behavioral patterns, including, but
not limited to, migration, surfacing, nursing,
breeding, feeding, or sheltering, to a point
where such behavioral patterns are
abandoned or significantly altered [Level B
Harassment].
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Summary of Request
On June 25, 2007, NMFS received an
application from the Navy requesting
authorization for the take of 24 species
of marine mammals incidental to
upcoming Navy training activities to be
conducted within the HRC, which
covers 235,000 nm2 around the Main
Hawaiian Islands (see map on page 17
of the application), over the course of 5
years. These training activities are
classified as military readiness
activities. These training activities may
incidentally take marine mammals
present within the HRC by exposing
them to sound from mid-frequency or
high frequency active sonar (MFAS/
HFAS) or to underwater detonations at
levels that NMFS associates with the
take of marine mammals. The Navy
requested authorization to take
individuals of 24 species of marine
mammals by Level B Harassment.
Further, though they do not anticipate it
to occur, the Navy requested
authorization to take, by injury or
mortality, up to 10 individuals each of
10 species over the course of the 5-year
period (bottlenose dolphin, Kogia spp.,
melon-headed whale, pantropical
spotted dolphin, pygmy killer whale,
short-finned pilot whale, striped
dolphin, and Cuvier’s, Longman’s, and
Blainville’s beaked whale).
Background of Navy Request
The proposed rule contains a
description of the Navy’s mission, their
responsibilities pursuant to Title 10 of
the United States Code, and the specific
purpose and need for the activities for
which they requested incidental take
authorization. The description
contained in the proposed rule has not
changed (73 FR 35510).
Description of the Specified Activities
The proposed rule contains a
complete description of the Navy’s
specified activities that are covered by
these final regulations, and for which
the associated incidental take of marine
mammals will be authorized in the
related LOAs. The proposed rule
describes the nature of the training
exercises involving both mid- and highfrequency active sonar (MFAS and
HFAS) and explosive detonations, as
well as the MFAS and HFAS sound
sources and explosive types. See 73 FR
35510, page 35512. The narrative
description of the action contained in
the proposed rule has not changed
except for two corrections and one
clarification, noted in the paragraph
below. Tables 1–3 summarize and
quantify the sonar exercise types, sonar
sources, and explosive exercise types
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occurs) follows: In the years without
RIMPAC, the sonar hours conducted
will be seasonally and spatially
distributed such that no additional
exposures of humpback whales to
MFAS/HFAS would occur beyond those
used to estimate take in the years with
a RIMPAC. In a simple example, in a
non-RIMPAC year, the Navy could
choose to conduct the RIMPAC-sized
lump of sonar hours either in the
summer when humpbacks are not
present, or in the winter but farther out
to sea where their activities would not
expose humpbacks to MFAS/HFAS, or
some combination of those two. This
clarification does not affect NMFS’
determinations.
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winter months is typically rare and
infrequent due to the required
mitigation measures, but exercises may
be planned for winter and NMFS and
the Navy’s analyses accounted for this
fact. Table 3 includes the correction
here. These two modifications are nonsubstantive and do not affect NMFS’
determinations.
Last, Table 1 (in this final rule)
indicates that RIMPAC exercises only
occur in the summer (when humpback
whales are not present) of every other
year, which is accurate. Table 2 shows
that the Navy plans to conduct the same
number of sonar hours in each year. The
needed clarification (to ensure no
unanticipated humpback whale take
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used in these training exercises and
contain minor corrections (from the
proposed rule) that did not affect NMFS’
analysis of the proposed action.
The last paragraph of the Mine
Neutralization section of the proposed
rule contained an error. For the final
rule, the sentence beginning ‘‘Standard
practices for tethered mines * * *’’
should be replaced with the following
sentence: ‘‘Standard practice for
tethered mines is to tie off the explosive
counter charge as closely as possible to
the mine case.’’ In the proposed rule,
Table 5 (which is Table 3 in this final
rule) mistakenly indicated that IEER
exercises would only occur in the
summer months. In fact, IEER use in the
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Description of Marine Mammals in the
Area of the Specified Activities
There are 27 marine mammal species
with possible or confirmed occurrence
in the HRC. Seven marine mammal
species listed as federally endangered
under the Endangered Species Act
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(ESA) occur in the HRC: The humpback
whale, North Pacific right whale, sei
whale, fin whale, blue whale, sperm
whale, and Hawaiian monk seal. The
most abundant marine mammals appear
to be dwarf sperm whales, striped
dolphins, and Fraser’s dolphins. The
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most abundant large whales are sperm
whales. Table 4 provides the estimated
abundance, estimated group size, and
estimated probability of detection
(based on Barlow 2006) of the marine
mammal species that occur in the HRC.
BILLING CODE 3510–22–P
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BILLING CODE 3510–22–C
The Navy has compiled information
on the abundance, behavior, status and
distribution, and vocalizations of
marine mammal species in the
Hawaiian waters from peer reviewed
literature, the Navy Marine Resource
Assessment, NMFS Stock Assessment
Reports, and marine mammal surveys
using acoustics or visual observations
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from aircraft or ships. This information
may be viewed in the Navy’s LOA
application and/or the Navy’s FEIS for
the HRC (see FOR FURTHER INFORMATION).
Additional information is available in
NMFS Stock Assessment Reports, which
may be viewed at: https://www.nmfs.
noaa.gov/pr/sars/species.htm. As
indicated in the proposed rule, based on
their rare occurrence in the HRC, the
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Navy and NMFS do not anticipate any
effects to Blue whales, North Pacific
right whales, or Northern elephant seals
and, therefore, they are not addressed
further in this document.
Because the consideration of areas
where marine mammals are known to
selectively breed or calve are important
to both the negligible impact finding
necessary for the issuance of an MMPA
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authorization and the need for NMFS to
put forth the means of affecting the least
practicable adverse impact paying
particular attention to rookeries, mating
grounds, and other areas of similar
significance, the proposed rule contains
a description of important reproductive
areas, with a special focus on humpback
whales (73 FR 35510, page 35519). That
section includes a figure that generally
illustrates humpback whale survey data
collected between 1993 and 2003 and
indicates areas of high and low density.
The description contained in the
proposed rule has not changed.
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A Brief Background on Sound
The proposed rule contains a section
that provides a brief background on the
principles of sound that are frequently
referred to in this rulemaking (73 FR
35510, pages 35521–35522). This
section also includes a discussion of the
functional hearing ranges of the
different groups of marine mammals (by
frequency) as well as a discussion of the
two main sound metrics used in NMFS
analysis (sound pressure level (SPL) and
sound energy level (SEL)). The
information contained in the proposed
rule has not changed.
Potential Effects of Specified Activities
on Marine Mammals
With respect to the MMPA, NMFS’
effects assessment serves four primary
purposes: (1) To prescribe the
permissible methods of taking (i.e.,
Level B Harassment (behavioral
harassment), Level A Harassment
(injury), or mortality, including an
identification of the number and types
of take that could occur by Level A or
B harassment or mortality) and to
prescribe other means of affecting the
least practicable adverse impact on such
species or stock and its habitat (i.e.,
mitigation); (2) to determine whether
the specified activity will have a
negligible impact on the affected species
or stocks of marine mammals (based on
the likelihood that the activity will
adversely affect the species or stock
through effects on annual rates of
recruitment or survival); (3) to
determine whether the specified activity
will have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (however,
there are no subsistence communities
that would be affected in the HRC, so
this determination is inapplicable for
the HRC); 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
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ways that MFAS/HFAS and underwater
explosive detonations may potentially
affect marine mammals (some of which
NMFS would not classify as
harassment); 73 FR 35510, pages 35522–
35534. 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); 73 FR 35510,
pages 35529–35534. The information
contained in Potential Effects of
Specified Activities on Marine
Mammals Section from the proposed
rule has not changed, except for one
correction noted below.
The proposed rule contained an error
in the Potential Effects of Specified
Activities on Marine Mammals Section
(73 FR 35510, page 35534). The
statement ‘‘A surface duct may be
present * * *’’ should be replaced with
the following statement: ‘‘Surface ducts
are present approximately 53 percent of
the time.’’ Note that the Navy’s model
for estimating effects on marine
mammals incorporates the likelihood of
strong surface ducts in the HRC (pers.
comm. J. Hibbard to J. Harrison, 2007)
and the exposure estimates it produces
reflect this.
Later, in the Estimated Take of Marine
Mammals Section, NMFS relates the
potential effects to marine mammals
from MFAS/HFAS and underwater
detonation of explosives discussed here
to the MMPA regulatory definitions of
Level A and Level B Harassment, and
mortality, and quantifies those effects.
Mitigation
In order to issue an incidental take
authorization (ITA) under section
101(a)(5)(A) of the MMPA, NMFS must
prescribe regulations setting forth the
‘‘permissible methods of taking
pursuant to such activity, and other
means of affecting the least practicable
adverse impact on such species or stock
and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance.’’ The
National Defense Authorization Act
(NDAA) of 2004 amended the MMPA as
it relates to military readiness activities
and the incidental take authorization
process such that ‘‘least practicable
adverse impact’’ shall include
consideration of personnel safety,
practicality of implementation, and
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impact on the effectiveness of the
‘‘military readiness activity’’. The HRC
training activities described in the
proposed rule are considered military
readiness activities.
NMFS reviewed the Navy’s proposed
HRC activities and the proposed HRC
mitigation measures (which the Navy
refers to as Protective Measures)
presented in the Navy’s application to
determine whether the activities and
mitigation measures were capable of
achieving the least practicable adverse
effect on marine mammals. NMFS
determined that further discussion was
necessary regarding: (1) Humpback
whales congregating in the winter in the
shallow areas of the HRC in high
densities to calve and breed; and (2) the
potential relationship between the
operation of MFAS/HFAS and marine
mammal strandings.
Any mitigation measure prescribed by
NMFS should be known to accomplish,
have a reasonable likelihood of
accomplishing (based on current
science), or contribute to the
accomplishment of one or more of the
general goals listed below:
(a) Avoidance or minimization of
injury or death of marine mammals
wherever possible (goals b, c, and d may
contribute to this goal).
(b) A reduction in the numbers of
marine mammals (total number or
number at biologically important time
or location) exposed to received levels
of MFAS/HFAS, underwater
detonations, or other activities expected
to result in the take of marine mammals
(this goal may contribute to a, above, or
to reducing harassment takes only).
(c) A reduction in the number of times
(total number or number at biologically
important time or location) individuals
would be exposed to received levels of
MFAS/HFAS, underwater detonations,
or other activities expected to result in
the take of marine mammals (this goal
may contribute to a, above, or to
reducing harassment takes only).
(d) A reduction in the intensity of
exposures (either total number or
number at biologically important time
or location) to received levels of MFAS/
HFAS, underwater detonations, or other
activities expected to result in the take
of marine mammals (this goal may
contribute to a, above, or to reducing the
severity of harassment takes only).
(e) A reduction in adverse effects to
marine mammal habitat, paying special
attention to the food base, activities that
block or limit passage to or from
biologically important areas, permanent
destruction of habitat, or temporary
destruction/disturbance of habitat
during a biologically important time.
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(f) For monitoring directly related to
mitigation—an increase in the
probability of detecting marine
mammals, thus allowing for more
effective implementation of the
mitigation (shut-down zone, etc.).
NMFS worked with the Navy to
identify additional practicable and
effective mitigation measures, which
included a careful balancing of the
likely benefit of any particular measure
to the marine mammals with the likely
effect of that measure on personnel
safety, practicality of implementation,
and impact on the ‘‘military-readiness
activity’’. NMFS and the Navy
developed two additional mitigation
measures that address the concerns
mentioned above, including a
humpback whale cautionary area and a
Stranding Response Plan.
The Navy’s proposed mitigation
measures, as well as the humpback
whale cautionary area and the Stranding
Response Plan, both of which are
required under these regulations, were
described in detail in the proposed rule
(73 FR 35510, pages 35535–35541). The
Navy’s measures address personnel
training, lookout and watchstander
responsibilities, and operating
procedures for training activities using
both MFAS/HFAS and explosive
detonations. No changes have been
made to the mitigation measures
described in the proposed rule, with one
correction and one addition, addressed
in the next paragraph. The final HRC
Stranding Response Plan, which
includes a shutdown protocol, a
stranding investigation plan, and a
requirement for Navy and NMFS to
implement an MOA that will establish
a framework whereby the Navy can (and
provide the Navy examples of how they
can best) assist NMFS with stranding
investigations in certain circumstances,
may be viewed at: https://www.nmfs.
noaa.gov/pr/permits/incidental.htm#
applications. Additionally, the
mitigation measures are included in full
in the codified text of the regulations.
The proposed rule contained a
measure in which the Navy indicated
that ‘‘prior to conducting the exercise,
remotely sensed sea surface temperature
maps would be reviewed. SINKEX and
air to surface missile (ASM) Training
activities would not be conducted
within areas where strong temperature
discontinuities are present, thereby
indicating the existence of
oceanographic fronts’’ (73 FR 35510,
page 35537). The Navy included this
measure in the LOA application in
error. The removal of the measure does
not change NMFS’ analysis and
therefore the measure is not included in
the final rule. Additionally, the
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following measure has been added to
the regulations: Night vision goggles
shall be available to all ships and air
crews for use as appropriate.
NMFS has determined that the Navy’s
proposed mitigation measures (from the
LOA application), along with the
Humpback Whale Cautionary Area and
the Stranding Response Plan (and when
the Adaptive Management (see Adaptive
Management below) component is taken
into consideration) are adequate means
of effecting the least practicable adverse
impacts on marine mammal species or
stocks and their habitat, paying
particular attention to rookeries, mating
grounds, and areas of similar
significance, while also considering
personnel safety, practicality of
implementation, and impact on the
effectiveness of the military readiness
activity. The justification for this
conclusion is discussed in the
Mitigation Conclusion section of the
proposed rule (73 FR 35510, pages
35540–35541). The Mitigation
Conclusion Section of the proposed rule
has not changed.
Research and Conservation Measures
for Marine Mammals
The Navy provides a significant
amount of funding and support for
marine research. The Navy provided
$26 million in Fiscal Year 2008 and
plans for $22 million in Fiscal Year
2009 to universities, research
institutions, federal laboratories, private
companies, and independent
researchers around the world to study
marine mammals. Over the past five
years the Navy has funded over $100
million in marine mammal research.
The U.S. Navy sponsors seventy percent
of all U.S. research concerning the
effects of human-generated sound on
marine mammals and 50 percent of such
research conducted worldwide. Major
topics of Navy-supported research
include the following:
• Better understanding of marine
species distribution and important
habitat areas,
• Developing methods to detect and
monitor marine species before and
during training,
• Understanding the effects of sound
on marine mammals, sea turtles, fish,
and birds, and
• Developing tools to model and
estimate potential effects of sound.
The Navy’s Office of Naval Research
currently coordinates six programs that
examine the marine environment and
are devoted solely to studying the
effects of noise and/or the
implementation of technology tools that
will assist the Navy in studying and
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tracking marine mammals. The six
programs are as follows:
• Environmental Consequences of
Underwater Sound,
• Non-Auditory Biological Effects of
Sound on Marine Mammals,
• Effects of Sound on the Marine
Environment,
• Sensors and Models for Marine
Environmental Monitoring,
• Effects of Sound on Hearing of
Marine Animals, and
• Passive Acoustic Detection,
Classification, and Tracking of Marine
Mammals.
The Navy has also developed the
technical reports referenced within this
document and the HRC EIS, such as the
Marine Resource Assessments.
Furthermore, research cruises by NMFS
and by academic institutions have
received funding from the U.S. Navy.
The Navy has sponsored several
workshops to evaluate the current state
of knowledge and potential for future
acoustic monitoring of marine
mammals. The workshops brought
together acoustic experts and marine
biologists from the Navy and other
research organizations to present data
and information on current acoustic
monitoring research efforts and to
evaluate the potential for incorporating
similar technology and methods on
instrumented ranges. However, acoustic
detection, identification, localization,
and tracking of individual animals still
requires a significant amount of research
effort to be considered a reliable method
for marine mammal monitoring. The
Navy supports research efforts on
acoustic monitoring and will continue
to investigate the feasibility of passive
acoustics as a potential mitigation and
monitoring tool.
Overall, the Navy will continue to
fund ongoing marine mammal research,
and is planning to coordinate long term
monitoring/studies of marine mammals
on various established ranges and
operating areas. The Navy will continue
to research and contribute to university/
external research to improve the state of
the science regarding marine species
biology and acoustic effects. These
efforts include mitigation and
monitoring programs; data sharing with
NMFS and via the literature for research
and development efforts; and future
research as described previously.
Long-Term Prospective Study
Apart from this final rule, NMFS,
with input and assistance from the Navy
and several other agencies and entities,
will perform a longitudinal
observational study of marine mammal
strandings to systematically observe and
record the types of pathologies and
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diseases and investigate the relationship
with potential causal factors (e.g., sonar,
seismic, weather). The proposed rule
contained an outline of the proposed
study (73 FR 35510, pages 35541–
35542). No changes have been made to
the longitudinal study as described in
the proposed rule.
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Monitoring
In order to issue an ITA for an
activity, section 101(a)(5)(A) of the
MMPA states that NMFS must set forth
‘‘requirements pertaining to the
monitoring and reporting of such
taking’’. The MMPA implementing
regulations at 50 CFR 216.104 (a)(13)
indicate that requests for LOAs must
include the suggested means of
accomplishing the necessary monitoring
and reporting that will result in
increased knowledge of the species and
of the level of taking or impacts on
populations of marine mammals that are
expected to be present.
Monitoring measures prescribed by
NMFS should accomplish one or more
of the following general goals:
(a) An increase in the probability of
detecting marine mammals, both within
the safety zone (thus allowing for more
effective implementation of the
mitigation) and in general to generate
more data to contribute to the effects
analyses.
(b) An increase in our understanding
of how many marine mammals are
likely to be exposed to levels of MFAS/
HFAS (or explosives or other stimuli)
that we associate with specific adverse
effects, such as behavioral harassment,
TTS, or PTS.
(c) An increase in our understanding
of how marine mammals respond
(behaviorally or physiologically) to
MFAS/HFAS (at specific received
levels), explosives, or other stimuli
expected to result in take and how
anticipated adverse effects on
individuals (in different ways and to
varying degrees) may impact the
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population, species, or stock
(specifically through effects on annual
rates of recruitment or survival)
(d) An increased knowledge of the
affected species.
(e) An increase in our understanding
of the effectiveness of certain mitigation
and monitoring measures.
(f) A better understanding and record
of the manner in which the authorized
entity complies with the incidental take
authorization.
Proposed Monitoring Plan for the HRC
As NMFS indicated in the proposed
rule, the Navy has (with input from
NMFS) fleshed out the details of and
made improvements to the HRC
Monitoring Plan. Additionally, NMFS
and the Navy have incorporated a
recommendation from the public, which
recommended the Navy hold a
workshop to discuss the Navy’s
Monitoring Plan (see Monitoring
Workshop section). The final HRC
Monitoring Plan, which is summarized
below, may be viewed at https://www.
nmfs.noaa.gov/pr/permits/
incidental.htm#applications.
The draft Monitoring Plan for the HRC
has been designed as a collection of
focused ‘‘studies’’ (described fully in the
HRC Monitoring Plan) to gather data
that will allow the Navy to address the
following questions:
(a) Are marine mammals exposed to
mid-frequency active sonar (MFAS),
especially at levels associated with
adverse effects (i.e., based on NMFS’
criteria for behavioral harassment, TTS,
or PTS)? If so, at what levels are they
exposed?
(b) If marine mammals are exposed to
MFAS in the HRC, do they redistribute
geographically within the HRC as a
result of continued exposure? If so, how
long does the redistribution last?
(c) If marine mammals are exposed to
MFAS, what are their behavioral
responses to various levels?
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(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 and explosives (e.g.,
PMAP, major exercise measures agreed
to by the Navy through permitting)
effective at avoiding TTS, injury, and
mortality of marine mammals?
Data gathered in these studies will be
collected by qualified, professional
marine mammal biologists that are
experts in their field. They will use a
combination of the following methods
to collect data:
• Visual Surveys—Vessel, Aerial and
Shore-based.
• Passive Acoustic Monitoring
(PAM).
• Marine Mammal observers (MMOs)
on Navy Vessels.
• Marine Mammal Tagging.
In the five proposed study designs (all
of which cover multiple years), the
above methods will be used separately
or in combination to monitor marine
mammals in different combinations
before, during, and after training
activities utilizing MFAS/HFAS or
explosive detonations. Table 5 contains
a summary of the Monitoring effort that
is planned for each study in each year
(effort may vary slightly between years
or study type, but overall effort will
remain constant). The HRC Monitoring
Plan is designed to collect data on all
marine mammals and sea turtles
encountered during monitoring studies.
However, priority will be given to ESAlisted species and taxa in which MFAS
exposure and strandings have been
linked under certain circumstances.
Because of the important reproductive
area and the fact that humpback whales
are present in very high densities in
certain areas of the HRC, the Navy plans
to dedicate a designated subset of their
monitoring effort specifically to these
high-density areas.
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Monitoring Workshop
During the public comment period on
the proposed rule for the HRC, NMFS
received a comment which, in
consultation with the Navy, we have
chosen to incorporate into the final rule
(in a modified form). One commenter
recommended that a workshop or panel
be convened to solicit input on the
monitoring plan from researchers,
experts, and other interested parties.
The HRC proposed rule included an
adaptive management component and
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both NMFS and the Navy believe that a
workshop would provide a means for
Navy and NMFS to consider input from
participants in determining whether or
how to modify monitoring techniques to
more effectively accomplish the goals of
monitoring set forth earlier in the
document. NMFS and the Navy believe
that this workshop concept is valuable
in relation to all of the Range Complexes
and major training exercise LOAs that
NMFS is working on with the Navy at
this time, and consequently this single
Monitoring Workshop will be included
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1463
as a component of all of the LOAs that
NMFS will be processing for the Navy
in the next year or so.
The Navy, with guidance and support
from NMFS, will convene a Monitoring
Workshop, including marine mammal
and acoustic experts as well as other
interested parties, in 2011. The
Monitoring Workshop participants will
review the monitoring results from the
previous two years of monitoring
pursuant to the HRC rule as well as
monitoring results from other Navy
rules issued after HRC (e.g., the Atlantic
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Fleet Active Sonar Training, Southern
California Range Complex, and other
rules). The Monitoring Workshop
participants would provide their
individual recommendations to the
Navy and NMFS on the monitoring
plan(s) after also considering the current
science (including Navy R&D
developments) 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.
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Integrated Comprehensive Monitoring
Plan
In addition to the Monitoring Plan for
the HRC, the Navy will complete an
Integrated Comprehensive Monitoring
Program (ICMP) Plan by the end of
2009. The ICMP will provide the
overarching coordination that will
support compilation of data from rangespecific monitoring plans (e.g., HRC
Range Complex plan) as well as Navy
funded research and development (R&D)
studies. The ICMP will coordinate the
monitoring programs progress towards
meeting its goals and develop a data
management plan. The ICMP will be
evaluated annually to provide a matrix
for progress and goals for the following
year, and will make recommendations
on adaptive management for refinement
and analysis of the monitoring methods.
The primary objectives of the ICMP
are to:
• Monitor and assess the effects of
Navy activities on protected species;
• Ensure that data collected at
multiple locations is collected in a
manner that allows comparison between
and among different geographic
locations;
• Assess the efficacy and practicality
of the monitoring and mitigation
techniques;
• Add to the overall knowledge-base
of marine species and the effects of
Navy activities on marine species.
The ICMP will be used both as: (1) A
planning tool to focus Navy monitoring
priorities (pursuant to ESA/MMPA
requirements) across Navy Range
Complexes and Exercises; and (2) an
adaptive management tool, through the
consolidation and analysis of the Navy’s
monitoring and watchstander data, as
well as new information from other
Navy programs (e.g., R&D), and other
appropriate newly published
information.
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In combination with the 2011
Monitoring Workshop and the adaptive
management component of the HRC rule
and the other planned Navy rules (e.g.
AFAST and SOCAL), the ICMP could
potentially provide a framework for
restructuring the monitoring plans and
allocating monitoring effort based on the
value of particular specific monitoring
proposals (in terms of the degree to
which results would likely contribute to
stated monitoring goals, as well as the
likely technical success of the
monitoring based on a review of past
monitoring results) that have been
developed through the ICMP
framework, instead of allocating based
on maintaining an equal (or
commensurate to effects) distribution of
monitoring effort across Range
complexes. For example, if careful
prioritization and planning through the
ICMP (which would include a review of
both past monitoring results and current
scientific developments) were to show
that a large, intense monitoring effort in
Hawaii would likely provide extensive,
robust and much-needed data that could
be used to understand the effects of
sonar throughout different geographical
areas, it may be appropriate to have
other Range Complexes dedicate money,
resources, or staff to the specific
monitoring proposal identified as ‘‘high
priority’’ by the Navy and NMFS, in lieu
of focusing on smaller, lower priority
projects divided throughout their home
Range Complexes.
The ICMP will identify:
• A means by which NMFS and the
Navy would jointly consider prior years’
monitoring results and advancing
science to determine if modifications
are needed in mitigation or monitoring
measures to better effect the goals laid
out in the Mitigation and Monitoring
sections of the HRC rule.
• Guidelines for prioritizing
monitoring projects.
• If, as a result of the workshop and
similar to the example described in the
paragraph above, the Navy and NMFS
decide it is appropriate to restructure
the monitoring plans for multiple ranges
such that they are no longer evenly
allocated (by Range Complex), but
rather focused on priority monitoring
projects that are not necessarily tied to
the geographic area addressed in the
rule, the ICMP will be modified to
include a very clear and unclassified
recordkeeping system that will allow
NMFS and the public to see how each
Range Complex/project is contributing
to all of the ongoing monitoring
(resources, effort, money, etc.).
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Past Monitoring in the HRC
The proposed rule contained a
detailed review of the previous marine
mammal monitoring conducted in the
HRC, which was conducted in
compliance with the terms and
conditions of multiple biological
opinions issued for MFAS training
activities (73 FR 35510, pages 35544–
35548). No changes have been made to
the discussion contained in the
proposed rule.
Adaptive Management
The final regulations governing the
take of marine mammals incidental to
Navy training exercises in the HRC will
contain an adaptive management
component. Our understanding of the
effects of MFAS/HFAS and explosives
on marine mammals is still in its
relative infancy, and yet the science in
this field continues to improve. These
circumstances make the inclusion of an
adaptive management component both
valuable and necessary within the
context of 5-year regulations for
activities that have been associated with
marine mammal mortality in certain
circumstances and locations (though not
the HRC). The use of adaptive
management will give NMFS the ability
to consider new data from different
sources to determine (in coordination
with the Navy) on an annual basis if
mitigation or monitoring measures
should be modified or added (or
deleted) if new data suggests that such
modifications are appropriate (or are not
appropriate) for subsequent annual
LOAs.
Following are some of the possible
sources of applicable data:
• Results from the Navy’s monitoring
from the previous year (either from the
HRC or other locations).
• Findings of the Workshop that the
Navy will convene in 2011 to analyze
monitoring results to date, review
current science, and recommend
modifications, as appropriate to the
monitoring protocols to increase
monitoring effectiveness.
• Compiled results of Navy funded
research and development (R&D) studies
(presented pursuant to the ICMP, which
is discussed elsewhere in this
document).
• Results from specific stranding
investigations (either from the HRC or
other locations, and involving
coincident MFAS/HFAS or explosives
training or not involving coincident
use).
• Results from the Long Term
Prospective Study described below.
• Results from general marine
mammal and sound research (funded by
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the Navy (described below) or
otherwise).
Mitigation measures could be
modified or added (or deleted) if new
data suggest that such modifications
would have (or do not have) a
reasonable likelihood of accomplishing
the goals of mitigation laid out in this
final rule and if the measures are
practicable. NMFS would also
coordinate with the Navy to modify or
add to (or delete) the existing
monitoring requirements if the new data
suggest that the addition of (or deletion
of) a particular measure would more
effectively accomplish the goals of
monitoring laid out in this final rule.
The reporting requirements associated
with this rule are designed to provide
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 to discuss the monitoring
reports, Navy R&D developments, and
current science and whether mitigation
or monitoring modifications are
appropriate.
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Reporting
In order to issue an ITA for an
activity, section 101(a)(5)(A) of the
MMPA states that NMFS must set forth
‘‘requirements pertaining to the
monitoring and reporting of such
taking’’. Effective reporting is critical to
ensure compliance with the terms and
conditions of an LOA, and to provide
NMFS and the Navy with data of the
highest quality based on the required
monitoring.
As NMFS noted in its proposed rule,
additional detail has been added to the
reporting requirements since they were
outlined in the proposed rule. The
updated reporting requirements are all
included below. A subset of the
information provided in the monitoring
reports may be classified and not
releasable to the public.
NMFS will work with the Navy to
develop tables that allow for efficient
submission of the information required
below.
General Notification of Injured or Dead
Marine Mammals
Navy personnel will ensure that
NMFS (regional stranding coordinator)
is notified immediately (or as soon as
operational security allows) if an
injured or dead marine mammal is
found during or shortly after, and in the
vicinity of, any Navy training exercise
utilizing MFAS, HFAS, or underwater
explosive detonations. The Navy will
provide NMFS with species or
description of the animal(s), the
condition of the animal(s) (including
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carcass condition if the animal is dead),
location, time of first discovery,
observed behaviors (if alive), and photo
or video (if available). The Stranding
Response Plan contains more specific
reporting requirements for specific
circumstances.
Annual HRC Monitoring Plan Report
The Navy shall submit a report
annually on October 1 describing the
implementation and results (through
August 1 of the same year) of the HRC
Monitoring Plan, described above. Data
collection methods will be standardized
across range complexes to allow for
comparison in different geographic
locations. Although additional
information will also be gathered, the
marine mammal observers (MMOs)
collecting marine mammal data
pursuant to the HRC Monitoring Plan
shall, at a minimum, provide the same
marine mammal observation data
required in the MFAS/HFAS major
Training Exercises section of the Annual
HRC Exercise Report referenced below.
The HRC Monitoring Plan Report may
be provided to NMFS within a larger
report that includes the required
Monitoring Plan Reports from multiple
Range Complexes.
Annual HRC Exercise Report
The Navy will submit an Annual HRC
Exercise Report on October 1 of every
year (covering data gathered through
August 1 (or completion of RIMPAC if
later than Aug 1)). This report shall
contain the subsections and information
indicated below.
MFAS/HFAS Major Training Exercises
This section shall contain the
following information for Major
Training Exercises (MTEs, which
include RIMPAC, USWEX, and Multi
Strike Group) conducted in the HRC:
(a) Exercise Information (for each
MTE):
(i) Exercise designator.
(ii) Date that exercise began and
ended.
(iii) Location.
(iv) Number and types of active
sources used in the exercise.
(v) Number and types of passive
acoustic sources used in exercise.
(vi) Number and types of vessels,
aircraft, etc., participating in exercise.
(vii) Total hours of observation by
watchstanders.
(viii) Total hours of all active sonar
source operation.
(ix) Total hours of each active sonar
source (along with explanation of how
hours are calculated for sources
typically quantified in alternate way
(buoys, torpedoes, etc.)).
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(x) Wave height (high, low, and
average during exercise).
(b) Individual marine mammal
sighting info (for each sighting in each
MTE).
(i) Location of sighting.
(ii) Species (if not possible—
indication of whale/dolphin/pinniped).
(iii) Number of individuals.
(iv) Calves observed (y/n).
(v) Initial Detection Sensor.
(vi) Indication of specific type of
platform observation made from
(including, for example, what type of
surface vessel, i.e., FFG, DDG, or CG)
(vii) Length of time observers
maintained visual contact with marine
mammal(s).
(viii) Wave height (in feet).
(ix) Visibility.
(x) Sonar source in use (y/n).
(xi) Indication of whether animal is
<200yd, 200–500yd, 500–1000yd, 1000–
2000yd, or >2000yd from sonar source
in (x) above.
(xiii) Mitigation Implementation—
Whether operation of sonar sensor was
delayed, or sonar was powered or shut
down, and how long the delay was.
(xiv) If source in use (x) is
hullmounted, true bearing of animal
from ship, true direction of ship’s travel,
and estimation of animal’s motion
relative to ship (opening, closing,
parallel)
(xv) Observed behavior—
Watchstanders shall report, in plain
language and without trying to
categorize in any way, the observed
behavior of the animals (such as animal
closing to bow ride, paralleling course/
speed, floating on surface and not
swimming, etc.)
(c) An evaluation (based on data
gathered during all of the MTEs) of the
effectiveness of mitigation measures
designed to avoid exposing marine
mammals to mid-frequency sonar. This
evaluation shall identify the specific
observations that support any
conclusions the Navy reaches about the
effectiveness of the mitigation.
ASW Summary
This section shall include the
following information as summarized
from both MTEs and non-major training
exercises (unit-level exercises, such as
TRACKEXs):
(i) Total annual hours of each type of
sonar source (along with explanation of
how hours are calculated for sources
typically quantified in alternate way
(buoys, torpedoes, etc.))
(ii) Total hours (from December 15
through April 15) of hullmounted active
sonar operation occurring in the dense
humpback areas generally shown on the
Mobley map (73 FR 35510, page 35520)
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plus a 5-km buffer, but not including the
Pacific Missile Range Facility. NMFS
and the Navy will work together to
develop the exact boundaries of this
area.
(iii) Total estimated annual hours of
hull-mounted active sonar operation
conducted in Humpback Whale
Cautionary area between December 15
and April 15.
(iv) Cumulative Impact Report—To
the extent practicable, the Navy, in
coordination with NMFS, shall develop
and implement a method of annually
reporting non-major (i.e., other than
RIMPAC, USWEX, or Multi-Strike
Group Exercises) training exercises
utilizing hull-mounted sonar. The report
shall present an annual (and seasonal,
where practicable) depiction of nonmajor training exercises geographically
across the HRC. The Navy shall include
(in the HRC 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.
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SINKEXs
This section shall include the
following information for each SINKEX
completed that year:
(a) 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).
(ix) Narrative description of sensors
and platforms utilized for marine
mammal detection and timeline
illustrating how marine mammal
detection was conducted.
(b) Individual marine mammal
observation (by Navy lookouts) info.
(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.
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(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: (1) The modeled injury
threshold radius for the largest
explosive used in that exercise type in
that OPAREA (91 m for SINKEX in
HRC); (2) the required exclusion zone (1
nm for SINKEX in HRC); (3) the
required observation distance (if
different than the exclusion zone (2 nm
for SINKEX in HRC); and (4) greater
than the required observed distance. For
example, in this case, the observer
would indicate if < 91 m, from 91 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 munition type in use at time of
marine mammal detection.
Improved Extended Echo-Ranging
System (IEER) Summary
This section shall include an annual
summary of the following IEER
information:
(i) Total number of IEER events
conducted in the HRC.
(ii) Total expended/detonated rounds
(buoys).
(iii) Total number of self-scuttled
IEER rounds.
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 will provide the information
described below for all of their
explosive exercises. Until the Navy 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.
(i) Total annual number of each type
of explosive exercise (of those identified
as part of the ‘‘specified activity’’ in this
final rule) conducted in the HRC.
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(iii) Total annual expended/detonated
rounds (missiles, bombs, etc.) for each
explosive type.
Sonar Exercise Notification
The Navy shall submit to the NMFS
Office of Protected Resources (specific
contact information to be provided in
LOA) either an electronic (preferably) or
verbal report within fifteen calendar
days after the completion of any major
exercise (RIMPAC, USWEX, or Multi
Strike Group) indicating:
(1) Location of the exercise.
(2) Beginning and end dates of the
exercise.
(3) Type of exercise (i.e., RIMPAC,
USWEX, or Multi Strike Group).
HRC 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
HRC Exercise Reports and HRC
Monitoring Plan Reports). This report
will be submitted at the end of the
fourth year of the rule (November 2012),
covering activities that have occurred
through June 1, 2012.
Comprehensive National ASW Report
By June, 2014, the Navy shall submit
a draft National Report that analyzes,
compares, and summarizes the active
sonar data gathered (through January 1,
2014) from the watchstanders and
pursuant to the implementation of the
Monitoring Plans the HRC, the Atlantic
Fleet Active Sonar Training, the
Southern California (SOCAL) Range
Complex, the Marianas Range Complex,
the Northwest Training Range, the Gulf
of Alaska, and the East Coast Undersea
Warfare Training Range.
The Navy shall respond to NMFS
comments and requests for additional
information or clarification on the HRC
Comprehensive Report, the
Comprehensive National ASW report,
the Annual HRC Exercise Report, or the
Annual HRC Monitoring Plan Report (or
the multi-Range Complex Annual
Monitoring Plan Report, if that is how
the Navy chooses to submit the
information) if submitted within 3
months of receipt. These reports will be
considered final after the Navy has
addressed NMFS’ comments or
provided the requested information, or
three months after the submittal of the
draft if NMFS does not comment by
then.
Comments and Responses
On June 23, 2008 (73 FR 35510),
NMFS published a proposed rule in
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response to the Navy’s request to take
marine mammals incidental to military
readiness training exercises in the HRC
and requested comments, information
and suggestions concerning the request.
During the 30-day public comment
period, NMFS received 8 comments
from private citizens, comments from
the Marine Mammal Commission
(MMC) and the Office of Hawaiian
Affairs, and several sets of comments
from non-governmental organizations,
including, the Natural Resources
Defense Council (NRDC) (which
commented on behalf of The Humane
Society of the United States, the
International Fund for Animal Welfare,
Cetacean Society International, Ocean
Mammal Institute, the International
Ocean Noise Coalition, Seaflow, and the
Ocean Futures Society and its founder
Jean-Michel Cousteau), the Cascadia
Research Collective (CRC), Ziphius
EcoServices, and Smultea
Environmental Sciences, LLC. The
comments are summarized and sorted
into general topic areas and are
addressed below. Full copies of the
comment letters may be accessed at
https://www.regulations.gov.
Monitoring and Reporting
Comment 1: One commenter stated
that ‘‘It is advisable to hold a multi-day
workshop to discuss controversial
issues related to the problem.’’ The
commenter further indicated that the
workshop should include
representatives from the Navy, NMFS,
relevant marine mammal researchers,
NGOs (e.g., NRDC), and invited experts
on certain topics of interest. The goal of
the workshop should be to move
towards consensus on a way forward for
the monitoring plan.
Response: NMFS believes that a
workshop consisting of the Navy,
NMFS, researchers, invited experts, and
other interested parties, in combination
with an adaptive management plan that
allows for modification to the
monitoring plan, would provide a
means for the Navy to potentially make
changes to the Monitoring Plan that
would more effectively accomplish
some of the goals of monitoring set forth
earlier in the Monitoring section. NMFS
and the Navy have coordinated on this
point and the Navy will convene a
workshop in 2011. The workshop and
how it will interact with the adaptive
management component are discussed
in the Monitoring Workshop section of
this final rule. The Monitoring
Workshop participants will be asked to
submit individual recommendations to
the Navy and NMFS, and both agencies
will work together to determine whether
modifications to the HRC monitoring are
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necessary based on the
recommendations. As necessary, NMFS
would incorporate any changes into
future LOAs and future rules. However,
we disagree with the commenter’s
suggestion that the workshop
participants seek to achieve consensus
on a way forward for the monitoring
plan. NMFS has statutory responsibility
to prescribe regulations pertaining to
monitoring and reporting, and will, in
coordination with the Navy, develop the
most effective and appropriate
monitoring and reporting protocols for
future authorizations.
Comment 2: Two commenters made
several recommendations regarding the
formatting and understandability of the
monitoring plan.
Response: NMFS incorporated these
recommendations where appropriate.
For example, a map of the area that the
ICMP covers was added to the plan, a
list of the animals in the HRC was
added, and bulleted lists will replace
long paragraphs in some places.
However, we did not incorporate the
commenters recommendations in all
cases, for example, the commenter
recommended that a lot of the analysis
contained in the proposed rule be
included in the Monitoring plan, such
as a summary of Southall et al., 2007,
or the regulatory definitions of Level A
and Level B harassment, which NMFS
believes would needlessly lengthen and
complicate the Plan and generally be
duplicative.
Comment 3: Two commenters asked
for more detail, and associated
references, in several areas of the
methods sections.
Response: NMFS has provided
additional detail (including citations)
concerning the survey methods used in
the monitoring plan in the final rule.
Comment 4: One commenter stated:
‘‘The Navy improperly assumes that
they have no impact on the marine
mammals. It is clear that the draft plan
begins with the assumption that the
Navy has no impact on marine
mammals, or that the current mitigation
is adequate to eliminate impacts. This is
not supported by facts, and it
invalidates the entire purpose of the
plan. The Navy must acknowledge that
sonar testing may indeed impact marine
mammals and provide references, and
must be willing to work as an active
partner in a plan to investigate the
extent and severity of such impacts, and
how to reduce them to insignificant
levels. Otherwise, this entire exercise is
just ‘window dressing’ and will be a
major waste of taxpayer dollars.’’
Response: NMFS disagrees with this
commenter’s assertion. It is possible that
the commenter mistook the fact that the
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Navy phrased some of their goals as null
hypotheses (‘‘If marine mammals and
sea turtles are exposed to MFAS, what
are their behavioral responses? Are they
different at various levels?’’) to mean
that they think there are no effects. The
Navy’s LOA application and EIS clearly
discuss the potential adverse effects that
marine mammals may experience when
exposed to MFAS. The Navy has
worked and will continue to work as an
active partner to investigate the extent
and severity of the impacts and how to
reduce them (see Navy Research section
of this final rule).
Comment 5: A few commenters asked
why the Navy did not consider
additional survey methods, or
modifications to the existing methods,
beyond those currently included in the
plan, such as: Specified focal follows of
one animal before, during, and after
sonar; photo-identification of marine
mammals to look at residency patterns;
having a helicopter on board, on call to
opportunistically observe marine
mammals around sonar transmissions;
or doing biopsy sampling to assess
stress hormones.
Response: There are a lot of different
methods available with which to
monitor marine mammals and the Navy
considered a wide range of methods in
the development of their plan. NMFS
considered all of the public comments
(including the recommended additional
survey methods) received during this
rulemaking. Some of the methods
suggested by the public, such as the
photo-identification method, would
likely be feasible and provide useful
information, while other methods, such
as having a helicopter on standby,
would be difficult both financially and
operationally. Nevertheless, the Navy
must work within the framework of the
available resources and the operational
constraints associated with doing work
in the vicinity of a complex military
exercise. NMFS provided input during
the development of the plan and
believes that results from the required
monitoring will provide valuable
information regarding the effects of
MFAS on marine mammals.
Additionally, by including the
Monitoring Plan as a requirement of the
LOA, NMFS is compliant with the
MMPA requirement to prescribe
regulations setting forth the
requirements pertaining to the
monitoring and reporting of taking. That
being said, the Navy and NMFS
understand the importance of marine
mammal monitoring to determine the
effects of MFAS, which is why the Navy
agreed to conduct the Workshop
referred to in Comment 1 during which
the workshop participants will review
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and assess the monitoring results (from
this Monitoring Plan and others from
other Range complexes and areas) and
make informed recommendations for
how to move forward with the best
Monitoring strategy.
Comment 6: The Marine Mammal
Commission was supportive of the use
of Adaptive Management, but wanted a
more detailed implementation plan.
Response: NMFS has included
additional detail regarding how
adaptive management will be
implemented. Please see the Adaptive
Management, Monitoring Workshop,
and Integrated Comprehensive
Monitoring Plan sections of the final
rule.
Comment 7: Multiple commenters
questioned whether the Marine
Mammal Observers identified in the
Monitoring Plan are independent
scientists or Navy employees? Some
commenters questioned the objectivity
of Navy scientists.
Response: Independent scientists will
be conducting the vast majority of the
observations pursuant to the Monitoring
Plan. Navy scientists will be involved in
a small portion of the field work and
some of the post-monitoring analysis.
The Navy is responsible for both the
funding and implementation of a
substantial amount of marine mammal
and acoustic research and NMFS has no
concerns regarding the objectivity of the
reported results from either these
research projects or the monitoring
required pursuant to the MMPA
authorization.
Comment 8: During aerial surveys,
information on headings/orientation of
animals should be collected as these
data can later be examined to assess
movement/response of animals relative
to locations and received sound levels
of MFAS and underwater detonations.
Response: As NMFS noted in the
proposed rule, additional detail has
been added to the Reporting
Requirements section of the final rule. A
requirement that Navy lookouts report
the relative directions of both the
marine mammals and the sonar source
has been included. NMFS also included
a requirement that the MMOs collecting
data for the Monitoring Plan collect, at
a minimum, the same data outlined in
the Reporting Requirements section for
the Navy lookouts.
Comment 9: One commenter was
concerned that the Navy would not
begin collecting data until mid-late 2009
when the ICMP was finalized.
Response: The ICMP is an overarching
framework for all of the Navy’s Rangespecific MMPA Monitoring Plans and
does not include a field-work
component (rather it addresses
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prioritization, standardization, and
summarization of actual data-gathering).
The Navy actually began doing some of
the data collection in 2007 outside of
the commitments made through the
HRC EIS process, and they will begin
collecting field data pursuant to the
HRC-specific Monitoring Plan shortly
after the authorized exercises begin in
early 2009.
Comment 10: Two commenters
questioned whether the Navy had
considered whether a statistically sound
sample size had been developed to
answer the questions that the
monitoring is trying to answer. One
commenter stated: ‘‘To determine the
sample sizes required to assess impacts
and the validity of this monitoring
effort, the statistical power should be
estimated, with a range of potential
effect sizes, and taking into account
information available from previous
monitoring efforts with vessel or aerial
platforms, to predict sighting rates given
the amount of effort planned. Planning
on, for example, 40 hours of aerial
surveys associated with a particular
exercise, is likely to provide such small
sample sizes of sightings that the power
to assess redistribution of animals may
be close to zero.’’
Response: The Navy will contract a
team of marine mammal experts to
determine monitoring plan
implementation, sample size and
analysis parameters. The data from
Hawaii will be pooled (as appropriate)
with data collected from other range
complexes to maximize data collection
each year. No conclusions will be made
without statistically valid sample size.
Furthermore, the study designed to
assess the redistribution of animals not
only uses aerial surveys, but aerial
surveys in conjunction with a passive
acoustic component to include an array
of ten to fifteen autonomous acoustic
recording buoys, such as a Highfrequency Acoustic Recording Package
(HARP), which will be deployed for
months at a time. Using both of these
methods together, the Navy is more
likely to detect a change in the
distribution of marine mammals.
Comment 11: One commenter asserts
that the deployment of five satellite tags
on individuals prior to an exercise is not
likely to be sufficient to assess reactions
or redistribution during the exercise.
Response: The Navy has revised the
HRC Monitoring Plan such that the goal
is to tag 15 animals in FY 2010, 25
animals in FY 2011, and 30 animals in
both FY 2012 and 2013.
Comment 12: One commenter stated:
‘‘A large proportion of marine mammals
are missed in aerial surveys; this needs
to be taken into account when assessing
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the efficacy of using aerial surveys for
monitoring potential behavioral
impacts. The fact that observers onboard naval vessels sighted no marine
mammals during USWEX 06–04 and
07–02 illustrates either that marine
mammals are strongly reacting to
sounds produced by these vessels at
distances far greater than the observers
are able to monitor (and are thus not
being detected), or that the on-board
observer program for mitigating impacts
is extremely ineffective, contrary to the
statement that ‘data from watchstanders
is generally useful to indicate the
presence or absence of marine mammals
within the safety zones’ (pg. 35547).’’
Response: The Navy has considered
the strengths and weaknesses of the
different marine mammal survey
methods in the development of the
Monitoring Plan. In order to monitor
potential behavioral effects, the Navy’s
HRC Monitoring Plan outlines a study
design that includes aerial monitoring,
vessel monitoring, passive acoustic
monitoring, and marine mammal
tagging. NMFS disagrees with the
assertion that a lack of marine mammal
sightings during two exercises means
that marine mammals must be strongly
reacting at great distances—rather, it
could mean that animals are avoiding
the sound at a distance beyond which
the watchstanders can see (which would
not necessarily be classified as a strong
reaction), and separately, it could be a
reflection of the low marine mammal
density in offshore Hawaii (also—we
note that in some cases lookouts were
only required to report the marine
mammals that were detected within
2000 m—so other animals may have
been detected at greater distances, but
not reported. That issue has been
corrected in the current reporting
requirements, which require lookouts to
report all sightings). The mitigation
powerdown and shutdown zones are
relatively close to the ship (1000, 500,
and 200 yd) and there is no indication
that lookouts are missing animals that
are visibly detectable within these
distances—Navy After Action Reports
show anywhere from 0 to 26 marine
mammal sightings in Hawaii for one
exercise, and up to 133 sightings during
an exercise in California, and report
many sonar shutdowns (often when
animals are much farther from the
source than the distance at which
shutdowns are required). Nonetheless,
the Navy’s Monitoring Plan includes a
study designed to compare the detection
rate of Navy lookouts (who are
responsible for detecting marine
mammals for mitigation
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implementation) to scientifically trained
marine mammal observers.
Comment 13: One commenter noted:
‘‘The location of the Navy’s training
exercises are highly variable, with the
exception of the Navy’s ranges (PMRF,
etc.)’’ This commenter further asked if
these ranges are being studied and
whether there are fewer marine
mammals in frequently used ranges than
one might expect.
Response: The PMRF does not have
one of prototype systems being tested at
both the SOAR (Southern California
Range Complex) and AUTEC (Bahamas)
ranges. This prototype system being
tested at SOAR and AUTEC currently
has a limited ability to detect and
localize a few numbers of two species of
beaked whales of marine mammals in
real time. At PMRF, data collected from
range hydrophones have observed over
100,000 acoustic detections per hour
and, on some, over 6 million acoustic
detections in one day. This acoustic
data may suggest more marine mammals
present than expected (based on current
stock assessment numbers). The range at
PMRF is not currently being utilized for
the analysis of marine mammal behavior
during training exercises. The HRC
Monitoring Plan does not contain a
specific monitoring component for
PMRF. It is difficult to make inferences
regarding the reasons for marine
mammal use (i.e., the number of
animals) in any particular area with
focused anthropogenic activities if
observations were not made prior to the
focused human activities. However, for
the East Coast Undersea Warfare
Training Range Complex (USWTR), the
Navy has developed and implemented a
monitoring plan that is surveying for
marine mammals years in advance of
the construction of the Range (which
consists primarily of a large array of
hydrophones) so that the abundance
and distribution of marine mammals
can be compared before and after the
construction and operation of the Range.
Mitigation
Comment 14: One commenter asserts
that NMFS’ analysis ignores or
improperly discounts an array of
options that have been considered and
imposed by other active sonar users,
including avoidance of coastal waters,
high-value habitat, and complex
topography; the employment of a safety
zone more protective than the 1000-yard
power-down and 200-yard shutdown
accepted by NMFS; general passive
acoustic monitoring for whales; special
rules for surface ducting and lowvisibility conditions; monitoring and
shutdown procedures for sea turtles and
large schools of fish; and many others.
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The commenter further provides a
detailed list of 30 additional measures
that should be considered. Other
commenters made additional
recommendations of mitigation
measures that should be considered.
Response: NMFS considered a wide
range of mitigation options in our
analysis, including those listed by the
commenters. In order to issue an
incidental take authorization (ITA)
under Section 101(a)(5)(A) of the
MMPA, NMFS must set forth the
‘‘permissible methods of taking
pursuant to such activity, and other
means of affecting the least practicable
adverse impact on such species or stock
and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance.’’ The
National Defense Authorization Act
(NDAA) of 2004 amended the MMPA as
it relates to military-readiness activities
(which these Navy activities are) and
the incidental take authorization
process such that ‘‘least practicable
adverse impact’’ shall include
consideration of personnel safety,
practicality of implementation, and
impact on the effectiveness of the
‘‘military readiness activity’’. NMFS
worked with the Navy to identify
practicable and effective mitigation
measures, which included a careful
balancing of the likely benefit of any
particular measure to the marine
mammals with the likely effect of that
measure on personnel safety,
practicality of implementation, and
impact on the ‘‘military-readiness
activity’’. NMFS developed an
Environmental Assessment (EA)
specifically to help analyze the available
mitigation measures in regard to
potential benefits for marine mammals
(see goals of mitigation in the Mitigation
section of this proposed rule) and
practicability for the Navy. That EA,
which considered all of the measures
recommended by these public
comments, is currently available on the
NMFS Web site (https://www.nmfs.noaa.
gov/pr/permits/incidental.htm#
applications).
Comment 15: One commenter stated:
‘‘The Navy should conduct long-term
research on the distribution, abundance,
and population structuring of protected
species in the HRC. They should also
conduct research and development of
technologies to reduce the impacts of
active acoustic sources on marine
mammals.’’
Response: The MMPA does not
require that individuals who have
received an incidental take
authorization conduct research.
However, the Navy has voluntarily
developed and funded a number of
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research plans that are designed to
address the issues raised by the
commenter (see Research section).
Comment 16: One commenter asked
whether the Navy intends to forewarn
marine mammals by using small
explosions or noise so that marine
mammals would not be exposed to
hazardous detonations.
Response: No. However, there are
range clearance procedures to minimize
the likelihood that animals would be
exposed to hazardous levels of sound or
pressure (see Mitigation section).
Comment 17: The marine species
awareness training (MSAT) should be
updated more often. So little is known
about effects of sonar and underwater
noise, and ongoing research constantly
changes assumptions. NMFS, not the
Navy, should decide when updates are
‘‘appropriate.’’
Response: The Navy solicited input
from NMFS on the MSAT training,
initially, and NMFS will continue to
make recommendations regarding the
MSAT training, as appropriate.
However, a large portion of the
information contained in the training is
of a general nature that does not
necessarily require frequent updates.
Comment 18: One commenter asked
about the duration of a lookout’s shift
and was concerned that lookouts may
fatigue quickly.
Response: Navy lookouts are critical
to both training and operational success,
as well as personnel safety. The Navy
takes the potential fatigue of the lookout
into consideration when scheduling
them. A typical lookout shift is 4 hours,
with the lookout rotating into a different
location every 1 hour. NMFS does not
believe that fatigue would set in within
this relatively short time and typically
recommends no longer than a 4-hour
shift for marine mammal observers.
Comment 19: NRDC recommends
prescription of specific mitigation
requirements for individual categories
(or sub-categories) of testing and
training activities, in order to maximize
mitigation given varying sets of
operational needs. Also, the Navy
should require that other nations abide
by U.S. mitigation measures when
training in the HRC, except where their
own measures are more stringent.
Response: The Navy’s standard
protective measures include measures
that are specific to certain categories of
activities. For example, different
exclusion zones are utilized for hullmounted sonar and dipping sonar, and
different range clearance procedures are
used for SINKEXs and IEER exercises.
Pursuant to the Navy’s 2000 Policy for
Environmental Compliance at Sea,
when foreign navies participate in
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exercises with the U.S. Navy, the U.S.
Navy provides them with the mitigation
requirements (under the MMPA and
ESA) and strongly encourages foreign
navies to implement the mitigation
requirements.
Comment 20: The Marine Mammal
Commission recommends that, if the
National Marine Fisheries Service issues
a final rule to authorize the taking of
small numbers of marine mammals
incidental to the proposed military
training operations, the Navy be
required to:
• Explain all analytical procedures
and provide all data used to estimate
take levels in sufficient detail that
reviewers can understand, reconstruct,
and verify the estimated risks;
• Calibrate and verify the
performance of the proposed visual and
passive acoustic monitoring programs
before operations begin so that all
interested parties can evaluate the
effectiveness of the mitigation measures;
• Retain the power-down or
shutdown period of 30 minutes for most
marine mammals, expand it to 60
minutes for deep-diving species, and
provide follow-up data on the
effectiveness and costs associated with
this mitigation measure;
• Suspend activities if a beaked
whale or other marine mammal is killed
or seriously injured and the death or
injury appears to be associated with that
activity, and resume the activity only
after a review by the Service of the
circumstances of the death or injury and
the Navy’s plans for avoiding additional
incidents; and
• Provide a release date for the
comprehensive report of monitoring and
watchstander data from operations in
the HRC, the Southern California Range
Complex, and Atlantic Fleet Active
Sonar Training activities.
Response: Following are the
responses to the MMCs bulleted
recommendations:
• NMFS believes that Appendix J of
the Navy’s HRC EIS (which is
referenced in the rule) adequately
explains the analytical procedures and
provides the data used to estimate take
levels in sufficient detail that the
reviewers can understand and verify the
estimated risks. However, reviewers
would not be able to reconstruct the
process exactly because inherent to the
overall exposure model is the CASS/
GRAB submodel, the specific details of
which cannot be included in the EIS
because the model is a Navy owned,
restricted distribution model available
only to U.S. Government Agencies and
their contractors. This high fidelity
acoustic propagation model (CASS/
GRAB) used for marine mammal effects
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analysis is the same model used for the
operational use of tactical sonar, and it
is included in the Navy’s Oceanographic
and Atmospheric Master Library
(OAML), which has a rigorous
acceptance process for all databases,
models and algorithms prior to being
accepted into OAML.
• Navy lookouts are specifically
trained to detect anomalies in the water
around the ship and both the safety of
Navy personnel and success in the
training exercise depend on the lookout
being able to detect objects (or marine
mammals) effectively around the ship.
NMFS has reviewed the Navy’s After
Action Reports from previous exercises
and they show that lookouts are
detecting marine mammals, and
implementing sonar shutdowns as
required when they do. That said, the
HRC Monitoring Plan contains a study
in which Navy lookouts will be on
watch simultaneously with non-Navy
marine mammal observers and their
detection rates will be compared. The
Navy’s HRC Monitoring Plan contains a
segment that will compare the detection
capabilities of Navy watchstanders to
non-Navy marine mammal observers.
The passive acoustic systems used to
assist with marine mammal detection
are the same systems used in the tactical
training, and their performance must be
regularly calibrated and verified in
order to be effectively used in the
training exercises. Additionally, the
regulations and subsequent
authorization would require the Navy to
provide ‘‘an evaluation (based on data
gathered during all of the major training
exercises) of the effectiveness of
mitigation measures designed to avoid
exposing marine mammals to midfrequency sonar. This evaluation shall
identify the specific observations that
support any conclusions the Navy
reaches about the effectiveness of the
mitigation included in the
authorization.’’ Last, the rule contains
an adaptive management component
that specifies that NMFS and the Navy
will meet on an annual basis to evaluate
the Navy Reports (on both Navy lookout
observations as well as Monitoring Plan
reporting) and other new information
(such as Navy R & D developments or
new science) to ascertain whether
mitigation or monitoring modifications
are appropriate.
• NMFS does retain the power-down
or shutdown period of 30 minutes for
most marine mammals, but does not
concur with the MMC that we should
expand the delay (until sonar can be
restarted after a shutdown due to a
marine mammal sighting) to 60 minutes
for deep-diving species for the following
reasons:
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• Just because an animal can dive for
longer than 30 minutes does not mean
that they always do, so the 60 minute
delay would only potentially add value
in instances when animals had
remained under water for more than 30
minutes.
• Navy vessels typically move at 10–
12 knots (5–6 m/sec) when operating
sonar and potentially much faster when
not. Fish et. al. (2006) measured speeds
of 7 species of odontocetes and found
that they ranged from 1.4–7.30 m/sec.
Essentially, if a vessel was moving at the
typical sonar speed, or faster, an animal
would need to be swimming near max
speed for an hour to stay within the
safety zone of a vessel. This further
narrows the circumstances in which the
60-minute delay would add value.
• Additionally, the animal would
need to have stayed in the immediate
vicinity of the sound source for an hour.
Considering the maximum area that
both the vessel and the animal could
cover in an hour, it is improbable that
this would randomly occur. Moreover,
considering that many animals have
been shown to avoid both acoustic
sources and ships without acoustic
sources, it is improbable that a deepdiving cetacean (as opposed to a
dolphin that might bow ride) would
choose to remain in the immediate
vicinity of the source. NMFS believes
that it is unlikely that a single cetacean
would remain in the safety zone of a
Navy sound source for more than 30
minutes.
• Last, in many cases, the lookouts
are not able to differentiate species to
the degree that would be necessary to
implement this measure. Plus, Navy
operators have indicated that increasing
the number of mitigation decisions that
need to be made based on biological
information is more difficult for the
lookouts (because it is not their area of
expertise). In this case NMFS does not
believe that it will add to the protection
of marine mammals in the vast majority
of cases, and therefore we have not
required it.
• NMFS is requiring the Navy to
abide by a Stranding Response Plan
(viewable at https://www.nmfs.noaa.gov/
pr/permits/incidental.htm#applications)
that clearly lays out the steps the Navy
would take in the event of a stranding
and summarizes how NMFS plans to
handle the investigation in a timely
manner. In the event of a live stranding,
there is a 14-nm area around the
animals in which the Navy will not
operate sonar—to ensure that the
distressed animals are not put at further
risk. In the event of a stranding
involving dead animals—NMFS’
investigation will ideally include an
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aerial survey to ensure that additional
animals are not stranded in the vicinity.
However, if the stranded animals are
dead, the Navy will not be required to
shut down. It is not possible to
immediately determine whether sonar
contributed to a marine mammal
stranding and investigations into the
cause of death of stranded marine
mammals take months or more to
complete, and are often inconclusive. It
would be impracticable to delay the
Navy’s training activities for an
indeterminate amount of time when we
have no idea if their action contributed
to the stranding. That said, NMFS and
the Navy are committed to fully
investigating strandings that occur
coincident with major Navy training
exercises and to using any information
gathered in the implementation of
adaptive management.
Comment 21: The Navy should apply
mitigation prescribed by the Hawaii
Office of Planning and other state
regulators, by the courts, by other navies
or research centers, or by the U.S. Navy
in the past or in other contexts. In
addition, the Navy should engage in
timely and regular reporting to NOAA,
state coastal management authorities,
and the public to describe and verify
use of mitigation measures during
testing and training activities.
Response: NMFS (with input from the
Navy) has considered recommendations
that have been received from the
sources the commenter cites above. As
mentioned in the response to Comment
14, NMFS developed an Environmental
Assessment (EA), which is available at
https://www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications,
specifically to help analyze the available
mitigation measures in regard to
potential benefits for marine mammals
(see goals of mitigation in the Mitigation
section of this proposed rule) and
practicability for the Navy. The Navy
will be required to submit annual
reports and these reports will be made
available to the public upon the Notice
to the public (in the Federal Register) of
the issuance of subsequent LOAs. The
reports will include a description of the
mitigation measures implemented
during major exercises and will also
include an evaluation of the
effectiveness of any mitigation measure
implemented.
Acoustic Threshold for Behavioral
Harassment
Comment 22: The NRDC submitted a
comprehensive critique of the risk
function (authored by Dr. David Bain),
which NMFS has posted on our Web
site (https://www.nmfs.noaa.gov/pr/
permits/incidental.htm#applications).
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NRDC summarized some general
limitations of the risk function and
included a fairly detailed critique of the
specific structure of and parameters
chosen for use in the model. Following
are some of the general topics addressed
in the letter:
• Factors that Dr. Bain thinks should
be addressed by the model, such as
social interactions and multiple sources.
• Critique of the datasets that NMFS
used to populate the risk function
(described Level B Harasssment—Risk
Function section of the proposed rule):
(1) Controlled Laboratory Experiments
with Odontocetes (SSC Dataset); (2)
Mysticete Field Study (Nowacek et. al.,
2004), and (3) Odontocet Field Data
(Haro Strait—USS Shoup).
• Consideration of some datasets that
were considered by NMFS, but not used
in the risk function.
• A critique of the parameters (A, B,
and K) used in the risk function.
• A sensitivity analysis of the
parameters (i.e., takes were modeled
while applying variable values for the
A, B, and K values).
Dr. Bain included a summary of his
concerns and an abbreviated version is
included below. Additionally (and not
included in the summary), Dr. Bain
suggested that the effect of multiple
sources may be both different and
greater than the effects of fewer sources
and provided supporting examples.
Dr. Bain’s Summary follows
(comments that were in Dr. Bains
summary, but have been addressed
elsewhere in this Comment Response
section, are not included below):
• In summary, development of a
function that recognizes individual
variation is a step in the right direction.
• The selected equation is likely to
produce underestimates of takes due to
asymmetries in the number of
individuals affected if parameters are
either underestimated or overestimated
due to uncertainty. Thus it will be
important to use the risk function in a
precautionary manner.
• The sensitivity analysis reveals the
importance of using as many datasets as
possible. First, for historical reasons,
there has been an emphasis on high
energy noise sources and the species
tolerant enough of noise to be observed
near them. Exclusion of the rarer
datasets demonstrating responses to low
levels of noise biases the average
parameter values, and hence
underestimates effects on sensitive
species.
• A similar mistake was made with
the right whale data. The level at which
100 percent of individuals responded
was used as the value at which 50
percent of individuals responded (B+K).
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Likewise, the level at which 100 percent
of killer whales responded to midfrequency sonar is less than the value
derived for B+K in the HRC SDEIS
(Dept. Navy 2008b).
• It is likely that biological B values
should be in the range from just
detectable above ambient noise to120
dB re 1 μPa. The resulting mathematical
B value could be tens of dB lower, not
the 120 dB re 1 μPa proposed. For many
species, risk may approach 100 percent
in the range from 120–135 dB re 1 μPa,
putting K in the 15–45 dB range.
• The A values do not seem well
supported by the data, and in any case,
are likely to be misleading in social
species as the risk function is likely to
be asymmetrical with a disproportionate
number of individuals responding at
low noise levels. Rather than one
equation fitting all species well,
parameters are likely to be species
typical.
• As realistic parameter values are
lower than those employed in the HRC
SDEIS (Dept. Navy 2008b), AFAST DEIS
(Dept. Navy 2008a) and related DEIS’s,
take numbers should be recalculated to
reflect the larger numbers of individuals
likely to be taken. The difference
between the parameter values estimated
here and those used in the SDEIS
suggests takes were underestimated by
two orders of magnitude.
Response: Many of the limitations
outlined in Dr. Bains document were
raised by other commenters and are
addressed elsewhere in this Comment
and Response Section and will not be
raised and addressed again here. Below,
NMFS responds to the specific points
summarized above.
• The effects of multiple sources:
Mathematically, the Navy’s exposure
model has already accounted for takes
of animals exposed to multiple sources
in the number of estimated takes. NMFS
concurs with the commenter, however,
in noting that the severity of responses
of the small subset of animals that are
actually exposed to multiple sources
simultaneously could potentially be
greater than animals exposed to a single
source due to the fact that received
level, both SPL and SEL, would be
slightly higher and because contextually
it could be perceived as more
threatening to an animal to receive
multiple stimuli coming from
potentially multiple directions at once
(for example, marine mammals have
been shown to respond more severely to
sources coming directly towards them,
vs. obliquely (Wartzok, 2004)).
However, it is also worth noting that
according to information provided by
the Navy, surface vessels do not
typically operate closer than 10–20
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miles from another surface vessel (and
greater distance is ideal), and other
sonar sources, such as dipping sonar
and sonobuoys, are almost always used
20 or more miles away from the surface
vessel. This means that if the two most
powerful sources were operating at the
closest distance they are likely to (10
miles), in the worst case scenario,
animals that would have been exposed
to 150 dB SPL or less (taken from table
16 of the proposed rule) may be exposed
to slightly higher levels or to similar
levels or less coming from multiple
directions.
• Underestimates of takes due to
asymmetries in the number of
individuals affected when parameters
are underestimated and overestimated
due to uncertainty: The commenter’s
point is acknowledged. When a
sensitivity analysis is conducted and
parameters are varied (both higher and
lower values used)—the degree of
difference in take estimates is much
greater when the parameter is adjusted
in one direction than in the other,
which suggests that the way that this
generalized model incorporates
uncertainty may not be conservative.
However, in all cases when the
adjustment of the parameter in a certain
direction results in a disproportionately
(as compared to an adjustment in the
other direction) large increase in the
number of takes, it is because the model
is now estimating that a larger
percentage of animals will be taken at
greater distances from the source. This
risk function is based completely on the
received level of sound. As discussed in
the proposed rule, there are other
contextual variables that are very
important to the way that an animal
responds to a sound, such as nearness
of the source, relative movement
(approaching or retreating), or the
animals familiarity with the source.
Southall et al. (2007) indicates that the
presence of high-frequency components
and a lack of reverberation (which are
indicative of nearness) may be more
relevant acoustic cues of spatial
relationship than simply exposure level
alone. In the HRC, an animal exposed to
between 120 and 130 dB may be more
than 65 nm from the sonar source.
NMFS is not aware of any data that
describe the response of any marine
mammals to sounds at that distance,
much less data that indicate that an
animal responded in a way we would
classify as harassment at that distance.
Because of this, NMFS does not believe
it is currently possible or appropriate to
modify the model to further address
uncertainty if doing so results in the
model predicting that much larger
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numbers of animals will be taken at
great distances from the source when we
have no data to suggest that that would
occur.
• Using many datasets: NMFS has
explained both in the rule, and then
again elsewhere in these comments,
why we chose the three datasets we did
to define the risk function. As Dr. Bain
points out, there are datasets that report
marine mammal responses to lower
levels of received sound. However,
because of the structure of the curve
NMFS is using and what it predicts
(Level B Harassment), we need datasets
that show a response that we have
determined qualifies as harassment (in
addition to needing a source that is
adequately representative of MFAS and
reliable specific received level
information), which many of the lower
level examples do not.
• 50-percent vs. 100-percent
response: Dr. Bain asserts that two of the
three datasets (Nowacek et. al., 2004
and Haro Strait—USS SHOUP) that
NMFS uses to derive the 50-percent
response probability in the risk function
actually report a 100-percent response at
the indicated received levels. For the
Haro Strait dataset, a range of estimated
received levels at the closest approach
to the J Pod were estimated. Given that
neither the number of individual
exposures or responses were available,
the mean of this range was used as a
surrogate for the 50-percent response
probability in the development of the
risk function. For the Nowacek data,
NMFS used 139.2 dB, which is the
mean of the received levels at which 5
of 6 animals showed a significant
response to the signal. However, viewed
another way, of 6 animals, one animal
did not respond to the signal and the
other five responded at received levels
of 133 dB, 135 dB, 137 dB, 143 dB, and
148 dB, which means that 3 of the 6
animals (50 percent) showed a
significant response at 139.2 dB or less.
• 120 dB basement value: When the
broad array of data reported from
exposures across taxa and to varied
sources are reviewed, NMFS believes
that 120 dB is an appropriate B value for
a curve designed to predict responses
that rise to the level of an MMPA
harassment (not just any response). The
available data do not support the
commenter’s assertion that risk may
approach 100 percent in the range from
120–135 dB for many species. For
example, the Southall et al. (2007)
summary of behavioral response data
clearly shows, in almost every table (for
all sound types), reports of events in
which animals showed no observable
response, or low-level responses NMFS
would not likely consider harassment,
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in the 120 to 135-dB range. For the
species (the harbor porpoise) for which
the data do support that assertion,
which the Southall et al. (2007) paper
considers ‘‘particularly sensitive’’,
NMFS has implemented the use of a
species-specific step function threshold
of 120 dB SPL.
• The A value: Please see the second
bullet of this response for the first part
of the answer. NMFS concurs with the
commenter that species-specific
parameters would likely be ideal,
however there are not currently enough
applicable data to support separate
curves for each species. We note,
though, that even with species-specific
parameters, the context of the exposure
will still likely result in a substantive
variability of behavioral responses to the
same received level by the same species.
• Recalculation: For the reasons
described in the bullets above in this
response, NMFS disagrees with the
commenter’s assertion that the
parameters used in the proposed rule
and the EIS are unrealistic and that they
result in take estimates that are too
small by two orders of magnitude. We
do not believe that a recalculation is
necessary.
The science in the field of marine
mammals and underwater sound is
evolving relatively rapidly. NMFS is in
the process of revisiting our acoustic
criteria with the goal of developing a
framework (Acoustic Guidelines) that
allows for the regular and defensible
incorporation of new data into our
acoustic criteria. We acknowledge that
this model has limitations, however,
they are primarily based on the lack of
applicable quantitative data. We believe
that the best available science has been
used in the development of the criteria
used in this and other concurrent Navy
rules and that this behavioral
harassment threshold far more
accurately represents the number of
marine mammals that will be taken than
the criteria used in the RIMPAC 2006
authorization. We appreciate the input
from the public and intend to consider
it further as we move forward and
develop the Acoustic Guidelines.
Comment 23: One commenter
expressed the concern that NMFS
blindly relies on TTS studies conducted
on 7 captive animals of two species (to
the exclusion of copious data on
animals in the wild) as a primary source
of data for the behavioral harassment
threshold. The commenter further
asserts that these studies (on highly
trained animals that do not represent a
normal range of variation within their
own species, as they have been housed
in a noisy bay for most of their lives)
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have major deficiencies, which NMFS
ignores by using the data.
Response: As mentioned in Comment
22, the SSC Dataset (Controlled
Laboratory Experiments with
Odontocetes) is not the primary source
of data for the behavioral harassment
threshold, it is one of three datasets
(other two datasets are from wild
species exposed to noise in the field)
treated equally in the determination of
the K value (equates to midpoint) of the
behavioral risk function. NMFS
recognizes that certain limitations may
exist when one develops and applies a
risk function to animals in the field
based on captive animal behavioral
data. However, we note that for the SSC
Dataset: (1) Researchers had superior
control over and ability to quantify
noise exposure conditions; (2)
behavioral patterns of exposed marine
mammals were readily observable and
definable; and, (3) fatiguing noise
consisted of tonal noise exposures with
frequencies contained in the tactical
mid-frequency sonar bandwidth. NMFS
does not ignore the deficiencies of these
data, rather we weighed them against
the value of the data and compared the
dataset to the other available datasets
and decided that the SSC dataset was
one of the three appropriate datasets to
use in the development of the risk
function.
Comment 24: NMFS fails to include
data from the July 2004 Hanalei Bay
event, in which 150–200 melon-headed
whales were embayed for more than 24
hours during the Navy’s Rim of the
Pacific exercise. According to the
Navy’s analysis, predicted mean
received levels (from mid-frequency
sonar) inside and at the mouth of
Hanalei Bay ranged from 137.9 dB to
149.2 dB. NMFS’ failure to incorporate
these numbers into its methodology as
another data set is not justifiable.
Response: NMFS’ investigation of the
Hanalei event concluded that there was
insufficient evidence to determine
causality. There are a number of
uncertainties about sonar exposure and
other potential contributing factors and
assumptions inherent to a
reconstruction of events in which sonar
was the causative agent that simply
preclude this determination. Because of
this, NMFS did not use the numbers
(137.9–149.2 dB) in our methodology.
Additionally, even if NMFS had
concluded that MFAS were the
causative agent, insufficient evidence
exists regarding the received level when
the animals responded (there is no
information regarding where they were
when they would have first heard the
sound).
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Comment 25: One commenter stated
‘‘NMFS excludes a substantial body of
research on wild animals (and some
research on other experimental animals
as well, within a behavioral
experimental protocol). Perhaps most
glaringly, while the related DEIS
prepared for the Navy’s Atlantic Fleet
Active Sonar Training activities appears
to acknowledge the strong sensitivity of
harbor porpoises by setting an absolute
take threshold of 120 dB (SPL)—a
sensitivity that, as NMFS has noted, is
reflected in numerous wild and captive
animal studies—the agencies
improperly fail to include any of these
studies in their data set. The result is
clear bias, for even if one assumes (for
argument’s sake) that the SPAWAR data
has value, NMFS has included a
relatively insensitive species in setting
its general standard for marine
mammals while excluding a relatively
sensitive one.’’
Response: As explained in the Level
B Harassment (Risk Function) section of
the proposed rule the risk function is
based primarily on three datasets (SSC
dataset, Nowacek et al. (2004), and Haro
Strait—USS SHOUP) in which marine
mammals exposed to mid-frequency
sound sources were reported to respond
in a manner that NMFS would classify
as Level B Harassment. NMFS
considered the ‘‘substantial body of
research’’ that the commenter refers to
but was unable to find other datasets
that were suitable in terms of all of the
following: The equivalency of the sound
source to MFAS, a reported behavioral
response that NMFS would definitively
consider Level B Harassment, and a
received level reported with high
confidence. The SSC dataset is only one
of three used and, in fact, the other 2
datasets (which are from wild animals—
killer whales and North Atlantic right
whales) both report behavioral
responses at substantively lower levels
(i.e., the ‘‘relatively insensitive’’ species
is not driving the values in the
function).
Separately, combined wild and
captive data support the conclusion that
harbor porpoises (high-frequency
hearing specialists) are quite sensitive to
a variety of anthropogenic sounds at
very low exposures (Southall et al.,
2007). Southall et al. (which refer to
harbor porpoises as particularly
sensitive species) report that all
recorded exposures exceeding 140 dB
SPL induced profound and sustained
avoidance behavior in wild harbor
porpoises. Unlike for the mid-frequency
and low-frequency species, there are
also no reported instances where harbor
porpoises were exposed to higher levels
and did not have a high response score.
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For these reasons, harbor porpoises are
considered especially sensitive and
NMFS determined that it is appropriate
to apply a more conservative threshold.
Comment 26: The risk function must
take into account the social ecology of
some marine mammal species. For
species that travel in tight-knit groups,
an effect on certain individuals can
adversely influence the behavior of the
whole. Should those individuals fall on
the more sensitive end of the spectrum,
the entire group or pod can suffer
significant harm at levels below what
the Navy would use as the mean. In
developing its ‘‘K’’ parameter, NMFS
must take account of such potential
indirect effects.
Response: The risk function is
intended to define the received level of
MFAS at which exposed marine
mammals will experience behavioral
harassment. The issue the commenter
raises is related to the Navy’s exposure
model—not the risk function. However,
because of a lack of related data there
is no way to numerically address this
issue in the model. Although the point
the commenter raises is valid, one could
also assert that if certain animals in a
tight knit group were less sensitive it
would have the opposite effect on the
group. Additionally, the modeling is
based on uniform marine mammal
density (distributed evenly over the
entire area of potential effect), which
does not consider the fact that marine
mammals appearing in pods will be
easier to detect and, therefore, the Navy
will be more likely to implement
mitigation measures that avoid exposing
the animals to the higher levels received
within 1000m of the source.
Comment 27: NMFS’ threshold is
applied in such a way as to preclude
any assessment of long-term behavioral
impacts on marine mammals. It does not
account, to any degree, for the problem
of repetition: the way that apparently
insignificant impacts, such as subtle
changes in dive times or vocalization
patterns, can become significant if
experienced repeatedly or over time.
Response: NMFS threshold does not
preclude any assessment of long-term
behavioral impacts on marine mammals.
The threshold is a quantitative tool that
NMFS uses to estimate individual
behavioral harassment events.
Quantitative data relating to long-term
behavioral impacts are limited, and
therefore NMFS’ assessment of longterm behavioral impacts is qualitative in
nature (see Diel Cycle section in
Negligible Impact Analysis section).
NMFS analysis discusses the potential
significance of impacts that continue
more than 24 hours and/or are repeated
on subsequent days and, though it does
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not quantify those impacts, further
indicates that these types of impacts are
not likely to occur because of the nature
of the Navy’s training activities and the
large area over which they are
conducted.
Comment 28: One commenter noted
that the threshold used in the Proposed
Rule differs from the one used by the
Navy to estimate marine mammal take
during previous exercises (i.e., instead
of using an energy level (EL) standard of
173 dB re 1 microPa2•s, NMFS applies
a pressure (SPL)-based dose-response
function that begins at 120 dB re 1
microPa and reaches its mean at 165 dB
re 1 μPa). The commenter was
concerned that under 173 dB (EL)
threshold, the RIMPAC 2006 event was
expected to result in slightly less than
33,000 behavioral takes of marine
mammals—while under the risk
function, RIMPAC events conducted
with the same number of hours of sonar
use would supposedly cause fewer than
6,000 takes. The commenter requests
that NMFS provide a take estimate using
the 173 dB (EL) standard.
Response: NMFS develops and
implements thresholds based on the
best available science, not on how
changing the threshold will affect the
number of estimated takes. As described
in the proposed rule, the decision to use
a risk continuum approach instead of a
step function was based on the fact that
behavioral responses are very individual
and context-specific and a risk function
allows for this variation to be
considered in the take estimate, versus
a step function, which assumes that
every animal will be harassed at the
same received level in every situation.
Although both SPL and SEL are
valuable metrics for predicting the
behavioral responses of marine
mammals to sound, SPL is currently the
best metric with which to assess the
available behavioral response data
because it is the metric that has most
often been measured or estimated
during behavioral disturbance studies
(Southall et al., 2007). Additionally,
SEL is more difficult to estimate in the
field than SPL. Regarding the decrease
in the number of estimated takes for
current RIMPAC exercises as compared
to RIMPAC 2006, NMFS notes the
following items, other than the new
threshold, that have contributed to the
reduction in the take estimate:
• The RIMPAC 2006 take estimate
was calculated for 532 hours of sonar,
while the current RIMPAC estimate is
based on 399 hours of sonar.
• In 2006, the Navy model did not
subtract out the land mass area when
multiplying the ensonified area by the
animal density to determine the
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estimated marine mammal exposures.
Currently, the Navy has implemented a
post-modeling calculation that allows
them to account for that.
• For the 2006 RIMPAC, all of the
surface vessel sonar hours were
modeled as using the 53C hull-mounted
sonar source, though both 53C and 56C
sources are used in Hawaii. The 56C
hull-mounted sonar source is typically
operated at 10 dB SPL lower source
level than the 53C sonar source (225 vs.
235 dB), which means that the
horizontal ensonified area around the
source is at least 10 times smaller—
which translates to substantially fewer
animals exposed to received sound
levels associated with MMPA takes. In
modeling impacts for this rulemaking,
the Navy more accurately modeled both
53C and 56C sonar sources in the
exposure analysis, which contributes to
the more realistic lower take estimate.
• Currently, the Navy applies marine
mammal depth profiles to the take
estimate that allows for consideration of
where in the water column marine
mammals are likely to be in relation to
the propagated sound. Alternatively, in
2006, marine mammals were only
distributed 2-dimensionally, which
meant that an exposed animal was
always counted as having been exposed
to whatever the highest level of sound
in the entire vertical water column was.
NMFS will continue to evaluate new
science and thresholds will likely
evolve gradually in response to
applicable data. Requiring the Navy to
calculate take estimates based on an
outdated threshold would cost the Navy
unnecessary resources and would not
result in any added value to the effects
analysis or the protection of marine
mammals.
Comment 29: ‘‘NMFS appears to have
misused data garnered from the Haro
Strait incident—one of only three data
sets it considers—by including only
those levels of sound received by the ‘J’
pod of killer whales when the USS
Shoup was at its closest approach.
These numbers represent the maximum
level at which the pod was harassed; in
fact, the whales were reported to have
broken off their foraging and to have
engaged in significant avoidance
behavior at far greater distances from
the ship, where received levels would
have been orders of magnitude lower.
We must insist that NMFS provide the
public with the Navy’s propagation
analysis for the Haro Strait event, which
it used in preparing its 2005 Assessment
of the incident.’’
Response: NMFS used the levels of
sound received by the ‘‘J’’ pod when the
USS Shoup was at its closest approach
because a review of the videotapes and
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other materials by NMFS detailing the
behavior of the animals in relation to
the location of the Navy vessels showed
that it was after the closest approach of
the vessel that the whales were observed
responding in a manner that NMFS
would classify as ‘‘harassed’’. Though
animals were observed potentially
responding to the source at greater
distances, NMFS scientists believed that
the responses observed at greater
distances were notably less severe and
would not rise to the level of an MMPA
harassment. Though the received levels
observed in relation to the lesser
responses could be used in some types
of analytical tools, the risk continuum
specifically requires that we use
received sound levels that are
representative of when an MMPA
harassment occurred. The Navy’s report
may be viewed at: https://www.
acousticecology.org/docs/
SHOUPNavyReport0204.pdf.
Acoustic Threshold for TTS
Comment 30: NRDC argues that a 190
dB re 1 μPa2-s TTS threshold would
have ‘‘fit the applicable data’’ better
than the 195–dB threshold (i.e., the data
better support a 190–dB TTS threshold)
NMFS and the Navy have established
for MFAS and would have had the
advantage of being marginally more
conservative given the enormous
uncertainties surrounding the effects of
mid-frequency sonar on marine
mammals.
Response: The most recent and best
available scientific information, i.e.,
Southall et al. (2007), support the
application of the 195–dB SEL TTSonset threshold for cetaceans and nonpulse sounds (such as MFAS).
Published TTS data are limited to
bottlenose dolphin and beluga (six
publications); however, in order to be
precautionary, where data exist for both
species, the authors use the more
conservative result (usually for beluga)
to represent TTS-onset for all midfrequency cetaceans. NMFS scientists
and the authors of Southall et al. (2007)
believe that the existing data support a
195–dB threshold.
Acoustic Threshold for Injury
Comment 31: One commenter stated
that: ‘‘The take estimates do not reflect
other non-auditory physiological
impacts, as from stress and from chronic
exposure’’.
Response: The commenter is correct,
the Navy’s estimated take numbers do
not reflect non-auditory physiological
impacts because the quantitative data
necessary to address those factors in the
exposure model do not exist. However,
NMFS acknowledges that a subset of the
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animals that are taken by Harassment
will also likely experience non-auditory
physiological effects and these effects
are addressed in the proposed rule (see
Stress Responses section).
Comment 32: The Navy’s exclusive
reliance on energy flux density as its
unit of analysis does not take other
potentially relevant acoustic
characteristics into account. Reflecting
this uncertainty, the Navy should
establish a dual threshold for marine
mammal injury.
Response: NMFS currently uses the
injury threshold recommended by
Southall et al. (2007) for MFAS.
Specifically, NMFS uses the 215-dB SEL
sound exposure level threshold (the
commenter refers to it as energy flux
density level). Southall et al. (2007)
presents a dual threshold for injury,
which also includes a 230–dB peak
pressure level threshold. NMFS
discussed this issue with the Navy early
in the MMPA process and determined
that the 215-dB SEL injury threshold
was the more conservative of the two
thresholds (i.e., the 230-dB peak
pressure threshold occurs much closer
to the source than the 215-dB SEL
threshold) and therefore it was not
necessary to consider the 230-dB peak
pressure threshold further. For example,
an animal will be within the 215-dB
SEL threshold and counted as a take
before it is exposed to the 230-dB
threshold. NMFS concurs with Southall
et al. (2007), which asserts that for an
exposed individual, whichever criterion
is exceeded first, the more
precautionary of the two measures
should be used as the operative injury
criterion.
Comment 33: One commenter
suggested that the Navy has not
explained how they determine when or
how injuries or harassment of marine
mammals have occurred during the
specified activities.
Response: It is difficult to detect when
animals experience behavioral
harassment. Though it would likely be
easier to detect if an animal were
injured as a result of the Navy’s
activities, it is still difficult because of
the fact that marine mammals spend a
lot of time underwater (where they
cannot be visually observed) and
because of the large areas that Navy
training activities cover (i.e., they do not
stay in one area for a long time). The
Navy has a robust Monitoring Plan that
utilizes vessel monitoring, aerial
monitoring, passive acoustic
monitoring, and tagging and is intended
to detect and report marine mammal
responses to MFAS exposure. However,
in order to quantify the takes that are
likely to occur as a result of particular
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training exercises, the Navy must make
estimates based on the propagation of
sound from their sources, the density of
marine mammals in the area, and the
acoustic thresholds, which predict at
what received level of sound an animal
will be harassed and were developed by
NMFS using the best available science.
Comment 34: One commenter asserts
that most whales injured or killed by
sonar will not be found, or they will
sink and die rather than beach
themselves on shore. Further, the
commenter states, the proposed tests
and war games will likely injure and
harass many more marine mammals
than the number of takings requested by
the Navy.
Response: For the reasons set forth in
this rulemaking, NMFS does not believe
that the Navy’s training will result in
more take than is authorized in these
final regulations. The Navy has been
conducting MFAS/HFAS training
exercises in the HRC for over 40 years.
Though monitoring specifically to
determine the effects of sonar on marine
mammals was not being conducted
prior to 2006 and the symptoms
indicative of potential acoustic trauma
were not as well recognized prior to the
mid-nineties, people have been
collecting stranding data in Hawaii for
25 years. Though not all dead or injured
animals are expected to end up on the
shore (some may be preyed upon or
float out to sea), one might expect that
if marine mammals were being harmed
by sonar with any regularity or in large
numbers, more evidence would have
been detected over the 40-yr period. An
average of 24 stranding events per year
are documented in Hawaii. However, as
described in the rule, NMFS and the
Navy have definitively determined that
the use of MFAS was a contributing
factor in 5 stranding events worldwide,
none of which took place in Hawaii.
Comment 35: One commenter stated:
‘‘[M]arine mammals are stressed by
many other factors, the most critical
being global warming, which is both
increasing the temperature of the oceans
and acidifying them, with observed
changes in food supplies and timing of
migrations. Allowing use of active sonar
may be the last straw for some of these
species. It is important to protect marine
mammals until it is known that
populations can sustain limited and
completely quantified incidental
harassment and death. Since that is not
known at present, NOAA should not
allow the Navy to proceed with active
sonar testing as requested.’’
Response: NMFS acknowledges that
global warming is a threat to some
species of marine mammals. For the
reasons described in this rulemaking,
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NMFS believes that the Navy’s model,
combined with NMFS’ designated
thresholds, is able to adequately
quantify the number of marine
mammals that will likely be ‘‘taken’’ by
the Navy’s proposed activity. Further,
based on the analysis contained in this
rule, NMFS was able to conclude that
the total taking of marine mammals over
the 5-yr period incidental to the Navy’s
training activities would have a
negligible impact on the affected species
or stock (i.e., would not have adverse
effects on the annual rates of survival or
recruitment in the affected populations
or stocks). Therefore, NMFS has issued
these regulations and plans to issue
Letters of Authorization for this activity.
Of note—pursuant to the MMPA, NMFS
does not ‘‘allow’’ or disallow the Navy
to proceed with their activities; rather,
NMFS either authorizes or does not
authorize the take of marine mammals
incidental to the specified activities that
are analyzed.
Comment 36: One commenter asserts
that NMFS disregards data gained from
actual whale mortalities. The
commenter cites to peer-reviewed
literature that indicates that sound
levels at the most likely locations of
beaked whales beached in the Bahamas
strandings run far lower than the Navy’s
threshold for injury here: approximately
150–160 dB re 1 μPa for 50–150
seconds, over the course of the transit.
A further modeling effort, undertaken in
part by the Office of Naval Research, the
commenter states, suggests that the
mean exposure level of beaked whales,
given their likely distribution in the
Bahamas’ Providence Channels and
averaging results from various
assumptions, may have been lower than
140 dB re 1 μPa. Last the commenter
suggests that when duration is factored
in, evidence would support a maximum
energy level (‘‘EL’’) threshold for serious
injury on the order of 182 dB re 1
μPa2·s, at least for beaked whales.
Response: No one knows where the
beaked whales were when they were
first exposed to MFAS in the Bahamas
or the duration of exposure for
individuals (in regards to maximum EL)
and, therefore, we cannot accurately
estimate the received level that triggered
the response that ultimately led to the
stranding. Therefore, NMFS is unable to
quantitatively utilize any data from this
event in the mathematical model
utilized to estimate the number of
animals that will be ‘‘taken’’ incidental
to the Navy’s proposed action. However,
NMFS does not disregard the data; the
proposed rule includes a qualitative
discussion of the Bahamas stranding
and four other strandings that NMFS
and the Navy concur that the operation
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of MFAS likely contributed to. These
data illustrate a ‘‘worst case scenario’’ of
the range of potential effects from sonar
and the analysis of these strandings
supports the Navy’s request for
authorization to take 10 individuals of
several species by mortality over the 5yr period.
Comment 37: One commenter states:
‘‘NMFS fails to take proper account of
published research on bubble growth in
marine mammals, which separately
indicates the potential for injury and
death at lower [received sound] levels.
According to the best available scientific
evidence, gas bubble growth is the
causal mechanism most consistent with
the observed injuries. NMFS’ argument
to the contrary simply misrepresents the
available literature.’’
Response: The proposed rule
contained a detailed discussion of the
many hypotheses involving both
acoustically-mediated and behaviorallymediated bubble growth. NMFS
concluded that there is not sufficient
evidence to definitively say that any of
these hypotheses accurately describe the
exact mechanism that leads from sonar
exposure to a stranding. Despite the
many theories involving bubble
formation (both as a direct cause of
injury and an indirect cause of
stranding), Southall et al. (2007)
summarizes that scientific agreement or
complete lack of information exists
regarding the following important
points: (1) Received acoustical exposure
conditions for animals involved in
stranding events; (2) pathological
interpretation of observed lesions in
stranded marine mammals; (3) acoustic
exposure conditions required to induce
such physical trauma directly; (4)
whether noise exposure may cause
behavioral reactions (such as atypical
diving behavior) that secondarily cause
bubble formation and tissue damage;
and (5) the extent the post mortem
artifacts introduced by decomposition
before sampling, handling, freezing, or
necropsy procedures affect
interpretation of observed lesions.
Comment 38: One commenter states:
‘‘[C]oncerning direct physiological
effects, only a few studies provide
empirical information on the levels at
which noise-induced loss in hearing
sensitivity occurs in nonhuman
animals. Given the lack of data, and
importance of hearing in the ocean,
shouldn’t we follow the precautionary
principle for underwater noise?’’
Response: The TTS thresholds are
based on published data gathered from
beluga whales, bottlenose dolphins,
California sea lions, harbor seals, and
elephant seals via several different
studies. The PTS threshold (for
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estimating PTS onset, which is
considered to occur in conditions
causing 40 dB of TTS, based on research
on several terrestrial mammal species) is
derived by combining measured or
estimated TTS onset levels in marine
mammals and the estimated ‘‘growth’’ of
TTS in certain terrestrial mammals
exposed to increasing noise levels
(Southall et al., 2007). Precautionary
choices were made at several decision
points in the development of these
thresholds and Southall et al. (2007)
indicate that the approach is to
‘‘acknowledge scientific uncertainty and
to err on the side of overestimating the
possibility of PTS (i.e., on the side of
underestimating the exposure required
to cause PTS onset).’’ For example, 40
dB of TTS is considered the onset of
PTS; however, this is likely somewhat
precautionary because, based on
previous studies of terrestrial mammals,
there is often complete recovery from
TTS of this magnitude or greater (i.e.,
PTS is not induced).
Effects Analysis
Comment 39: ‘‘Why is impaired
communication considered for these
rules, but not in the Navy EIS?’’
Response: The Navy’s conceptual
framework, the figure in the Navy’s EIS
in which they outline the potential
effects on marine mammals from
exposure to sonar, includes a box
indicating behavioral changes to
vocalizations. Further, the HRC EIS
contains a detailed section on masking,
which is closely associated with any
communication impairment that might
result from MFAS exposure (NMFS
included a brief discussion of
communication impairment in the same
section as masking). Both NMFS and the
Navy believe that both masking and
communication impairment are
relatively unlikely to occur as a result of
MFAS exposure because of the pulse
length and duty cycle of the MFAS
signal.
Comment 40: One commenter asked
why the MMPA rules find greater stress
responses than the Navy EIS.
Response: Both the proposed rule and
the EIS discuss stress responses as
related to marine mammal exposure to
MFAS. Because of the lack of
quantitative data, neither document
attempts to quantify the number of
animals that will likely experience a
stress response or the specific degree of
distress these animals may experience—
i.e., the rule does not ‘‘find greater stress
responses’’ than the EIS.
Comment 41: One commenter noted
that the proposed rule said: ‘‘Little is
known about the breeding and calving
behaviors of many of the marine
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mammals that occur in the HRC.’’ Then
he questioned how such precise
predictions of harm can be made.
Response: What is not indicated
above is that, though little is known
about the breeding and calving
behaviors of many of the marine
mammals that occur in the HRC, what
is known is that these behaviors are
most likely occurring in areas outside of
the HRC (mysticetes other than
humpback whales) or that there are not
likely specific focused areas of
reproductive importance in the HRC.
Therefore, we do not expect focused
effects of sonar to occur in an important
reproductive area. When this is
combined with the fact that we do not
expect injury of marine mammals to
occur (because of the mitigation
measures), we do predict a lack of harm.
Comment 42: One commenter noted
the LOA application requirement to
provide the anticipated impact of the
activity upon the species or stock. The
commenter indicated that there is not
enough data to answer the question
adequately and that they are skeptical of
Navy data as it ‘‘has been shown to be
unreliable.’’ Further, the commenter
‘‘generally feels that it is unwise to rely
on an applicant’s data set and urge that
independent analysis be done.’’ Last,
they assert that ‘‘Because there is a
paucity of Navy data regarding their
own estimates for takes, it is reasonable
for NMFS to take a conservative and
precautionary view towards issuing
permits regarding the extremely broad,
long-term, and harmful actions
proposed.’’
Response: The commenter does not
provide any information to support his
assertion that the Navy data ‘‘has been
shown to be unreliable’’. NMFS relies
upon the data that the Navy (or any
applicant) provides in our analysis, but
also conducts an independent review of
the data and incorporates additional
data into our analysis as appropriate.
Next, NMFS is not sure what the
commenter meant when he stated:
‘‘Because there is a paucity of Navy data
regarding their own estimates for takes.’’
NMFS strives to always make decisions
based on the best scientific data. In
circumstances of scientific uncertainty
and potentially high risk when a
decision is necessary, NMFS errs on the
side of being more conservative,
whenever that conclusion is supported
by the agency’s record.
Comment 43: One commenter stated:
‘‘[T]here is a disconnect that exists
between the modeling adopted by
NMFS in estimating species take and
the scope of the authorization that
NMFS has issued. NMFS’ rule would
permit the Navy to operate anywhere
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around the range without any
substantive restriction. If NMFS’
analysis is dependent on certain
assumptions about the Navy’s training—
including, for example, the siting of
exercises—it must incorporate those
assumptions as limitations on the
training that the Navy is authorized to
perform. Otherwise, there can be no
assurance that takes will remain within
even the limits that NMFS has
proposed.’’
Response: As it relates to humpback
whales only, NMFS analysis is
dependent on certain assumptions about
the Navy’s training (the assumption that
a relatively small portion of the overall
Navy training will occur within the
areas that are known to contain high
densities of humpback whales in the
winter months (referred to as the
Mobley Area because of a map he
compiled)). Because of the need for
operational flexibility, the Navy cannot
commit to limiting their sonar use over
the entire Mobley Area (though they
will implement the humpback whale
cautionary area measure specifically in
the Maui Basin). However, the following
facts support the idea that hours of
sonar training will be relatively low in
the Mobley Area and that effects on
humpback whales will be relatively less
severe:
• SPORTS data from 2007 indicates
that the Navy operated sonar for a total
of approximately 30 hours in the
Mobley Area.
• Though SPORTS was not operative
prior to 2007, the Navy indicated that
sonar use in the Mobley Area prior to
2007 was similarly limited.
• The Navy generally asserts that the
majority of the exercises are in waters
2,000–4,000 km deep. This means that
the exercises are 2–15 km (1–8 nm), or
farther, out from the densest areas of
humpbacks, which would suggest,
based on propagation information
provided by the Navy, that the majority
of behavioral takes of humpbacks would
occur at received levels less than 150–
160 dB. This further suggests that the
overall potential severity of the effects is
likely less than one would anticipate if
humpbacks were not selectively using
the shallower, inshore areas and the
Navy were not conducting the majority
of their exercises in deeper areas.
That being said, however, NMFS
concurs with the commenter that NMFS
needs to ensure that the Navy’s effects
remain within the bounds of those
anticipated by and analyzed within the
rule. For this reason, NMFS has added
a reporting requirement that requires the
Navy to annually report the number of
hours of sonar operation within the
Mobley Area. The rule also includes an
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adaptive management component,
which means that NMFS and the Navy
have the flexibility to modify mitigation
or monitoring measures if appropriate.
Comment 44: One commenter asserts
that the Navy’s exposure model fails to
consider the following important points:
• Possible synergistic effects of using
multiple sources in the same exercise,
or the combined effects of multiple
exercises.
• Indirect effects, such as the
potential for mother-calf separation, that
can result from short-term disturbance.
• In assuming animals are evenly
distributed—the magnifying effects of
social structure, whereby impacts on a
single animal within a pod, herd, or
other unit may affect the entire group.
• In assuming that every whale
encountered during subsequent
exercises is essentially a new whale—
the cumulative impacts on the breeding,
feeding, and other activities of species
and stocks.
Response: The commenter is correct,
the Navy’s model does not consider the
points listed above because the
quantitative data necessary to include
those concepts in a mathematical model
do not currently exist. However, NMFS
and the Navy have qualitatively
addressed those concerns in their effects
analyses in the rule and in the Navy’s
EIS.
Comment 45: One commenter noted
that the numbers of modeled hours in
the Navy’s EIS and NMFS’ Proposed
Rule are lower than those set forth in
the DEIS (by half), due, apparently, to
the Navy’s application of its new Sonar
Positional Reporting System (SPORTS).
The commenter further notes that the
discrepancy in use hours between the
DEIS and EIS raises some question
about SPORTS’ reliability. The
commenter recommends that NMFS
require the Navy to compare SPORTS
data with logs retained by the Pacific
Fleet, over a sample period, to confirm
that SPORTS reporting does indeed
capture all mid-frequency sonar use in
the Hawaii Range Complex, and then
publicly report the total number of
sonar use hours occurring on the HRC
on no less than an annual basis, to
ensure that levels remain below the
levels established here.
Response: SPORTS is the single
method that the Navy has available to
them to accurately keep track of hours
of sonar operation. Prior to the
implementation of this system, the Navy
estimated the hours of sonar operation
based on other operational factors, such
as the length of the whole exercise.
Their estimates were conservative,
which is why the numbers went down
when they began using the SPORTS.
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NMFS is requiring (see Reporting
Requirements section) the Navy to
report the number of hours of sonar
operation on an annual basis, however,
the Navy will decide how best to
provide that information, which at this
point in time includes the use of
SPORTS.
Comment 46: One commenter stated:
‘‘NMFS does not properly account for
reasonably foreseeable reverberation
effects (as in the Haro Strait incident),
giving no indication that its modeling
sufficiently represents areas in which
the risk of reverberation is greatest.’’
Response: The model does indirectly
incorporate surface-ducting (surface
reverberation), as conditions in the
model are based on nominal conditions
calculated from a generalized digitalized
monthly average. Though the model
does not consider reverberations, these
effects are generally at received levels
many orders of magnitude below those
of direct exposures (as demonstrated in
the Haro Strait analysis associated with
bottom reverberation) and thus
contribute essentially nothing to the
cumulative SEL exposure and would
not result in the exposure of an animal
to a higher SPL than the direct
exposure, which is already considered
by the model.
Comment 47: How will oceanographic
conditions (e.g., water temperature
profiles, water depth, salinity, etc.) be
factored into the modeling of received
sound levels of MFAS and underwater
detonations? Which oceanographic data
sources will be used?
Response: The Take Calculation
section of the proposed rule generally
discusses how these and other variables
are factored into the take estimates and
references Appendix J of the Navy’s
FEIS for HRC, which contains the
details of the model and how these
variables are incorporated. Due to the
importance that propagation loss plays
in ASW, the Navy has invested heavily
over the last four to five decades in
measuring and modeling environmental
parameters. The result of this effort is
the following collection of global
databases of environmental parameters
that are accepted as standards for all
Navy modeling efforts:
• Water depth—Digital Bathymetry
Data Base Variable Resolution (DBDBV),
• Sound speed—Generalized
Dynamic Environmental Model (GDEM),
• Bottom loss—Low-Frequency
Bottom Loss (LFBL), Sediment
Thickness Database, and HighFrequency Bottom Loss (HFBL), and
• Wind speed—U.S. Navy Marine
Climatic Atlas of the World.
Comment 48: One commenter cites
concerns that the Navy’s take estimates
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(for monk seals specifically) are
substantively lower in the FEIS than the
DEIS. Further comments indicate some
confusion regarding whether any monk
seals are expected to be injured by the
predicted exposures to MFAS or
explosives.
Response: Though this comment is
outside the purview of the MMPA,
NMFS directs the commenter to the
Navy’s Supplement to the DEIS, which
clearly explains that the implementation
of the new system for keeping track of
sonar hours (SPORTS) resulted in fewer
estimated hours of sonar operation,
which in turn results in lower take
estimates. Separately, to clarify—based
on the model, no monk seals will be
exposed to any injurious levels of sound
or pressure. Additionally, though a few
seals were modeled as being exposed to
levels that could result in TTS, NMFS
believes that these exposures are not
likely to occur when the mitigation is
taken into consideration (see Negligible
Impact Analysis).
Comment 49: One commenter stated:
‘‘NMFS has not considered the best
available evidence of population
structuring in Hawaiian marine
mammals: Notably, NMFS does not
account (in its abundance estimates) for
evidence of considerable site fidelity by
Cuvier’s and Blainville’s beaked whales,
which is suggestive of residency and
additional population structuring.
NMFS significantly overestimates the
size of these populations and thus
significantly underestimates the
proportion that would be taken and the
effects that its repeated activities would
have.’’
Response: NMFS’ analysis includes
qualitative consideration of the
evidence of site fidelity by Cuvier’s and
Blainville’s beaked whales (see Resident
Populations/Additional Management
Units section in the proposed rule).
NMFS considers the abundance
estimates of designated marine mammal
stocks and these beaked whale groups
have not been designated as separate
stocks by NMFS. As discussed in the
indicated section, if the nature of the
Navy’s training exercises was such that
they were disproportionately
conducting sonar in a certain fairly large
area that largely overlapped with a
particular demographically isolated
population, stock, or resident
population, additional analysis might be
needed to determine what additional
impacts might occur. However, due to
the Navy’s need to train in a variety of
bathymetric conditions and in the
vicinity of a variety of other resources
throughout the Main Hawaiian Islands,
the location of the Navy’s training
exercises are highly variable, and no
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focused impacts are anticipated in the
vicinity of these groups.
Comment 50: One commenter asked
why the rule finds a stronger correlation
between sonar and marine mammal
strandings than the Navy EIS and why
the rule finds more serious effects than
the Navy EIS?
Response: Both the EIS and the
proposed rule discuss the association
between the 5 specific marine mammal
strandings and the use of MFAS and
both the rule and the EIS discuss a wide
range of potential physiological and
behavioral effects on marine mammals
from MFAS, ranging from avoidance to
PTS to bubble formation that could
cause tissue damage. The rule utilizes
the same estimated take numbers that
the EIS does. NMFS disagrees with the
assumptions underlying the
commenter’s question and, therefore,
cannot answer the question.
General Opposition
Comment 51: The NRDC urged NMFS
to withdraw its proposed rule on the
Hawaii Range Complex and to revise the
document prior to its recirculation for
public comment. They suggested NMFS
revisit its profoundly flawed analysis of
environmental impacts and prescribe
mitigation measures that truly result in
the least practicable adverse impact on
marine species.
Response: NMFS has addressed
specific comments related to the effects
analysis here and the mitigation
measures in the Mitigation
Environmental Assessment. We do not
believe that the analysis is flawed and
we believe that the prescribed measures
will result in the least practicable
adverse impacts on the affected species
or stock. Therefore, NMFS does not
intend to withdraw its rule on the HRC.
Comment 52: A few commenters
expressed general opposition to Navy
activities and NMFS’ issuance of an
MMPA authorization.
Response: NMFS appreciates the
commenter’s concern for the marine
mammals that live in the area of the
proposed activities. However, the
MMPA directs NMFS to issue an
incidental take authorization if certain
findings can be made. NMFS has
determined that the Navy training
activities in the HRC will have a
negligible impact on the affected species
or stock and, therefore, we plan to issue
the requested MMPA authorization.
MMPA
Comment 53: One commenter stated:
‘‘Currently, the Hawaiian monk seal
population has reached a critical point
where recovery of the species is
questionable, which should be
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considered grounds for the termination
of sonars in and around areas where the
Hawaiian monk seal is known to be
present.’’
Response: As with other species, the
Navy is required to powerdown if a
monk seal is detected within 1000 yds
of the sonar source (and powerdown
further if the seal is detected within 500
yd and shutdown if the seal is detected
within 200 yds). Monk seals generally
forage at depths of less than 100 m (109
yd), but occasionally dive to depths of
over 500 m (546 yd). The majority of
ASW training in the HRC, however,
takes place in waters 4 to 8 times deeper
than even this known (500-m (546-yd))
maximum and it is very rare for ASW
training to take place in waters as
shallow as 100 m (109 yd) in depth. So,
generally, monk seals are less likely to
be in the vicinity of ASW activities, and
we believe that watchstanders are likely
to spot the seals before they could close
within the distance necessary to sustain
TTS, which would be less than 100 m
(109 yd).
Comment 54: One commenter
expressed general opposition to the
marine mammal take that NMFS had
proposed to authorize and presented
several reasons why MFAS was not
necessary. The same commenter
discussed the purpose of the MMPA and
suggested that the Navy had not earned
the right to take any marine mammals.
Response: Under section 101(a)(5)(A)
of the MMPA, NMFS must make the
decision of whether or not to issue an
authorization based on the applicant’s
proposed action that the applicant
submits—the MMPA does not contain a
mechanism for NMFS to question the
need for the action that the applicant
has proposed (unless the action is
illegal). Similarly, any U.S. citizen
(including the Navy) can request and
receive an MMPA authorization as long
as all of the necessary findings can be
made, it is not necessary that the Navy
or any other entity ‘‘earn the right’’.
Comment 55: ‘‘Any organism that
frequents the HRC is protected by state
law even when outside the three mile
state boundary. Many of the species
affected by active sonars are affected by
this legislation. Therefore if any of these
animals are thought to be caused harm,
this would fall under state jurisdiction
thus requiring state involvement in the
decision making process. We call on
NMFS to involve the state in the
decision making process.’’
Response: It is unclear what statute
the commenter is referring to. In any
case, however, NMFS may only
authorize the take of marine mammals
incidental to a specified activity. NMFS
ensures that the proposed activities are
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consistent with or in compliance with
the applicable federal statutes before
issuing an authorization.
Other
Comment 56: OHA advocates for a
narrow view by NMFS of the number of
take permits to be issued for the
proposed actions and a determination
that the proposed and even ongoing
activities in the HRC do adversely affect
Hawaiian Monk seals and other marine
mammals.
Response: NMFS determined that the
training activities proposed to be
conducted in the HRC and the issuance
of an MMPA authorization may affect
listed marine mammals such as the
Hawaiian monk seal. Consequently, the
Navy and NMFS (the branch that issues
an MMPA authorization) consulted with
NMFS under section 7 of the ESA. In a
Biological Opinions (BiOp), NMFS
concluded that the Navy’s training
activities in the HRC and NMFS’
issuance of these regulations and the
2009 LOA are not likely to jeopardize
the continued existence of threatened or
endangered species or destroy or
adversely modify any designated critical
habitat. NMFS also determined that the
Navy’s training activities and NMFS
issuance of the LOA were likely to
adversely affect the affected marine
mammal stocks and species and issued
an incidental take statement. The ITS
issued for the LOA will contain
implementing terms and conditions to
minimize the effects on ESA-listed
species of the marine mammal take
authorized through the 2009 LOA.
Comment 57: One commenter was
concerned that State commerce could be
jeopardized as the sonar could
negatively impact the humpback whale
populations and other marine species,
which draw over 900,000 visitors to the
state. The commenter questioned
whether these effects had been
adequately addressed.
Response: NMFS recommends that
the commenter review the Navy’s EIS to
obtain information about the potential
socio-economic impacts resulting from
the Navy’s use of sonar in the HRC.
Comment 58: ‘‘Fish are affected by
sonars, airguns and other underwater
noises. With possible physical damage,
decreased catch size and altered
behaviors resulting from HRC activities,
the Magnuson Stevens Fishery Act may
question the validity of these exercises.’’
Response: NMFS reviewed the Navy’s
Essential Fish Habitat and Coral Reef
Assessment for the HRC and concurred
with the Navy that it is unlikely that the
proposed project would have adverse
impacts to EFH provided the proposed
mitigation measures were implemented
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(see Essential Fish habitat
Determination section).
Comment 59: A few members of the
public submitted comments on the
Navy’s EIS that they did not clearly tie
to the proposed rule.
Response: The purpose of this
comment period was for the public to
provide comments on the proposed rule.
Responses were not provided to
comments on the EIS if their bearing on
the MMPA authorization was not clear.
Comment 60: How will all the sunken
objects—hulks, sonobuoys, explosive
devices, etc.—affect marine life? They
will attract plant growth and animals
that feed on the plants, changing the
ecosystem. And what toxins will they
release into the ocean?
Response: The Navy’s HRC FEIS
analyzed how sunken objects, such as
sonobuoys and expended explosive
devices, would affect marine life. The
Navy found that the likelihood of a
marine mammal or fish encountering
and having an adverse interaction with
expended materials was remote. Also,
the Navy found that the potential
ingestion of toxins, such as the small
amount of propellant or stimulant
remaining in the spent boosters or on
pieces of missile debris, by marine
mammals or fish species would be
remote because of (1) atmospheric
dispersion, (2) the diluting and
neutralizing effects of seawater, and (3)
the relatively small area that could
potentially be affected.
Comment 61: The NRDC notes that
NMFS is preparing an environmental
assessment on the environmental effects
of various mitigation measures, and
suggests that if NMFS intends to rely on
this document for its Final Rule, or if
this document constitutes significant
new information, NMFS must postpone
finalizing the rule and open up its
assessment to public comment.
Response: NMFS is not required to
provide advance notice and opportunity
for comment on the draft Environmental
Assessment. This document does not
constitute significant new information,
rather it is a summary of the universe of
mitigation measures (many of them
recommended in public comments) that
NMFS considered when developing the
MMPA authorization with a discussion
of their potential benefits to marine
mammals and their practicability of
implementation. Much of the
information, especially as it relates to
practicability of implementation, was
included in the Navy’s EIS. Finally,
NMFS and the Navy have provided the
public with a substantial amount of
environmental information related to
the HRC activities (e.g., during the
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1479
Navy’s EIS process and NMFS’ MMPA
process).
Comment 62: One commenter was
concerned about the effects of the
Navy’s training in the
¯
¯
Papahanaumokuakea Marine National
Monument, which contains the largest
coral reef area in Hawaii, one of the
largest and most important assemblages
of tropical seabirds in the world, greater
than 98 percent of the world’s Laysan
and black-footed albatrosses nests, the
majority of the population of the
Hawaiian monk seal, and over 90
percent of the Hawaiian green sea turtle
nests there. The Navy proposes to
increase the impacts to this remarkable
area and the effects could be dramatic.
Response: Most of this comment does
not pertain to NMFS’ authority pursuant
to the MMPA. However, NMFS notes
that only a very small part of the
¯
¯
Papahanaumokuakea Marine National
Monument overlaps with the HRC, and
it is in a remote portion of the HRC.
Therefore, NMFS anticipates relatively
few hours of sonar operation to occur in
that area. Additionally, the effects of
this action are temporary and acoustic
in nature, and NMFS does not expect
them to result in harm to the protected
natural and cultural resources of these
areas. The Northwestern Hawaiian
Islands Marine National Monument
proclamation contains the following
language ‘‘The prohibitions required by
this proclamation shall not apply to
activities and exercises of the Armed
Forces (including those carried out by
the United States Coast Guard) that are
consistent with applicable laws.’’
Comment 63: Several commenters
included potentially technical
comments that NMFS could not
interpret from the context in which they
were presented, such as: ‘‘Sonar hours
should not be averaged, because longer
exposure leads to more disruption of
feeding, caring for young, mating,
resting, and other activities necessary to
animals’ long-term well-being’’ or ‘‘OHA
also asks that NMFS consider the NMFS
defined refresh rate of 24 hours, which
represents the amount of time in which
individual marine mammals can be
harassed no more than once when
considering authorizing their take
permits for this proposed action.’’
Response: NMFS is not responding to
these comments because the meaning of
the comment is not clear.
Estimated Take of Marine Mammals
As mentioned previously, with
respect to the MMPA, NMFS’ effects
assessments serve three primary
purposes: (1) To put forth the
permissible methods of taking (i.e.,
Level B Harassment (behavioral
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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 HRC, so
this determination is inapplicable for
the HRC); and (4) to prescribe
requirements pertaining to monitoring
and reporting.
In the Estimated Take of Marine
Mammals section of the proposed rule,
NMFS related the potential effects to
marine mammals from MFAS/HFAS
and underwater detonation of
explosives (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 training activities that the Navy
intends to conduct. The subsections of
this analysis are discussed individually
below.
Definition of Harassment
The Definition of Harassment section
of the proposed rule contained the
definitions of Level A and Level B
Harassments, and a discussion of which
of the previously discussed potential
effects of MFAS/HFAS or explosive
detonations fall into the categories of
Level A Harassment (permanent
threshold shift (PTS), acoustically
mediated bubble growth, behaviorally
mediated bubble growth, and physical
disruption of tissues resulting from
explosive shock wave) or Level B
Harassment (temporary threshold shift
(TTS), acoustic masking and
communication impairment, and
behavioral disturbance rising to the
level of harassment); 73 FR 35510, pages
35549–35550. 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
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the development and application of the
acoustic criteria for both MFAS/HFAS
and explosive detonations (73 FR 35510,
pages 35550–35555). No changes have
been made to the discussion contained
in this section of the proposed rule.
NMFS has also summarized the acoustic
criteria below.
For MFAS/HFAS, NMFS uses
acoustic criteria for PTS, TTS, and
behavioral harassment.
NMFS’ TTS criteria (which indicate
the received level at which onset TTS
(>6 dB) is induced) for MFAS/HFAS are
as follows:
• Cetaceans—195 dB re 1 μPa2¥s
(based on mid-frequency cetaceans—no
published data exist on auditory effects
of noise in low or high frequency
cetaceans (Southall et al. (2007)).
• Pinnipeds (monk seals)—204 dB re
1 μPa2¥s (based on data from elephant
seals, which are the most closely related
to the monk seal).
NMFS uses the following acoustic
criteria for injury (Level A Harassment):
• Cetaceans—215 dB re 1 μPa2¥s
(based on mid-frequency cetaceans)—no
published data exist on auditory effects
of noise in low or high frequency
cetaceans (Southall et al. (2007))
• Pinnipeds (monk seals)—224 dB re
1 μPa2¥s (based on data from elephant
seals, which are the most closely related
to the monk seal).
For the behavioral harassment
criteria, NMFS uses acoustic risk
functions developed by NMFS and the
Navy to estimate the probability of
behavioral responses to MFAS/HFAS
(interpreted as the percentage of the
exposed population) that NMFS would
classify as harassment for the purposes
of the MMPA given exposure to specific
received levels of MFAS (73 FR 35510,
page 35554).
Table 13 in the proposed rule
summarizes the acoustic criteria for
explosive detonations (73 FR 35510,
page 35555).
Take Calculations
Estimating the take that will result
from the proposed activities entails the
following four steps: Propagation model
estimates animals exposed to sources at
different levels; further modeling
determines number of exposures to
levels indicated in criteria above (i.e.,
number of takes); post-modeling
corrections refine estimates to make
them more accurate; mitigation is taken
into consideration in post-modeling
analysis. More information regarding
the models used, the assumptions used
in the models, and the process of
estimating take is available in Appendix
J of the Navy’s FEIS for the HRC.
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(1) In order to quantify the types of
take described in previous sections that
are predicted to result from the Navy’s
specified activities, the Navy first uses
a sound propagation model that predicts
the number of animals that will be
exposed to a range of levels of pressure
and energy (of the metrics used in the
criteria) from MFAS/HFAS and
explosive detonations based on several
important pieces of information,
including:
• Characteristics of the sound sources
• Sonar source characteristics
include: Source level (with horizontal
and vertical directivity corrections),
source depth, center frequency, source
directivity (horizontal/vertical beam
width and horizontal/vertical steer
direction), and ping spacing.
• Explosive source characteristics
include: The weight of an explosive, the
type of explosive, the detonation depth,
number of successive explosions.
• Transmission loss (in 20
representative environmental provinces
across 8 sonar modeling areas) based on:
Water depth; sound speed variability
throughout the water column (presume
surface duct is present in HRC); bottom
geo-acoustic properties (bathymetry);
and wind speed.
• The density of each marine
mammal species in the HRC (see Table
14), horizontally distributed uniformly
and vertically distributed according to
dive profiles based on field data.
(2) Next, the criteria discussed in the
previous section are applied to the
estimated exposures to predict the
number of exposures that exceed the
criteria, i.e., the number of takes by
Level B Harassment, Level A
Harassment, and mortality.
(3) During the development of the EIS
for the HRC, NMFS and the Navy
determined that the output of the model
could be made more realistic by
applying post-modeling corrections to
account for the following:
• Acoustic footprints for sonar
sources must account for land masses
(by subtracting them out).
• Acoustic footprints for sonar
sources should not be added
independently, rather, the degree to
which the footprints from multiple
ships participating in the same exercise
would typically overlap needs to be
taken into consideration.
• Acoustic modeling should account
for the maximum number of individuals
of a species that could potentially be
exposed to sonar within the course of 1
day or a discreet continuous sonar event
if less than 24 hours.
(4) Mitigation measures are taken into
consideration. For example, in some
cases the raw modeled numbers of
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exposures to levels predicted to result in
Level A Harassment from exposure to
sonar might indicate that 1 fin whale
would be exposed to levels of sonar
anticipated to result in PTS. However, a
fin whale would need to be within
approximately 10 m of the source vessel
in order to be exposed to sound pressure
levels that would result in PTS. Because
of the mitigation measures
(watchstanders and shutdown zone),
size of fin whales, and nature of fin
whale behavior, it is highly unlikely
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that a fin whale would be exposed to
those levels, and therefore, NMFS
would not expect fin whales to
experience injury as a result of sonar
use. Table 6 contains the Navy’s take
estimates as well as the number of takes
that these regulations and the associated
LOAs will authorize. The table contains
a few minor corrections that did not
affect NMFS analysis.
(5) The Navy’s specified activities
have been described based on best
estimates of the number of MFAS/HFAS
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hours that the Navy will conduct. The
exact number of hours may vary from
year to year, but will not exceed the 5year total indicated in Table 3 (by
multiplying the yearly estimate by 5) by
more than 10-percent. NMFS estimates
that a 10-percent increase in sonar hours
would result in approximately a 10percent increase in the number of takes,
and we have considered this possibility
in our analysis.
BILLING CODE 3510–22–P
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BILLING CODE 3510–22–C
Mortality
Evidence from five beaked whale
strandings, all of which have taken
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place outside the HRC, and have
occurred over approximately a decade,
suggests that the exposure of beaked
whales to mid-frequency sonar in the
presence of certain conditions (e.g.,
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multiple units using tactical sonar, steep
bathymetry, constricted channels, strong
surface ducts, etc.) may result in
strandings, potentially leading to
mortality. Although these physical
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factors believed to contribute to the
likelihood of beaked whale strandings
are not present in the Hawaiian Islands
in the aggregate, scientific uncertainty
exists regarding what other factors, or
combination of factors, may contribute
to beaked whale strandings.
Accordingly, to allow for scientific
uncertainty regarding contributing
causes of beaked whale strandings and
the exact behavioral or physiological
mechanisms that can lead to the
ultimate physical effects (stranding and/
or death), the Navy has requested
authorization for take, by serious injury
or mortality, of 10 individuals of each
of the following species over the course
of the five-year rule: bottlenose dolphin,
Kogia spp., melon-headed whale,
pantropical spotted dolphin, pygmy
killer whale, short-finned pilot whale,
striped dolphin, Cuvier’s, Longman’s,
and Blainville’s beaked whales.
Although the Navy has requested take
by serious injury or mortality, neither
agency expects that marine mammal
strandings or mortality would result
from the operation of mid-frequency
sonar during Navy exercises within the
HRC.
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Effects on Marine Mammal Habitat
NMFS’ proposed rule for the HRC
included a detailed section that
addressed the effects of the Navy’s
training activities on Marine Mammal
Habitat (73 FR 35510, pages 35559–
35560). The analysis concluded that the
Navy’s training activities would have
minimal effects on fish, essential fish
habitat, or marine mammal habitat
provided the Navy’s mitigation
measures were implemented. No
changes have been made to the
discussion contained in this section of
the proposed rule.
Analysis and Negligible Impact
Determination
Pursuant to NMFS’ regulations
implementing the MMPA, an applicant
is required to estimate the number of
animals that will be ‘‘taken’’ by the
specified activities (i.e., takes by
harassment only, or takes by
harassment, injury, and/or death). This
estimate informs the analysis that NMFS
must perform to determine whether the
activity will have a ‘‘negligible impact’’
on the species or stock. Level B
(behavioral) harassment occurs at the
level of the individual(s) and does not
assume any resulting population-level
consequences, though there are known
avenues through which behavioral
disturbance of individuals can result in
population-level effects (for example:
Pink-footed geese (Anser
brachyrhynchus) in undisturbed habitat
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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 has a 17-percent
reproductive success). A negligible
impact finding is based on the lack of
likely adverse effects on annual rates of
recruitment or survival (i.e., populationlevel effects). An estimate of the number
of Level B harassment takes, alone, is
not enough information on which to
base an impact determination. In
addition to considering estimates of the
number of marine mammals that might
be ‘‘taken’’ through behavioral
harassment, NMFS must consider other
factors, such as the likely nature of any
responses (their intensity, duration,
etc.), the context of any responses
(critical reproductive time or location,
migration, etc.), or any of the other
variables mentioned in the first
paragraph (if known), as well as the
number and nature of estimated Level A
takes, the number of estimated
mortalities, and effects on habitat.
Generally speaking, and especially with
other factors being equal, the Navy and
NMFS anticipate more severe effects
from takes resulting from exposure to
higher received levels (though this is in
no way a strictly linear relationship
throughout species, individuals, or
circumstances) and less severe effects
from takes resulting from exposure to
lower received levels.
In the Analysis and Negligible Impact
Determination section of the proposed
rule, NMFS addressed the issues
identified in the preceding paragraph in
combination with additional detailed
analysis regarding the severity of the
anticipated effects, and including
species (or group)-specific discussions,
to determine that Navy training
exercises utilizing MFAS/HFAS and
underwater detonations will have a
negligible impact on the marine
mammal species and stocks present in
the HRC. No changes have been made to
the discussion contained in this section
of the proposed rule.
Subsistence Harvest of Marine
Mammals
NMFS has determined that the
issuance of these regulations and
subsequent LOAs for Navy training
exercises in the HRC would not have an
unmitigable adverse impact on the
availability of the affected species or
stocks for taking for subsistence uses,
since there are no such uses in the
specified area.
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1483
Endangered Species Act (ESA)
There are seven marine mammal
species and five sea turtle species listed
as threatened or endangered under the
ESA with confirmed or possible
occurrence in the study area: Humpback
whale, North Pacific right whale, sei
whale, fin whale, blue whale, sperm
whale, and Hawaiian monk seal,
loggerhead sea turtle, the green sea
turtle, hawksbill sea turtle, leatherback
sea turtle, and olive ridley sea turtle.
Pursuant to section 7 of the ESA, the
Navy has consulted with NMFS on this
action. NMFS has also consulted
internally on the issuance of regulations
under section 101(a)(5)(A) of the MMPA
for this activity. In a Biological Opinion
(BiOp), NMFS concluded that the
Navy’s training activities in the HRC
and NMFS’ issuance of these regulations
are not likely to jeopardize the
continued existence of threatened or
endangered species or destroy or
adversely modify any designated critical
habitat.
NMFS (the Endangered Species
Division) will also issue BiOps and
associated incidental take statements
(ITSs) to NMFS (the Permits,
Conservation, and Recreation Division)
to exempt the take (under the ESA) that
NMFS authorizes in the LOAs under the
MMPA. Because of the difference
between the statutes, it is possible that
ESA analysis of the applicant’s action
could produce a take estimate that is
different than the takes requested by the
applicant (and analyzed for
authorization by NMFS under the
MMPA process), despite the fact that the
same proposed action (i.e., number of
sonar hours and explosive detonations)
was being analyzed under each statute.
When this occurs, NMFS staff
coordinate to ensure that that the most
conservative (lowest) number of takes
are authorized. For the Navy’s proposed
training in the HRC, 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 their analysis
indicates that fewer will be taken than
estimated by the applicant). Therefore,
the number of authorized takes in
NMFS’ LOA(s) will reflect the lower
take numbers from the ESA
consultation, though the specified
activities (i.e., number of sonar hours,
etc.) will remain the same. Alternately,
these regulations indicate the maximum
number of takes that may be authorized
under the MMPA.
The ITS(s) issued for each LOA will
contain implementing terms and
conditions to minimize the effect of the
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marine mammal take authorized
through the 2009 LOA (and subsequent
LOAs in 2010, 2011, 2012, and 2013).
With respect to listed marine mammals,
the terms and conditions of the ITSs
will be incorporated into the LOAs.
NEPA
NMFS participated as a cooperating
agency on the Navy’s Final
Environmental Impact Statement (FEIS)
for the Hawaii Range Complex, which
was published on May 9, 2008. NMFS
subsequently adopted the Navy’s EIS for
the purpose of complying with the
MMPA. Additionally, NMFS prepared
an Environmental Assessment (EA) that
tiered off the Navy’s FEIS. The EA
analyzed the environmental effects of
several different mitigation alternatives
for the issuance of the HRC rule and
subsequent LOAs. A finding of no
significant impact was issued for the
Mitigation EA on December 30, 2008.
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Determination
Based on the analysis contained
herein, and in the proposed rule (and
other related documents), of the likely
effects of the specified activity on
marine mammals and their habitat and
dependent upon the implementation of
the mitigation measures, NMFS finds
that the total taking from Navy training
exercises utilizing MFAS/HFAS and
underwater explosives in the HRC over
the 5 year period will have a negligible
impact on the affected species or stocks
and will not result in an unmitigable
adverse impact on the availability of
marine mammal species or stocks for
taking for subsistence uses because no
subsistence uses exist in the HRC.
NMFS has issued regulations for these
exercises that prescribe the means of
effecting the least practicable adverse
impact on marine mammals and their
habitat and set forth requirements
pertaining to the monitoring and
reporting of that taking.
Classification
This action does not contain a
collection of information requirement
for purposes of the Paperwork
Reduction Act.
Pursuant to the procedures
established to implement section 6 of
Executive Order 12866, the Office of
Management and Budget has
determined that this final rule is
significant.
Pursuant to the Regulatory Flexibility
Act, the Chief Counsel for Regulation of
the Department of Commerce has
certified to the Chief Counsel for
Advocacy of the Small Business
Administration that this final rule, if
adopted, would not have a significant
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economic impact on a substantial
number of small entities. The
Regulatory Flexibility Act requires
Federal agencies to prepare an analysis
of a rule’s impact on small entities
whenever the agency is required to
publish a notice of proposed
rulemaking. However, a Federal agency
may certify, pursuant to 5 U.S.C. section
605(b), that the action will not have a
significant economic impact on a
substantial number of small entities.
The Navy is the entity that will be
affected by this rulemaking, not a small
governmental jurisdiction, small
organization or small business, as
defined by the Regulatory Flexibility
Act. Any requirements imposed by a
Letter of Authorization issued pursuant
to these regulations, and any monitoring
or reporting requirements imposed by
these regulations, will be applicable
only to the Navy. Because this action, if
adopted, would directly affect the Navy
and not a small entity, NMFS concludes
the action would not result in a
significant economic impact on a
substantial number of small entities.
The Assistant Administrator for
Fisheries has determined that there is
good cause under the Administrative
Procedure Act (5 U.S.C. 553(d)(3)) to
waive the 30-day delay in effective date
of the measures contained in the final
rule. Since January 23, 2007, the Navy
has been conducting military readiness
activities employing mid-frequency
active sonar (MFAS) pursuant to a 2year MMPA National Defense
Exemption (NDE). The NDE serves as a
bridge to long-term compliance with the
MMPA while the Navy prepared its
Environmental Impact Statement and
pursued the necessary MMPA
incidental take authorization for the
HRC. The NDE will expire on January
23, 2009, by which time it is imperative
that the regulations and the measures
identified in a subsequent LOA become
effective. Any delay of these measures
would result in either: (1) A suspension
of ongoing or planned naval exercises,
which would disrupt vital sequential
training and certification processes
essential to national security; or (2) the
Navy’s non-compliance with the MMPA
(should the Navy conduct exercises
without an LOA), thereby resulting in
the potential for unauthorized takes of
marine mammals upon expiration of the
NDE. National security interests and the
need for MMPA compliance after
January 23, 2009, dictate that these
measures go into effect immediately.
The Navy is the entity subject to the
regulations and has informed NMFS
that it is imperative that these measures
be effective on or before January 23,
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2009. Finally, as recognized by the
President and the United States
Supreme Court, the training proposed to
be conducted in the HRC is in the
paramount interest of the United States.
Any delay in the implementation of
these measures would raise serious
national security implications.
Therefore, these measures will become
effective upon filing.
List of Subjects in 50 CFR Part 216
Exports, Fish, Imports, Incidental
take, Indians, Labeling, Marine
mammals, Navy, Penalties, Reporting
and recordkeeping requirements,
Seafood, Sonar, Transportation.
Dated: January 2, 2009.
John Oliver,
Deputy Assistant Administrator for
Operations, National Marine Fisheries
Service.
For reasons set forth in the preamble,
50 CFR Part 216 is amended as follows:
■
PART 216—REGULATIONS
GOVERNING THE TAKING AND
IMPORTING OF MARINE MAMMALS
1. The authority citation for part 216
continues to read as follows:
■
Authority: 16 U.S.C. 1361 et seq.
2. Subpart P is added to part 216 to
read as follows:
■
Subpart P—Taking Marine Mammals
Incidental to U.S. Navy Training in the
Hawaii Range Complex (HRC)
Sec.
216.170 Specified activity and specified
geographical region.
216.171 Effective dates and definitions.
216.172 Permissible methods of taking.
216.173 Prohibitions.
216.174 Mitigation.
216.175 Requirements for monitoring and
reporting.
216.176 Applications for Letters of
Authorization.
216.177 Letters of Authorization.
216.178 Renewal of Letters of
Authorization.
216.179 Modifications to Letters of
Authorization.
Subpart P—Taking Marine Mammals
Incidental to U.S. Navy Training in the
Hawaii Range Complex (HRC)
§ 216.170 Specified activity and specified
geographical region.
(a) Regulations in this subpart apply
only to the U.S. Navy for the taking of
marine mammals that occurs in the area
outlined in paragraph (b) of this section
and that occurs incidental to the
activities described in paragraph (c) of
this section.
(b) The taking of marine mammals by
the Navy is only authorized if it occurs
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within the Hawaii Operational Area,
which extends from 16 to 43° N. lat. and
from 150 to 179° degrees W. long.
(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) and high
frequency active sonar (HFAS) sources
for U.S. Navy anti-submarine warfare
(ASW) training in the amounts
indicated below (+/¥10 percent):
(i) AN/SQS–53 (hull-mounted
sonar)—up to 6420 hours over the
course of 5 years (an average of 1284
hours per year)
(ii) AN/SQS–56 (hull-mounted
sonar)—up to 1915 hours over the
course of 5 years (an average of 383
hours per year)
(iii) AN/AQS–22 (helicopter dipping
sonar)—up to 5050 dips over the course
of 5 years (an average of 1010 dips per
year)
(iv) SSQ–62 (sonobuoys)—up to
12115 sonobuoys over the course of 5
years (an average of 2423 sonobuoys per
year)
(v) MK–48 (torpedoes)—up to 1565
torpedoes over the course of 5 years (an
average of 313 torpedoes per year)
(vi) AN/BQQ–10 (submarine mounted
sonar)—up to 1000 hours over the
course of 5 years (an average of 200 per
year)
(2) The detonation of the underwater
explosives indicated in paragraph
(c)(2)(i) of this section conducted as part
of the training exercises indicated in
paragraph (c)(2)(ii) of this section:
(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–83 (574 lbs).
(G) MK–84 (945 lbs).
(H) MK–48 (851 lbs).
(I) Demolition Charges (20 lbs).
(J) EER/IEER (5 lbs).
(ii) Training Events:
(A) Mine Neutralization—up to 340
exercises over the course of 5 years (an
average of 68 per year).
(B) Air-to-Surface MISSILEX—up to
250 exercises over the course of 5 years
(an average of 50 per year).
(C) Surface-to-Surface MISSILEX—up
to 60 exercises over the course of 5 years
(an average of 12 per year).
(D) BOMBEX—up to 195 exercises
over the course of 5 years (an average of
38 per year).
(E) SINKEX—up to 30 exercises over
the course of 5 years (an average of 6 per
year).
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(F) Surface-to-Surface GUNEX—up to
455 exercises over the course of 5 years
(an average of 91 per year).
(G) Naval Surface Fire Support—up to
140 exercises over the course of 5 years
(an average of 28 per year).
§ 216.171
Effective dates and definitions.
(a) Regulations are effective January 5,
2009 through January 5, 2014.
(b) The following definitions are
utilized in these regulations:
(1) Uncommon Stranding Event
(USE)—A stranding event that takes
place during a major training exercise
and involves any one of the following:
(i) Two or more individuals of any
cetacean species (not including mother/
calf pairs, unless of species of concern
listed in next bullet) found dead or live
on shore within a two day period and
occurring on same shore lines or facing
shorelines of different islands.
(ii) A single individual or mother/calf
pair of any of the following marine
mammals of concern: Beaked whale of
any species, Kogia sp., Risso’s dolphin,
melon-headed whale, pilot whales,
humpback whales, sperm whales, blue
whales, fin whales, sei whales, or monk
seal.
(iii) A group of 2 or more cetaceans
of any species exhibiting indicators of
distress.
(2) Shutdown (this definition
specifically applies only to the word as
used in § 216.174(a)(1)(xxviii)(A)(1) and
(2))—The cessation of MFAS operation
or detonation of explosives within 14
nm of any live, in the water animal
involved in a USE.
§ 216.172
Permissible methods of taking.
(a) Under Letters of Authorization
issued pursuant to §§ 216.106 and
216.177, the Holder of the Letter of
Authorization may incidentally, but not
intentionally, take marine mammals
within the area described in
§ 216.170(b), provided the activity is in
compliance with all terms, conditions,
and requirements of these regulations
and the appropriate Letter of
Authorization.
(b) The activities identified in
§ 216.170(c) must be conducted in a
manner that minimizes, to the greatest
extent practicable, any adverse impacts
on marine mammals and their habitat.
(c) The incidental take of marine
mammals under the activities identified
in § 216.170(c) is limited to the
following species, by the indicated
method of take and the indicated
number of times:
(1) Level B Harassment (+/¥10
percent of the number of takes indicated
below):
(i) Mysticetes:
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(A) Humpback whale (Megaptera
novaeangliae)—49470 (an average of
9894 annually).
(B) Minke whale (Balaenoptera
acutorostrata)—320 (an average of 64
annually).
(C) Sei whale (Balaenoptera
borealis)—230 (an average of 46
annually).
(D) Fin whale (Balaenoptera
physalus)—230 (an average of 46
annually).
(E) Bryde’s whale (Balaenoptera
edeni)—320 (an average of 64 annually).
(ii) Odontocetes:
(A) Sperm whales (Physeter
macrocephalus)—3905 (an average of
781 annually).
(B) Pygmy sperm whales (Kogia
breviceps)—4325 (an average of 865
annually).
(C) Dwarf sperm whale (Kogia sima)—
10610 (an average of 2122 annually).
(D) Cuvier’s beaked whale (Ziphius
cavirostris)—5750 (an average of 1150
annually).
(E) Blainville’s beaked whale
(Mesoplodon densirostris)—1785 (an
average of 357 annually).
(F) Longman’s beaked whale
(Indopacetus pacificus)—525 (an
average of 105 annually).
(G) Rough-toothed dolphin (Steno
bredanensis)—5385 (an average of 1077
annually).
(H) Bottlenose dolphin (Tursiops
truncatus)—3670 ( an average of 734
annually).
(I) Pan-tropical dolphins (Stenella
attenuata)—10995 (an average of 2199
annually).
(J) Spinner dolphins (Stenella
longirostris)—2105 (an average of 421
annually).
(K) Striped dolphins (Stenella
coeruleoalba)—16045 (an average of
3209 annually).
(L) Risso’s dolphin (Grampus
griseus)—2485 (an average of 497
annually).
(M) Melon-headed whale
(Peponocephala electra)—2985 (an
average of 597 annually).
(N) Fraser’s dolphin (Lagenodelphis
hosei)—6235 (an average of 1247
annually).
(O) Pygmy killer whale (Feresa
attenuata)—980 (an average of 196
annually).
(P) False killer whale (Pseudorca
crassidens)—230 (an average of 46
annually).
(Q) Killer whale (Orcinus orca)—230
(an average of 46 annually).
(R) Short-finned pilot whale
(Globicephala macrorynchus)—8990 (an
average of 1798 annually).
(iii) Pinnipeds: Hawaiian monk seal
(Monachus schauinslandi)—550 (an
average of 110 annually).
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(2) Level A Harassment and/or
mortality of no more than 10
individuals total of each of the species
listed below over the course of the 5year regulations: Bottlenose dolphin
(Tursiops truncatus), Pygmy and Dwarf
sperm whales (Kogia breviceps and
sima), Melon-headed whale
(Peponocephala electra), Pantropical
spotted dolphin (Stenella attenuata),
Pygmy killer whale (Feresa attenuata),
Short-finned pilot whale (Globicephala
macrorynchus), Striped dolphin
(Stenella coeruleoalba), and Cuvier’s
beaked whale (Ziphius cavirostris),
Blainville’s beaked whale, (Mesoplodon
densirostris), Longman’s beaked whale
(Indopacetus pacificus).
§ 216.173
Prohibitions.
Notwithstanding takings
contemplated in § 216.172 and
authorized by a Letter of Authorization
issued under §§ 216.106 and 216.177,
no person in connection with the
activities described in § 216.170 may:
(a) Take any marine mammal not
specified in § 216.172(c);
(b) Take any marine mammal
specified in § 216.172(c) other than by
incidental take as specified in
§ 216.172(c)(1) and (2);
(c) Take a marine mammal specified
in § 216.172(c) if such taking results in
more than a negligible impact on the
species or stocks of such marine
mammal; or
(d) Violate, or fail to comply with, the
terms, conditions, and requirements of
these regulations or a Letter of
Authorization issued under §§ 216.106
and 216.177.
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§ 216.174
Mitigation.
(a) When conducting training
activities identified in § 216.170(c), the
mitigation measures contained in the
Letter of Authorization issued under
§§ 216.106 of this chapter and 216.177
must be implemented. These mitigation
measures include, but are not limited to:
(1) Mitigation Measures for ASW
training: (i) All lookouts onboard
platforms involved in ASW training
events shall review the NMFS-approved
Marine Species Awareness Training
(MSAT) material prior to use of midfrequency active sonar.
(ii) All Commanding Officers,
Executive Officers, and officers standing
watch on the Bridge shall have reviewed
the MSAT material prior to a training
event employing the use of midfrequency active sonar.
(iii) Navy lookouts shall undertake
extensive training in order to qualify as
a watchstander in accordance with the
Lookout Training Handbook
(NAVEDTRA, 12968–D).
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(iv) Lookout training shall include onthe-job instruction under the
supervision of a qualified, experienced
watchstander. Following successful
completion of this supervised training
period, Lookouts shall complete the
Personal Qualification Standard
program, certifying that they have
demonstrated the necessary skills (such
as detection and reporting of partially
submerged objects).
(v) Lookouts shall be trained in the
most effective means to ensure quick
and effective communication within the
command structure in order to facilitate
implementation of mitigation measures
if marine species are spotted.
(vi) On the bridge of surface ships,
there shall be at least three people on
watch whose duties include observing
the water surface around the vessel.
(vii) All surface ships participating in
ASW exercises shall, in addition to the
three personnel on watch noted
previously, have at all times during the
exercise at least two additional
personnel on watch as lookouts.
(viii) Personnel on lookout and
officers on watch on the bridge shall
have at least one set of binoculars
available for each person to aid in the
detection of marine mammals.
(ix) On surface vessels equipped with
mid-frequency active sonar, pedestal
mounted ‘‘Big Eye’’ (20x110) binoculars
shall be present and in good working
order.
(x) Personnel on lookout shall employ
visual search procedures employing a
scanning methodology in accordance
with the Lookout Training Handbook
(NAVEDTRA 12968–D).
(xi) After sunset and prior to sunrise,
lookouts shall employ Night Lookouts
Techniques in accordance with the
Lookout Training Handbook.
(xii) 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.
(xiii) CPF shall distribute the final
mitigation measures contained in the
LOA and BO to the Fleet.
(xiv) Commanding Officers 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.
(xv) 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.
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(xvi) During mid-frequency active
sonar training activities, personnel shall
utilize all available sensor and optical
systems (such as Night Vision Goggles)
to aid in the detection of marine
mammals.
(xvii) Navy aircraft participating in
exercises at sea shall conduct and
maintain, when operationally feasible
and safe, surveillance for marine
mammals as long as it does not violate
safety constraints or interfere with the
accomplishment of primary operational
duties.
(xviii) Aircraft with deployed
sonobuoys shall use only the passive
capability of sonobuoys when marine
mammals are detected within 200 yards
(182 m) of the sonobuoy.
(xix) Marine mammal detections shall
be reported immediately to assigned
Aircraft Control Unit 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.
(xx) Safety Zones—When marine
mammals are detected by any means
(aircraft, shipboard lookout, or
acoustically) the Navy shall ensure that
MFAS transmission levels are limited to
at least 6 dB below normal operating
levels if any detected marine mammals
are within 1000 yards (914 m) of the
sonar dome (the bow).
(A) Ships and submarines shall
continue to limit maximum MFAS
transmission levels by this 6-dB factor
until the marine mammal has been seen
to leave the area, has not been detected
for 30 minutes, or the vessel has
transited more than 2,000 yards (1828
m) beyond the location of the last
detection.
(B) The Navy shall ensure that MFAS
transmissions will be limited to at least
10 dB below the equipment’s normal
operating level if any detected animals
are within 500 yards (457 m) of the
sonar dome. Ships and submarines shall
continue to limit maximum ping levels
by this 10-dB factor until the marine
mammal has been seen to leave the area,
has not been detected for 30 minutes, or
the vessel has transited more than 2000
yards (1828 m) beyond the location of
the last detection.
(C) The Navy shall ensure that MFAS
transmissions are ceased if any detected
marine mammals are within 200 yards
of the sonar dome. MFAS transmissions
will not resume until the marine
mammal has been seen to leave the area,
has not been detected for 30 minutes, or
the vessel has transited more than 2,000
yards beyond the location of the last
detection.
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(D) Special conditions applicable for
dolphins and porpoises only: If, after
conducting an initial maneuver to avoid
close quarters with dolphins or
porpoises, the Officer of the Deck
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.
(E) If the need for power-down should
arise as detailed in ‘‘Safety Zones’’ in
paragraph (a)(1)(xx) of this section,
Navy shall follow the requirements as
though they were operating at 235 dB—
the normal operating level (i.e., the first
power-down will be to 229 dB,
regardless of at what level above 235 dB
sonar was being operated).
(xxi) Prior to start up or restart of
active sonar, operators shall check that
the Safety Zone radius around the
sound source is clear of marine
mammals.
(xxii) Sonar levels (generally)—Navy
shall operate sonar at the lowest
practicable level, not to exceed 235 dB,
except as required to meet tactical
training objectives.
(xxiii) Helicopters shall observe/
survey the vicinity of an ASW Exercise
for 10 minutes before the first
deployment of active (dipping) sonar in
the water.
(xxiv) Helicopters shall not dip their
sonar within 200 yards (183 m) of a
marine mammal and shall cease pinging
if a marine mammal closes within 200
yards (183 m) after pinging has begun.
(xxv) Submarine sonar operators shall
review detection indicators of closeaboard marine mammals prior to the
commencement of ASW training
activities involving active midfrequency sonar.
(xxvi) Night vision goggles shall be
available to all ships and air crews, for
use as appropriate.
(xxvii) Humpback Whale Cautionary
Area: An area extending 5km (2.7 nm)
from a line drawn from Kaunakakai on
the island of Molokai to Kaena Point on
the Island of Lanai; and an area
extending 5 km (2.7 nm) from a line
drawn from Kaunolu on the Island of
Lanai to the most Northeastern point on
the Island of Kahoolawe; and within a
line drawn from Kanapou Bay on the
Island of Kahoolawe to Kanahena Point
on the Island of Maui and a line drawn
from Cape Halawa on the Island of
Molokai to Lipo Point on the Island of
Maui, excluding the existing submarine
operating area.
(A) Should national security needs
require MFAS training and testing in the
cautionary area between 15 December
and 15 April, it must be personally
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authorized by the Commander, U.S.
Pacific Fleet based on his determination
that training and testing in that specific
area is required for national security
purposes. This authorization shall be
documented by the CPF in advance of
transiting and training in the cautionary
area, and the determination shall be
based on the unique characteristics of
the area from a military readiness
perspective, taking into account the
importance of the area for humpback
whales and the need to minimize
adverse impacts on humpback whales
from MFAS whenever practicable.
Further, Commander, U.S. Pacific Fleet
will provide specific direction on
required mitigation measures prior to
operational units transiting to and
training in the cautionary area.
(B) The Navy shall provide advance
notification to NMFS of any such
activities (listed in paragraph
(a)(1)(xxvii)(A)of this section).
(C) The Navy shall include in its
periodic reports for compliance with the
MMPA whether or not activities
occurred in the Humpback Whale
Cautionary Area and any observed
effects on humpback whales due to the
conduct of these activities.
(xxviii) The Navy shall abide by the
letter of the ‘‘Stranding Response Plan
for Major Navy Training Exercises in the
HRC’’ to include the following
measures:
(A) Shutdown Procedures—When an
Uncommon Stranding Event (USE—
defined in § 216.171(b)) occurs during a
Major Training Exercise (MTE,
including RIMPAC, USWEX, or MultiStrike Group Exercise) in the HRC, the
Navy shall implement the procedures
described below.
(1) The Navy shall implement a
Shutdown (as defined § 216.171(b))
when advised by a NMFS Office of
Protected Resources Headquarters
Senior Official designated in the HRC
Stranding Communication Protocol that
a USE involving live animals has been
identified and that at least one live
animal is located in the water. NMFS
and Navy will maintain a dialogue, as
needed, regarding the identification of
the USE and the potential need to
implement shutdown procedures.
(2) Any shutdown in a given area
shall remain in effect in that area until
NMFS advises the Navy that the
subject(s) of the USE at that area die or
are euthanized, or that all live animals
involved in the USE at that area have
left the area (either of their own volition
or herded).
(3) If the Navy finds an injured or
dead animal floating at sea during an
MTE, the Navy shall notify NMFS
immediately or as soon as operational
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1487
security considerations allow. The Navy
shall provide NMFS with species or
description of the animal(s), the
condition of the animal(s) including
carcass condition if the animal(s) is/are
dead), location, time of first discovery,
observed behavior (if alive), and photo
or video (if available). Based on the
information provided, NMFS will
determine if, and advise the Navy
whether a modified shutdown is
appropriate on a case-by-case basis.
(4) In the event, following a USE, that
qualified individuals are attempting to
herd animals back out to the open ocean
and animals are not willing to leave, or
animals are seen repeatedly heading for
the open ocean but turning back to
shore, NMFS and the Navy shall
coordinate (including an investigation
of other potential anthropogenic
stressors in the area) to determine if the
proximity of MFAS training activities or
explosive detonations, though farther
than 14 nm from the distressed
animal(s), is likely contributing to the
animals’ refusal to return to the open
water. If so, NMFS and the Navy will
further coordinate to determine what
measures are necessary to improve the
probability that the animals will return
to open water and implement those
measures as appropriate.
(B) Within 72 hours of NMFS
notifying the Navy of the presence of a
USE, the Navy shall provide available
information to NMFS (per the HRC
Communication Protocol) regarding the
location, number and types of acoustic/
explosive sources, direction and speed
of units using MFAS, and marine
mammal sightings information
associated with training activities
occurring within 80 nm (148 km) and 72
hours prior to the USE event.
Information not initially available
regarding the 80 nm (148 km), 72 hour
period prior to the event will be
provided as soon as it becomes
available. The Navy will provide NMFS
investigative teams with additional
relevant unclassified information as
requested, if available.
(C) Memorandum of Agreement
(MOA)—The Navy and NMFS shall
develop a MOA, or other mechanism
consistent with federal fiscal law
requirements (and all other applicable
laws), that will establish a framework
whereby the Navy can (and provide the
Navy examples of how they can best)
assist NMFS with stranding
investigations in certain circumstances.
(xxix) 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.
(xxx) 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).
(2) Mitigation for IEER—The
following are protective measures for
use with Extended Echo Ranging/
Improved Extended Echo Ranging (EER/
IEER) given an explosive source
generates the acoustic wave used in this
sonobuoy.
(i) Crews shall conduct aerial visual
reconnaissance of the drop area prior to
laying their intended sonobuoy pattern.
This search should be conducted below
500 yards (457 m) at a slow speed, if
operationally feasible and weather
conditions permit. In dual aircraft
training activities, crews are allowed to
conduct coordinated area clearances.
(ii) Crews shall conduct a minimum
of 30 minutes of visual and acoustic
monitoring of the search area prior to
commanding the first post detonation.
This 30-minute observation period may
include pattern deployment time.
(iii) For any part of the briefed pattern
where a post (source/receiver sonobuoy
pair) will be deployed within 1,000
yards (914 m) of observed marine
mammal activity, the Navy shall deploy
the receiver ONLY and monitor while
conducting a visual search. When
marine mammals are no longer detected
within 1,000 yards (914 m) of the
intended post position, co-locate the
explosive source sonobuoy (AN/SSQ–
110A) (source) with the receiver.
(iv) When able, crews will conduct
continuous visual and aural monitoring
of marine mammal activity. This is to
include monitoring of own-aircraft
sensors from first sensor placement to
checking off station and out of
communication range of these sensors.
(v) Aural Detection: If the presence of
marine mammals is detected aurally,
then that shall cue the aircrew to
increase the diligence of their visual
surveillance. Subsequently, if no marine
mammals are visually detected, then the
crew may continue multi-static active
search.
(vi) Visual Detection:
(A) If marine mammals are visually
detected within 1,000 yards (914 m) of
the explosive source sonobuoy (AN/
SSQ–110A) intended for use, then that
payload shall not be detonated.
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Aircrews may utilize this post once the
marine mammals have not been resighted for 30 minutes, or are observed
to have moved outside the 1,000 yards
(914 m) safety buffer.
(B) Aircrews may shift their multistatic active search to another post,
where marine mammals are outside the
1,000 yards (914 m) safety buffer.
(vii) 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 1,000 yard (914 m) safety buffer,
visually clear of marine mammals, is
maintained around each post as is done
during active search operations.
(viii) Aircrews shall only leave posts
with unexploded charges in the event of
a sonobuoy malfunction, an aircraft
system malfunction, or when an aircraft
must immediately depart the area due to
issues such as fuel constraints,
inclement weather, and in-flight
emergencies. In these cases, the
sonobuoy will self-scuttle using the
secondary or tertiary method.
(ix) The navy shall ensure all
payloads are accounted for. Explosive
source sonobuoys (AN/SSQ–110A) that
cannot be scuttled shall be reported as
unexploded ordnance via voice
communications while airborne, then
upon landing via naval message.
(x) Marine mammal monitoring shall
continue until out of own-aircraft sensor
range.
(3) Mitigation for Demolitions
(DEMOs) and Mine Countermeasure
(MCM) Training (Up to 20 lb).
(i) Exclusion Zones—Explosive
charges shall not be detonated if a
marine mammal is detected within 700
yards (640 m) of the detonation site.
(ii) Pre-Exercise Surveys—For MCM
training activities, the Navy shall
conduct a pre-exercise survey 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.
If a marine mammal is detected within
the survey area, the exercise shall be
suspended until the animal voluntarily
leaves the area.
(iii) Post-Exercise Surveys—Surveys
within the same radius shall also be
conducted within 30 minutes after the
completion of the explosive event.
(iv) Reporting—Any evidence of a
marine mammal that may have been
injured or killed by the action shall be
reported immediately to NMFS.
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(v) Mine Laying Training—Though
mine laying training operations involve
aerial drops of inert training shapes on
floating targets, measures 1, 2, and 3 for
Demolitions and Mine countermeasures
will apply to mine laying training. To
the maximum extent feasible, the Navy
shall retrieve inert mine shapes dropped
during Mine Laying Training.
(4) Mitigation for SINKEX, GUNEX,
MISSILEX, and BOMBEX. (i) All
weapons firing shall be conducted
during the period 1 hour after official
sunrise to 30 minutes before official
sunset.
(ii) Extensive range clearance
operations shall be conducted in the
hours prior to commencement of the
exercise.
(iii) An exclusion zone with a radius
of 1.0 nm (1.85 km) shall be established
around each target. An additional buffer
of 0.5 nm (0.93 km) shall be added to
account for errors, target drift, and
animal movements. Additionally, a
safety zone, which extends out an
additional 0.5 nm (0.93 km), shall be
surveyed. Together, the zones extend
out 2 nm (3.7 km) from the target.
(iv) A series of surveillance overflights shall be conducted within the
exclusion and the safety zones, prior to
and during the exercise, when feasible.
Survey protocol would be as follows:
(A) Overflights within the exclusion
zone 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 (SAR)
Tactical Aid (TACAID).
(B) All visual surveillance activities
shall be conducted by Navy personnel
trained in visual surveillance. At least
one member of the mitigation team shall
have completed the Navy’s marine
mammal training program for lookouts.
(C) In addition to the overflights, the
exclusion zone shall be monitored by
passive acoustic means, when assets are
available. This passive acoustic
monitoring shall be maintained
throughout the exercise. Potential assets
include sonobuoys, which can be
utilized to detect any vocalizing marine
mammals in the vicinity of the exercise.
The sonobuoys shall be re-seeded as
necessary throughout the exercise.
Additionally, passive sonar onboard
submarines may be utilized to detect
any vocalizing marine mammals in the
area. The Officer Conducting the
Exercise (OCE) shall 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.
(D) On each day of the exercise, aerial
surveillance of the exclusion and safety
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zones shall commence two hours prior
to the first firing.
(E) The results of all visual, aerial,
and acoustic searches shall be reported
immediately to the OCE. No weapons
launches or firing would commence
until the OCE declares the safety and
exclusion zones free of marine
mammals.
(F) If a marine mammal observed
within the exclusion zone is diving,
firing shall be delayed until the animal
is re-sighted outside the exclusion zone,
or 30 minutes has elapsed.
(G) During breaks in the exercise of 30
minutes or more, the exclusion zone
shall again be surveyed for any marine
mammals. If marine mammals are
sighted within the exclusion zone, the
OCE would be notified, and the
procedure described in paragraph
(a)(4)(iv)(F) of this section would be
followed.
(H) Upon sinking of the vessel, a final
surveillance of the exclusion zone shall
be monitored for two hours, or until
sunset, to verify that no marine
mammals were harmed.
(v) Aerial surveillance would be
conducted using helicopters or other
aircraft based on necessity and
availability. These aircraft shall be
capable of (and shall, to the extent
practicable) flying at the slow safe
speeds necessary to enable viewing of
marine mammals with unobstructed, or
minimally obstructed, downward and
outward visibility. The Navy may cancel
the exclusion and safety zone surveys in
the event that a mechanical problem,
emergency search and rescue, or other
similar and unexpected event preempts
the use of one of the aircraft onsite for
the exercise.
(vi) 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 of 4 or
above, the Navy shall utilize additional
aircraft (conducting tight search
patterns), if available, to increase survey
efforts within the zones.
(vii) The exercise shall not be
conducted unless the exclusion zone
can be adequately monitored visually.
(viii) In the unlikely event that any
marine mammals are observed to be
harmed in the area, a detailed
description of the animal shall be
documented, the location noted, and if
possible, photos taken. This information
would be provided to NMFS.
(b) [Reserved]
§ 216.175 Requirements for monitoring
and reporting.
(a) As outlined in the HRC Stranding
Communication Plan, the Holder of the
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Authorization must notify NMFS
immediately (or as soon as clearance
procedures allow) if the specified
activity identified in § 216.170(c) is
thought to have resulted in the mortality
or injury of any marine mammals, or in
any take of marine mammals not
identified in § 216.172(c).
(b) The Holder of the Letter of
Authorization must conduct all
monitoring and required reporting
under the Letter of Authorization,
including abiding by the HRC
Monitoring Plan.
(c) The Navy shall complete an
Integrated Comprehensive Monitoring
Plan (ICMP) in 2009. This planning and
adaptive management tool shall include:
(1) A method for prioritizing
monitoring projects that clearly
describes the characteristics of a
proposal that factor into its priority.
(2) A method for annually reviewing,
with NMFS, monitoring results, Navy
R&D, and current science to use for
potential modification of mitigation or
monitoring methods.
(3) A detailed description of the
Monitoring Workshop to be convened in
2011 and how and when Navy/NMFS
will subsequently utilize the findings of
the Monitoring Workshop to potentially
modify subsequent monitoring and
mitigation.
(4) An adaptive management plan.
(5) A method for standardizing data
collection across Range Complexes.
(d) General Notification of Injured or
Dead Marine Mammals—Navy
personnel shall ensure that NMFS
(regional stranding coordinator) is
notified immediately (or as soon as
clearance procedures allow) if an
injured or dead marine mammal is
found during or shortly after, and in the
vicinity of, any Navy training exercise
utilizing MFAS, HFAS, or underwater
explosive detonations. The Navy shall
provide NMFS with species or
description of the animal(s), the
condition of the animal(s) (including
carcass condition if the animal is dead),
location, time of first discovery,
observed behaviors (if alive), and photo
or video (if available). The Navy shall
consult the Stranding Response Plan to
obtain more specific reporting
requirements for specific circumstances.
(e) Annual HRC Monitoring Plan
Report—The Navy shall submit a report
annually on October 1 describing the
implementation and results (through
August 1 of the same year) of the HRC
Monitoring Plan, described in
§ 216.175(b). Data collection methods
will be standardized across range
complexes to allow for comparison in
different geographic locations. Although
additional information will be gathered,
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1489
the marine mammal observers (MMOs)
collecting marine mammal data
pursuant to the HRC Monitoring Plan
shall, at a minimum, provide the same
marine mammal observation data
required in § 216.175(f)(1).
The HRC Monitoring Plan Report may
be provided to NMFS within a larger
report that includes the required
Monitoring Plan Reports from multiple
Range Complexes.
(f) Annual HRC Exercise Report—The
Navy shall submit an Annual HRC
Exercise Report on October 1 of every
year (covering data gathered through
August 1 (or completion of RIMPAC if
later than Aug 1) of the same year). This
report shall contain information
identified in subsections 216.175(f)(1)—
(f)(5).
(1) MFAS/HFAS Major Training
Exercises—This section shall contain
the following information for Major
Training Exercises (MTEs, which
include RIMPAC, USWEX, and Multi
Strike Group) conducted in the HRC:
(i) Exercise Information (for each
MTE):
(A) Exercise designator.
(B) Date that exercise began and
ended.
(C) Location.
(D) Number and types of active
sources used in the exercise.
(E) Number and types of passive
acoustic sources used in exercise.
(F) Number and types of vessels,
aircraft, etc., participating in exercise.
(G) Total hours of observation by
watchstanders.
(H) Total hours of all active sonar
source operation.
(I) Total hours of each active sonar
source (along with explanation of how
hours are calculated for sources
typically quantified in alternate way
(buoys, torpedoes, etc.)).
(J) Wave height (high, low, and
average during exercise).
(ii) Individual marine mammal
sighting info (for each sighting in each
MTE).
(A) Location of sighting.
(B) Species (if not possible—
indication of whale/dolphin/pinniped).
(C) Number of individuals.
(D) Calves observed (y/n).
(E) Initial Detection Sensor.
(F) Indication of specific type of
platform observation made from
(including, for example, what type of
surface vessel, i.e., FFG, DDG, or CG).
(G) Length of time observers
maintained visual contact with marine
mammal.
(H) Wave height (in feet).
(I) Visibility.
(J) Sonar source in use (y/n).
(K) Indication of whether animal is
<200yd, 200–500yd, 500–1000yd, 1000–
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2000yd, or >2000yd from sonar source
in paragraph (f)(1)(ii)(J) of this section.
(L) Mitigation Implementation—
Whether operation of sonar sensor was
delayed, or sonar was powered or shut
down, and how long the delay was.
(M) If source in use (see paragraph
(f)(1)(ii)(J) of this section) is
hullmounted, true bearing of animal
from ship, true direction of ship’s travel,
and estimation of animal’s motion
relative to ship (opening, closing,
parallel).
(N) Observed behavior—
Watchstanders shall report, in plain
language and without trying to
categorize in any way, the observed
behavior of the animals (such as animal
closing to bow ride, paralleling course/
speed, floating on surface and not
swimming, etc.).
(iii) An evaluation (based on data
gathered during all of the MTEs) of the
effectiveness of mitigation measures
designed to avoid exposing to midfrequency sonar. This evaluation shall
identify the specific observations that
support any conclusions the Navy
reaches about the effectiveness of the
mitigation.
(2) ASW Summary—This section
shall include the following information
as summarized from both MTEs and
non-major training exercises (i.e., unitlevel exercises, such as TRACKEXs):
(i) Total annual hours of each type of
sonar source (along with explanation of
how hours are calculated for sources
typically quantified in alternate way
(buoys, torpedoes, etc.)).
(ii) Total hours (from December 15
through April 15) of hullmounted active
sonar operation occurring in the dense
humpback areas plus a 5-km buffer, but
not including the Pacific Missile Range
Facility. The Navy shall work with
NMFS to develop the exact boundaries
of this area.
(iii) Total estimated annual hours of
hull-mounted active sonar operation
conducted in Humpback Whale
Cautionary area between December 15
and April 15.
(iv) Cumulative Impact Report—To
the extent practicable, the Navy, in
coordination with NMFS, shall develop
and implement a method of annually
reporting non-major (i.e., other than
RIMPAC, USWEX, or Multi-Strike
Group Exercises) training exercises
utilizing hull-mounted sonar. The report
shall present an annual (and seasonal,
where practicable) depiction of nonmajor training exercises geographically
across the HRC. The Navy shall include
(in the HRC annual report) a brief
annual progress update on the status of
development until an agreed-upon (with
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NMFS) method has been developed and
implemented.
(3) SINKEXs—This section shall
include the following information for
each SINKEX completed that year:
(i) Exercise information (gathered for
each SINKEX):
(A) Location.
(B) Date and time exercise began and
ended.
(C) Total hours of observation by
watchstanders before, during, and after
exercise.
(D) Total number and types of rounds
expended/explosives detonated.
(E) Number and types of passive
acoustic sources used in exercise.
(F) Total hours of passive acoustic
search time.
(G) Number and types of vessels,
aircraft, etc., participating in exercise.
(H) Wave height in feet (high, low and
average during exercise).
(I) Narrative description of sensors
and platforms utilized for marine
mammal detection and timeline
illustrating how marine mammal
detection was conducted.
(ii) Individual marine mammal
observation (by Navy lookouts)
information (gathered for each marine
mammal sighting):
(A) Location of sighting.
(B) Species (if not possible, indicate
whale, dolphin or pinniped).
(C) Number of individuals.
(D) Whether calves were observed.
(E) Initial detection sensor.
(F) Length of time observers
maintained visual contact with marine
mammal.
(G) Wave height.
(H) Visibility.
(I) Whether sighting was before,
during, or after detonations/exercise,
and how many minutes before or after.
(J) Distance of marine mammal from
actual detonations (or target spot if not
yet detonated)—use four categories to
define distance:
(1) The modeled injury threshold
radius for the largest explosive used in
that exercise type in that OPAREA (91
m for SINKEX in HRC);
(2) The required exclusion zone (1 nm
for SINKEX in HRC);
(3) The required observation distance
(if different than the exclusion zone (2
nm for SINKEX in HRC); and
(4) Greater than the required observed
distance. For example, in this case, the
observer would indicate if < 91 m, from
91 m—1 nm, from 1 nm—2 nm, and >
2 nm.
(K) Observed behavior—
Watchstanders will report, in plain
language and without trying to
categorize in any way, the observed
behavior of the animal(s) (such as
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animal closing to bow ride, paralleling
course/speed, floating on surface and
not swimming etc.), including speed
and direction.
(L) Resulting mitigation
implementation—Indicate whether
explosive detonations were delayed,
ceased, modified, or not modified due to
marine mammal presence and for how
long.
(M) If observation occurs while
explosives are detonating in the water,
indicate munition type in use at time of
marine mammal detection.
(4) IEER Summary—This section shall
include an annual summary of the
following IEER information:
(i) Total number of IEER events
conducted in the HRC.
(ii) Total expended/detonated rounds
(buoys).
(iii) Total number of self-scuttled
IEER rounds.
(5) Explosives Summary—To the
extent practicable, the Navy will
provide the information described
below for all of their explosive
exercises. Until the Navy 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.
(i) Total annual number of each type
of explosive exercises (of those
identified as part of the ‘‘specified
activity’’ in this final rule) conducted in
the HRC.
(ii) Total annual expended/detonated
rounds (missiles, bombs, etc.) for each
explosive type.
(g) Sonar Exercise Notification—The
Navy shall submit to the NMFS Office
of Protected Resources (specific contact
information to be provided in LOA)
either an electronic (preferably) or
verbal report within fifteen calendar
days after the completion of any major
exercise. (RIMPAC, USWEX, or Multi
Strike Group) indicating:
(1) Location of the exercise.
(2) Beginning and end dates of the
exercise.
(3) Type of exercise (e.g., RIMPAC,
USWEX, or Multi Strike Group).
(h) HRC 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 HRC
Exercise Reports and HRC Monitoring
Plan Reports). This report will be
submitted at the end of the fourth year
of the rule (November 2012), covering
activities that have occurred through
June 1, 2012.
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(i) Comprehensive National ASW
Report—By June 2014, the Navy shall
submit a draft Comprehensive National
Report that analyzes, compares, and
summarizes the active sonar data
gathered (through January 1, 2014) from
the watchstanders in accordance with
the Monitoring Plans for the HRC, the
Atlantic Fleet Active Sonar Training,
the Southern California (SOCAL) Range
Complex, the Marianas Range Complex,
the Northwest Training Range, the Gulf
of Alaska, and the East Coast Undersea
Warfare Training Range.
(j) The Navy shall respond to NMFS
comments and requests for additional
information or clarification on the HRC
Comprehensive Report, the draft
National ASW report, the Annual HRC
Exercise Report, or the Annual HRC
Monitoring Plan Report (or the multiRange 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.
(k) In 2011, the Navy shall convene a
Monitoring Workshop in which the
Monitoring Workshop participants will
be asked to review the Navy’s
Monitoring Plans and monitoring results
and make individual recommendations
(to the Navy and NMFS) of ways of
improving the Monitoring Plans. The
recommendations shall be reviewed by
the Navy, in consultation with NMFS,
and modifications to the Monitoring
Plan shall be made, as appropriate.
§ 216.176 Applications for Letters of
Authorization.
To incidentally take marine mammals
pursuant to the regulations in this
subpart, the U.S. citizen (as defined by
§ 216.103 of this chapter) conducting
the activity identified in § 216.170(c)
(the U.S. Navy) must apply for and
obtain either an initial Letter of
Authorization in accordance with
§ 216.177 or a renewal under § 216.178.
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§ 216.177
Letters of Authorization.
(a) A Letter of Authorization, unless
suspended or revoked, will be valid for
a period of time not to exceed the period
of validity of this subpart, but must be
renewed annually subject to annual
renewal conditions in § 216.178.
(b) Each Letter of Authorization will
set forth:
(1) Permissible methods of incidental
taking;
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(2) Means of effecting the least
practicable adverse impact on the
species, its habitat, and on the
availability of the species for
subsistence uses (i.e., mitigation); and
(3) Requirements for mitigation,
monitoring and reporting.
(c) Issuance and renewal of the Letter
of Authorization will be based on a
determination that the total number of
marine mammals taken by the activity
as a whole will have no more than a
negligible impact on the affected species
or stock of marine mammal(s).
§ 216.178 Renewal of Letters of
Authorization.
(a) A Letter of Authorization issued
under §§ 216.106 and 216.177 for the
activity identified in § 216.170(c) will be
renewed annually upon:
(1) Notification to NMFS that the
activity described in the application
submitted under § 216.176 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;
(2) Timely receipt (by the dates
indicated in these regulations) of the
monitoring reports required under
§ 216.175(c) through (j); and
(3) A determination by the NMFS that
the mitigation, monitoring and reporting
measures required under § 216.174 and
the Letter of Authorization issued under
§§ 216.106 and 216.177, 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
this § 216.106 and § 216.178 indicates
that a substantial modification, as
determined by NMFS, to the described
work, mitigation or monitoring
undertaken during the upcoming season
will occur, the NMFS will provide the
public a period of 30 days for review
and comment on the request. Review
and comment on renewals of Letters of
Authorization are restricted to:
(1) New cited information and data
indicating that the determinations made
in this document are in need of
reconsideration, and
(2) Proposed changes to the mitigation
and monitoring requirements contained
in these regulations or in the current
Letter of Authorization.
(c) A notice of issuance or denial of
a renewal of a Letter of Authorization
will be published in the Federal
Register.
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1491
(d) NMFS, in response to new
information and in consultation with
the Navy, may modify the mitigation or
monitoring measures in subsequent
LOAs if doing so creates a reasonable
likelihood of more effectively
accomplishing the goals of mitigation
and monitoring. 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 HRC or other locations).
(2) Findings of the Monitoring
Workshop that the Navy will convene in
2011 (§ 216.175(q)).
(3) Compiled results of Navy funded
research and development (R&D) studies
(presented pursuant to the ICMP
(§ 216.175(d)).
(4) Results from specific stranding
investigations (either from the HRC
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. (6) Results from
general marine mammal and sound
research (funded by the Navy (or
otherwise).
§ 216.179 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 216.177 and
subject to the provisions of this subpart
shall be made until after notification
and an opportunity for public comment
has been provided. For purposes of this
paragraph, a renewal of a Letter of
Authorization under § 216.178, 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 § 216.172(c), a
Letter of Authorization issued pursuant
to §§ 216.106 and 216.177 may be
substantively modified without prior
notification and an opportunity for
public comment. Notification will be
published in the Federal Register
within 30 days subsequent to the action.
[FR Doc. E9–37 Filed 1–5–09; 4:15 pm]
BILLING CODE 3510–22–P
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Agencies
[Federal Register Volume 74, Number 7 (Monday, January 12, 2009)]
[Rules and Regulations]
[Pages 1456-1491]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-37]
[[Page 1455]]
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Part III
Department of Commerce
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National Oceanic and Atmospheric Administration
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50 CFR Part 216
Taking and Importing Marine Mammals; U.S. Navy Training in the Hawaii
Range Complex; Final Rule
Federal Register / Vol. 74, No. 7 / Monday, January 12, 2009 / Rules
and Regulations
[[Page 1456]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 216
[Docket No. 080519680-81530-02]
RIN 0648-AW86
Taking and Importing Marine Mammals; U.S. Navy Training in the
Hawaii 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 training activities conducted within the Hawaii Range
Complex (HRC) for the period of January 2009 through January 2014. The
Navy's training activities are considered military readiness activities
pursuant to the Marine Mammal Protection Act (MMPA), as amended by the
National Defense Authorization Act of 2004 (NDAA). These regulations,
which allow for the issuance of ``Letters of Authorization'' (LOAs) for
the incidental take of marine mammals during the described activities
and specified timeframes, prescribe the permissible methods of taking
and other means of affecting the least practicable adverse impact on
marine mammal species and their habitat, as well as requirements
pertaining to the monitoring and reporting of such taking.
DATES: Effective January 5, 2009 through January 5, 2014.
ADDRESSES: A copy of the Navy's application, which contains a list of
the references used in this document, NMFS' Record of Decision (ROD),
and other documents cited herein, may be obtained by writing to Michael
Payne, Chief, Permits, Conservation and Education Division, Office of
Protected Resources, National Marine Fisheries Service, 1315 East-West
Highway, Silver Spring, MD 20910-3225 or by telephone via the contact
listed here.
FOR FURTHER INFORMATION CONTACT: Jolie Harrison, Office of Protected
Resources, NMFS, (301) 713-2289, ext. 166.
SUPPLEMENTARY INFORMATION: Extensive supplementary information was
provided in the proposed rule for this activity, which was published in
the Federal Register on Monday, June 23, 2008 (73 FR 35510). This
information will not be reprinted here in its entirety; rather, all
sections from the proposed rule will be represented herein and will
contain either a summary of the material presented in the proposed rule
or a note referencing the page(s) in the proposed rule where the
information may be found. Any information that has changed since the
proposed rule was published will be addressed herein. Additionally,
this final rule contains a section that responds to the comments
received during the public comment period.
Background
Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.)
direct the Secretary of Commerce (Secretary) to allow, upon request,
the incidental, but not intentional taking of marine mammals by U.S.
citizens who engage in a specified activity (other than commercial
fishing) during periods of not more than five consecutive years each if
certain findings are made and regulations are issued or, if the taking
is limited to harassment and of no more than 1 year, the Secretary
shall issue a notice of proposed authorization for public review.
Authorization shall be granted if NMFS finds that the taking will
have a negligible impact on the species or stock(s), will not have an
unmitigable adverse impact on the availability of the species or
stock(s) for subsistence uses, and if the permissible methods of taking
and requirements pertaining to the mitigation, monitoring and reporting
of such taking are set forth.
NMFS has defined ``negligible impact'' in 50 CFR 216.103 as:
an impact resulting from the specified activity that cannot be
reasonably expected to, and is not reasonably likely to, adversely
affect the species or stock through effects on annual rates of
recruitment or survival.
The NDAA (Pub. L. 108-136) removed the ``small numbers'' and
``specified geographical region'' limitations and amended the
definition of ``harassment'' as it applies to a ``military readiness
activity'' to read as follows (Section 3(18)(B) of the MMPA):
(i) Any act that injures or has the significant potential to
injure a marine mammal or marine mammal stock in the wild [Level A
Harassment]; or
(ii) any act that disturbs or is likely to disturb a marine
mammal or marine mammal stock in the wild by causing disruption of
natural behavioral patterns, including, but not limited to,
migration, surfacing, nursing, breeding, feeding, or sheltering, to
a point where such behavioral patterns are abandoned or
significantly altered [Level B Harassment].
Summary of Request
On June 25, 2007, NMFS received an application from the Navy
requesting authorization for the take of 24 species of marine mammals
incidental to upcoming Navy training activities to be conducted within
the HRC, which covers 235,000 nm\2\ around the Main Hawaiian Islands
(see map on page 17 of the application), over the course of 5 years.
These training activities are classified as military readiness
activities. These training activities may incidentally take marine
mammals present within the HRC by exposing them to sound from mid-
frequency or high frequency active sonar (MFAS/HFAS) or to underwater
detonations at levels that NMFS associates with the take of marine
mammals. The Navy requested authorization to take individuals of 24
species of marine mammals by Level B Harassment. Further, though they
do not anticipate it to occur, the Navy requested authorization to
take, by injury or mortality, up to 10 individuals each of 10 species
over the course of the 5-year period (bottlenose dolphin, Kogia spp.,
melon-headed whale, pantropical spotted dolphin, pygmy killer whale,
short-finned pilot whale, striped dolphin, and Cuvier's, Longman's, and
Blainville's beaked whale).
Background of Navy Request
The proposed rule contains a description of the Navy's mission,
their responsibilities pursuant to Title 10 of the United States Code,
and the specific purpose and need for the activities for which they
requested incidental take authorization. The description contained in
the proposed rule has not changed (73 FR 35510).
Description of the Specified Activities
The proposed rule contains a complete description of the Navy's
specified activities that are covered by these final regulations, and
for which the associated incidental take of marine mammals will be
authorized in the related LOAs. The proposed rule describes the nature
of the training exercises involving both mid- and high-frequency active
sonar (MFAS and HFAS) and explosive detonations, as well as the MFAS
and HFAS sound sources and explosive types. See 73 FR 35510, page
35512. The narrative description of the action contained in the
proposed rule has not changed except for two corrections and one
clarification, noted in the paragraph below. Tables 1-3 summarize and
quantify the sonar exercise types, sonar sources, and explosive
exercise types
[[Page 1457]]
used in these training exercises and contain minor corrections (from
the proposed rule) that did not affect NMFS' analysis of the proposed
action.
The last paragraph of the Mine Neutralization section of the
proposed rule contained an error. For the final rule, the sentence
beginning ``Standard practices for tethered mines * * *'' should be
replaced with the following sentence: ``Standard practice for tethered
mines is to tie off the explosive counter charge as closely as possible
to the mine case.'' In the proposed rule, Table 5 (which is Table 3 in
this final rule) mistakenly indicated that IEER exercises would only
occur in the summer months. In fact, IEER use in the winter months is
typically rare and infrequent due to the required mitigation measures,
but exercises may be planned for winter and NMFS and the Navy's
analyses accounted for this fact. Table 3 includes the correction here.
These two modifications are non-substantive and do not affect NMFS'
determinations.
Last, Table 1 (in this final rule) indicates that RIMPAC exercises
only occur in the summer (when humpback whales are not present) of
every other year, which is accurate. Table 2 shows that the Navy plans
to conduct the same number of sonar hours in each year. The needed
clarification (to ensure no unanticipated humpback whale take occurs)
follows: In the years without RIMPAC, the sonar hours conducted will be
seasonally and spatially distributed such that no additional exposures
of humpback whales to MFAS/HFAS would occur beyond those used to
estimate take in the years with a RIMPAC. In a simple example, in a
non-RIMPAC year, the Navy could choose to conduct the RIMPAC-sized lump
of sonar hours either in the summer when humpbacks are not present, or
in the winter but farther out to sea where their activities would not
expose humpbacks to MFAS/HFAS, or some combination of those two. This
clarification does not affect NMFS' determinations.
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[[Page 1458]]
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Description of Marine Mammals in the Area of the Specified Activities
There are 27 marine mammal species with possible or confirmed
occurrence in the HRC. Seven marine mammal species listed as federally
endangered under the Endangered Species Act (ESA) occur in the HRC: The
humpback whale, North Pacific right whale, sei whale, fin whale, blue
whale, sperm whale, and Hawaiian monk seal. The most abundant marine
mammals appear to be dwarf sperm whales, striped dolphins, and Fraser's
dolphins. The most abundant large whales are sperm whales. Table 4
provides the estimated abundance, estimated group size, and estimated
probability of detection (based on Barlow 2006) of the marine mammal
species that occur in the HRC.
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The Navy has compiled information on the abundance, behavior,
status and distribution, and vocalizations of marine mammal species in
the Hawaiian waters from peer reviewed literature, the Navy Marine
Resource Assessment, NMFS Stock Assessment Reports, and marine mammal
surveys using acoustics or visual observations from aircraft or ships.
This information may be viewed in the Navy's LOA application and/or the
Navy's FEIS for the HRC (see FOR FURTHER INFORMATION). Additional
information is available in NMFS Stock Assessment Reports, which may be
viewed at: https://www.nmfs.noaa.gov/pr/sars/species.htm. As indicated
in the proposed rule, based on their rare occurrence in the HRC, the
Navy and NMFS do not anticipate any effects to Blue whales, North
Pacific right whales, or Northern elephant seals and, therefore, they
are not addressed further in this document.
Because the consideration of areas where marine mammals are known
to selectively breed or calve are important to both the negligible
impact finding necessary for the issuance of an MMPA
[[Page 1460]]
authorization and the need for NMFS to put forth the means of affecting
the least practicable adverse impact paying particular attention to
rookeries, mating grounds, and other areas of similar significance, the
proposed rule contains a description of important reproductive areas,
with a special focus on humpback whales (73 FR 35510, page 35519). That
section includes a figure that generally illustrates humpback whale
survey data collected between 1993 and 2003 and indicates areas of high
and low density. The description contained in the proposed rule has not
changed.
A Brief Background on Sound
The proposed rule contains a section that provides a brief
background on the principles of sound that are frequently referred to
in this rulemaking (73 FR 35510, pages 35521-35522). This section also
includes a discussion of the functional hearing ranges of the different
groups of marine mammals (by frequency) as well as a discussion of the
two main sound metrics used in NMFS analysis (sound pressure level
(SPL) and sound energy level (SEL)). The information contained in the
proposed rule has not changed.
Potential Effects of Specified Activities on Marine Mammals
With respect to the MMPA, NMFS' effects assessment serves four
primary purposes: (1) To prescribe the permissible methods of taking
(i.e., Level B Harassment (behavioral harassment), Level A Harassment
(injury), or mortality, including an identification of the number and
types of take that could occur by Level A or B harassment or mortality)
and to prescribe other means of affecting the least practicable adverse
impact on such species or stock and its habitat (i.e., mitigation); (2)
to determine whether the specified activity will have a negligible
impact on the affected species or stocks of marine mammals (based on
the likelihood that the activity will adversely affect the species or
stock through effects on annual rates of recruitment or survival); (3)
to determine whether the specified activity will have an unmitigable
adverse impact on the availability of the species or stock(s) for
subsistence uses (however, there are no subsistence communities that
would be affected in the HRC, so this determination is inapplicable for
the HRC); 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); 73 FR 35510, pages 35522-35534. 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); 73 FR 35510,
pages 35529-35534. The information contained in Potential Effects of
Specified Activities on Marine Mammals Section from the proposed rule
has not changed, except for one correction noted below.
The proposed rule contained an error in the Potential Effects of
Specified Activities on Marine Mammals Section (73 FR 35510, page
35534). The statement ``A surface duct may be present * * *'' should be
replaced with the following statement: ``Surface ducts are present
approximately 53 percent of the time.'' Note that the Navy's model for
estimating effects on marine mammals incorporates the likelihood of
strong surface ducts in the HRC (pers. comm. J. Hibbard to J. Harrison,
2007) and the exposure estimates it produces reflect this.
Later, in the Estimated Take of Marine Mammals Section, NMFS
relates the potential effects to marine mammals from MFAS/HFAS and
underwater detonation of explosives discussed here to the MMPA
regulatory definitions of Level A and Level B Harassment, and
mortality, and quantifies those effects.
Mitigation
In order to issue an incidental take authorization (ITA) under
section 101(a)(5)(A) of the MMPA, NMFS must prescribe regulations
setting forth the ``permissible methods of taking pursuant to such
activity, and other means of affecting the least practicable adverse
impact on such species or stock and its habitat, paying particular
attention to rookeries, mating grounds, and areas of similar
significance.'' The National Defense Authorization Act (NDAA) of 2004
amended the MMPA as it relates to military readiness activities and the
incidental take authorization process such that ``least practicable
adverse impact'' shall include consideration of personnel safety,
practicality of implementation, and impact on the effectiveness of the
``military readiness activity''. The HRC training activities described
in the proposed rule are considered military readiness activities.
NMFS reviewed the Navy's proposed HRC activities and the proposed
HRC mitigation measures (which the Navy refers to as Protective
Measures) presented in the Navy's application to determine whether the
activities and mitigation measures were capable of achieving the least
practicable adverse effect on marine mammals. NMFS determined that
further discussion was necessary regarding: (1) Humpback whales
congregating in the winter in the shallow areas of the HRC in high
densities to calve and breed; and (2) the potential relationship
between the operation of MFAS/HFAS and marine mammal strandings.
Any mitigation measure prescribed by NMFS should be known to
accomplish, have a reasonable likelihood of accomplishing (based on
current science), or contribute to the accomplishment of one or more of
the general goals listed below:
(a) Avoidance or minimization of injury or death of marine mammals
wherever possible (goals b, c, and d may contribute to this goal).
(b) A reduction in the numbers of marine mammals (total number or
number at biologically important time or location) exposed to received
levels of MFAS/HFAS, underwater detonations, or other activities
expected to result in the take of marine mammals (this goal may
contribute to a, above, or to reducing harassment takes only).
(c) A reduction in the number of times (total number or number at
biologically important time or location) individuals would be exposed
to received levels of MFAS/HFAS, underwater detonations, or other
activities expected to result in the take of marine mammals (this goal
may contribute to a, above, or to reducing harassment takes only).
(d) A reduction in the intensity of exposures (either total number
or number at biologically important time or location) to received
levels of MFAS/HFAS, underwater detonations, or other activities
expected to result in the take of marine mammals (this goal may
contribute to a, above, or to reducing the severity of harassment takes
only).
(e) A reduction in adverse effects to marine mammal habitat, paying
special attention to the food base, activities that block or limit
passage to or from biologically important areas, permanent destruction
of habitat, or temporary destruction/disturbance of habitat during a
biologically important time.
[[Page 1461]]
(f) For monitoring directly related to mitigation--an increase in
the probability of detecting marine mammals, thus allowing for more
effective implementation of the mitigation (shut-down zone, etc.).
NMFS worked with the Navy to identify additional practicable and
effective mitigation measures, which included a careful balancing of
the likely benefit of any particular measure to the marine mammals with
the likely effect of that measure on personnel safety, practicality of
implementation, and impact on the ``military-readiness activity''. NMFS
and the Navy developed two additional mitigation measures that address
the concerns mentioned above, including a humpback whale cautionary
area and a Stranding Response Plan.
The Navy's proposed mitigation measures, as well as the humpback
whale cautionary area and the Stranding Response Plan, both of which
are required under these regulations, were described in detail in the
proposed rule (73 FR 35510, pages 35535-35541). The Navy's measures
address personnel training, lookout and watchstander responsibilities,
and operating procedures for training activities using both MFAS/HFAS
and explosive detonations. No changes have been made to the mitigation
measures described in the proposed rule, with one correction and one
addition, addressed in the next paragraph. The final HRC Stranding
Response Plan, which includes a shutdown protocol, a stranding
investigation plan, and a requirement for Navy and NMFS to implement an
MOA that will establish a framework whereby the Navy can (and provide
the Navy examples of how they can best) assist NMFS with stranding
investigations in certain circumstances, may be viewed at: https://
www.nmfs.noaa.gov/pr/permits/incidental.htm#applications. Additionally,
the mitigation measures are included in full in the codified text of
the regulations.
The proposed rule contained a measure in which the Navy indicated
that ``prior to conducting the exercise, remotely sensed sea surface
temperature maps would be reviewed. SINKEX and air to surface missile
(ASM) Training activities would not be conducted within areas where
strong temperature discontinuities are present, thereby indicating the
existence of oceanographic fronts'' (73 FR 35510, page 35537). The Navy
included this measure in the LOA application in error. The removal of
the measure does not change NMFS' analysis and therefore the measure is
not included in the final rule. Additionally, the following measure has
been added to the regulations: Night vision goggles shall be available
to all ships and air crews for use as appropriate.
NMFS has determined that the Navy's proposed mitigation measures
(from the LOA application), along with the Humpback Whale Cautionary
Area and the Stranding Response Plan (and when the Adaptive Management
(see Adaptive Management below) component is taken into consideration)
are adequate means of effecting the least practicable adverse impacts
on marine mammal species or stocks and their habitat, paying particular
attention to rookeries, mating grounds, and areas of similar
significance, while also considering personnel safety, practicality of
implementation, and impact on the effectiveness of the military
readiness activity. The justification for this conclusion is discussed
in the Mitigation Conclusion section of the proposed rule (73 FR 35510,
pages 35540-35541). The Mitigation Conclusion Section of the proposed
rule has not changed.
Research and Conservation Measures for Marine Mammals
The Navy provides a significant amount of funding and support for
marine research. The Navy provided $26 million in Fiscal Year 2008 and
plans for $22 million in Fiscal Year 2009 to universities, research
institutions, federal laboratories, private companies, and independent
researchers around the world to study marine mammals. Over the past
five years the Navy has funded over $100 million in marine mammal
research. The U.S. Navy sponsors seventy percent of all U.S. research
concerning the effects of human-generated sound on marine mammals and
50 percent of such research conducted worldwide. Major topics of Navy-
supported research include the following:
Better understanding of marine species distribution and
important habitat areas,
Developing methods to detect and monitor marine species
before and during training,
Understanding the effects of sound on marine mammals, sea
turtles, fish, and birds, and
Developing tools to model and estimate potential effects
of sound.
The Navy's Office of Naval Research currently coordinates six
programs that examine the marine environment and are devoted solely to
studying the effects of noise and/or the implementation of technology
tools that will assist the Navy in studying and tracking marine
mammals. The six programs are as follows:
Environmental Consequences of Underwater Sound,
Non-Auditory Biological Effects of Sound on Marine
Mammals,
Effects of Sound on the Marine Environment,
Sensors and Models for Marine Environmental Monitoring,
Effects of Sound on Hearing of Marine Animals, and
Passive Acoustic Detection, Classification, and Tracking
of Marine Mammals.
The Navy has also developed the technical reports referenced within
this document and the HRC EIS, such as the Marine Resource Assessments.
Furthermore, research cruises by NMFS and by academic institutions have
received funding from the U.S. Navy.
The Navy has sponsored several workshops to evaluate the current
state of knowledge and potential for future acoustic monitoring of
marine mammals. The workshops brought together acoustic experts and
marine biologists from the Navy and other research organizations to
present data and information on current acoustic monitoring research
efforts and to evaluate the potential for incorporating similar
technology and methods on instrumented ranges. However, acoustic
detection, identification, localization, and tracking of individual
animals still requires a significant amount of research effort to be
considered a reliable method for marine mammal monitoring. The Navy
supports research efforts on acoustic monitoring and will continue to
investigate the feasibility of passive acoustics as a potential
mitigation and monitoring tool.
Overall, the Navy will continue to fund ongoing marine mammal
research, and is planning to coordinate long term monitoring/studies of
marine mammals on various established ranges and operating areas. The
Navy will continue to research and contribute to university/external
research to improve the state of the science regarding marine species
biology and acoustic effects. These efforts include mitigation and
monitoring programs; data sharing with NMFS and via the literature for
research and development efforts; and future research as described
previously.
Long-Term Prospective Study
Apart from this final rule, NMFS, with input and assistance from
the Navy and several other agencies and entities, will perform a
longitudinal observational study of marine mammal strandings to
systematically observe and record the types of pathologies and
[[Page 1462]]
diseases and investigate the relationship with potential causal factors
(e.g., sonar, seismic, weather). The proposed rule contained an outline
of the proposed study (73 FR 35510, pages 35541-35542). No changes have
been made to the longitudinal study as described in the proposed rule.
Monitoring
In order to issue an ITA for an activity, section 101(a)(5)(A) of
the MMPA states that NMFS must set forth ``requirements pertaining to
the monitoring and reporting of such taking''. The MMPA implementing
regulations at 50 CFR 216.104 (a)(13) indicate that requests for LOAs
must include the suggested means of accomplishing the necessary
monitoring and reporting that will result in increased knowledge of the
species and of the level of taking or impacts on populations of marine
mammals that are expected to be present.
Monitoring measures prescribed by NMFS should accomplish one or
more of the following general goals:
(a) An increase in the probability of detecting marine mammals,
both within the safety zone (thus allowing for more effective
implementation of the mitigation) and in general to generate more data
to contribute to the effects analyses.
(b) An increase in our understanding of how many marine mammals are
likely to be exposed to levels of MFAS/HFAS (or explosives or other
stimuli) that we associate with specific adverse effects, such as
behavioral harassment, TTS, or PTS.
(c) An increase in our understanding of how marine mammals respond
(behaviorally or physiologically) to MFAS/HFAS (at specific received
levels), explosives, or other stimuli expected to result in take and
how anticipated adverse effects on individuals (in different ways and
to varying degrees) may impact the population, species, or stock
(specifically through effects on annual rates of recruitment or
survival)
(d) An increased knowledge of the affected species.
(e) An increase in our understanding of the effectiveness of
certain mitigation and monitoring measures.
(f) A better understanding and record of the manner in which the
authorized entity complies with the incidental take authorization.
Proposed Monitoring Plan for the HRC
As NMFS indicated in the proposed rule, the Navy has (with input
from NMFS) fleshed out the details of and made improvements to the HRC
Monitoring Plan. Additionally, NMFS and the Navy have incorporated a
recommendation from the public, which recommended the Navy hold a
workshop to discuss the Navy's Monitoring Plan (see Monitoring Workshop
section). The final HRC Monitoring Plan, which is summarized below, may
be viewed at https://www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications.
The draft Monitoring Plan for the HRC has been designed as a
collection of focused ``studies'' (described fully in the HRC
Monitoring Plan) to gather data that will allow the Navy to address the
following questions:
(a) Are marine mammals exposed to mid-frequency active sonar
(MFAS), especially at levels associated with adverse effects (i.e.,
based on NMFS' criteria for behavioral harassment, TTS, or PTS)? If so,
at what levels are they exposed?
(b) If marine mammals are exposed to MFAS in the HRC, do they
redistribute geographically within the HRC as a result of continued
exposure? If so, how long does the redistribution last?
(c) If marine mammals are exposed to MFAS, what are their
behavioral responses to various 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 and
explosives (e.g., PMAP, major exercise measures agreed to by the Navy
through permitting) effective at avoiding TTS, injury, and mortality of
marine mammals?
Data gathered in these studies will be collected by qualified,
professional marine mammal biologists that are experts in their field.
They will use a combination of the following methods to collect data:
Visual Surveys--Vessel, Aerial and Shore-based.
Passive Acoustic Monitoring (PAM).
Marine Mammal observers (MMOs) on Navy Vessels.
Marine Mammal Tagging.
In the five proposed study designs (all of which cover multiple
years), the above methods will be used separately or in combination to
monitor marine mammals in different combinations before, during, and
after training activities utilizing MFAS/HFAS or explosive detonations.
Table 5 contains a summary of the Monitoring effort that is planned for
each study in each year (effort may vary slightly between years or
study type, but overall effort will remain constant). The HRC
Monitoring Plan is designed to collect data on all marine mammals and
sea turtles encountered during monitoring studies. However, priority
will be given to ESA-listed species and taxa in which MFAS exposure and
strandings have been linked under certain circumstances. Because of the
important reproductive area and the fact that humpback whales are
present in very high densities in certain areas of the HRC, the Navy
plans to dedicate a designated subset of their monitoring effort
specifically to these high-density areas.
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Monitoring Workshop
During the public comment period on the proposed rule for the HRC,
NMFS received a comment which, in consultation with the Navy, we have
chosen to incorporate into the final rule (in a modified form). One
commenter recommended that a workshop or panel be convened to solicit
input on the monitoring plan from researchers, experts, and other
interested parties. The HRC proposed rule included an adaptive
management component and both NMFS and the Navy believe that a workshop
would provide a means for Navy and NMFS to consider input from
participants in determining whether or how to modify monitoring
techniques to more effectively accomplish the goals of monitoring set
forth earlier in the document. NMFS and the Navy believe that this
workshop concept is valuable in relation to all of the Range Complexes
and major training exercise LOAs that NMFS is working on with the Navy
at this time, and consequently this single Monitoring Workshop will be
included as a component of all of the LOAs that NMFS will be processing
for the Navy in the next year or so.
The Navy, with guidance and support from NMFS, will convene a
Monitoring Workshop, including marine mammal and acoustic experts as
well as other interested parties, in 2011. The Monitoring Workshop
participants will review the monitoring results from the previous two
years of monitoring pursuant to the HRC rule as well as monitoring
results from other Navy rules issued after HRC (e.g., the Atlantic
[[Page 1464]]
Fleet Active Sonar Training, Southern California Range Complex, and
other rules). The Monitoring Workshop participants would provide their
individual recommendations to the Navy and NMFS on the monitoring
plan(s) after also considering the current science (including Navy R&D
developments) 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.
Integrated Comprehensive Monitoring Plan
In addition to the Monitoring Plan for the HRC, the Navy will
complete an Integrated Comprehensive Monitoring Program (ICMP) Plan by
the end of 2009. The ICMP will provide the overarching coordination
that will support compilation of data from range-specific monitoring
plans (e.g., HRC Range Complex plan) as well as Navy funded research
and development (R&D) studies. The ICMP will coordinate the monitoring
programs progress towards meeting its goals and develop a data
management plan. The ICMP will be evaluated annually to provide a
matrix for progress and goals for the following year, and will make
recommendations on adaptive management for refinement and analysis of
the monitoring methods.
The primary objectives of the ICMP are to:
Monitor and assess the effects of Navy activities on
protected species;
Ensure that data collected at multiple locations is
collected in a manner that allows comparison between and among
different geographic locations;
Assess the efficacy and practicality of the monitoring and
mitigation techniques;
Add to the overall knowledge-base of marine species and
the effects of Navy activities on marine species.
The ICMP will be used both as: (1) A planning tool to focus Navy
monitoring priorities (pursuant to ESA/MMPA requirements) across Navy
Range Complexes and Exercises; and (2) an adaptive management tool,
through the consolidation and analysis of the Navy's monitoring and
watchstander data, as well as new information from other Navy programs
(e.g., R&D), and other appropriate newly published information.
In combination with the 2011 Monitoring Workshop and the adaptive
management component of the HRC rule and the other planned Navy rules
(e.g. AFAST and SOCAL), the ICMP could potentially provide a framework
for restructuring the monitoring plans and allocating monitoring effort
based on the value of particular specific monitoring proposals (in
terms of the degree to which results would likely contribute to stated
monitoring goals, as well as the likely technical success of the
monitoring based on a review of past monitoring results) that have been
developed through the ICMP framework, instead of allocating based on
maintaining an equal (or commensurate to effects) distribution of
monitoring effort across Range complexes. For example, if careful
prioritization and planning through the ICMP (which would include a
review of both past monitoring results and current scientific
developments) were to show that a large, intense monitoring effort in
Hawaii would likely provide extensive, robust and much-needed data that
could be used to understand the effects of sonar throughout different
geographical areas, it may be appropriate to have other Range Complexes
dedicate money, resources, or staff to the specific monitoring proposal
identified as ``high priority'' by the Navy and NMFS, in lieu of
focusing on smaller, lower priority projects divided throughout their
home Range Complexes.
The ICMP will identify:
A means by which NMFS and the Navy would jointly consider
prior years' monitoring results and advancing science to determine if
modifications are needed in mitigation or monitoring measures to better
effect the goals laid out in the Mitigation and Monitoring sections of
the HRC rule.
Guidelines for prioritizing monitoring projects.
If, as a result of the workshop and similar to the example
described in the paragraph above, the Navy and NMFS decide it is
appropriate to restructure the monitoring plans for multiple ranges
such that they are no longer evenly allocated (by Range Complex), but
rather focused on priority monitoring projects that are not necessarily
tied to the geographic area addressed in the rule, the ICMP will be
modified to include a very clear and unclassified recordkeeping system
that will allow NMFS and the public to see how each Range Complex/
project is contributing to all of the ongoing monitoring (resources,
effort, money, etc.).
Past Monitoring in the HRC
The proposed rule contained a detailed review of the previous
marine mammal monitoring conducted in the HRC, which was conducted in
compliance with the terms and conditions of multiple biological
opinions issued for MFAS training activities (73 FR 35510, pages 35544-
35548). No changes have been made to the discussion contained in the
proposed rule.
Adaptive Management
The final regulations governing the take of marine mammals
incidental to Navy training exercises in the HRC will contain an
adaptive management component. Our understanding of the effects of
MFAS/HFAS and explosives on marine mammals is still in its relative
infancy, and yet the science in this field continues to improve. These
circumstances make the inclusion of an adaptive management component
both valuable and necessary within the context of 5-year regulations
for activities that have been associated with marine mammal mortality
in certain circumstances and locations (though not the HRC). The use of
adaptive management will give NMFS the ability to consider new data
from different sources to determine (in coordination with the Navy) on
an annual basis if mitigation or monitoring measures should be modified
or added (or deleted) if new data suggests that such modifications are
appropriate (or are not appropriate) for subsequent annual LOAs.
Following are some of the possible sources of applicable data:
Results from the Navy's monitoring from the previous year
(either from the HRC or other locations).
Findings of the Workshop that the Navy will convene in
2011 to analyze monitoring results to date, review current science, and
recommend modifications, as appropriate to the monitoring protocols to
increase monitoring effectiveness.
Compiled results of Navy funded research and development
(R&D) studies (presented pursuant to the ICMP, which is discussed
elsewhere in this document).
Results from specific stranding investigations (either
from the HRC or other locations, and involving coincident MFAS/HFAS or
explosives training or not involving coincident use).
Results from the Long Term Prospective Study described
below.
Results from general marine mammal and sound research
(funded by
[[Page 1465]]
the Navy (described below) or otherwise).
Mitigation measures could be modified or added (or deleted) if new
data suggest that such modifications would have (or do not have) a
reasonable likelihood of accomplishing the goals of mitigation laid out
in this final rule and if the measures are practicable. NMFS would also
coordinate with the Navy to modify or add to (or delete) the existing
monitoring requirements if the new data suggest that the addition of
(or deletion of) a particular measure would more effectively accomplish
the goals of monitoring laid out in this final rule. The reporting
requirements associated with this rule are designed to provide 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 to
discuss the monitoring reports, Navy R&D developments, and current
science and whether mitigation or monitoring modifications are
appropriate.
Reporting
In order to issue an ITA for an activity, section 101(a)(5)(A) of
the MMPA states that NMFS must set forth ``requirements pertaining to
the monitoring and reporting of such taking''. Effective reporting is
critical to ensure compliance with the terms and conditions of an LOA,
and to provide NMFS and the Navy with data of the highest quality based
on the required monitoring.
As NMFS noted in its proposed rule, additional detail has been
added to the reporting requirements since they were outlined in the
proposed rule. The updated reporting requirements are all included
below. A subset of the information provided in the monitoring reports
may be classified and not releasable to the public.
NMFS will work with the Navy to develop tables that allow for
efficient submission of the information required below.
General Notification of Injured or Dead Marine Mammals
Navy personnel will ensure that NMFS (regional stranding
coordinator) is notified immediately (or as soon as operational
security allows) if an injured or dead marine mammal is found during or
shortly after, and in the vicinity of, any Navy training exercise
utilizing MFAS, HFAS, or underwater explosive detonations. The Navy
will provide NMFS with species or description of the animal(s), the
condition of the animal(s) (including carcass condition if the animal
is dead), location, time of first discovery, observed behaviors (if
alive), and photo or video (if available). The Stranding Response Plan
contains more specific reporting requirements for specific
circumstances.
Annual HRC Monitoring Plan Report
The Navy shall submit a report annually on October 1 describing the
implementation and results (through August 1 of the same year) of the
HRC Monitoring Plan, described above. Data collection methods will be
standardized across range complexes to allow for comparison in
different geographic locations. Although additional information will
also be gathered, the marine mammal observers (MMOs) collecting marine
mammal data pursuant to the HRC Monitoring Plan shall, at a minimum,
provide the same marine mammal observation data required in the MFAS/
HFAS major Training Exercises section of the Annual HRC Exercise Report
referenced below.
The HRC Monitoring Plan Report may be provided to NMFS within a
larger report that includes the required Monitoring Plan Reports from
multiple Range Complexes.
Annual HRC Exercise Report
The Navy will submit an Annual HRC Exercise Report on October 1 of
every year (covering data gathered through August 1 (or completion of
RIMPAC if later than Aug 1)). This report shall contain the subsections
and information indicated below.
MFAS/HFAS Major Training Exercises
This section shall contain the following information for Major
Training Exercises (MTEs, which include RIMPAC, USWEX, and Multi Strike
Group) conducted in the HRC:
(a) Exercise Information (for each MTE):
(i) Exercise designator.
(ii) Date that exercise began and ended.
(iii) Location.
(iv) Number and types of active sources used in the exercise.
(v) Number and types of passive acoustic sources used in exercise.
(vi) Number and types of vessels, aircraft, etc., participating in
exercise.
(vii) Total hours of observation by watchstanders.
(viii) Total hours of all active sonar source operation.
(ix) Total hours of each active sonar source (along with
explanation of how hours are calculated for sources typically
quantified in alternate way (buoys, torpedoes, etc.)).
(x) Wave height (high, low, and average during exercise).
(b) Individual marine mammal sighting info (for each sighting in
each MTE).
(i) Location of sighting.
(ii) Species (if not possible--indication of whale/dolphin/
pinniped).
(iii) Number of individuals.
(iv) Calves observed (y/n).
(v) Initial Detection Sensor.
(vi) Indication of specific type of platform observation made from
(including, for example, what type of surface vessel, i.e., FFG, DDG,
or CG)
(vii) Length of time observers maintained visual contact with
marine mammal(s).
(viii) Wave height (in feet).
(ix) Visibility.
(x) Sonar source in use (y/n).
(xi) Indication of whether animal is <200yd, 200-500yd, 500-1000yd,
1000-2000yd, or >2000yd from sonar source in (x) above.
(xiii) Mitigation Implementation--Whether operation of sonar sensor
was delayed, or sonar was powered or shut down, and how long the delay
was.
(xiv) If source in use (x) is hullmounted, true bearing of animal
from ship, true direction of ship's travel, and estimation of animal's
motion relative to ship (opening, closing, parallel)
(xv) Observed behavior--Watchstanders shall report, in plain
language and without trying to categorize in any way, the observed
behavior of the animals (such as animal closing to bow ride,
paralleling course/speed, floating on surface and not swimming, etc.)
(c) An evaluation (based on data gathered during all of the MTEs)
of the effectiveness of mitigation measures designed to avoid exposing
marine mammals to mid-frequency sonar. This evaluation shall identify
the specific observations that support any conclusions the Navy reaches
about the effectiveness of the mitigation.
ASW Summary
This section shall include the following information as summarized
from both MTEs and non-major training exercises (unit-level exercises,
such as TRACKEXs):
(i) Total annual hours of each type of sonar source (along with
explanation of how hours are calculated for sources typically
quantified in alternate way (buoys, torpedoes, etc.))
(ii) Total hours (from December 15 through April 15) of hullmounted
active sonar operation occurring in the dense humpback areas generally
shown on the Mobley map (73 FR 35510, page 35520)
[[Page 1466]]
plus a 5-km buffer, but not including the Pacific Missile Range
Facility. NMFS and the Navy will work together to develop the exact
boundaries of this area.
(iii) Total estimated annual hours of hull-mounted active sonar
operation conducted in Humpback Whale Cautionary area between December
15 and April 15.
(iv) Cumulative Impact Report--To the extent practicable, the Navy,
in coordination with NMFS, shall develop and implement a method of
annually reporting non-major (i.e., other than RIMPAC, USWEX, or Multi-
Strike Group Exercises) training exercises utilizing hull-mounted
sonar. The report shall present an annual (and seasonal, where
practicable) depiction of non-major training exercises geographically
across the HRC. The Navy shall include (in the HRC 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.
SINKEXs
This section shall include the following information for each
SINKEX completed that year:
(a) 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).
(ix) Narrative description of sensors and platforms utilized for
marine mammal detection and timeline illustrating how marine mammal
detection was conducted.
(b) Individual marine mammal observation (by Navy lookouts) info.
(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: (1)
The modeled injury threshold radius for the largest explosive used in
that exercise type in that OPAREA (91 m for SINKEX in HRC); (2) the
required exclusion zone (1 nm for SINKEX in HRC); (3) the required
observation distance (if different than the exclusion zone (2 nm for
SINKEX in HRC); and (4) greater than the required observed distance.
For example, in this case, the observer would indicate if < 91 m, from
91 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 munition type in use at time of marine mammal
detection.
Improved Extended Echo-Ranging System (IEER) Summary
This section shall include an annual summary of the following IEER
information:
(i) Total number of IEER events conducted in the HRC.
(ii) Total expended/detonated rounds (buoys).
(iii) Total number of self-scuttled IEER rounds.
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 will provide the information described below for
all of their explosive exercises. Until the Navy 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.
(i) Total annual number of each type of explosive exercise (of
those identified as part of the ``specified activity'' in this final
rule) conducted in the HRC.
(iii) Total annual expended/detonated rounds (missiles, bombs,
etc.) for each explosive type.
Sonar Exercise Notification
The Navy shall submit to the NMFS Office of Protected Resources
(specific contact information to be provided in LOA) either an
electronic (preferably) or verbal report within fifteen calendar days
after the completion of any major exercise (RIMPAC, USWEX, or Multi
Strike Group) indicating:
(1) Location of the exercise.
(2) Beginning and end dates of the exercise.
(3) Type of exercise (i.e., RIMPAC, USWEX, or Multi Strike Group).
HRC 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 HRC Exercise Reports and HRC Monitoring Plan Reports).
This report will be submitted at the end of the fourth year of the rule
(November 2012), covering activities that have occurred through June 1,
2012.
Comprehensive National ASW Report
By June, 2014, the Navy shall submit a draft National Report that
analyzes, compares, and summarizes the active sonar data gathered
(through January 1, 2014) from the watchstanders and pursuant to the
implementation of the Monitoring Plans the HRC, the Atlantic Fleet
Active Sonar Training, the Southern California (SOCAL) Range Complex,
the Marianas Range Complex, the Northwest Training Range, the Gulf of
Alaska, and the East Coast Undersea Warfare Training Range.
The Navy shall respond to NMFS comments and requests for additional
information or clarification on the HRC Comprehensive Report, the
Comprehensive National ASW report, the Annual HRC Exercise Report, or
the Annual HRC Monitoring Plan Report (or the multi-Range Complex
Annual Monitoring Plan Report, if that is how the Navy chooses to
submit the information) if submitted within 3 months of receipt. These
reports will be considered final after the Navy has addressed NMFS'
comments or provided the requested information, or three months after
the submittal of the draft if NMFS does not comment by then.
Comments and Responses
On June 23, 2008 (73 FR 35510), NMFS published a proposed rule in
[[Page 1467]]
response to the Navy's request to take marine mammals incidental to
military readiness training exercises in the HRC and requested
comments, information and suggestions concerning the request. During
the 30-day public comment period, NMFS received 8 comments from private
citizens, comments from the Marine Mammal Commission (MMC) and the
Office of Hawaiian Affairs, and several sets of comments from non-
governmental organizations, including, the Natural Resources Defense
Council (NRDC) (which commented on behalf of The Humane Society of the
United States, the International Fund for Animal Welfare, Cetacean
Society International, Ocean Mammal Institute, the International Ocean
Noise Coalition, Seaflow, and the Ocean Futures Society and its founder
Jean-Michel Cousteau), the Cascadia Research Collective (CRC), Ziphius
EcoServices, and Smultea Environmental Sciences, LLC. The comments are
summarized and sorted into general topic areas and are addressed below.
Full copies of the comment letters may be accessed at https://
www.regulations.gov.
Monitoring and Reporting
Comment 1: One commenter stated that ``It is advisable to hold a
multi-day workshop to discuss controversial issues related to the
problem.'' The commenter further indicated that the workshop should
include representatives from the Navy, NMFS, relevant marine mammal
researchers, NGOs (e.g., NRDC), and invited experts on certain topics
of interest. The goal of the workshop should be to move towards
consensus on a way forward for the monitoring plan.
Response: NMFS believes that a workshop consisting of the Navy,
NMFS, researchers, invited experts, and other interested parties, in
combination with an adaptive management plan that allows for
modification to the monitoring plan, would provide a means for the Navy
to potentially make changes to the Monitoring Plan that would more
effectively accomplish some of the goals of monitoring set forth
earlier in the Monitoring section. NMFS and the Navy have coordinated
on this point and the Navy will convene a workshop in 2011. The
workshop and how it will interact with the adaptive management
component are discussed in the Monitoring Workshop section of this
final rule. The Monitoring Workshop participants will be asked to
submit individual recommendations to the Navy and NMFS, and both
agencies will work together to determine whether modifications to the
HRC monitoring are necessary based on the recommendations. As
necessary, NMFS would incorporate any changes into future LOAs and
future rules. However, we disagree with the commenter's suggestion that
the workshop participants seek to achieve consensus on a way forward
for the monitoring plan. NMFS has statutory responsibility to prescribe
regulations pertaining to monitoring and reporting, and will, in
coordination with the Navy, develop the most effective and appropriate
monitoring and reporting protocols for future authorizations.
Comment 2: Two commenters made several recommendations regarding
the formatting and understandability of the monitoring plan.
Response: NMFS incorporated these recommendations where
appropriate. For example, a map of the area that the ICMP covers was
added to the plan, a list of the animals in the HRC was added, and
bulleted lists will replace long paragraphs in some places. However, we
did not incorporate the commenters recommendations in all cases, for
example, the commenter recommended that a lot of the analysis contained
in the proposed rule be included in the Monitoring plan, such as a
summary of Southall et al., 2007, or the regulatory definitions of
Level A and Level B harassment, which NMFS believes would needlessly
lengthen and complicate the Plan and generally be duplicative.
Comment 3: Two commenters asked for more detail, and associated
references, in several areas of the methods sections.
Response: NMFS has provided additional detail (including citations)
concerning the survey methods used in the monitoring plan in the final
rule.
Comment 4: One commenter stated: ``The Navy improperly assumes that
they have no impact on the marine mammals. It is clear that the draft
plan begins with the assumption that the Navy has no impact on marine
mammals, or that the current mitigation is adequate to eliminate
impacts. This is not supported by facts, and it invalidates the entire
purpose of the plan. The Navy must acknowledge that sonar testing may
indeed impact marine mammals and provide references, and must be
willing to work as an active partner in a plan to investigate the
extent and severity of such impacts, and how to reduce them to
insignificant levels. Otherwise, this entire exercise is just `window
dressing' and will be a major waste of taxpayer dollars.''
Response: NMFS disagrees with this commenter's assertion. It is
possible that the commenter mistook the fact that the Navy phrased some
of their goals as null hypotheses (``If marine mammals and sea turtles
are exposed to MFAS, what are their behavioral responses? Are they
different at various levels?'') to mean that they think there are no
effects. The Navy's LOA application and EIS clearly discuss the
potential adverse effects that marine mammals may experience when
exposed to MFAS. The Navy has worked and will continue to work as an
active partner to investigate the extent and severity of the impacts
and how to reduce them (see Navy Research section of this final rule).
Comment 5: A few commenters asked why the Navy did not consider
additional survey methods, or modifications to the existing methods,
beyond those currently included in the plan, such as: Specified focal
follows of one animal before, during, and after sonar; photo-
identification of marine mammals to look at residency patterns; having
a helicopter on board, on call to opportunistically observe marine
mammals around sonar transmissions; or doing biopsy sampling to assess
stress hormones.
Response: There are a lot of different methods available with which
to monitor marine mammals and the Navy considered a wide range of
methods in the development of their plan. NMFS considered all of the
public comments (including the recommended additional survey methods)
received during this rulemaking. Some of the methods suggested by the
public, such as the photo-identification method, would likely be
feasible and provide useful information, while other methods, such as
having a helicopter on standby, would be difficult both financially and
operationally. Nevertheless, the Navy must work within the framework of
the available resources and the operational constraints associated with
doing work in the vicinity of a complex military exercise. NMFS
provided input during the development of the plan and believes that
results from the required monitoring will provide valuable information
regarding the effects of MFAS on marine mammals. Additionally, by
including the Monitoring Plan as a requirement of the LOA, NMFS is
compliant with the MMPA requirement to prescribe regulations setting
forth the requirements pertaining to the monitoring and reporting of
taking. That being said, the Navy and NMFS understand the importance of
marine mammal monitoring to determine the effects of MFAS, which is why
the Navy agreed to conduct the Workshop referred to in Comment 1 during
which the workshop participants will review
[[Page 1468]]
and assess the monitoring results (from this Monitoring Plan and others
from other Range complexes and areas) and make informed recommendations
for how to move forward with the best Monitoring strategy.
Comment 6: The Marine Mammal Commission was supportive of the use
of Adaptive Management, but wanted a more detailed implementation plan.
Response: NMFS has included additional detail regarding how
adaptive management will be implemented. Please see the Adaptive
Management, Monitoring Workshop, and Integrated Comprehensive
Monitoring Plan sections of the final rule.
Comment 7: Multiple commenters questioned whether the Marine Mammal
Observers identified in the Monitoring Plan are independent scientists
or Navy employees? Some commenters questioned the objectivity of Navy
scientists.
Response: Independent scientists will be conducting the vast
majority of the observations pursuant to the Monitoring Plan. Navy
scientists will be involved in a small portion of the field work and
some of the post-monitoring analysis. The Navy is responsible for both
the funding and implementation of a substantial amount of marine mammal
and acoustic research and NMFS has no concerns regarding the
objectivity of the reported results from either these research projects
or the monitoring required pursuant to the MMPA authorization.
Comment 8: During aerial surveys, information on headings/
orientation of animals should be collected as these data can later be
examined to assess movement/response of animals relative to locations
and received sound levels of MFAS and underwater detonations.
Response: As NMFS noted in the proposed rule, additional detail has
been added to the Reporting Requirements section of the final rule. A
requirement that Navy lookouts report the relative directions of both
the marine mammals and the sonar source has been included. NMFS also
included a requirement that the MMOs collecting data for the Monitoring
Plan collect, at a minimum, the same data outlined in the Reporting
Requirements section for the Navy lookouts.
Comment 9: One commenter was concerned that the Navy would not
begin collecting data until mid-late 2009 when the ICMP was finalized.
Response: The ICMP is an overarching framework for all of the
Navy's Range-specific MMPA Monitoring Plans and does not include a
field-work component (rather it addresses prioritization,
standardization, and summarization of actual data-gathering). The Navy
actually began doing some of the data collection in 2007 outside of the
commitments made through the HRC EIS process, and they will begin
collecting field data pursuant to the HRC-specific Monitoring Plan
shortly after the authorized exercises begin in early 2009.
Comment 10: Two commenters questioned whether the Navy had
considered whether a statistically sound sample size had been developed
to answer the questions that the monitoring is trying to answer. One
commenter stated: ``To determine the sample sizes required to assess
impacts and the validity of this monitoring effort, the statistical
power should be es