Taking and Importing Marine Mammals: Taking Marine Mammals Incidental to U.S. Navy Operations of Surveillance Towed Array Sensor System Low Frequency Active Sonar, 50289-50322 [2012-20214]
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Vol. 77
Monday,
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August 20, 2012
Part IV
Department of Commerce
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National Oceanic and Atmospheric Administration
50 CFR Part 218
Taking and Importing Marine Mammals: Taking Marine Mammals Incidental
to U.S. Navy Operations of Surveillance Towed Array Sensor System Low
Frequency Active Sonar; Final Rule
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Federal Register / Vol. 77, No. 161 / Monday, August 20, 2012 / Rules and Regulations
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 218
[Docket No. 110808485–2148–02]
RIN 0648–BB14
Taking and Importing Marine
Mammals: Taking Marine Mammals
Incidental to U.S. Navy Operations of
Surveillance Towed Array Sensor
System Low Frequency Active Sonar
National Marine Fisheries
Service, National Oceanic and
Atmospheric Administration,
Commerce.
ACTION: Final rule.
AGENCY:
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FOR FURTHER INFORMATION CONTACT:
Jeannine Cody, Office of Protected
Resources, NMFS, (301) 427–8401.
SUPPLEMENTARY INFORMATION:
Executive Summary
Upon application from the
U.S. Navy (Navy), we (the National
Marine Fisheries Service) are issuing
regulations under the Marine Mammal
Protection Act to govern the
unintentional taking of marine
mammals incidental to conducting
operations of Surveillance Towed Array
Sensor System (SURTASS) Low
Frequency Active (LFA) sonar on a
maximum of four naval surveillance
vessels in areas of the Pacific, Atlantic,
and Indian Oceans and the
Mediterranean Sea, from the period of
August 15, 2012, through August 15,
2017. These regulations: allow us to
issue Letters of Authorization (LOA) for
the incidental take of marine mammals
during the Navy’s specified activities
and timeframes; set forth the
permissible methods of taking; set forth
other means of effecting the least
practicable adverse impact on marine
mammal species and their habitat; and
set forth requirements pertaining to the
monitoring and reporting of the
incidental take.
DATES: Effective August 15, 2012,
through August 15, 2017.
ADDRESSES: To obtain an electronic
copy of: the Navy’s application (which
contains a list of the references within
this document); our Record of Decision;
and other documents that we have cited
in this document, write to P. Michael
Payne, Chief, Permits and Conservation
Division, Office of Protected Resources,
National Marine Fisheries Service, 1315
East-West Highway, Silver Spring, MD
20910–3225, or download electronic
copies at: https://www.nmfs.noaa.gov/pr/
permits/incidental.htm#applications or
telephone the contact listed here (see
FOR FURTHER INFORMATION CONTACT).
The Navy released a Final
Supplemental Environmental Impact
Statement/Supplemental Overseas
SUMMARY:
Environmental Impact Statement
(FSEIS/SOEIS) for employment of
SURTASS LFA sonar on June 8, 2012.
The public may view the document at:
https://www.surtass-lfa-eis.com. We
participated in the development of this
document as a cooperating agency
under the Council on Environmental
Quality’s regulations implementing the
National Environmental Policy Act of
1972.
This regulation allows us to issue
Letters of Authorization to the Navy
(upon their request) for the incidental
take of marine mammals during
SURTASS LFA sonar operations. The
SURTASS LFA sonar system is a longrange, low frequency sonar that has both
active and passive acoustic components.
The Navy will use the system for longrange detection of quiet, hard-to-find
submarines. The Navy’s activities are
military readiness activities under the
Marine Mammal Protection Act of 1972,
as amended (MMPA; 16 U.S.C. 1631 et
seq.) as defined by the National Defense
Authorization Act for Fiscal Year 2004
(NDAA; Pub. L. 108–136).
This is the third rule for SURTASS
LFA sonar operations under the Marine
Mammal Protection Act. The 2007
regulations governing take incidental to
SURTASS LFA sonar activities expire
on August 15, 2012. We published the
first rule, effective from August 2002
through August 2007, on July 16, 2002
(67 FR 46712), and published the
second rule on August 21, 2007 (72 FR
46846). For this five-year period (August
2012 through August 2017), covered
under this regulation, the Navy is
proposing to conduct the same types of
sonar activities as they have conducted
over the past nine years.
Purpose and Need for This Regulatory
Action
In 2011, we received an application
from the Navy requesting five-year
regulations and Letters of
Authorizations to take marine
mammals, by harassment, incidental to
conducting SURTASS LFA sonar
operations in areas of the world’s oceans
from August 2012 through August 2017.
These operations, which constitute a
military readiness activity, have the
potential to cause behavioral
disturbance and injury (if not mitigated)
to marine mammals.
Section 101(a)(5)(A) of the MMPA
directs the Secretary of Commerce
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(Secretary) to authorize, upon request,
the incidental, but not intentional,
taking of marine mammals of a species
or population stock, by U.S. citizens
who engage in a specified activity (other
than commercial fishing) within a
specified geographical region if after
notice and public comment: (1) We
make certain findings; and (2) issue
regulations.
Under this five-year regulation, the
Navy will submit an annual application
to us for Letters of Authorizations for up
to four vessels to take marine mammals,
incidental to conducting SURTASS LFA
sonar operations.
This regulation establishes a
framework to authorize incidental take
through our issuing Letters of
Authorizations to the Navy for
SURTASS LFA sonar operations and
contains mitigation, monitoring, and
reporting requirements.
Legal Authority for the Regulatory
Action
Section 101(a)(5)(A) of the Marine
Mammal Protection Act and our
implementing regulations at 50 CFR part
216, subpart I provide the legal basis for
issuing the five-year regulations and
Letters of Authorization.
Summary of Major Provisions Within
the Regulation
The following provides a summary of
some of the major provisions within this
third rulemaking for SURTASS LFA
sonar:
• Required suspension/delay of
SURTASS LFA sonar transmissions if a
marine mammal enters the 2-kilometer
(km) (1.2-mile (mi); 1.1 nautical mile
(nm)) mitigation and buffer zones
around the vessel;
• Required geographic restrictions in
designated offshore biologically
important areas (OBIA) and within 22
km (14 mi; 12 nm) of any coastline,
including islands, for SURTASS LFA
sonar operations to protect marine
mammals;
• Required visual, passive acoustic
and active acoustic monitoring during
routine training, testing and military
operations of SURTASS LFA sonar to
support the implementation of
mitigation measures to protect marine
mammals;
• Required monitoring of ambient
noise data for incorporation into
appropriate ocean noise budget efforts
and analyses;
• Required monitoring of marine
mammal stranding incidents; and
• Required research on how marine
mammals (including harbor porpoises
(Phocoena phocoena) and beaked
whales (Mesoplodon spp.)) respond to
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SURTASS LFA sonar as well as research
on marine mammal vocalizations before,
during, and after designated exercises
with SURTASS LFA sonar.
Cost and Benefits
This final rule, specific only to the
Navy’s SURTASS LFA sonar operations,
is not significant under Executive Order
12866, Regulatory Planning and Review.
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Availability of Supporting Information
We provided extensive
SUPPLEMENTARY INFORMATION in the
Notice of the proposed rule for this
activity in the Federal Register on
Friday, January 6, 2012 (77 FR 842). We
did not reprint all of that information
here in its entirety; instead, we
represent all sections from the proposed
rule in this document and provide
either a summary of the material
presented in the proposed rule or a note
referencing the page(s) in the proposed
rule where the public can find the
information. We address any
information that has changed since the
proposed rule in this document.
Additionally, this final rule contains a
section that responds to the public
comments submitted during the 30-day
public comment period and the 15-day
extension of the comment period for the
proposed rule.
Background
Section 101(a)(5)(A) of the MMPA
directs the Secretary to authorize, upon
request, the incidental, but not
intentional, taking of small numbers of
marine mammals of a species or
population stock, by U.S. citizens who
engage in a specified activity (other than
commercial fishing) within a specified
geographical region if, after notice and
public comment: (1) We make certain
findings; and (2) we issue regulations.
We are required to grant authorization
for the incidental taking of marine
mammals if we find that the total taking
will have a negligible impact on the
species or stock(s); and will not have an
unmitigable adverse impact on the
availability of the species or stock(s) for
subsistence uses (where relevant). We
must also set forth the permissible
methods of taking; other means of
effecting the least practicable adverse
impact on the species or stock and its
habitat; and requirements pertaining to
the mitigation, monitoring, and
reporting of the takings.
Accordingly, this regulation, which
governs our issuance of Letters of
Authorization (LOA) to the Navy,
designates: (1) The permissible methods
of taking; (2) mitigation measures to
minimize adverse impacts to the lowest
level practicable on marine mammal
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species and their habitat; and (3)
requirements for monitoring and
reporting incidental take.
We have defined negligible impact in
50 CFR 216.103 as ‘‘* * * an impact
resulting from the specified activity that
cannot be reasonably expected to, and is
not reasonably likely to, adversely affect
the species or stock through effects on
annual rates of recruitment or survival.’’
The National Defense Authorization
Act of 2004 amended section
101(a)(5)(A) of the MMPA by removing
the small numbers and specified
geographic region provisions; revising
the definition of harassment as it
applies to a military readiness activity;
and explicitly requiring that our
determination of ‘‘least practicable
adverse impact’’ include consideration
of: (1) Personnel safety; (2) the
practicality of implementation; and (3)
impact on the effectiveness of the
military readiness activity.
With respect to military readiness
activities, the MMPA defines
harassment as ‘‘(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 August 17, 2011, we received an
application from the Navy requesting
rulemaking and LOAs for the take of
individuals of 94 species of marine
mammals (70 cetaceans and 24
pinnipeds), by Level A and Level B
harassment, incidental to upcoming
routine training and testing and use of
the SURTASS LFA sonar system during
military operations in areas of the
Pacific, Atlantic, and Indian Oceans and
the Mediterranean Sea over the course
of five years (2012–2017). The Navy
would use the sonar system on a
maximum of four naval surveillance
vessels during military operations
which they have designated as military
readiness activities.
The Navy states and we concur, that
these military readiness activities may
incidentally take marine mammals
present within the Navy’s mission areas
by exposing them to sound from lowfrequency active sonar sources. The
Navy requests authorization to take
individuals of these marine mammals
by Level A and Level B harassment.
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However, as we discuss later in this
document, the Navy will likely avoid
Level A harassment by implementing
required mitigation and monitoring
measures.
Please refer to Tables 9–27 (pages
123–140) of the Navy’s application for
detailed information on the estimated
percentages of marine mammal stocks
potentially affected by SURTASS LFA
sonar activities in areas of the Pacific,
Atlantic, and Indian Oceans and the
Mediterranean Sea per year. This final
rule does not specify the number of
marine mammals that may be taken in
the proposed locations because the
Navy calculates the take estimates
annually through various inputs such as
mission location, mission duration, and
season of operation.
As with the 2002 and 2007 rules, the
Navy will limit operation of SURTASS
LFA sonar to ensure that no more than
12 percent of any marine mammal stock
would be taken by Level B harassment,
annually, over the course of this rule.
This annual, per-stock cap applies
regardless of the number of SURTASS
LFA sonar vessels operating. The Navy
will use the 12 percent cap to guide its
mission planning for selecting potential
operational areas within each annual
authorization application.
As a result of the required mitigation
and monitoring measures and standard
operating procedures and the Navy’s
mission planning which, to the greatest
extent feasible considering national
security tasking, avoids conducting
SURTASS LFA sonar operations in
areas of high marine animal densities,
we believe that the incidental take of
marine mammals would likely be lower
than the Navy’s requested amount of
incidental take.
In the Navy’s application, their
acoustic analyses predict that less than
0.0001 percent of the endangered north
Pacific right whale (Eubalaena japonica)
population; less than 0.0001 of the
northern elephant seal (Mirounga
angustirostris) population; and 0.00
percent of the stocks of all other marine
mammal species may be exposed to
levels of sound likely to result in Level
A harassment. Quantitatively, the
Navy’s request translates into take
estimates of zero animals for any
species, including north Pacific right
whales. However, because the
probability of detection by the Navy’s
active High-Frequency Marine Mammal
Monitoring (HF/M3) sonar system
within the SURTASS LFA sonar
mitigation and buffer zones is not 100
percent, we will include a small number
of Level A harassment takes for marine
mammals over the course of the fiveyear regulations based on qualitative
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analyses. These are the only quantitative
adjustments that we have made to the
Navy’s requested takes from their
modeled exposure results.
Because the required mitigation
measures will minimize any potential
risk for mortality and SURTASS LFA
sonar has operated under previous
regulations for the last ten years without
any reports of mortality, we do not
expect any mortality to occur as a result
of the Navy’s SURTASS LFA sonar
operations. Thus, we are not authorizing
any mortality incidental to the Navy’s
routine training and testing and military
operations of the SURTASS LFA sonar
system.
Description of Specified Activities
The proposed rule included a
complete description of the Navy’s
specified activities covered by these
final regulations (for which we would
authorize the associated incidental take
of marine mammals in annual LOAs and
described the nature and levels of the
use of the SURTASS LFA sonar system
(77 FR 842; January 6, 2012; page 843–
846). These military readiness activities
for SURTASS LFA sonar consist of
routine training and testing as well as
use of the system during military
operations which involves acoustic
sources, including low frequency active
sonar and high-frequency active sonar
components. Below we summarize the
description of the specified activities
and one small correction from the
proposed rule.
Potential SURTASS LFA Sonar
Operational Areas
Based on the Navy’s current
operational requirements, potential
operations for SURTASS LFA sonar
vessels from August 2012 through
August 2017 would include areas
located in the Pacific, Indian, and
Atlantic Oceans and Mediterranean Sea.
The proposed rule provided a list of the
Navy’s potential operating areas in
Table 2 relevant to U.S. national
security interests (77 FR 842; January 6,
2012; page 843–844). Use of the
SURTASS LFA sonar system could
occur on a maximum of four naval
surveillance vessels: the United States
Naval Ship (USNS) ABLE, the USNS
EFFECTIVE, the USNS IMPECCABLE,
and the USNS VICTORIOUS.
The Navy will not operate SURTASS
LFA sonar in polar regions (i.e., Arctic
and Antarctic waters) of the world. The
Arctic Ocean, the Bering Sea (including
Bristol Bay and Norton Sound), portions
of the Norwegian, Greenland, and
Barents Seas north of 72° North (N)
latitude, plus Baffin Bay, Hudson Bay,
and the Gulf of St. Lawrence are nonoperational areas for SURTASS LFA
sonar. In the Antarctic, the Navy will
not conduct SURTASS LFA sonar
operations in areas south of 60° South
(S) latitude. The Navy has excluded
polar waters from operational planning
because of the inherent inclement
weather conditions and the navigational
and operational (equipment) danger that
icebergs pose to SURTASS LFA sonar
vessels. Further, the Navy would
operate SURTASS LFA sonar such that
the sound field does not exceed 180
decibels (dB) re: 1 mPa within the
coastal standoff zone (i.e., 22 km; 14mi;
12 nm from any coastline) or seaward of
any OBIA boundary for SURTASS LFA
sonar operations, identified later in this
document.
We have included additional
operational restrictions beyond what the
Navy proposed in their application for
SURTASS LFA sonar operations within
this rule. We are requiring: (1) An
additional 1-km (0.62 mi; 054 nm)
buffer around the Navy’s 1-km (0.62 mi;
054 nm) LFA sonar mitigation zone to
protect marine mammals from entering
the 180-dBisopleth around the
SURTASS LFA sonar vessel; and (2) an
additional 1-km (0.62 mi; 054 nm)
buffer seaward of the outer perimeter of
any OBIA.
Table 1 summarizes a projected
annual deployment schedule for one
surveillance vessel using SURTASS
LFA sonar.
TABLE 1—EXAMPLE ANNUAL DEPLOYMENT SCHEDULE FOR ONE SURVEILLANCE VESSEL USING SURTASS LFA SONAR
On mission
Days
Off mission
Days
Transit ...................................................................................
Active Transmissions.
432 transmission hours based on a 7.5% duty cycle. .........
54
In-Port Upkeep .....................................................................
40
240
Regular Overhaul .................................................................
31
Total Days on Mission ...................................................
294
Total Days off Mission .........................................................
71.
In the proposed rule, we incorrectly
stated that a normal SURTASS LFA
sonar deployment schedule for a single
vessel would involve 240 days of active
sonar transmissions (77 FR 842; January
6, 2012; page 843). The correct
statement is that the each vessel will
perform up to 240 days of active
operations and transmit SURTASS LFA
sonar up to 432 hours.
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Brief Background on Sound, Marine
Mammal Hearing, and Vocalization
An understanding of the basic
properties of underwater sound, marine
mammal hearing, and vocalization is
necessary to comprehend many of the
concepts and analyses presented in this
document. The proposed rule contains a
section that provides a brief background
on the principles of sound that are
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frequently referred to in this rulemaking
(77 FR 842; January 6, 2012; pages 857–
859). 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 sound metric used in
our analysis (sound pressure level and
single ping equivalent). The information
contained in the proposed rule has not
changed.
Acoustic stimuli (i.e., increased
underwater sound) generated by the
SURTASS LFA sonar system’s lowfrequency acoustic transmissions have
the potential to cause take of marine
mammals in the operational areas. The
operation of the SURTASS LFA sonar
system during at-sea operations would
result in the generation of sound or
pressure waves in the water at or above
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levels that we have determined would
result in take. This is the principal
means of marine mammal taking
associated with these military readiness
activities. At no point do we expect the
Navy to have more than four SURTASS
LFA sonar systems in use, and so this
rule analyzes the effects on marine
mammals due to the deployment of up
to four SURTASS LFA sonar systems
from 2012 through 2017.
Description of Marine Mammals in the
Area of the Specified Activities
Ninety-four (94) marine mammal
species or populations/stocks have
confirmed or possible occurrence within
potential SURTASS LFA sonar
operational areas in the Pacific,
Atlantic, and Indian Oceans and the
Mediterranean Sea. Twelve species of
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baleen whales (mysticetes), 58 species
of toothed whales, dolphins, or
porpoises (odontocetes), and 24 species
of seals or sea lions (pinnipeds) could
be affected by SURTASS LFA sonar
operations.
Fifteen of the 94 marine mammal
species are endangered and three of the
94 marine mammal species are
threatened under the Endangered
Species Act of 1973 (ESA; 16 U.S.C.
1531 et seq.). Marine mammal species
under our jurisdiction that are
endangered include: the blue whale
(Balaenoptera musculus); fin whale
(Balaenoptera physalus); sei whale
(Balaenoptera borealis); humpback
whale (Megaptera novaeangliae);
bowhead whale (Balaena mysticetus);
North Atlantic right whale (Eubalaena
glacialis); North Pacific right whale
(Eubalena japonica); southern right
whale (Eubalaena australis); gray whale
(Eschrichtius robustus); sperm whale
(Physeter macrocephalus); the Cook
Inlet stock of beluga whale
(Delphinapterus leucas); the Southern
Resident population of Killer whale
(Orca orcinus); the western distinct
population segment (DPS) of the Steller
sea lion (Eumetopias jubatus);
Mediterranean monk seal (Monachus
monachus); and Hawaiian monk seal
(Monachus schauinslandi). In addition,
the Hawaiian insular distinct
population segment of false killer whale
(Pseudorca crassidens) is a candidate
for proposed listing as endangered.
The three threatened marine mammal
species under our jurisdiction include:
the eastern distinct population segment
of the Steller sea lion (currently
proposed for delisting); the Guadalupe
fur seal (Arctocephalus townsendi) and
the southern distinct population
segment of the spotted seal (Phoca
largha).
The threatened and endangered
marine mammal species mentioned
previously are also depleted under the
Marine Mammal Protection Act. Other
species listed as depleted include: the
western north Atlantic coastal stock of
bottlenose dolphin (Tursiops truncatus);
the northeastern offshore stock of the
pantropical spotted dolphin (Stenella
attenuata); and the eastern stock of the
spinner dolphin (Stenella longirostris).
Ringed seals (Phoca hispida), bearded
seals (Erignathus barbatus), Chinese
river dolphins (Lipotes vexillifer) and
the vaquita (Phocoena sinus) do not
occur within the Navy’s potential
SURTASS LFA sonar operational areas
(see 77 FR 842; January 6, 2012; page
844).
The U.S. Fish and Wildlife Service is
responsible for managing the following
marine mammal species: southern sea
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otter (Enhydra lutris), polar bear (Ursus
maritimus), walrus (Odobenus
rosmarus), west African manatee
(Trichechus senegalensis), Amazonian
manatee (Trichechus inunguis), west
Indian manatee (Trichechus manatus),
and dugong (Dugong dugon). None of
these species occur in geographic areas
that would overlap with potential
SURTASS LFA sonar operational areas.
The Description of Marine Mammals
in the Area of the Specified Activities
section has not changed from what was
in the proposed rule (77 FR 842; January
6, 2012; pages 848–857). Tables 3
through 21 of the proposed rule
provided lists of marine mammal
species known to occur or potentially
occur within the Navy’s models of
potential SURTASS LFA sonar
operational areas relevant to U.S.
national security interests. Tables 4.5
through 4.23 in the 2012 FSEIS/SOEIS
also provide information on the
percentages of stocks potentially
affected by SURTASS LFA sonar
operations. Although not repeated in
this final rule, we have reviewed these
data, determined them to be the best
available scientific information for the
purposes of the rulemaking, and
consider this information part of the
administrative record for this action.
Potential Effects of the Specified
Activity on Marine Mammals
For the purpose of MMPA
authorizations, our effects assessments
serve four primary purposes:
(1) Identification of the permissible
methods of taking, meaning the nature
of the take (e.g., resulting from
anthropogenic noise versus from ship
strike, etc.); the regulatory level of take
(i.e., mortality versus Level A or Level
B harassment); and the estimated
amount of take;
(2) Informing the prescription of
means of effecting the least practicable
adverse impact on such species or stock
and its habitat (i.e., mitigation);
(3) Supporting the determination of
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); and
(4) Determining whether the specified
activity will have an unmitigable
adverse impact on the availability of the
species or stock(s) for subsistence uses.
In the Potential Effects of the
Specified Activity on Marine Mammals
section of the proposed rule, we
included a qualitative discussion of the
different ways that SURTASS LFA sonar
operations may potentially affect marine
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50293
mammals without consideration of
mitigation and monitoring measures
(see 77 FR 842; January 6, 2012; pages
860–874). Marine mammals may
experience direct physiological effects
(e.g., threshold shift and non-acoustic
injury, acoustic masking, impaired
communication, stress responses,
behavioral disturbance, stranding,
behavioral responses from vessel
movement, and injury or death from
vessel collisions). The information
contained in this section in the
proposed rule has not changed.
Later in the Estimated Take of Marine
Mammals section in this document, we
relate and quantify the potential effects
to marine mammals from SURTASS
LFA sonar operations discussed in this
section to the MMPA definitions of
Level A and Level B harassment.
Anticipated Effects on Marine Mammal
Habitat
We anticipate that the specified
activity may result in marine mammals
avoiding certain areas due to temporary
ensonification. This impact is temporary
and reversible, which we considered in
proposed rule as behavioral
modification. The main impact
associated with the activity would be
temporarily elevated noise levels and
the associated direct effects on marine
mammals.
We included a detailed discussion of
the potential effects of the Navy’s
SURTASS LFA sonar operations on
marine mammal habitat, including
critical habitat and marine mammal
prey species (77 FR 842; January 6,
2012; pages 874–875). The information
contained in the Anticipated Effects on
Marine Mammal Habitat section has not
changed from what was in the proposed
rule.
Mitigation
In order to issue regulations and
LOAs under section 101(a)(5)(A) of the
MMPA, we must set forth the
‘‘permissible methods of taking
pursuant to such activity, and other
means of effecting the least practicable
adverse impact on such species or stock
and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance.’’
The National Defense Authorization
Act for Fiscal Year 2004 amended
section 101(a)(5)(A) of the MMPA 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
routine training and testing as well as
use of the system during military
operations described in the SURTASS
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LFA sonar application qualify as
military readiness activities.
We have reviewed the Navy’s
proposed SURTASS LFA sonar
activities and the proposed mitigation
measures in the Navy’s application to
determine whether the resulting
activities and mitigation measures
would effect the least practicable
adverse impact on marine mammals
which includes a careful balancing of
the likely degree to which the measure
is expected to minimize adverse impacts
to marine mammals with the likely
effect of that measure on personnel
safety, practicality of implementation,
and impact of the effectiveness of the
military readiness activity (i.e.,
minimizing adverse impacts to the
lowest level practicable with mitigation
measures).
Any mitigation measure that we
prescribe should be able to accomplish,
have a reasonable likelihood of
accomplishing (based on current
science), or contribute to the
accomplishment of one or more of the
general goals listed here:
Goal (a): Avoidance or minimization
of injury or death of marine mammals
wherever possible (goals b, c, and d may
contribute to this goal).
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 SURTASS LFA sonar or other
activities expected to result in the take
of marine mammals (this goal may
contribute to goal a or to reducing
harassment takes only).
Goal (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 SURTASS LFA sonar
or other activities expected to result in
the take of marine mammals (this goal
may contribute to goal a or to reducing
harassment takes only).
Goal (d): A reduction in the intensity
of exposures (either total number or
number at biologically important time
or location) to received levels of
SURTASS LFA sonar or other activities
expected to result in the take of marine
mammals (this goal may contribute to
goal a or to reducing the severity of
harassment takes only).
Goal (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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Goal (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.
We described the Navy’s proposed
mitigation measures, as well as those
that we added, in detail in the proposed
rule (77 FR 842; January 6, 2012; pages
875–879). These required mitigation
measures, which are summarized below,
have not changed with the exception of
the addition of one more OBIA.
Following are the mitigation and
monitoring measures initially proposed
by the Navy:
• A 180-dB re:1 mPa isopleth
SURTASS LFA sonar mitigation zone
around the vessel;
• Delay or suspension of SURTASS
LFA sonar transmissions if the Navy
detects a marine mammal entering or
within the LFA sonar mitigation zone
(i.e., the 180-dB re: 1 mPa isopleth) by
any of the following detection methods;
(a) Visual monitoring;
(b) Passive acoustic monitoring; or
(c) Active acoustic monitoring;
• Geographic and operational
restrictions to avoid generating sound
levels above 180 dB re: 1 mPa in the
following areas:
(a) An OBIA; or
(b) Within coastal standoff zones (22
km; 14 mi; 12 nm of any coastline).
In the proposed rule, we added the
following mitigation requirements:
• An additional 1-km (0.62 mi; 054
nm) buffer zone around the 180-dB re:
1 mPa isopleth SURTASS LFA sonar
mitigation zone;
• An additional 1-km (0.62 mi; 054
nm) buffer zone seaward of any OBIA
boundary.
• Delay or suspension of SURTASS
LFA sonar transmissions if the Navy
detects a marine mammal entering the
1-km (0.62 mi; 054 nm) buffer zone
around the SURTASS LFA sonar
mitigation zone.
Within this final rule, we have added
additional mitigation measures based
upon comments received during the
public comment period for the proposed
rule (77 FR 842; January 6, 2012) and
the Navy’s 2011 Draft Supplemental
Environmental Impact Statement/
Overseas Environmental Impact
Statement.
Based on our evaluation of 367
potential areas within the Hoyt’s (2011)
2nd Edition of Marine Protected Areas
for Whales, Dolphins and Porpoises (see
Appendix F of the Navy’s 2012 FSEIS/
SOEIS), we identified three additional
areas for consideration as OBIAs for
marine mammals. They were: (1)
Abrolhos Bank in the southwest
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Atlantic Ocean; (2) an area within the
Southeast Shoal, Grand Bank in the
northwest Atlantic Ocean; and 3) an
area within Dogger Bank in the North
Sea.
Abrolhos Bank: For this rule, we have
added the Abrolhos Bank as an OBIA
based on its importance for humpback
whale breeding and calving. The
specified period of this OBIA would be
effective August through November. The
Navy concurs with our recommendation
to designate Abrolhos Bank as an OBIA.
Southeast Shoal, Grand Bank: There
is evidence from a single 1985 line
transect survey that humpback whales
foraged in this area in the past; however,
this information is almost 30 years old.
We and the Navy are continuing to
gather information to determine
whether this area meets the OBIA
criteria.
In the 2012 application for LOAs, the
Navy states that it does not plan to
operate within the northwest Atlantic
Ocean in the first year of this rule.
Utilizing the adaptive management
framework, we and the Navy will make
a decision before issuing the second
annual LOAs regarding whether this
area meets the OBIA criteria and, if so,
can be practicably implemented.
Dogger Bank: There is evidence from
a single 2007 line transect survey that
minke whales aggregated on the slope of
Dogger Bank to forage on sandeels (de
Boer, 2010). However, sandeels only
emerge from their sand burrows when
oceanographic conditions are optimal
(de Boer, 2010). There is not enough
information to support this area as a
sustained and predictable foraging
ground for minke whales at this time.
We will continue to monitor and reevaluate this area as researchers
complete additional surveys on Dogger
Bank within the next few years.
Utilizing the adaptive management
framework, we and the Navy will make
a decision before issuing the second
annual LOAs regarding whether this
area meets the OBIA criteria and, if so,
can be practicably implemented.
Operational Exception
We discussed the Navy’s need for an
operational exception for use of the
SURTASS LFA sonar system in the
proposed rule (77 FR 842; January 6,
2012; page 878). The information
contained in this section has not
changed from what was in the proposed
rule. Briefly, it may be necessary for the
Navy to operate in a manner that results
in SURTASS LFA sonar transmissions
generating sound levels above 180 dB
re: 1 mPa within an OBIA, or for Navy
to operate within an OBIA: (1) When it
is operationally necessary for the Navy
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to continue tracking an existing
underwater contact; or (2) when it is
operationally necessary for the Navy to
detect a new underwater contact within
the area. This exception does not apply
to routine training and testing with the
SURTASS LFA sonar systems.
Mitigation Conclusions
Based on our evaluation of the
proposed measures and other measures
considered by us or recommended by
the public, we have determined that the
required mitigation measures (including
the Adaptive Management component
described later in this document) are
means of effecting the least practicable
adverse impacts on marine mammal
species or stocks and their habitat,
paying particular attention to rookeries,
mating grounds, and areas of similar
significance, while also considering
personnel safety, practicality of
implementation, and impact on the
effectiveness of the military readiness
activity. The proposed rule contains
further support for this finding in the
Mitigation Conclusion section (77 FR
842; January 6, 2012; pages 878–879).
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Research
We included a discussion of the
Navy’s proposed research that increases
the knowledge base about marine
mammals and the potential effects from
underwater anthropogenic noise (77 FR
842; January 6, 2012; pages 879–880).
The information contained in Research
has not changed from what was in the
proposed rule.
Briefly, the Navy sponsors significant
research and monitoring projects for
living marine resources to study the
potential effects of its activities on
marine mammals. This ongoing marine
mammal research relates to hearing and
hearing sensitivity, auditory effects,
dive and behavioral response models,
noise impacts, beaked whale global
distribution, modeling of beaked whale
hearing and response, tagging of freeranging marine animals at-sea, and
radar-based detection of marine
mammals from ships. These research
projects may not be specifically related
to SURTASS LFA sonar operations;
however, they are crucial to the overall
knowledge base on marine mammals
and the potential effects from
underwater anthropogenic noise.
Monitoring
Section 101(a)(5)(A) of the MMPA
states that in order to issue an Incidental
Take Authorization for an activity, we
must set forth ‘‘requirements pertaining
to the monitoring and reporting of such
taking.’’ Our implementing regulations
at 50 CFR 216.104 (a)(13) indicate that
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requests for Letters of Authorization
must include the suggested means of
accomplishing the necessary monitoring
and reporting that will result in
increased knowledge of the species, the
level of taking, or impacts on
populations of marine mammals that we
expect to be present.
We provided a detailed description of
the general goals of monitoring and the
Navy’s proposed monitoring measures
in the proposed rule (77 FR 842; January
6, 2012; page 880). Within this final
rule, we have added additional
monitoring requirements for harbor
porpoises and beaked whales based
upon comments received during the
public comment periods for the
proposed rule. This additional
monitoring would augment the Navy’s
proposed monitoring efforts to increase
our understanding of how these species
respond–behaviorally or
physiologically–to SURTASS LFA
sonar.
Beaked Whale and Harbor Porpoise
Monitoring
Within the first year of the five-year
rule, the Navy will convene a Scientific
Advisory Group (SAG). Its goal will be
to analyze different types of monitoring
and research that could increase the
understanding of the potential effects of
low-frequency active sonar
transmissions on beaked whales and/or
harbor porpoises.
The Navy will work closely with the
SAG to characterize likely available
assets and resources to help them frame
their analysis, in order to identify
monitoring/research options that would
be most feasible for the Navy to
implement. SAG members will include
recognized marine biology and marine
bio-acoustic scientific subject matter
experts. The results from the SAG
meeting will be considered independent
scientific findings, fully accessible to
the public.
The Navy’s execution of any
monitoring/research with beaked
whales or harbor porpoises
recommended in the SAG’s findings
will necessarily depend on the
availability of scientists with the
appropriate background and experience
to execute the field research, as well as
the availability of adequate resources to
plan and conduct the research project
and to process, analyze, and report on
the collected data.
Following the SAG’s submission of
findings, and assuming the SAG
recommends going forward with beaked
whale and/or harbor porpoise
monitoring/research, the Navy will
either: (1) Draft a plan of action
outlining their strategy for
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50295
implementing the SAG’s
recommendations, or (2) describe, in
writing, why none of the SAG’s
recommendations are feasible and meet
with us to discuss any other potential
options.
With the exception of the additional
monitoring requirement for harbor
porpoises and beaked whales, the
information on monitoring in the
proposed rule has not changed.
Adaptive Management
Our understanding of the potential
effects of SURTASS LFA sonar on
marine mammals is continually
evolving. Reflecting this, this final
regulation governing the take of marine
mammals, incidental to the Navy’s
SURTASS LFA sonar operations
contains an adaptive management
component. We provided a description
of the general framework for adaptive
management in the proposed rule (77
FR 842; January 6, 2012; pages 880–
881). The information contained in this
section has not changed from the
proposed rule description.
This framework provides a
mechanism for NMFS and the Navy to
modify (or add or delete) mitigation or
monitoring measures, as appropriate,
based on new information.
The following are some of the
possible sources of new data that could
contribute to our decision to modify
mitigation or monitoring measures:
• Results from the Navy’s monitoring
from the previous year’s operation of
SURTASS LFA sonar.
• Compiled results of Navy-funded
research and development studies.
• Results from specific stranding
investigations.
• Results from general marine
mammal and sound research funded by
the Navy or other sponsors.
• Any information that reveals
marine mammals may have been taken
in a manner, extent or number not
authorized by this regulation or within
subsequent Letters of Authorization.
We would add, modify or delete
mitigation or monitoring measures in
consultation with the Navy if doing so
creates a reasonable likelihood of
accomplishing the goals of mitigation
and monitoring laid out in this final
rule. We and the Navy will meet
annually (if deemed necessary by either
agency) to discuss the monitoring
reports, Navy research and development
outcomes, current science, and
determine whether mitigation or
monitoring modifications are
appropriate.
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Reporting
SURTASS LFA Sonar Activity Concerns
In order to issue an incidental take
authorization for an activity, section
101(a)(5)(A) of the MMPA states that we
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 the Letters of
Authorization, and to provide us and
the Navy with data of the highest
quality based on the required
monitoring. A subset of the monitoring
reports’ information may be classified
and thus not releasable to the public.
We provided a detailed description of
the Navy’s proposed reporting
requirements in the proposed rule (77
FR 842; January 6, 2012; pages 881–
882). The information contained in the
Reporting section has not changed from
the proposed rule description. Briefly,
the reporting measures require the Navy
to provide: notification of injured or
dead marine mammals; notification of a
ship strike; quarterly mitigation
monitoring reports; annual reports; and
a five-year comprehensive report.
Comment 2: One commenter is
concerned that the Navy seems to take
very few steps to reduce its use of sonar
by using alternative technologies and
noted that the Navy could pursue the
use of other technologies for this action.
Response: The comment is beyond the
scope of our rulemaking for this action.
The Navy’s specified activity described
in their application for regulations is the
use of SURTASS LFA sonar, not
alternatives to SURTASS LFA sonar.
However, the Navy reviewed and
considered the use of non-acoustic
alternatives for underwater detection
(i.e., radar, laser, magnetic, infrared,
electronic, electric, hydrodynamic, and
biologic detection systems) in the 2012
FSEIS/SOEIS (see subchapter 1.1.4).
Table 1 in this Federal Register notice
summarizes a projected annual
deployment schedule for SURTASS
LFA sonar which amounts to 432 hours
(18 days) of active transmissions,
annually, for one surveillance vessel.
The SURTASS LFA sonar has a
relatively low duty cycle (i.e., the
amount of time of active sonar
transmissions divided by the amount of
time that the sonar is not transmitting)
of 7.5 to 10 percent. Thus, for an
estimated 18-day mission period,
SURTASS LFA sonar would be off
(quiet) for 90 to 92.5 percent of the time
and adding no sound into the water. On
an annual basis, the Navy would limit
each SURTASS LFA vessel to
transmitting no more than 4.9 percent of
the time (i.e., 432 hours within one year
(8,760 hours)).
Comments and Responses
On January 6, 2012, we published a
proposed rule (77 FR 842) in response
to the Navy’s request to take marine
mammals, incidental to conducting
SURTASS LFA sonar operations in
certain areas of the world’s oceans. We
requested comments, information, and
suggestions related to the request.
During the 30-day public comment
period, we received comments from the
Marine Mammal Commission
(Commission), the Natural Resources
Defense Council (NRDC), OceanCare,
the Surfrider Foundation, and 22 private
citizens. We also received comments
that appear to be directed solely at the
Navy’s draft 2011 Supplemental
Environmental Impact Statement/
Supplemental Overseas Environmental
Impact Statement. See the Navy’s 2012
FSEIS/SOEIS, which we have adopted.
We address the comments here.
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Marine Mammal Protection Act
Concerns
Comment 1: Citing the broad scope of
the Navy’s application, the complexity
of the proposed rule, and the need for
additional time for public comment, the
Natural Resources Defense Council
requested that we consider extending
the public comment period for an
additional 15 days.
Response: In response to the request,
we extended the public comment period
by 15 extra days (77 FR 6771, February
9, 2012).
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Threatened and Endangered Species
Comment 3: One commenter
expressed concern that the Navy had
underestimated the full impact that
sonar has on marine mammals,
particularly ones which are also listed
under the Endangered Species Act.
They stated: ‘‘The Navy’s application for
authorized use of SURTASS LFA sonar
states that the effects of sonar use will
not be greater on animals listed under
the ESA than the effects on other marine
mammals (LOA Application at page
114.)’’
Response: The commenter’s statement
is not accurate. First, the Navy has
analyzed the effects of SURTASS LFA
sonar on marine mammals, including
those listed under the Endangered
Species Act, in the 2001 Final
Environmental Impact Statement (Don,
2001), the 2007 Final Supplemental
Environmental Impact Statement (DoN,
2007) and the 2012FSEIS/SOEIS.
Specifically, the types of potential
effects on marine mammals from
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SURTASS LFA sonar operations
presented include: (1) Non-auditory
injury; (2) permanent loss of hearing; (3)
temporary loss of hearing; (4) behavioral
change; and (5) masking. We refer the
commenter to those documents for the
Navy’s analysis of the effects of
SURTASS LFA sonar on marine
mammals.
Second, we also analyzed the effects
of SURTASS LFA sonar on marine
mammals in the Potential Effects of the
Specified Activity on Marine Mammals
section of the proposed rule (77 FR 842;
January 6, 2012; pages 860–874). We
included a qualitative discussion of the
different ways that unmitigated
SURTASS LFA sonar operations may
result in direct physiological effects
(e.g., threshold shift and non-acoustic
injury, acoustic masking, impaired
communication, stress responses,
behavioral disturbance, stranding, and
effects from vessel movement and vessel
collisions). We anticipate that actual
effects to marine mammals (including
threatened and endangered species)
would be in the form of Level B
harassment (behavioral), due to the
required mitigation and monitoring
measures, and geographic restrictions.
While marine mammals could
potentially be affected by the SURTASS
LFA sonar sounds, we have determined
that these effects are not reasonably
likely to adversely affect the species or
stock through effects on annual rates of
recruitment or survival.
Finally, previous Endangered Species
Act section 7 consultations (NMFS,
2002, 2003, 2004, 2005, 2006, 2007,
2008, 2009, 2010, and 2011) and the
section 7 consultation for this rule have
analyzed the effects of SURTASS LFA
sonar operations on threatened and
endangered marine mammals and
concluded that the operation of the
SURTASS LFA sonar was not likely to
jeopardize the continued existence of
any endangered or threatened species
under our jurisdiction and would not
result in the destruction or adverse
modification of critical habitat.
Comment 4: One commenter stated:
‘‘The LOA application states that the
Jacksonville training would occur in the
winter, yet the winter months are the
time when this area is listed as an OBIA
(LOA Application at 11–13). Will the
Navy be conducting SURTASS LFA
training here during calving months? If
yes, what will the impact be on the
young whales? The diminished
population of North Atlantic Right
Whales should not have to compete
with the Navy for this area. The proper
time to conduct training here would be
in the summer months when the whales
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return to the New England and
Canadian coast.’’
Response: First, the Navy’s
application states that the Western
Atlantic/Jacksonville Operational Area
is a potential area for SURTASS LFA
sonar operations; it does not state that
training would occur in the area in the
winter. This area is one of 19 potential
sites that they modeled and analyzed
during the winter to assess potential
impacts to marine mammals for the rule
and the Letter of Authorization
application process.
We have designated the U.S. Right
Whale Seasonal Habitat as an OBIA
specifically to mitigate effects on north
Atlantic right whales and their calves
during the winter months. Moreover,
because we are also requiring the Navy
to implement an additional 1-km (0.62
mi; 054 nm) buffer zone seaward of the
outer perimeter of this OBIA, these
mitigation measures ensure that sound
levels within the area do not exceed
approximately 175dB re: 1 mPa from
November 15 through April 15, the
calving months.
If the Navy were to operate within the
greater Jacksonville Operational Area
outside of the U.S. Right Whale
Seasonal Habitat OBIA, the rule requires
the Navy to conduct visual, passive
acoustic, and active acoustic monitoring
and suspend/delay SURTASS LFA
sonar transmissions if a marine mammal
enters the 2-km (1.2-mi; 1.1-nm) LFA
mitigation and buffer zones around the
vessel.
In each annual application, the Navy
will include information if it plans to
operate (or not operate) within the
Western Atlantic/Jacksonville
Operational Area. Thus, at this time we
cannot say if the Navy intends to
operate in the Western Atlantic/
Jacksonville Operational Area during
the period of November through January
(i.e., calving months) with the exception
of the first year of SURTASS LFA sonar
operations, where the Navy has stated in
its application, that it does not intend to
operate in this area.
To clarify, Table 21 in the Navy’s
application presents estimates of the
percentage of marine mammal stocks
potentially affected by SURTASS LFA
sonar in the proposed mission area of
the Western Atlantic/Jacksonville
Operational Area. The Navy has
modeled potential effects to all marine
mammals in the Western Atlantic/
Jacksonville Operational Area during
the winter in the 2012 FSEIS/SOEIS (see
Tables 4–17 and C–29). If the Navy
conducted SURTASS LFA operations in
the winter, the Navy’s risk estimates
predict that 0.12 percent of the north
Atlantic right whale population could
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be potentially exposed to sound levels
that may lead to Level B harassment.
Comment 5: A commenter discussed
the Navy’s estimates of the percentage of
marine mammal stocks potentially
affected by SURTASS LFA sonar in the
proposed mission area of the Sea of
Japan operating area. He stated: ‘‘The
summer feeding grounds of Western
Gray [whales] is located in the Sea of
Okhotsk and is part of an OBIA which
restricts the Navy from training there.
The migratory patterns and route of
these whales is largely unknown but is
presumed to take them south to Korea.
If this is the case then the whales will
be migrating through the Sea of Japan
during the spring and fall, the modeled
season for training.’’
Response: Based upon the best
available information, we found few
data to support designating an area
within the Sea of Japan as a migration
corridor (i.e., an OBIA for SURTASS
LFA sonar). However, any western
Pacific gray whales transiting through
the Sea of Japan will be protected from
exposure to sound pressure levels
greater than approximately 175dB re: 1
mPa by the Navy’s three-part monitoring
protocols and required mitigation
measures contained in this regulation.
Comment 6: The same commenter as
in Comment 5 also stated: ‘‘There are
many other marine mammal
populations that are listed under the
ESA that occupy areas close to proposed
SURTASS LFA training areas. Due to
the fragile nature of these populations,
the Navy should afford these animals
extra protection to maximize their
chance of survival and recovery. The
SURTASS training in this area could
affect the whale’s navigation or
migration patterns and these
populations will not be able to recover
from endangered levels when human
interactions affect their behavior. The
Navy should make a concerted effort to
ensure that sonar is not used in areas
where ESA species are currently
migrating, calving, and feeding.’’
Response: See response to Comment
3. We are unclear as to which area or
species the commenter referred. We
designated OBIAs based on certain
criteria and the best available
information we had for marine
mammals to determine if any areas met
the criteria. In some cases, we
designated an OBIA because a species
listed under the Endangered Species Act
has designated critical habitat, breeds,
calves, migrates, or forages in a
particular area. For example, we
designated four OBIAs for north
Atlantic right whales, one OBIA each for
north Pacific right and fin whales, 10
OBIAs for humpback whales, and six
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50297
OBIAs for blue whales. Beyond that, the
standard mitigation and monitoring
measures that apply wherever the Navy
operates SURTASS LFA sonar will
ensure that marine mammals are not
exposed to sound levels that exceed
approximately 175 dB re: 1 mPa. Finally,
the Navy will perform mission planning
for annual Letters of Authorization
applications and would limit operation
of SURTASS LFA sonar to ensure that
no more than 12 percent of any marine
mammal stock would be taken by Level
B harassment annually, over the course
of this five-year regulation.
We anticipate that effects to marine
mammals (including threatened and
endangered species) would be in the
form of Level B harassment (behavioral),
due to the required mitigation measures,
geographic restrictions, and sporadic
nature of the SURTASS LFA sonar
operations. While marine mammals may
be affected by the SURTASS LFA sonar
sounds, we have determined that these
effects are not reasonably likely to
adversely affect the species or stock
through effects on annual rates of
recruitment or survival.
Comment 7: One commenter stated:
‘‘There exists significant risk to
Southern Resident Killer Whales
(SRKW), who are listed as an
endangered distinct species population
[distinct population segment] under the
ESA, in addition to being protected
under the MMPA. The critical habitat
for these animals is near the San Juan
Archipelago in Washington State, near
the U.S.-Canadian Border. If sonar use
causes mass strandings similar to the
incident in the Bahamas in 2000, it
could have permanent negative
consequences on the long-term survival
of this species. While the application
and proposed NMFS ruling say
harassment is the only foreseen
consequence, the mass stranding event
in the Bahamas strongly suggests at least
the possibility of significant mortality
occurring. Additionally J Pod, one of the
three SRKW pods, has already had a
brush with Navy sonar, along with
multiple other marine mammals in the
area. While the Navy claims there were
no adverse effects from the Sonar output
of the USS Shoup in May of 2003, local
scientists disagree, and NMFS’ own
findings were inconclusive. Such
uncertain or dissenting expert opinions
should create enough doubt in any
educated mind and the benefit of this
doubt should be given to the whales, not
the Navy.
This application should be
reconsidered. If an Unusual Mortality
Event (UME) were to occur in the San
Juan Islands, this would have a ripple
effect on the entire ecosystem not just
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the various marine mammals in the
area. Furthermore, if a UME were to
occur involving the SRKW population,
this would have a serious detriment on
the local tourism economy of the San
Juan Islands, creating a direct harm on
local citizens and the local economy in
addition to the ecological concerns
already mentioned.’’
Response: Based on the best available
information, SURTASS LFA sonar is not
associated with strandings of marine
mammals. SURTASS LFA sonar has
operated subject to our regulations for
the last nine years without any reports
of strandings since the Navy began
using the system operationally in the
early 2000s. The Stranding and
Mortality section in the proposed rule
(77 FR 842; January 6, 2012; pages 871–
872) presented information on the
potential for stranding from SURTASS
LFA sonar as well as information on
strandings associated with midfrequency active sonar use.
Over the past 12 years, there have
been five stranding events coincident
with military mid-frequency active
sonar use in which exposure to sonar is
believed (by NMFS and the Navy) to
have been a contributing factor to
strandings, including the Bahamas
(2000). We refer the reader to Cox et al.
(2006) for a summary of the Bahamas
strandings event.
We have also provided a summary of
the Navy’s acoustic modeling scenarios
and risk analysis methods in the
proposed rule (77 FR 842; January 6,
2012; pages 859–860). Based upon the
best available scientific information,
while marine mammals may be
potentially affected by the SURTASS
LFA sonar sounds, we have determined
that these effects are not reasonably
likely to adversely affect the species or
stock through effects on annual rates of
recruitment or survival.
Second, there are three areas
designated as critical habitat for the
Southern Resident killer whale: the
Summer Core Area in Haro Strait and
waters around the San Juan Islands;
Puget Sound; and the Strait of Juan de
Fuca (71 FR 69054, November 29, 2006).
These areas are within 22 km (14 mi; 12
nm) of the Washington coastline and
thus under our criteria are not OBIAs,
but rather fall within the coastal
exclusion zone, where sound pressure
levels will not exceed 180 dB re: 1 mPa.
We also note that sound pressure levels
will not exceed approximately 175 dB
re: 1 mPa at 1 km (0.62 mi; 054 nm)
seaward of the boundary of the OBIA for
the Olympic Coast National Marine
Sanctuary, the Prairie, Barkley Canyon,
and Nitnat Canyon.
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NMFS’ final rule designating critical
habitat for the Southern Resident killer
whale (71 FR 69054, November 29,
2006) did not recognize any offshore
areas (where the Navy could potentially
operate SURTASS LFA sonar) that
might qualify as an OBIA for the
Southern Resident killer whales.
Further, if the Navy were to operate in
offshore areas, where individuals of this
species are present, they would be
protected from sound pressure levels in
excess of approximately 175 dB re: 1
mPa via the Navy’s three-part monitoring
and shutdown/delay protocols.
Finally, the reporting measures in this
regulation require the Navy to provide
us with a notification that includes
reports of injured or dead marine
mammals as well as notification of a
ship strike.
Comment 8: One commenter stated:
‘‘The Administrative Procedure Act
requires agencies such as NMFS to give
a reasonable explanation of their
decisions. This is to prevent agency
decisions from being ‘‘arbitrary and
capricious.’’ In this case, part of the
Navy’s LOA application, and part of the
reasoning of NMFS, is that: (1) ESA
species won’t be additionally affected,
and (2) it is unlikely these effects will
rise past mere harassment. However, as
discussed in this comment, there is
evidence contradicting both of those
statements. We believe that when an
agency fails to at least address
contradictory evidence in its decision
making, those decisions will likely be
too arbitrary and capricious to satisfy
the APA.’’
Response: See our responses to
Comments 3, 4, and 5. While threatened
and endangered marine mammals may
be potentially affected by the SURTASS
LFA sonar sounds, we have determined
that these effects will be limited to Level
B behavioral harassment and are not
reasonably likely to adversely affect the
species or stock through effects on
annual rates of recruitment or survival,
NMFS has also determined this action is
not likely to jeopardize the continued
existence of any endangered or
threatened species under our
jurisdiction or result in the destruction
or adverse modification of critical
habitat.
We included a detailed discussion of
the potential effects of the Navy’s
SURTASS LFA sonar operations on
marine mammals (including threatened
and endangered species), marine
mammal habitat, critical habitat,
compliance with maritime laws, marine
protected areas, and potential
physiological and behavioral effects on
marine mammals in the Federal
Register notice of the proposed rule (77
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FR 842; January 6, 2012). We have
explained the basis for our findings
under 16 U.S.C. 1371(a)(5)(A) and our
implementing regulations to support
issuance of the final rule and Letters of
Authorization to the Navy. We disagree
that our findings in this rulemaking are
arbitrary and capricious.
Acoustic Thresholds for Threshold Shift
Comment 9: One commenter noted
that although the Navy is restricted from
testing sonar within 22 kilometers of
shore and within any Offshore
Biologically Important Area, the Navy
estimates that sonar waves can retain an
intensity of 140 decibels from as far
away as 300 miles (NRDC, Lethal
Sounds).
Response: We refer the commenter to
Appendix C of the 2012 FSEIS/SOEIS
for more detailed information on the
Navy’s modeling of sonar sound waves.
Richardson et al. (1995) stated that it
would be unlikely that any marine
mammal would remain for long in areas
where there was continuous underwater
noise exceeding 140 dB re: 1 mPa. In
fact, the Navy’s Low Frequency Sonar
Scientific Research Program, which
assessed the potential impacts of
SURTASS LFA sonar on the behavior of
low-frequency hearing specialists, noted
no reduction in sighting rates and no
reduction in acoustic detection within
the vicinity of the SURTASS LFA sonar
source vessel during the studies which
lasted for several weeks (DoN, 2001). In
all three phases of the Program (Clark et
al., 2001), most animals showed little to
no response to SURTASS LFA sonar
signals at received levels up to 155 dB
re: 1 mPa, and those individuals that did
show a response resumed normal
activities within tens of minutes. Thus,
avoidance of the greater than 140 dB re:
1 mPa zone of exposure occurred much
less than expected. At this received
level of sound, the Navy’s model for
SURTASS LFA sonar estimates that the
risk of significant change in a
biologically important behavioral is low
(less than one percent).
Behavioral Harassment Threshold
Comment 10: One commenter stated
that the MMPA itself states: ‘‘[T]here is
inadequate knowledge of the ecology
and population dynamics of such
marine mammals and of the factors
which bear upon their ability to
reproduce themselves successfully.’’ 16
U.S.C. 1361(2)(3). Broadly, this
inadequacy seems to be most exposed in
our understanding of Level B
harassment of these creatures by LFA
sonar, which involves such a vast and
as-yet-unknown spectrum of possible
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behavioral responses by the animals to
the technology.’’
Response: We don’t have a perfect
understanding of marine mammal
behavioral responses, but we have
sufficient information (based on
multiple LFA sonar-specific studies,
marine mammal hearing/physiology/
anatomy, and an extensive body of
studies that address impacts from
exposure to other anthropogenic
sources) to be able to assess potential
impacts and design mitigation and
monitoring measures to ensure that the
Navy’s action will avoid the worst
effects and have a negligible impact on
the affected species and stocks. With
this information, we can make the
necessary findings under 16 U.S.C.
1371(a)(5)(A) and our implementing
regulations and can say with confidence
that the Navy’s level of effort, including
its mission planning, adequately offset
the unknowns.
For example, the Navy’s Low
Frequency Sonar Scientific Research
Program (1997–98) assessed the
potential impacts of SURTASS LFA
sonar on the behavior of low-frequency
hearing specialists accounting for three
important behavioral contexts for baleen
whales: foraging, concentrated
migrations, and breeding. The sonar
playback experiments focused on baleen
species: (1) Blue and fin whales feeding
in the southern California Bight, (2) gray
whales migrating past the central
California coast, and (3) humpback
whales breeding off Hawaii. Over the
course of the sonar playback
experiments, the researchers exposed
the marine mammals to received levels
ranging from approximately 120 to 155
dB re: 1 mPa. They detected only minor,
short-term, behavioral responses by
changing their vocal activity, moving
away from the source vessel (Clark et
al., 2001). Post-playback, the whales (in
each case) resumed normal activities
within tens of minutes after the initial
exposure to the SURTASS LFA signal
(Clark et al., 2001).
In the Potential Effects of the
Specified Activity on Marine Mammals
section of the proposed rule (77 FR 842;
January 6, 2012; pages 860–874), we
included a qualitative discussion of the
different ways that SURTASS LFA sonar
operations may potentially affect marine
mammals, which was based on the LFA
sonar-specific study above as well as
many other studies addressing the
impacts of other anthropogenic sources.
Strandings and Mortality
Comment 11: Mass strandings of
marine mammals should haunt this
program, for although direct causal
relationships are difficult to establish
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between the sonar and the strandings,
evidence is not entirely lacking.
Response: See Response to Comment
7.
Offshore Biologically Important Areas
Comment 12: One commenter (who
was also a subject matter expert on the
panel that helped identify OBIAs) felt
that the review process to determine
OBIAs was limited, creating poor
precedent for identifying and protecting
marine mammal habitat. The
commenter described difficulty in
determining how representative the
selected areas for marine mammals were
or how well they reflected the collective
knowledge of a limited number of
solicited individuals.
The NRDC also commented that some
regions had no experts assigned to them
(e.g., Australia); some had only one (e.g.,
offshore Africa and South America) and
suggested that the subject matter experts
nominated only those areas they had
particular knowledge of rather than
attempt a systematic review of an entire
oceanic basin or region.
Response: We appreciate the first
commenter’s efforts in assisting us with
identifying OBIAs for SURTASS LFA
sonar and we believe that we have used
the best available information
(including but not limited to input from
subject matter experts) to identify
OBIAs globally.
We designate OBIAs (based upon
qualifying criteria) to protect marine
mammals in areas that are biologically
important for them. For this process we
used the best available data to assess
ocean areas greater than 22 km (14 mi;
12 nm) from any shoreline with: (1)
High densities of marine mammals; (2)
known/defined breeding/calving
grounds, foraging grounds, migration
routes; or (3) small, distinct populations
of marine mammals with limited
distributions.
To eliminate the potential for
geographic bias in the OBIA selection
process, our initial scoping of potential
OBIAs encompassed a review of 16
marine regions as designated by the
World Commission on Protected Areas
(IUCN World Commission on Protected
Areas—WCPA): Region 3—
Mediterranean; Region 4—northwest
Atlantic; Region 5—Northeast Atlantic;
Region 6—Baltic; Region 7—Wider
Caribbean; Region 8—West Africa;
Region 9—south Atlantic; Region 10—
central Indian Ocean; Region 11—
Arabian Sea; Region 12—East Africa;
Region 13—east Asian Sea; Region 14—
south Pacific; Region 15—northeast
Pacific; Region 16—northwest Pacific;
Region 17—southeast Pacific; and
Region 18—Australia/New Zealand. We
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did not include the polar regions (i.e.,
Regions 1 and 2) in our scoping process
because they are non-operational areas
for SURTASS LFA sonar.
Initially, we reviewed 403 existing
and potential marine protected areas
based on the World Database on
Protected Areas (WDPA) (IUCN and
UNEP, 2009), the Whale and Dolphin
Society’s online Directory of Cetacean
Protected Areas around the World
(2009) based upon Hoyt (2005), and
prior SURTASS LFA sonar OBIAs.
Within that initial review, over 80
percent (340) of the areas were within
22 km (14 mi; 12 nm) of the coastline
and are already included in the coastal
standoff zone, so they did not qualify for
further OBIA consideration. We
screened the remaining areas under our
OBIA criteria and produced a
preliminary list of 27 OBIAs for the
subject matter experts to review.
The subject matter experts with
expertise in geographic regions
including the Atlantic, Pacific, and
Indian Oceans, and the Mediterranean
Sea, provided their individual analyses
of our preliminary list of OBIA
nominees and provided additional
recommendations for additional OBIAs,
resulting in a total number of 73
potential OBIAs. We solicited subject
matter experts for Australia and New
Zealand but were unsuccessful in
finding any volunteers willing to
participate in our process. However, we
independently reviewed the waters
around Australia and New Zealand
(Region 18—Australia/New Zealand)
and suggested two OBIAs: OBIA # 18—
Great Barrier Reef 16° S to 21° S; and
OBIA # 19—Bonney Upwelling/
Southwestern Australia.
To ensure that we ranked the 73
nominated areas consistently, we
screened the nominations for sufficient
scientific support, assigning a rank of
zero (lowest) to four (highest) depending
upon the robustness of the supporting
documentation for the selection criteria.
Our classification methodology appears
on page D–104 of the FSEIS/SOEIS. This
framework we developed ensures that
the information available for each
potential OBIA supports the presence of
the relevant OBIA criteria. Briefly, the
scores are:
• Level 0, Not applicable: Information
does not meet our definition of the
corresponding OBIA criteria or the
OBIA criteria are not applicable.
• Level 1, Not eligible: Insufficient
detail for criteria evaluation or
insufficient detail for high density
specifically.
• Level 2, Eligible: Supporting
information derived from habitat
suitability models (non-peer reviewed),
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expert opinion, regional expertise, or
gray (non-peer reviewed) literature, but
requires more justification.
• Level 3, Eligible: Supporting
information derived from peer-reviewed
analysis, habitat suitability models
(peer-reviewed), or a survey specifically
aimed at investigating and supporting
the corresponding OBIA criteria
provides adequate justification.
• Level 4, Eligible: Supporting
information derived from peer-reviewed
analysis, habitat suitability models
(peer-reviewed), or a survey specifically
aimed at investigating and supporting
the corresponding OBIA criteria
provides strong justification.
In cases where the subject matter
expert did not provide enough support,
we contacted them for additional
supporting information and also
conducted our own re-analysis and
continued review of peer-reviewed
literature to supplement nominations
with little supporting documentation.
Areas that received a score of two or
higher were eligible for further
consideration, which resulted in 45
potential OBIAs. Further consideration
of marine mammal hearing frequency
sensitivity led us to screen out
additional areas that qualified solely on
the basis of their importance for mid- or
high-frequency hearing specialists (e.g.,
dolphins, toothed whales, and beaked
whales that hear best in the midfrequency (150 Hertz to 160 kilohertz)
and high-frequency (200 Hz to 180 kHz)
ranges; low frequency hearing
specialists, such as large baleen whales,
hear best in the low-frequency range of
7 Hz to 22 kHz (Southall, 2007)),
resulting in a list of 22 OBIA nominees
for the Navy’s consideration under a
practicability standard.
The list of 22 OBIAs reflects the
collective knowledge of not only the
subject matter experts but of our own
research, before and after their input,
which consisted of reading: peerreviewed scientific literature; reports
prepared by natural resource agencies in
other countries; reports from nongovernmental organizations involved in
marine conservation issues; and
doctoral dissertations and master’s
theses.
Table 2 presents the geographic scope
of the selected areas in the Proposed
Rule. We also note that some OBIAs
consist of multiple areas within a single
OBIA. Seven of the eight OBIAs for
South America, Australia, and the
Indian Ocean are newly-designated
areas for SURTASS LFA sonar
compared to the previous two
rulemakings.
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TABLE 2—GEOGRAPHIC SCOPE OF THE for marine mammals—an area within
the Southeast Shoal, Grand Bank in the
22 AREAS IN THE PROPOSED RULE
Number
selected
Marine area
Antarctic Convergence Zone ....
Atlantic Ocean—Northwest ......
Atlantic Ocean—Southeast ......
Atlantic Ocean—Southwest ......
Caribbean Sea ..........................
Indian Ocean ............................
Mediterranean Sea ...................
Pacific Ocean—Central/Eastern
Tropical .................................
Pacific Ocean—Northeast ........
Pacific Ocean—Northwest ........
Pacific Ocean—Southeast ........
Pacific Ocean—Southwest .......
1
4
1
2
1
2
1
Total ...................................
22
2
4
1
1
2
The commenter’s assertion that we
did not conduct a systematic review of
an oceanic basin or region is not
accurate. Hoyt (2005) is recognized as a
comprehensive global reference for
identifying marine protected areas for
whales, dolphins, and porpoises, and it
is only logical to use it as a starting
point for our identification of OBIAs
before asking subject matter experts for
additional recommendations. To date,
106 journal articles have cited Hoyt’s 1st
edition. Additionally, several marine
and biological experts have positively
reviewed Hoyt’s efforts as authoritative,
comprehensive, and up-to-date (e.g.,
Sylvia Earle; Edward O. Wilson; Carl
Gustaf Lundin, Head, IUCN Global
Marine and Polar Programme; William
Rossiter, Director, Cetacean Society
International; and one of the subject
matter experts we consulted for the
OBIA process). See https://www.
cetaceanhabitat.org/reviews.php for a
fuller list of reviews.
We compared the 1st and 2nd
editions of Hoyt (2005 and 2011) to
ensure that we did not overlook any
additional areas for consideration.
Appendix F of the 2012 FSEIS/SOEIS
includes the results of our re-analysis of
367 additional areas within the Hoyt’s
(2011) 2nd Edition of Marine Protected
Areas for Whales, Dolphins and
Porpoises for this final rule.
Based on our evaluation of the 367
potential areas within the Hoyt’s (2011)
2nd Edition of Marine Protected Areas
for Whales, Dolphins and Porpoises (see
Appendix F of the Navy’s 2012 FSEIS/
SOEIS), we have added one additional
OBIA, the Abrolhos Bank in the
southwest Atlantic Ocean which is a
breeding/calving area for endangered
humpback whales. The specified period
of this OBIA would be effective August
through November.
We also identified two additional
areas for further consideration as OBIAs
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northwest Atlantic Ocean and an area
within Dogger Bank in the North Sea.
However, because the supporting
information for these specific areas is
limited, we and the Navy are continuing
to gather information to determine
whether these areas meet the OBIA
criteria (see Mitigation section in this
document).
Finally, this final regulation
governing the take of marine mammals
incidental to the Navy’s SURTASS LFA
sonar operations contains an adaptive
management component. This provides
a mechanism for NMFS and the Navy to
modify (or add or delete) mitigation or
monitoring measures, as appropriate,
based on new information. We would
add, modify or delete mitigation or
monitoring measures in consultation
with the Navy if doing so creates a
reasonable likelihood of accomplishing
the goals of mitigation and monitoring
laid out in this final rule. This includes
our continued analysis of the Southeast
Shoal on the Grand Bank and an area
within Dogger Bank in the North Sea
within the first year of this rule.
Comment 13: One commenter
suggested that the expert panel did not
have a role in establishing the screening
criteria (determined in advance by us) to
select potential areas and following the
submission of potential areas by the
subject matter experts. They also
suggested that we unilaterally weighed
the scientific merits of each proposal
and did not afford the expert panel an
opportunity to participate in a group
discussion or decision-making process.
Response: The commenter correctly
noted that the expert panel did not have
a role in either establishing the
screening criteria for OBIAs or the final
decision-making process. The Process
Summary for Expert Input (Appendix
D–3 in the 2012 FSEIS/SOEIS), Stage 1
(c) specifically states that ‘‘NMFS will
incorporate expert input, as appropriate,
to produce the final OBIA nominees,
which will be included for
consideration in the Navy’s 2009 [2011]
draft supplemental environmental
impact statement (DSEIS) for SURTASS
LFA sonar.’’
The purpose of the panel was to
provide scientific information and make
additional, scientifically supportable,
OBIA recommendations based on the
criteria and within the process we set
up after careful consideration of the U.S.
District Court’s opinion and order
granting in part plaintiffs’ motion for
preliminary injunction in NRDC et al. v.
Gutierrez et al., 2008 WL 360852
(N.D.Cal.).
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Comment 14: NRDC and one other
commenter suggested that the OBIA
process failed to include habitat
suitability or density modeling for
marine mammals to confirm or,
crucially, augment the information
acquired from the subject matter
experts.
Response: We recognize that baseline
data on the distribution and behavior of
marine animals are limited for certain
areas of the world’s oceans. During our
OBIA designation process, we
instructed the subject matter experts to
use predictive habitat or density models
in their review process if appropriate.
Regarding our use of habitat suitability
or density modeling, we have used
results from habitat-based density
modeling to supplement information
provided by the subject matter experts.
For example, we considered habitatbased density modeling from Barlow et
al. (2009) in determining whether an
area within the Southern California
Bight, including Tanner and Cortes
Banks, met our OBIA criteria as an area
of blue whale concentration.
For offshore areas (those not
associated with coastal areas or within
a particular countries’ exclusive
economic zone) we agree that the data
are lacking. In these data-poor scenarios
there is debate about whether decision
makers should use predictive models to
forecast patterns in distribution or
density in wide-ranging and
heterogeneous areas (Praca et al., 2009).
Most models that relate cetacean
distribution or population density to
environmental factors are based on
easily measured environmental proxies
that substitute for the ultimate physical,
biological, historical, or behavioral
factors that interact to produce the
observed patterns in cetacean habitat
use. The relationship between a given
proxy and the underlying ecological
mechanism that it represents is likely to
be region-specific and might vary among
species in a given region. Furthermore,
the functional relationship defined by a
proxy is likely to depend upon the
spatial and temporal scale of the
ecological phenomenon that it
represents. Therefore, we should use
caution when extrapolating
relationships between a proxy and
cetacean distribution or density from
one study area to another that differs in
size or geographic location (Ferguson et
al., 2010).
Model validation (defined as
comparing model fit or predictions to
the data upon which the model was
built or to a novel data set) is a critical
component of cetacean-habitat
modeling. If the model’s fitted or
predicted values are largely biased or
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imprecise, the model cannot reliably
inform a question that it is designed to
address. For scenarios in which
cetacean distribution or density data are
scarce or completely lacking, such as in
open ocean areas outside of the United
States, our ability to quantitatively or
qualitatively validate cetacean-habitat
model predictions may be limited or
biased. In these situations, model
validation must rely on multiple sources
of scientific knowledge (including, but
not limited to: Personal observations of
distribution and density; known
migration routes; ecosystem dynamics,
such as inter-specific competition;
seasonality and environmental regime
shifts; live strandings; range expansions
or contractions due to changes in
population size; and historic whaling
data) or indigenous/local knowledge
(Ferguson et al., 2010).
While predictive models can indicate
regions with physical properties that
might have relatively high probabilities
of species occurrence, the actual
abundance/density estimates for the
region are often not known. Predictive
models are only as good as the input
data and the relationships between
animal abundance/density and physical
properties. Thus, they must have robust
data to accurately predict relationships
between animal abundance and/or
density and physical properties. Outside
of U.S. waters, some available models
may not be robust enough to predict a
species’ true niche due to inter-specific
and intra-specific dynamics and
interactions with the physical
environment.
Regarding the second point, we did
not rely solely on the subject matter
experts (see our responses to Comments
12 and 13). The subject matter experts’
inputs were a crucial component of our
selection processes; however, they were
only one component. We as the action
agency are responsible for the final
selection of the SURTASS LFA sonar
OBIAs. Because we independently
evaluated the subject matter expert’s
input as well as available data/
information for each recommended
OBIA, we do not believe that effort bias
on the part of the subject matter experts
was a factor in our determinations.
In areas not designated as an OBIA
(either because they did not meet the
criteria or because there weren’t
sufficient data to support the
designation), the regulation provides
mitigation and monitoring measures
that protect marine mammals
nevertheless. The regulation requires
the Navy to: (1) Restrict operations of
SURTASS LFA sonar such that the
sound field does not exceed 180 dB re:
1 mPa within 22 km (14 mi; 12 nm) of
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50301
any coastline; (2) Conduct visual,
passive acoustic, and active acoustic
monitoring; and (3) Perform delays/
shutdown protocols of active LFA sonar
transmissions when monitoring detects
a marine mammal effectively ensuring
that marine mammals are not exposed to
sound levels that exceed approximately
175 dB re: 1 mPa.
In addition to the Navy’s required
mitigation and monitoring protocols,
their annual application to us for LOAs
will use a sensitivity/risk assessment
process to assess potential impacts to
marine mammals (DoN, 2002; 2003;
2004; 2005; 2006). This process starts
with the Navy reviewing the proposed
mission areas and includes: (1) Data
collection and analyses for marine
mammal abundances/densities; (2)
spatial/temporal analyses for potential
geographic restrictions/migration
corridors/habitat preferences; (3)
mission area changes/refinements as
required; (4) risk analysis/estimates; and
(5) determination on the viability of a
mission area based on potential marine
mammal impacts. As with the 2002 and
2007 rules, the Navy will limit
operation of SURTASS LFA sonar to
ensure that no more than 12 percent of
any marine mammal stock would be
taken by Level B harassment annually,
over the course of this five-year
regulation. This annual per-stock cap
applies regardless of the number of
SURTASS LFA sonar vessels operating.
The Navy will use the 12 percent cap to
guide its mission planning and annual
authorization applications to the
greatest extent feasible considering
national security tasking.
We and the Navy recognize that
available information regarding marine
areas will evolve over the next five years
and these regulations include an
adaptive management component to
account for new data. This provides a
mechanism for NMFS and the Navy to
modify (or add or delete) mitigation or
monitoring measures, as appropriate,
based on new information. We would
add, modify or delete mitigation or
monitoring measures in consultation
with the Navy if doing so creates a
reasonable likelihood of accomplishing
the goals of mitigation and monitoring
laid out in this final rule. We and the
Navy will meet annually (if deemed
necessary by either agency) to discuss
the monitoring reports, Navy research
and development outcomes, current
science, and to determine whether
mitigation or monitoring modifications
are appropriate.
Comment 15: The NRDC and one
other commenter suggested that NMFS
had established an unreasonably high
bar for further consideration of OBIAS,
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rather than a precautionary approach,
even for areas where very little survey
data are available. They also took issue
with the proposed rule establishing only
21 discrete OBIAs within an area of
operations that includes nearly all of the
Atlantic, Pacific, and Indian Oceans and
the Mediterranean Sea and suggested
that we: did not advance most of the
recommended areas to the Navy for
discussion regardless of practicability;
gave little weight to expert opinion;
reviewed the first edition of Hoyt’s
(2005) Marine Protected Areas for
Whales, Dolphins, and Porpoises and
relied heavily upon the experts to
supply additional information; and did
not consider areas with rankings of
‘‘two’’ even if they featured baleen
whale habitat.
Response: See our response to
Comment 12 for a description of our
evaluation process and pages 877–878
in the Federal Register notice of the
proposed rule (77 FR 842; January 6,
2012). Table 2 (in Response to Comment
12) presents information on the
geographic scope of the OBIAs. For this
rulemaking, we have designated more
than double the number of OBIAs in
previous rulemakings for SURTASS
LFA sonar, and more than 60 percent of
these OBIAs are outside of U.S. waters.
Contrary to NRDC’s assertion, we
forwarded all of the subject matter
experts’ recommended areas (including
those that did not qualify under the
selection criteria) to the Navy for
discussion. During each phase of the
OBIA scoping process, the Navy had
access to the following: Our initial
screening matrix of 403 potential areas
in the world; the potential 27 areas that
we presented to the subject matter
experts for review; the 73 potential
OBIAs recommended by us, the experts
and the Navy; the 45 areas resulting
after we screened them for adequate
scientific support (i.e., areas with a
score of 2 or higher for at least one
eligibility criteria); and the 22 areas that
remained after screening for hearing
specialization. The ‘‘bar for further
consideration’’ the commenter refers to
was our requirement that the
description of the area recommended by
an expert contain enough information
for us to verify that it met our criteria.
In cases where justification from subject
matter experts was limited, we and the
Navy conducted additional literature
reviews to search for further support for
those potential OBIA nominees. The
practicability inquiry is immaterial if
the area does not meet our standards for
an OBIA in the first place.
In fact, based upon our continued reanalysis of the world’s oceans, we have
designated one additional OBIA
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(Abrolhos Bank in the southwest
Atlantic Ocean) in addition to the 22
that we proposed.
We disagree that our process set an
unreasonably high bar for further
consideration and we recognize that
many areas throughout the world’s
oceans have little data to support an
OBIA designation at this time. The
regulation’s adaptive management
provision allows us and the Navy to reevaluate areas during the annual request
for LOAs as new information becomes
available. We will continue to conduct
literature reviews and use robust habitat
modeling results to support our
reconsideration of these data-poor areas;
and would consider modifying
geographic restrictions as appropriate.
In the meantime, the other protective
measures in this regulation will be in
effect.
Although habitat is a contributing
factor to supporting our biological
criteria for OBIAs, we did not base our
recommendations on areas that solely
feature baleen whale habitat. For areas
based on habitat suitability models
(non-peer reviewed), expert opinion,
regional expertise, or gray literature (i.e.,
non-peer reviewed studies), we ranked
these areas as a two (Eligible: Requires
More Justification). Contrary to the
commenter’s assertion, under our
classification methodology, we
considered areas with a rank of two or
higher as eligible for consideration as an
OBIA for SURTASS LFA sonar
operations. Thus, we included the
subject matter expert’s submitted areas
within the initial screening for OBIA
candidates. Many of these
recommended areas did not meet our
additional screening criterion for lowfrequency hearing specialization.
The commenter’s assertion that we
did not conduct a systematic review of
an oceanic basin or region is not
accurate. Hoyt (2005) is recognized as a
comprehensive global reference for
identifying marine protected areas for
whales, dolphins, and porpoises. It was
a logical starting point for our
identification of OBIAs. Later, we
compared the 1st and 2nd editions of
Hoyt (2005 and 2011) to ensure that we
did not overlook any additional areas
for consideration. We provide the
results in Appendix F of the 2012
FSEIS/SOEIS. Based on that review, we
have designated the following
additional OBIA: Abrolhos Bank off the
Brazilian Coast in the southwest
Atlantic Ocean for humpback whales
effective August through November.
Further, we and the Navy are
continuing to gather current supporting
information to continue to review the
Southeast Shoal area, Grand Bank in the
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northwest Atlantic Ocean and Dogger
Bank in the North Sea under the OBIA
criteria. Because the Navy does not
intend to operate within the northwest
Atlantic Ocean or North Sea this year,
we and the Navy will make a decision
on this area as a potential OBIA within
the first year of this rule under the
adaptive management framework.
To reiterate, we incorporated expert
input, as appropriate, to produce the
proposed OBIAs (see Comment 12). The
commenter’s statement about ‘‘heavy
reliance on experts’’ disregards the
extensive analysis that we and the Navy
conducted during the initial phase of
the identification process as well as our
continual efforts to update information
on potential OBIAs during the rule
making for this regulation.
Comment 16: The NRDC stated that
for at least one major area that
remained, we failed to consider more
limited forms of mitigation when a
complete exclusion was deemed
impracticable, a failure that led to a
complete lack of additional protection
for the Southern California Bight.
Response: We designate OBIAs to
protect marine mammals. OBIAs are not
intended to protect areas per se. Also,
the comment ignores the required
mitigation and monitoring measures for
any Navy SURTASS LFA sonar
activities within the area, which will
provide protection for marine mammals.
We note that within the Southern
California Bight, we require the Navy to
limit the SURTASS LFA sonar sound
field so that it does not exceed 180 dB
re: 1 mPa within 22 km (14 mi; 12 nm)
of any coastline, including offshore
islands such as San Clemente and San
Nicolas Islands, and the Channel Islands
National Marine Sanctuary. This would
include additional protections for
smaller areas within the Southern
California Bight such as the San
Clemente and San Nicholas Islands.
Also, the Navy will restrict SURTASS
LFA sonar operations in the vicinity of
known recreational and commercial
dive sites to ensure that the sound field
at such sites does not exceed received
levels of 145 dB re: 1 mPa. Within the
Southern California Bight, the Navy has
designated Tanner and Cortes Banks
and the Channel Islands National
Marine Sanctuary, as recreational dive
sites.
Since the publication of the proposed
rule, we have consulted with the Navy
on the practicability of finding other
means of limiting SURTASS LFA sonar
activities within the Southern California
Bight to reduce adverse effects to marine
mammals without impacting operations.
The Navy is not currently planning to
use the SURTASS LFA sonar system in
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the Southern California Bight. If the
Navy were to plan use of SURTASS LFA
sonar per the 2012 FSEIS/SOEIS, the
Navy would include the details of that
plan in their LOA application for the
applicable year. At that time, we and the
Navy would discuss what, if any, other
measures are appropriate in light of the
projected use of SURTASS LFA sonar
and relevant current information
available for the species potentially
affected by that use.
Comment 17: The NRDC stated: ‘‘The
result of all this is to establish only 21
offshore biologically important areas—
21 areas within an MMPA application
that encompasses 70–75 percent of the
world’s oceans, including almost the
entirety of the Atlantic, Pacific, and
Indian Oceans and the Mediterranean
Sea. In its 2002, 2003, and 2008
opinions on SURTASS LFA, the District
Court repeatedly emphasized the
importance of geographic mitigation to
reduce impacts from the LFA system,
the need to ensure meaningful inclusion
of OBIAs throughout the LFA operating
area, and the agencies’ obligation to
affirmatively identify and protect
marine mammal habitat. The agencies’
draft approach to designating OBIAs—
which leaves most of the Navy’s
operating area unrepresented and shifts
much of the burden for justifying
individual areas to experts—does not
satisfy the requirements of NEPA and
MMPA or the Court’s concerns.
Response: Under the regulation, the
total area that would be available for
SURTASS LFA sonar operations over
the five-year period is about 70–75
percent of the world’s oceans. This in
no way equates to SURTASS LFA sonar
operations affecting even close to 70–75
percent of the world’s ocean areas
during any given annual period for the
LOAs. Based on its annual projected
operational needs, the Navy will
identify the particular geographic areas
in which it intends to operate its four
SURTASS LFA sonar vessels. In doing
so, the Navy considers marine mammal
habitats, seasonal activities, and
behavioral activities during the process
of determining potential mission areas
and, to the greatest extent feasible
considering national security tasking,
avoids planning and conducting
SURTASS LFA sonar operations in
areas of known high marine animal
densities (i.e., hot spots). Also, in
performing mission planning for its
annual LOA applications the Navy
would limit operation of SURTASS LFA
sonar to ensure that no more that 12
percent of any marine mammal stock
would be taken by Level B harassment
annually, over the course of this rule.
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We believe that our OBIA analysis
was comprehensive (see Comments 12
and 14). We and the Navy conducted
separate bibliographic research to look
for OBIA candidates in all potential
operating areas, even before involving
the subject matter experts in our
process. And in all cases, we not only
applied biologically-based criteria but
also required a minimum level of
supporting scientific documentation to
designate an area as an OBIA.
In designing the OBIA selection
process for this rulemaking, we
carefully considered and took into
account the articulated concerns of the
U.S. district court and believe the
process addresses those concerns.
Recognizing that many areas throughout
the world’s oceans currently have few
data to support an OBIA designation at
this time, we and the Navy will
continue to conduct literature reviews
under the adaptive management
provision of this regulation.
Comment 18: The NRDC stated:
‘‘Offshore biologically important areas
(OBIAs) lie at the core of the proposed
rule, representing the sole difference
between the new preferred alternative
and the one selected by the agencies
during the 2007 SEIS and rulemaking
processes, and ultimately rejected by the
Court. DSEIS at 2–11 to 2–13. Obtaining
sufficient data on potential OBIAs
throughout the Navy’s entire proposed
operating area is therefore critical.
NRDC v. Gutierrez, Case No. 07–4771–
EDL, 2008 WL 360852 at *7 (N.D. Cal.
2008) (‘‘* * * having chosen not to
confine operations to relatively sterile
areas of the ocean and seasons of the
year and to reduce the coastal exclusion
zone, the Secretary must make a serious
effort to investigate plausible candidates
for OBIAs’’).’’
Response: See Comments 12 and 14.
We conducted a detailed, global
evaluation for OBIA candidates. Our
responsibility under 16 U.S.C.
1371(a)(5)(A) and our implementing
regulations is to prescribe the means of
effecting the least practicable adverse
impact, which involves consideration of
impacts on military readiness training
and operations. To that end, we, in
coordination with the Navy, developed
a suite of mitigation measures for this
and previous rulemakings. OBIAs are an
important component, but they are by
no means the only one or the ‘‘core’’
mitigation measure. The U.S. district
court, in litigation over our previous
rule, took issue with our process for
identifying and designating OBIAs. We
have remedied the identified deficiency.
Comment 19: The NRDC stated that
despite the lack of available density
information for most locations and
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regions, we did not provide density
modeling for any area beyond the
United States. They also advocated the
use of existing habitat suitability and/or
density models, such as the one
licensed by St. Andrews University’s
Sea Mammal Research Unit (SMRU).
Response: As the NRDC letter notes,
the Navy, under license agreements
with St. Andrews University’s Sea
Mammal Research Unit and Dr. Kristin
Kaschner, developed a preliminary
database of marine mammal density
estimations for the Navy’s areas of
responsibility that are the result of
habitat suitability predictive modeling.
For their environmental compliance
efforts for mid-frequency active sonar
training, the Navy uses a hierarchy of
desired methods to estimate marine
mammal density in the areas where they
plan to train. The St. Andrews/Kaschner
methodology is the least preferred
method (used only when nothing else is
available), with habitat-based density
estimates and stratified density
estimates being the first and second
method of choice. However, for helping
to estimate density, it is better than
simply spreading an abundance
estimate across the entire ocean since it
considers species extent and attempts to
characterize relative occurrence. As
noted in our response to Comment 14,
methods that extrapolate significantly
past the areas where marine mammal
surveys have actually been conducted
and into ecologically different regions
are far less likely to be accurate. While
the Navy’s groundtruthing exercises
have shown the model to be relatively
accurate for predicting most Atlantic
species within a few hundred miles of
the Atlantic Coast, they found the model
inaccurate off the Pacific Coast and have
not been able to validate the model in
any other areas.
Density estimates are necessary for
the Navy to estimate take. The St.
Andrews estimates serve as the least
preferred option for calculating take for
the Navy’s mid-frequency active sonar
training activities. However, for the
reasons noted above, this method for
estimating density does not produce
estimates that are considered robust or
accurate enough to support the
designation of OBIAs under our criteria
and requirements.
Comment 20: The NRDC and several
other commenters recommended that
we consider the approach of using
proxies such as: persistent
oceanographic features (e.g., high
primary productivity and nutrient
enrichment processes); relative densities
of non-marine mammal species (i.e.,
apex predators and fish); all continental
shelf waters and waters 100 km (62 mi)
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seaward of the continental slope; waters
within 100 km (62 mi) of all islands and
seamounts that rise within 500 meters
(1,640 feet) to identify marine mammal
hotspots or supplement our OBIA
analysis in data-poor regions.
Response: OBIAs are but one
component of a suite of required
mitigation and related monitoring
measures designed to effect the least
practicable adverse impact on marine
mammals. The regulation prescribes
mitigation and monitoring measures for
SURTASS LFA sonar operations in
areas that have persistent oceanographic
features and seamounts and island
chains that did not meet our OBIA
criteria or fall within the 22 km (14 mi;
12 nm) coastal exclusion zone. The
Navy is to delay/shutdown active
SURTASS LFA sonar transmissions
when they detect a marine mammal
within the 2-km (1.2-mi; 1.1-nm) LFA
sonar mitigation and buffer zones
around the vessel by visual, passive
acoustic, and active acoustic monitoring
protocols, effectively ensuring that
marine mammals are not exposed to
sound levels that exceed 175 dB re: 1
mPa.
Our process for selecting, assessing,
and designating OBIAs for SURTASS
LFA sonar relies on three specific
screening criteria for biological
importance for marine mammals. These
include areas with: (a) High densities of
marine mammals; or (b) known/defined
breeding/calving grounds, foraging
grounds, migration routes; or (c) small,
distinct populations of marine mammals
with limited distributions. Additionally,
the area must be 22 km (14 mi; 12 nm)
seaward of any coastline. The
commenters’ recommendations do not
meet the criteria we established.
That said, we recognize that the
ecological processes recommended by
the commenters support cetacean
habitats and have considered their
guidance in reviewing and designating
OBIAs. Information regarding data poor
areas is likely to evolve over the fiveyear course of the final rule and beyond,
and NMFS will consider new
information to continue identifying
OBIAs for SURTASS LFA sonar
operations. Under our adaptive
management framework, we will
consider these factors along with our
selection criteria to consider future
modifications to the OBIA list. This
provides a mechanism for NMFS and
the Navy to modify (or add or delete)
mitigation or monitoring measures, as
appropriate, based on new information.
We would add, modify or delete
mitigation or monitoring measures in
consultation with the Navy if doing so
creates a reasonable likelihood of
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accomplishing the goals of mitigation
and monitoring laid out in this final
rule.
As a part of our global OBIA selection
process, we reviewed continental shelf
and slope areas and have designated
OBIAs located on the northeast U.S.
continental, northwest U.S. continental,
Patagonian, Bahamian, Madagascar, east
Brazilian, the northeast Australian, the
southeast Australian, the Sakhalin
Island, and the southeast U.S.
continental shelves or slopes.
In our review of areas with enhanced
productivity associated with seamounts,
we have designated seven OBIAs which
meet the commenters’
recommendations. These areas include
the Silver and Navidad Banks and the
Abrolhos Bank in the Atlantic Ocean;
the Costa Rica Dome; the Prairie,
Barkley, and Nitnat Canyons; Davidson
Seamount within the Monterey Bay
National Marine Sanctuary; and
Penguin Bank in the Pacific Ocean; and
Walters Shoal in the Indian Ocean.
Finally, over half of the OBIAs are
located in areas categorized as Class I,
highly productive or Class II,
moderately productive ecosystems
based on SeaWiFS global primary
productivity estimates (NOAA, 2012).
In areas that are not designated an
OBIA, the standard operational
mitigation and monitoring measures
will apply wherever the Navy operates
SURTASS LFA sonar. These required
mitigation and monitoring measures and
delay/shutdown protocols will ensure
that marine mammals are not exposed to
sound levels that exceed approximately
175 dB re: 1 mPa.
Comment 21: The NRDC
recommended the Transition Zone
Chlorophyll Front north of the Hawaiian
Islands as an example likely to represent
important habitat for cetacean species
based upon persistent oceanographic
features and relative densities of nonmarine mammal species. They also
stated that the size of some of these
areas is not in itself a reasonable bar
against designating them as an OBIA.
Response: See response to Comment
20.
With regard to the Transition Zone
Chlorophyll Front north of the Hawaiian
Islands, several studies have reported
that northern fur seals, Dall’s porpoises,
northern right whale dolphins, and
Pacific white-sided dolphins occur as
bycatch in squid driftnets in the region
(Baba et al., 1993; Buckland et al., 1993;
Yatsu et al., 1993). Applying our OBIA
criteria, we found no supporting
information that these species are
present in high densities or that they
use this area in concentrated numbers
for foraging, breeding/calving, or
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migration. Nor are these species a small
distinct population within the area.
Furthermore, these species are not
categorized as low frequency hearing
specialists. At this time, the data are not
sufficient to consider the Transition
Zone Chlorophyll Front as an OBIA.
With regards to the second point
related to the size of a potential OBIA,
see our Response to Comment 17. We
note that several of the OBIAs including
the Costa Rica Dome (year-round
restriction), Georges Bank (year-round),
and the Antarctic Convergence Zone
(October through March), and the
Bonney Upwelling (December through
May), have persistent oceanographic
features and are quite large in size.
Comment 22: The NRDC stated: ‘‘the
DSEIS explicitly rejects Challenger
Bank, an area that has repeatedly been
shown to seasonally host humpback
whales on their northward migration, on
the grounds that ‘‘the available sighting
data and information are insufficient to
clearly demonstrate that the Challenger
Bank individually is the most
significant biologically important area
in Bermudian waters for humpback
whales DSEIS at D–81.’’
Response: DSEIS subchapter 4.5.2.3
on the Challenger Bank (Bermuda) OBIA
did not adequately describe the
justifications for excluding this area as
an OBIA. The Navy has revised this
section of the 2012 FSEIS/SOEIS based
upon re-analysis of this area.
Briefly, Challenger Bank did not
qualify under the foraging criterion for
humpback whales. Also, the waters off
the Bank did not qualify as a defined
migration route even though there are
anecdotal observations of whales
transiting near the Bank. As noted in
our original analysis of the area, Stone
et al. (1987) hypothesized that
humpback whales may feed in
Bermudian waters and suggested the
possibility that humpback whales feed
at Bermuda while transiting northward.
Other peer-reviewed articles (Clapham
and Mattila, 1990; Baraff et al., 1991)
repeated Stone et al.’s (1987) hypothesis
but did not provide additional specific
and sufficient scientific justification to
support our selection of this area as an
OBIA at this time.
Comment 23: The NRDC stated: ‘‘The
proposed Dogger Bank OBIA was shown
in a survey of the German exclusive
economic zone to contain ‘‘fairly high’’
densities of harbor porpoises, is
associated with several oceanographic
features relevant to marine mammal
distribution (e.g., a submerged sandbar),
and has been proposed by the German
government as an MPA, yet is
unaccountably accorded a ‘‘one’’ on
NMFS’ scale. DSEIS at D–286. NMFS
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should review its low ranking of areas
such as Dogger Bank.’’
Response: We have re-analyzed our
ranking for the Dogger Bank area for
harbor porpoises. To clarify, this is an
area that we independently evaluated
and considered as a potential OBIA for
harbor porpoises. Further consideration
of marine mammal hearing frequency
sensitivity led us to screen out Dogger
Bank as an OBIA for SURTASS LFA
sonar because harbor porpoises are midfrequency hearing specialists.
Germany’s Federal Agency for Nature
Conservation conducted aerial surveys
within the German exclusive economic
zone and 12 nautical mile zone to assess
proposed Sites of Community
Importance under the European Union
Habitats Directive. They reported that
the north-east survey area of the Dogger
Bank Special Area of Concern (SAC), off
the North Friesian islands of Sylt and
Amrum, showed the highest mean
summer densities (2.75 individuals per
square kilometer (indiv./km2) in 2002
and 3.7 indiv./km2) of harbor porpoises
(Gilles, Herr, Lehnert, Scheidat, &
Siebert, 2008). These areas fall under
this regulation’s coastal standoff
restriction that requires the Navy to
restrict operation of SURTASS LFA
sonar such that the sound field does not
exceed 180 dB re: 1 mPa within 22 km
(14 mi; 12 nm) of any coastline and as
a result we did not consider these areas
for OBIA status.
In 2010, the Joint Nature Conservation
Committee (JNCC) re-evaluated the
Dogger Bank SAC according to the
European Habitats Directive selection
criteria and guiding principles in
response to scientific questions on the
site’s justification for harbor porpoises.
They concluded that the data indicated
that there is no difference in occurrence
of harbor porpoise within the Dogger
Bank SAC (identified for its sandbank
habitat) compared to outside the SAC
(JNCC, 2010). They also concluded that
there is not ‘‘good population density
(in relation to neighboring areas) and
that the Dogger Bank SAC cannot be
considered a ‘‘clearly identifiable area
essential to the life and reproduction’’ of
harbor porpoise, and that therefore the
species should not be a qualifying
feature for the site (JNCC, 2010).
Based on the best available
information, we arrived at similar
conclusions that the area is not eligible
as an OBIA for harbor porpoises under
the high density criterion at this time.
Moreover, there is not enough
information at this time to support
designation of this area as an OBIA for
low-frequency hearing specialists. We
will continue to monitor and re-evaluate
this area under the adaptive
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management framework as researchers
complete additional surveys on Dogger
Bank within the next few years. We and
the Navy will make a decision before
issuing the second annual LOAs
regarding whether this area meets the
OBIA criteria and, if so, can be
practicably implemented
Comment 24: The NRDC stated:
‘‘Given the extent of the area available
for LFA operations, the lack of
comparative density data in most parts
of the world, and NMFS’ express
reliance on experts, it is reasonable for
the agencies to consider the
practicability of recommended OBIAs
that score a ‘‘one’’ or above on NMFS’
scale.’’
Response: See Comment 12. The
description of the area should contain
enough information for us to verify that
it met our defining criteria, because in
our view it is not appropriate to
designate OBIAs without sufficient
scientific justification. Also, we discuss
the classification methodology for all
OBIA rankings in the 2012 FSEIS/SOEIS
subchapter 4.5.2 and pages D–104 and
D–225.
Comment 25: The NRDC stated: ‘‘Yet
NMFS has effectively shifted the burden
of identifying OBIA to its volunteer
experts, appearing to have screened out
areas where its experts did not supply
‘‘sufficient’’ information even though
additional information might be
available. For the Gulf of Mexico, where
NMFS’ expert recommended the
inclusion of slope waters between the
200 m and 1000 m depth contours, the
agency merely listed the ‘‘background’’
information that the expert provided,
and without explanation gave the area
two disqualifying ‘‘ones’’ for ‘‘high
density’’ and ‘‘foraging’’ and ‘‘zeroes’’ in
every other habitat category. SDEIS at
D–290. Even supposing arguendo that
these rankings were reasonable, the
agency apparently did not compile other
information that might support the
recommendation, even though such
information was readily available, nor
did it consider on its own any
alternative areas in the Gulf, including
parts of the recommended OBIA, that
might have additional support. Cf., e.g.,
Appendix B to this letter. Instead,
NMFS appears to have relied entirely on
its expert to define the OBIA boundary
and justify it. That form of burdenshifting is not acceptable.’’
Response: See Comments 12 and 15.
We, along with the Navy, again
reviewed the latest and best available
scientific information and could not
locate adequate information to support
designation of an OBIA for SURTASS
LFA sonar between the 200- and 1,000m depth contours in the Gulf of Mexico
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(see Appendix F of the 2012 FSEIS/
SOEIS). At this time, we believe that
assigning a rank of one (Not Eligible:
Insufficient Information) for the 200and 1,000-m (656 and 3,281 feet) depth
contours in the Gulf of Mexico is
reasonable and based on the best
available science.
Several papers noted that most marine
mammal species had a wide spatial
distribution along the slope as well as
a wide temporal distribution (Mullin et
al., 1991; Davis et al., 1998;
Baumgartner et al., 2001). Also, the
inter-annual variability of the
Mississippi River discharge itself may
also have significant impact on sperm
whale distributions along the 1,000-m
isobath between Mississippi Canyon
and De Soto Canyon (Jochens et al.,
2008).
The basic unit of sperm whale social
organization is the breeding or mixed
herd consisting of mature females,
juveniles of both sexes, and calves.
Studies have reported aggregations of
female and mixed juvenile/calf groups
commonly sighted around the
Mississippi Canyon in summer 2004
(Thomsen et al., 2011). Conversely, in
summer 2005, Jochens et al. (2008)
observed only lone/bachelor males
around the Mississippi Canyon and did
not observe any mixed herds (Thomsen,
et al., 2011). Regarding the inter-annual
differences in sighting between the two
surveys, Jochens et al. (2008) noted that
they observed no members of the mixed
groups ‘‘core population’’, which could
be caused by changing oceanographic
conditions between the two surveys as
the Mississippi River’s 2005 discharge
level was 59 percent of the average
summer monthly outflow.
Until such time that more robust
information becomes available that
supports the biological criteria (i.e.,
marine mammals present in high
densities or an area on the slope with
known/defined breeding/calving
grounds, foraging grounds, migration
routes, or an area with small, distinct
populations of marine mammals with
limited distributions) on the continental
slope of the northern Gulf of Mexico, we
do not designate this area as an OBIA
for SURTASS LFA sonar operations.
However, within our adaptive
management framework, we will
consider new information during the
five-year period of this regulation to
consider future modifications to the
OBIA list. This provides a mechanism
for NMFS and the Navy to modify (or
add or delete) mitigation or monitoring
measures, as appropriate, based on new
information. We would add, modify or
delete mitigation or monitoring
measures in consultation with the Navy
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if doing so creates a reasonable
likelihood of accomplishing the goals of
mitigation and monitoring laid out in
this final rule.
If SURTASS LFA sonar operations
were to occur on the continental slope
of the northern Gulf of Mexico, marine
mammals present in the operational
area are protected by the Navy’s
mitigation protocols, including: (1)
Restricting operations of SURTASS LFA
sonar such that the sound field does not
exceed 180 dB re: 1 mPa within 22 km
(14 mi; 12 nm) of any coastline; (2)
Conducting visual, passive acoustic, and
active acoustic monitoring; (3)
Performing delays/shutdown protocols
of active LFA sonar transmissions when
monitoring detects a marine mammal,
which effectively ensures marine
mammals will not be exposed to sound
pressure levels greater than
approximately 175 dB; and (4)
Performing mission planning for annual
Letters of Authorization applications.
Comment 26: The NRDC stated: ‘‘The
agency incorrectly assumes that certain
established or proposed MPAs and
recommended OBIAs are located
entirely within 12 nm of shore. For
example, the Papahanaumokuakea
Marine National Monument was
apparently excluded early in the OBIA
process on the assumption that it does
not extend seaward of that distance,
which is incorrect.’’
Response: We concur that the
Papahanaumokuakea (Northwestern
Hawaiian Islands) Marine National
Monument boundaries extend seaward
of the 22-km (12-nm) coastal standoff
zone. However, areas noted for breeding
or wintering of low-frequency hearing
specialists are within the coastal
standoff zone and are not located
outside of any portion of the Monument
seaward of the coastal standoff zone.
Thus, there is not enough information to
support designation around any islands
outside the 22 km (14 mi; 12 nm) coastal
standoff zone at this time.
Johnston et al. (2007) modeled the
extent and spatial location of humpback
whale wintering habitat across the
Hawaiian Archipelago, using
bathymetry and averaged sea surface
temperature data. Using the data, they
produced polygons identifying areas
shallower than 200 m and warmer than
21.1°C as potential wintering habitat. To
ground-truth their data, they also
conducted a pilot survey across the
Northwest Hawaiian Islands and
reported nine sightings of humpback
whales (n = 19) during the 15-day
cruise, including three groups with
small calves or exhibiting breeding
behaviors. All of the sightings occurred
in warm, shallow water at or within
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their predicted habitat regions. They
detected humpback whales on the
shallow banks surrounding Nihoa
Island, Necker Island, Gardner
Pinnacles, Maro Reef, and Lisianski
Island (Johnston et al., 2007). Based on
the best available information, this area
that extends seaward of the 22-km (14mi; 12-nm) coastal standoff zone does
not qualify as an OBIA for SURTASS
LFA sonar.
Comment 27: The NRDC stated that
we did not consider the following areas
in our OBIA analysis: (1) Areas of
Increased Awareness designated by the
Navy in the Atlantic Fleet Active Sonar
Training EIS; (2) areas identified in Hoyt
(2011); (3) areas referenced in the
previous LFA sonar rulemakings; (4)
important habitats in the Northwest
Pacific Ocean and in the Gulf of Mexico;
(5) areas off the main Hawaiian Islands;
(6) areas in southeast Alaska that the
SPLASH project identified as seasonal
habitat or migration corridors for
humpback whales; and (7) the North
Atlantic right whale migration corridor.
Response: Following is a summary of
our consideration of the areas identified
by the commenter. See responses to
comments in Chapter 7 of the Navy’s
2012 FSEIS/SOEIS for detailed
information on our analyses.
• Areas of Increased Awareness: The
commenter’s assertion is inaccurate.
First, several of the Areas of Increased
Awareness are protected by the coastal
standoff restriction where we require
the Navy to limit the SURTASS LFA
sonar sound field so that it does not
exceed 180 dB re: 1 mPa within 22 km
(14 mi; 12 nm) of any coastline. Second,
several of these areas are within OBIAs
1, 3, and 4, which include the North
Atlantic right whale critical habitat
areas as well as areas in the Gulf of
Maine, the Great South Channel,
Georges Bank, and the southeastern U.S.
right whale seasonal habitat.
• Hoyt (2011): We compared the 1st
and 2nd editions of Hoyt (2005 and
2011) to ensure that we have not
overlooked any additional areas for
consideration. The results are in
Appendix F of the Navy’s 2012 FSEIS/
SOEIS. Based on that review and after
discussion with the Navy, we have
designated an additional OBIA: the
Abrolhos Bank off the Brazilian Coast in
the Southwest Atlantic Ocean.
• Habitat in the Northwest Pacific
Ocean: Even though there is evidence of
baleen whale activity in waters around
the Emperor Seamount Chain, Oyashio/
Kuroshio Currents, Ogasawara and
Mariana Archipelagos, and Shatsky
Rise, they do not meet the selection
criteria for an OBIA as we did not find
scientific evidence that these whales
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occur in these waters in densities higher
than any other similar location or use
these areas in concentrated numbers for
breeding/calving, foraging, or migration.
See responses to comments in Chapter
7 of the Navy’s 2012 FSEIS/SOEIS for
detailed information on our analyses.
• Gulf of Mexico: See Comment 25.
• Hawaiian Islands: See Comment 26.
• Southeast Alaska: The commenters
have mischaracterized what the
SPLASH report states regarding
migration corridors for humpback
whales in the North Pacific Ocean. The
SPLASH report neither delineates nor
depicts migration corridors, but instead
describes and depicts movements of
individually tagged whales between the
winter and summer grounds
(Calambokidis et al., 2008). The
SPLASH report details the complexity
of humpback whale movements in the
North Pacific, which encompass much
of the North Pacific Ocean between the
Hawaiian and Japanese Islands and the
Gulf of Alaska and waters of
northeastern Russia. We did not exclude
this area from the selection process. For
example, we considered Fairweather
Grounds, although not specifically
mentioned in the SPLASH report
(Calambokidis et al., 2008), but
ultimately did not select the area as a
potential OBIA for foraging in
southeastern Alaska waters based on a
lack of supporting information.
Additionally, we also reviewed the
Glacier Bay National Park and Preserve,
southeastern Alaska.
• North Atlantic Right Whale: The
commenter notes the existence of ‘‘the
North Atlantic right whale migration
corridor’’ in waters less than 200 meters
in depth off the U.S. Atlantic coast. The
available sighting data, collected over
several decades, are insufficient to
represent a specific migration corridor
for the North Atlantic right whale off the
U.S. Atlantic coast or elsewhere in the
North Atlantic Ocean (Kenney, 2012
personal communication). The winter
locations and movements of much of the
North Atlantic right whale population
are currently unknown (Waring, et al.,
2010).
• Areas Referenced in Previous LFA
sonar Rules: We have re-evaluated all
areas referenced in the previous LFA
sonar rulemakings. For additional
information see the 2012 FSEIS/SOEIS,
Appendices D and F and the Navy’s
response to public comments.
Monitoring
Comment 28: The Commission
recommends that we issue the final rule,
provided that we require the Navy to
monitor for 60 minutes before resuming
SURTASS LFA sonar transmissions
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after a delay or suspension related to the
sighting of a marine mammal in the LFA
sonar mitigation or buffer zones unless
the Navy observes the animal leaving
those zones.
Response: In this rulemaking, as in
our past regulations for SURTASS LFA
sonar, we require the Navy to
immediately delay or suspend
SURTASS LFA sonar transmissions if
they detect a marine mammal within or
about to enter the SURTASS LFA sonar
mitigation and buffer zones. During the
delay/suspension, the Navy would still
operate the HF/M3 active sonar system
to monitor for the presence of marine
mammals as well as conducting visual
and passive acoustic monitoring. The
Navy may resume operations no sooner
than 15 minutes after:
(1) All marine mammals have left the
SURTASS LFA sonar mitigation and
buffer zones; and
(2) Visual, passive acoustic, and
active acoustic monitoring have
determined that there are no further
detections of marine mammals within
the SURTASS LFA sonar mitigation and
buffer zones.
We believe that requiring the
extension of the post-contact monitoring
for an additional 45 minutes is not
warranted due to the proven
effectiveness of the HF/M3 active sonar
system. The HF/M3 active sonar system
provides 24-hour, all-weather, active
acoustic monitoring of the 180-dB
SURTASS LFA sonar mitigation zone
and the 1-km (0.62 mi; 0.54 nm) buffer
zone around the LFA sonar mitigation
zone. In all, the Navy can effectively
monitor for marine mammals for
approximately 2-km (1.2 mi; 1.1 nm)
around the vessel. The HF/M3 active
sonar system’s effective detection
probability for marine mammals within
the SURTASS LFA sonar mitigation
zone approaches 100 percent, based on
multiple pings. Combined with the
passive acoustic (estimated 25 percent
detection probability) and visual
monitoring (estimated nine percent
detection probability) requirements, all
three systems together have an effective
detection probability of at least 99
percent at 1 km (0.62 mi; 0.54 nm) from
the vessel. Based upon our review of
nine years of data from monitoring
reports on previous SURTASS LFA
sonar activities (i.e., the best available
information), we consider the likelihood
of the Navy not detecting a marine
mammal within the SURTASS LFA
sonar mitigation zone to be extremely
small (less than one percent).
The Navy has evaluated the
effectiveness of the monitoring
measures in the 2007 Final
Comprehensive Report (DoN, 2007) and
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the 2011 Final Comprehensive Report
(DoN, 2011) submitted under 50 CFR
216.186(c). These reports are available
to the public (see ADDRESSES).
Comment 29: The Commission
recommends that we issue the final rule,
provided that we require the Navy to
monitor (i.e., visually, passive and
active acoustically) for a minimum of 30
minutes after SURTASS LFA sonar
transmissions cease, using visual
observation (if during daylight hours as
defined in the proposed regulations),
passive acoustics, and the active sonar
system.
Response: In this rulemaking, as in
our past regulations for SURTASS LFA
sonar, we require the Navy to continue
the three-part monitoring program for at
least 15 minutes after completing a
SURTASS LFA sonar transmission
exercise. We decline to extend the postoperational monitoring by an additional
15 minutes.
Per the MMPA, our prescription of the
Navy’s mitigation measures reflects a
careful balancing of the likely benefit of
any particular measure for marine
mammals with the likely effect of that
measure on personnel safety,
practicality of implementation, and
impact on the effectiveness of the
military readiness activity. Over the last
nine years, there have been few marine
mammal detections, either by visual
observation, passive acoustic or active
acoustic monitoring, during the 15minute post-transmission period.
Imposing additional data collection
requirements, such as extending posttransmission monitoring to 30 minutes,
would not meaningfully increase our
knowledge of the species or SURTASS
LFA sonar impacts to warrant the
additional time and cost expenditures.
Moreover, the Navy must balance the
small benefits gained by obtaining this
incremental amount of additional data
against the impact on fleet operations
that the additional delay would
necessarily entail. Waiting an additional
15 minutes before recovering the towed
SURTASS horizontal line array and the
SURTASS LFA sonar vertical line array
would delay the ship’s ability to depart
the area at the normal transiting speed
of 10 knots (kts) (11.5 miles per hour
(mph); 18.5 km per hour (kph)) (rather
than the slower operating speed with
deployed arrays of three kts (3.5 mph;
5.5 kph).
This regulation also requires the Navy
to conduct visual monitoring from the
ship’s bridge during daylight hours (30
minutes before sunrise and until 30
minutes before sunset) for marine
mammals during active SURTASS LFA
sonar operations. Although not required
by the regulation, the ship’s lookouts are
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monitoring the area at all times,
including during array retrieval and
non-transmission periods. The Navy
will report marine mammal detections
noted by the lookouts during nontransmission periods in the quarterly,
annual, and five-year comprehensive
reports.
Research
Comment 30: One commenter noted
that the research conducted by both
environmental advocacy groups and
government entities such as the Navy
were useful; encouraged all parties to
maintain reasonable efforts and
resources reserved for continued
research; and asked that we should
remain vigilant and responsive to the
results.
Response: We agree and require the
Navy to conduct monitoring and
research that will result in increased
knowledge of the species, the level of
taking, or impacts on populations of
marine mammals that we expect to be
present during SURTASS LFA sonar
operations. Also, this final regulation
governing the take of marine mammals
incidental to Navy’s SURTASS LFA
sonar operations contains an adaptive
management component. This provides
a mechanism for NMFS and the Navy to
modify (or add or delete) mitigation or
monitoring measures, as appropriate,
based on new information. We would
add, modify or delete mitigation or
monitoring measures in consultation
with the Navy if doing so creates a
reasonable likelihood of accomplishing
the goals of mitigation and monitoring
laid out in this final rule. We and the
Navy will meet annually (if deemed
necessary by either agency) to discuss
the monitoring reports, Navy research
and development outcomes, current
science, and determine whether
mitigation or monitoring modifications
are appropriate.
NEPA Concerns
Comment 31: The NRDC stated that
the proposed rule fails to consider
single dual criteria alternative for
coastal protection, despite the Court’s
recognition of the importance of the
continental shelf.
Response: In light of the
comprehensive efforts to identify and
analyze areas of biological importance
outside of the 22 km (14 mi; 12 nm)
coastal standoff zone and the need for
broad operational flexibility, the Navy
considered the dual criteria for coastal
exclusion zones within the overall OBIA
analysis process (see Subchapter 4.5.6 of
the Navy’s 2012 FSEIS/SOEIS).
Subchapter 4.8.1 (Alternatives
Previously Considered) in the Navy’s
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2012 FSEIS/SOEIS and subchapter 2.6.4
in the Navy’s 2007 FEIS provide a
summary of the results of the detailed
analysis of the differences in potential
impacts if the coastal standoff were
increased from 22 km (14 mi; 12 nm) to
46 km (29 mi; 25 nm).
Of the 21 OBIAs in the proposed rule,
17 included continental shelf/slope
areas and similar coastal areas. We
reviewed the continental shelf area in
the northwest Atlantic Ocean (with
input from the Navy and subject matter
experts) and determined that
designating the entire eastern seaboard
out to the 200-m (656-ft) isobath did not
meet the criteria for a single OBIA.
However, several scientificallysupported areas over the continental
shelf met the criteria for an OBIA. They
are:
• Georges Bank (OBIA #1);
• Roseway Basin Right Whale
Conservation Area (OBIA #2);
• Great South Channel (OBIA #3)
including North Atlantic right whale
critical habitat, Stellwagen Bank
National Marine Sanctuary, and areas
within the Gulf of Maine; and
• Southeastern U.S. Right Whale
Seasonal Habitat (North Atlantic right
whale critical habitat) (OBIA #4).
In addition to our review of the
continental shelf area in the northwest
Atlantic Ocean, the final rule designates
OBIAs in the northwest U.S.
continental, Patagonian, Bahamian,
Madagascar, east Brazilian, the
northeast Australian, the southeast
Australian, and Sakhalin Island shelves
or slopes.
Comment 32: In October 2011, the
NRDC requested a meet and confer with
the parties to the 2008 SURTASS LFA
sonar litigation. Their comment on our
proposed rule states that we did not
make any modifications to the proposed
rule based on their concerns with the
proposed mitigation measures (as noted
in the Navy’s 2011 Draft Supplemental
Environmental Impact Statement/
Supplemental Overseas Environmental
Impact Statement) nor was there an
effort to meet and confer. They further
state that they seek mitigation that
conservatively identifies and protects
important habitat, reflects the global
scope of the Navy’s action, and
addresses the Court’s concerns.
Response: See our Responses to
Comments 12, 14, 17 and 20. The
‘‘meet-and-confer’’ provision contained
in the 2008 Stipulated Settlement
Agreement Order (Civ. Action No. 07–
4771–EDL) relates to altering the agreedupon operating areas contained in that
specific agreement for the five-year
period of the 2007 Rule.
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Comment 33: The NRDC states: ‘‘The
fundamental purpose of an EIS is to
compel decision-makers to take a ‘‘hard
look’’ at a particular action—both at the
environmental impacts it will have and
at the alternatives and mitigation
measures available to reduce those
impacts—before a decision to proceed is
made 40 CFR 1500.1(b), 1502.1;
Baltimore Gas & Electric v. NRDC, 462
U.S. 87, 97 (1983). To that end, NEPA
requires agencies to make every attempt
to obtain and disclose data necessary to
analyze environmental effects and make
a reasoned choice among alternatives.
See 40 CFR 1502.22(a). The simple
assertion that ‘‘no information exists’’
does not suffice; unless the costs of
securing the information are exorbitant
or the means to obtain it are not known,
NEPA requires that it be obtained. Id.;
see, e.g., Cabinet Resource Group v. U.S.
Fish and Wildlife Service, 465
F.Supp.2d 1067, 1100 (D. Mont. 2006).
Additionally, the alternatives analysis to
support NMFS’ rulemaking requires a
full consideration of available
mitigation measures.
Response: See the Navy’s response to
Comment NRDC–04 in the Navy’s 2012
FSEIS/SOEIS and our Response to
Comment 20.
With regard to taking a hard look at
data poor areas, the adaptive
management component of our
regulation provides a mechanism for us
and the Navy to modify (or add or
delete) mitigation or monitoring
measures, as appropriate, based on new
information. We would add, modify or
delete mitigation or monitoring
measures in consultation with the Navy
if doing so creates a reasonable
likelihood of accomplishing the goals of
mitigation and monitoring laid out in
this final rule. We and the Navy will
meet annually (if deemed necessary by
either agency) to discuss the monitoring
reports, Navy research and development
outcomes, current science, and
determine whether mitigation or
monitoring modifications are
appropriate (see the 2012 FSEIS/SOEIS
Subchapter 1.4.5).
Comment 34: The NRDC stated that
the proposed rule and DSEIS screened
out more than 20 recommended OBIAs
that otherwise received habitat rankings
of ‘‘two’’ or greater, on the grounds that
they are not of high importance for nonbaleen whales including areas in the
Northeast Atlantic, the Mediterranean
Sea, and the Gully. They believe this
approach to be non-precautionary and
inappropriate for the marine mammal
species on which the SURTASS LFA
sonar system has not been tested. They
cite that certain species other than
baleen whales, such as sperm whales
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and pinnipeds, have greater acoustic
sensitivity in the low frequencies than
do odontocetes as a group; and a
number of other species, such as beaked
whales and harbor porpoises, have
demonstrated sensitivity to a variety of
sounds at relatively low acoustic
thresholds. NRDC further stated:
‘‘Originally, NMFS intended to treat
frequency specialization as one factor
among several in determining the
relative importance of a would-be OBIA.
Including such areas in practicability
discussions with the Navy, and
addressing them on a case-by-case basis,
is required under the MMPA, and is a
reasonable alternative that should be
considered, and adopted, in the SEIS.’’
Response: In the Federal Register
publication of the proposed rule for our
initial determination, we explained that
it was appropriate to consider marine
mammal OBIAs only for those species
whose best hearing sensitivity is in the
low frequency range and screen out
areas that qualified solely on the basis
of their importance for mid- or highfrequency hearing specialist species
such as sperm whales, beaked whales,
and harbor porpoises (77 FR 842;
January 6, 2012; page 877). We have
carefully considered the commenter’s
recommendations, and following is a
more detailed explanation of how we
plan to proceed with a modification to
our plan for these species.
We and the Navy both acknowledge
the evidence showing that beaked
whales and harbor porpoises have
responded to a variety of sources (but
not SURTASS LFA sonar) at lower
received levels than other species
respond to those same sources. Even if
one assumed that beaked whales or
harbor porpoises similarly also respond
to SURTASS LFA sonar at lower
received levels than other taxa, in light
of their very decreased sensitivity to this
frequency, the distances at which
beaked whales and harbor porpoises can
hear LFA sonar sounds (and therefore be
expected to respond) are still
significantly less than those for lowfrequency hearing specialist species.
Additionally, (which is the difference
between the animal’s hearing threshold
for a particular frequency and the
received sound level) for beaked whales
and harbor porpoises at the LFA sonar
frequency is significantly lower than the
sensation level for low-frequency
hearing specialists. In addition, the
sensation level for beaked whales and
harbor porpoises at the LFA sonar
frequency is also smaller than their
sensation level when exposed to higher
frequencies. These facts may lessen the
likelihood of a response. So–whereas
the extensive distances at which low
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frequency specialist species might hear
and potentially respond to the
SURTASS LFA sonar source support the
designation of large areas as OBIAs to,
where practicable, limit operation and
reduce impacts to mysticetes in areas of
high densities or important behaviors,
the far shorter distances from the LFA
sonar source at which beaked whales or
harbor porpoises might potentially
respond would not support operational
limitations across large areas in the form
of OBIAs. The SURTASS LFA sonar
mitigation and buffer zones and the
coastal standoff zones will offer
significant protection for beaked whales
and harbor porpoises from a sound
source that they are less physically
equipped to hear than are mysticetes.
Further, regarding the original
assumption that beaked whales or
harbor porpoises might respond to
SURTASS LFA sonar in the same
manner and at the same lower received
levels (than other taxa) that they
respond to other sound sources, some
scientists suggest that the ecological
context of LFA sonar sweeps (which are
similar to mysticete vocalizations) for
beaked whales and harbor porpoises is
such that one should not expect them to
negatively respond. However, we, and
the scientists we consulted, are unaware
of targeted data to support this
hypothesis (though there were
opportunistic observations of these
species during the Low Frequency
Sound Scientific Research Program
(LFA SRP)), which is why we
recommended that the Navy augment
their monitoring plan to address
whether and how these species respond
to LFA sonar, which they did (see the
Beaked Whale and Harbor Porpoise
Monitoring Section).
Regarding the inclusion of OBIAs for
pinnipeds and sperm whales because
they are more sensitive to lower
frequency sounds than other
odontocetes: we have included OBIAs
for pinnipeds where warranted (OBIA
8—Patagonian Shelf Break), and we
have not identified any areas that meet
the OBIA criteria based solely on sperm
whales. We, in consultation with the
Navy, will consider designating OBIAs
for sperm whales if, through the
adaptive management process, areas
that meet the OBIA criteria are
identified. Based on vocalizations,
anatomy, and other information, sperm
whales are likely to be more sensitive in
the LFA sonar frequency range than
other odontocetes and therefore the
distance at which they would hear and
potentially respond to the source is
likely more similar to mysticetes.
Accordingly, we will consider the
designation of OBIAs for that species
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should supporting information become
available.
Comment 35: The NRDC stated: ‘‘Both
LFA I and LFA II [litigation] recognize
that the burden to identify OBIAs rests
squarely with the agencies. As the Court
has noted, ‘‘it is improper for NMFS, the
government agency tasked by the
MMPA with requiring measures to
ensure the least practicable impact on
marine mammals when authorizing
takes, to shift the burden to members of
the public to prove that additional
exclusion areas are warranted.’’ NRDC
v. Gutierrez, 2008 WL 360852 at *8. It
is equally improper for the agencies to
shift that same burden to other agencies
or experts. Id. (observing that NMFS had
‘improperly shifted the burden to its
own parent agency to provide detailed
information regarding the marine life
there’).’’
Response: See Comments 12 and 13.
We did not shift the burden of
identifying OBIAs to other agencies or
to the subject matter experts.
Comment 36: The NRDC stated: ‘‘The
agencies have improperly rejected
numerous [OBIA] areas on the grounds
that they occur entirely within the
Navy’s 22-km (12 nm) coastal exclusion
zone. First, NMFS failed to consider the
relevance of identifying important nearcoastal habitat to establishing
meaningful buffer zones for these areas.
Instead, it summarily ruled out the vast
majority of established and proposed
MPAs as ineligible for additional
protection because they fall within the
coastal zone (see DSEIS at D–39 to D–
101), and instructed its experts to
nominate only areas extending at least
partly beyond the 12 nm limit (DSEIS at
D–4). (This problem is soluble by
generally enlarging the coastal stand-off
zone.).’’ Citing Navy’s the behavioral
risk function, the NRDC suggested that
the agencies should consider and adopt
wider buffer zones around their OBIAs.
Response: The Navy has stated in
their request for regulations and Letters
of Authorization that they will not
operate SURTASS LFA sonar vessels
within 22 km (14 mi; 12 nm) of any
coastline, including islands. Therefore,
focusing our efforts to nominate areas
outside of this zone is logical and
appropriate.
Regarding the commenter’s suggestion
that the Navy adopt a wider buffer zone
around OBIAs, we refer the commenter
to Response to Comment NRDC–17 of
the Navy’s 2012 FSEIS/SOEIS.
Comment 37: The NRDC stated:
‘‘Under the various settlement
agreements and orders that have helped
govern use of the LFA system since
2002, the Navy has practicably avoided
several biologically important areas in
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the western Pacific, particularly off the
coast of Asia and in the Philippine Sea.
It is not entirely clear how NMFS
considered these areas in the present
process, since the DSEIS suggests that
its regional experts proposed somewhat
different (and generally more expansive)
boundaries than the ones adopted in the
course of negotiation in LFA I and LFA
II; in any case, however, all but one of
these candidate OBIAs were rejected,
most receiving scores of ‘‘zero’’ (or at
best ‘‘one’’) on the agency‘s scale.
NMFS’ evaluation of these areas is
highly problematic. Even though they
occur in a region where little
comparative density information is
available and thus require the use of
alternative sources to assess; even
though they are supported by expert
recommendation; even though
additional sources suggest the
occurrence there of small, localized
populations and endemism in some
species; and even though avoidance of
at least part of these areas appears
practicable, at least on a seasonal
basis—none of these potential
avoidance areas was assessed for its
practicability. See, e.g., DSEIS at D–338
(scoring as ‘‘zero’’ a resident population
of fin whales in the Yellow Sea and East
China Sea that exhibits morphological
differences from other fin whales). Nor,
apparently, did NMFS attempt to obtain
additional data on these areas beyond
what its regional experts proposed.’’
Response: See Comments 12, 13, and
14 regarding the scope of our analyses.
These areas cited in the comment do not
meet the biological criteria for
designation as an OBIA so there was no
need for a practicability assessment by
the Navy. Moreover, the Stipulated
Settlement Agreement Order setting
forth those areas explicitly stated it was
not intended to serve as precedent for
future rulemaking.
Regarding fin whales in the north
Pacific Ocean, we found no new data to
clarify the population structure of the
species. Mizroch et al. (2009) reviewed
the distribution and movement data
available for the region and cited
literature from the late 1950s and early
1960s, noting the possibility of a nonmigratory stock of fin whales in the East
China Sea. We note that these are the
same citations provided by the subject
matter expert. Fujino (1960) suggested
that whales caught in the East China Sea
were part of a local population that did
not migrate to northern waters. In
addition to Fujino’s immunogenetic
findings, he analyzed unpublished data
that indicated fin whales from the East
China Sea were different from other
North Pacific fin whales in terms of
growth rate, length at sexual maturity,
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external body proportions, shape of
skull and shape and growth rate of
baleen.
Comment 38: The NRDC stated:
‘‘According to the DSEIS, the Navy
eliminated the Southern California
Bight from the list of ‘‘eligible’’ OBIAs
because it determined that ‘‘avoiding
this area is impracticable.’’ DSEIS at 4–
80. The Navy does not provide any
specific information on LFA training in
the SOCAL Range Complex, making a
full assessment difficult; but even
assuming that its determination is wellfounded, more analysis is required. As
it stands, the DSEIS appears to consider
the practicability only of a complete,
year-round LFA sonar exclusion. It does
not consider any procedural
requirements (e.g., requiring Fleet-level
approval for use), substantive standards
(e.g., allowing use only when certain
criteria are met), or targeted restrictions
(e.g., limiting the number of activities
per annum or avoiding biologically
important periods such as the blue
whale foraging season), or any other
mitigation methods that would protect
this vital habitat while allowing the
Navy use for training purposes. The
Southern California Bight is an area of
high importance to multiple marine
mammal species, including several
species of endangered baleen whales,
and maintains, despite some apparent
shifts in habitat, what is certainly one of
the largest concentrations of blue
whales on the planet. Reconsideration
of this area is essential. NMFS should
confirm that no other areas have been
rejected thus far for reasons of
practicability.’’
Response: See Comment 16 regarding
our discussions with the Navy on the
practicality of more limited time/area
closures for this area. The Navy’s 2012
FSEIS/SOEIS (Subchapter 4.5.2.3)
provided specific and sufficient
information to support the Navy’s
determination that avoiding this area is
operationally impracticable. Because of
the year-round training that occurs on
this range, the Southern California
Range Complex was the only OBIA
candidate that the Navy considered to
be operationally impracticable to avoid.
The Navy is not currently planning to
use SURTASS LFA sonar in the
Southern California Bight. If the Navy
were to plan use of SURTASS LFA
pursuant to the FSEIS/SOEIS, the Navy
would include the details of that plan in
the Letter of Authorization application
for the applicable year. At that time, we
and the Navy will discuss what, if any,
other measures are practicable in light
of the projected use of SURTASS LFA
sonar and best information available for
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the species potentially affected by that
use.
Regarding consideration of other areas
by the Navy, we confirm that the Navy
has not eliminated other areas from
consideration based upon practicability.
Comment 39: The NRDC stated:
‘‘Finally, the Navy may be able to
affirmatively define its operating area,
in some regions, in a way that avoids
high-value habitat and most if not all
OBIAs. As the Court has observed,
confining LFA operations to areas and
seasons of lesser concern would be an
effective means of mitigation. See NRDC
v. Gutierrez, 2008 WL 360852 at *6.
While the Navy has indicated that it
cannot, as a general rule, practicably site
its activities in low-value habitat for
marine mammals, that option may be
available in some regions. The Navy’s
current operating area off Hawaii, for
example, which was established
through the 2008 settlement agreement
in LFA II, effectively avoids most if not
all of the areas of greatest importance to
small, localized populations of marine
mammals around the main Hawaiian
Islands, as well as the
Papahanaumokuakea Marine National
Monument. The agencies should
consider using this reasonable
alternative in specific places, like
Hawaii, where it may be viable.’’
Response: The Navy’s annual Letters
of Authorization application process
(2011 DSEIS/SOEIS Sub-chapter 2.4.2)
includes the goal ‘‘ * * * to identify
marine areas for SURTASS LFA sonar
routine testing, training and military
operations that would have the least
practicable adverse impacts on marine
mammals, while meeting National
Security objectives.’’ This entails, as
part of the SURTASS LFA sonar
sensitivity/risk assessment approach,
the evaluation of operating areas with
minimal marine mammal/animal
activities, as portrayed in Figure 2–3
and discussed in Subchapter 4.4 of the
2012 FSEIS/SOEIS. As to the
commenter’s proposal for the Navy to
adopt the 2008 settlement agreement’s
coastal standoff distance in specific
places, like Hawaii, we refer the
commenter to the comprehensive OBIA
analysis process that was detailed in the
2012 FSEIS/SOEIS Appendix D and in
Appendix F of the final document. We
believe that the OBIA analysis process
incorporated the prospect of the Navy
avoiding areas of importance to small,
distinct populations of marine mammals
with limited distributions including
around the main Hawaiian Islands and
elsewhere to the greatest extent feasible
considering national security tasking.
Comment 40: The NRDC stated:
‘‘Finally, the Navy’s summary analysis,
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as the Court recognized, does not take
into account the shelf’s particular
environmental importance and
vulnerability. NRDC v. Gutierrez, 2008
WL 360852 at *23 (‘‘the importance of
the location of the continental shelf to
the environmental impact’’). The LFA II
Court agreed that the Navy need not
necessarily analyze the specific dualcriteria exclusion [i.e., a 22-km versus a
46-km coastal standoff zone] established
in the previous years’ injunction for the
Philippine Sea; however, it also found
that this did not excuse the Navy ‘from
evaluating a dual criteria alternative that
would meet the stated purpose and
need, such as a dual criteria alternative
used in some areas, but not others, with
an exception for non-routine military
tracking operations. NRDC v. Gutierrez,
2008 WL 360852 at *23. The Court
based its conclusion particularly on the
importance of the location of the
continental shelf to the environmental
impact and the fact that the Navy has
been operating under a dual criteria for
five years. The Court’s point is all the
more salient to the present DSEIS, given
that the Navy has been operating with
dual criteria throughout the western
Pacific (i.e., its entire effective operating
area) for almost ten years now.’’
NRDC further stated: ‘‘The Court
observed in LFA II that NMFS’ failure
to properly designate OBIAs rendered
more serious’ its failure to consider
dual-criteria alternatives for the
continental shelf. SDEIS at *13. The
Court did not say that an OBIA analysis
could render a dual-criteria analysis
completely unnecessary—but even if it
could, the agencies’ analysis in the
DSEIS simply does not fill the need that
the Court identified.’’
Response: All SURTASS LFA sonar
operations must occur under the
geographic restriction of a coastal
standoff range of at least 22 km (14 mi;
12 nm).
We, along with the Navy, considered
the biological importance of the
continental shelf outside the current
coastal standoff range within the OBIA
analysis (see Response to Comment 31).
Comment 41: The NRDC stated: ‘‘The
Court, in 2008, observed that the Navy’s
impact analysis did not reflect the latest
abundance data, particularly for ‘small
localized’ populations of marine
mammals. NRDC v. Gutierrez, 2008 WL
360852 at *16–17. Unfortunately, in the
present DSEIS, the Navy appears again
to have used basin-wide or pelagic
abundance estimates in determining the
size of some more discrete marine
mammal populations, as, for example,
around Hawaii. DSEIS at 4–61 to 4–62.
The Navy should use the latest, most
precautionary data, to properly reflect
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new information on marine mammal
population structuring.
Response: The Navy used pelagic data
because the Navy intends to operate in
offshore, pelagic waters. However, they
have included modeled estimates for the
false killer whale insular stock around
Hawaii in addition to information on
the pelagic stock in the 2012 FSEIS/
SOEIS.
Also, the Navy has revised the 2012
FSEIS/SOEIS to include modeled data
on the coastal bottlenose dolphin stocks
off U.S. east coast (southern migratory
coastal stock, northern Florida coastal
stock, and central Florida coastal stock).
We refer the reader to Tables 4–14, 4–
15, 4–17, C–26, C–27, and C–29 in the
Navy’s 2012 FSEIS/SOEIS.
We also note that one of our
qualifying criteria for designating OBIAs
is small, distinct populations of marine
mammals with limited distributions.
Comment 42: The NRDC stated that
the proposed rule and DSEIS heavily
relied on the LFA Scientific Research
Program (SRP) in establishing risk
parameters for the LFA sonar system.
They also noted that the new DSEIS
appears to put even more reliance on
the SRP, applying it directly to nonfocal species and suggested that the
SRP’s focal follow technique could not
detect more complex changes in
responses. Finally, the NRDC advocated
that we take a more conservative
approach in extrapolating from the SRP.
Response: We agree that technologies
that produce finer resolution data have
advanced since conclusion of the LFA
LFS SRP. However, very few active
underwater systems/sensors have the
benefit of such a directed and extensive
research effort as have the LFS SRP. The
results of the LFS SRP are still sound
(See Response to Comment 9).
Moreover, there has never been
evidence of SURTASS LFA sonar
causing injury, and all analysis and
modeling results support the conclusion
that no more than 12 percent of any
marine mammal species or stock has
been taken by Level B harassment from
SURTASS LFA sonar on an annual
basis. In fact the percentages have been
much lower for the majority of marine
mammal stocks.
Comment 43: ‘‘The Navy’s preferred
alternative would allow LFA training to
proceed within the Navy’s existing U.S.
ranges (among many other locations),
particularly the Hawaii Range Complex
and SOCAL Range Complex. Within
these ranges, the Navy has greater
opportunity to apply additional
monitoring measures. While the 2007
SEIS evaluated and rejected a number of
supplemental measures, it did not
consider the use of passive gliders or
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other passive acoustic systems to
monitor the potential on-range operating
area in advance of LFA activity, whether
to ensure that densities of target species
are sufficiently low before exercises
begin, to relocate or adjust the timing of
an LFA exercise, or for another planning
purpose. Nor of course could the earlier
SEIS evaluate the various new marine
mammal monitoring techniques
developed by the Office of Naval
Research and other bodies over the last
four years. The Navy should consider
additional monitoring measures when
operating LFA close to shore or in
established Navy ranges.’’
Response: We authorize Navy Range
Complex mitigation and monitoring
requirements under separate
regulations. When SURTASS LFA sonar
operates on a Navy range complex, it
does so under its current final rule and
Letter of Authorization
The commenter also refers to various
new marine mammal monitoring
techniques developed by the Office of
Naval Research (ONR) and other bodies
over the last four years. We understand
that the Navy’s Deputy for Undersea
Surveillance, under the Chief of Naval
Operations, maintains a cooperative
relationship with ONR’s Marine
Mammals Program and, as such, will be
aware of any new marine mammal
monitoring systems or techniques that
could potentially be used with
SURTASS LFA sonar, depending on its
safety, efficacy, cost-effectiveness, and
practicability.
Miscellaneous Issues
Comment 44: Several individuals,
OceanCare, and the Surfrider
Foundation, expressed general
opposition to SURTASS LFA sonar
activities and to our issuance of a
Marine Mammal Protection Act
authorization because of the danger of
killing or harassing marine life. Another
individual protested our decision to
allow continued harassment of marine
mammals by the United States Navy and
stated: ‘‘NMFS’ responsibility is to act
as such a steward, not to rubber stamp
proposals which have the potential to
cause significant harm to the majestic
marine mammals which roam the
oceans of the world.’’
Response: We appreciate the
commenters’ concerns for the marine
life in the areas of the proposed
activities. We note that over the course
of the previous two rules, the Navy has
reported no incidents of injury to or
mortality of any marine mammal.
However, because the probability of
detection by the active sonar system
within the SURTASS LFA sonar
mitigation zone is not 100 percent, we
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50311
will include a small number of Level A
harassment takes for marine mammals
over the course of the five-year rule.
The activities, described in detail in
the Proposed Rule (77 FR 842; January
6, 2012), include the use of active
acoustic sources incidental to upcoming
routine training and testing and use of
the SURTASS LFA sonar system during
military operations. It is our
responsibility to determine whether the
activities will have a negligible impact
on the affected species or stocks; will
have an unmitigable adverse impact on
the availability of the species or stock(s)
for subsistence uses, where relevant;
and to prescribe the means of effecting
the least practicable adverse impact on
the affected species or stocks and their
habitat, as well as monitoring and
reporting requirements.
Regarding authorizing harassment, the
Marine Mammal Protection Act allows
U.S. citizens (which includes the Navy)
to request take of marine mammals
incidental to specified activities, and
requires us to authorize such taking if
we can make the necessary findings
required by law and if we set forth the
appropriate prescriptions. As explained
throughout this rulemaking, we have
made the necessary findings under 16
U.S.C. 1371(a)(5)(A) to support issuance
of this final rule and Letters of
Authorization to the Navy.
Comment 45: One commenter stated:
‘‘In Winter v. Natural Resources Defense
Council, 555 U.S. 7, 12 (2008), the court
strongly suggested that even if
irreparable harm to the marine
mammals could be found due to the
Navy’s activities, ‘any such injury is
outweighed by the public interest and
the Navy’s interest in effective, realistic
training of its soldiers.’ The court, in
weighing the Navy’s interests against
the perceived environmental impact,
went so far as to state: ‘[T]he proper
determination of where the public
interest lies does not strike us as a close
question.’ Accordingly, the record fails
to show environmental impact
projections that outweigh the public
interest in national defense here. First,
the proposal itself indicates that no
mortalities of protected marine
mammals are anticipated (77 FR 842–
01, 846). Second, projected Level A
Harassment seems practically nonexistent as well (0.0001% of north
Pacific right whale stocks and 0.00% of
all other species) (77 FR 842–01, 884).’’
Response: This comment is beyond
the scope of this rulemaking.
Estimated Take of Marine Mammals
In the Estimated Take of Marine
Mammals section of the proposed rule,
we related the potential effects to
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marine mammals from SURTASS LFA
sonar operations to the Marine Mammal
Protection Act’s definitions of Level A
and Level B harassment and attempted
to quantify the effects that might occur
from the specific activities that the Navy
intends to conduct (77 FR 842; January
6, 2012; pages 882–884).
In the Estimates of Potential Marine
Mammal Exposure section of the
proposed rule, we described in detail
how the Navy calculated its take
estimates through modeling (77 FR 842;
January 6, 2012; pages 883–884). Briefly,
the Navy must predict the sound field
to which a given marine mammal
species could be exposed over time to
assess the potential effects on marine
mammals by the SURTASS LFA sonar
source operating at a given site. This is
a multi-part process involving:
(1) The ability to predict or estimate
an animal’s location in space and time;
(2) The ability to predict or estimate
the three-dimensional sound field at
these times and locations;
(3) The integration of these two data
sets into the Acoustic Integration Model
(AIM) to estimate the total acoustic
exposure for each animal in the
modeled population; and
(4) Converting the resultant
cumulative exposures (within the postAIM analysis) for a modeled population
into an estimate of the risk of a
significant disturbance of a biologically
important behavior (i.e., a take estimate
for Level B harassment of marine
mammals based upon an estimated
percentage of each stock affected by
SURTASS LFA sonar operations) or an
assessment of risk in terms of injury of
marine mammals (i.e., a take estimate
for Level A harassment of marine
mammals based on a cumulative
exposure of greater than or equal to 180dB re: 1 mPa single ping equivalent).
Because it is infeasible to model
enough representative sites to cover all
potential SURTASS LFA operating
areas, the Navy’s application presented
19 modeled sites as examples to provide
take estimates for potential operating
areas based on the current political
climate. These data are examples of
areas where the Navy could request
Letters of Authorization under the 5year rule because they are in areas of
potential strategic importance and/or
areas of possible naval fleet exercises.
Thus the proposed rule did not specify
the number of marine mammals that
may be taken in the proposed locations
because these are determined annually
through various inputs such as mission
location, mission duration, and season
of operation.
For this final rule, we are adopting the
Navy’s estimates shown in the 2012
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Final Supplemental Environmental
Impact Statement/Supplemental
Overseas Environmental Impact
Statement (Tables 4.4 through 4.23) as
the best scientific information currently
available. The Navy continuously
updates the analyses with new marine
mammal biological data (e.g., behavior,
distribution, abundance, and density)
whenever new information becomes
available.
For the annual applications for Letters
of Authorization, the Navy proposes to
present both the estimated percentage of
a stock and the corresponding estimated
numbers of individual animals of a
stock that may be potentially harassed
by SURTASS LFA sonar.
We do not expect that marine
mammals would be injured by
SURTASS LFA sonar because a marine
mammal should be detected through the
three-part monitoring program (visual,
passive acoustic and active acoustic
monitoring) and the Navy would
suspend or delay active transmissions.
The probability of detection of a marine
mammal by the HF/M3 active sonar
system within the SURTASS LFA sonar
mitigation zone approaches 100 percent
based on multiple pings (see the 2001
FOEIS/EIS, Subchapters 2.3.2.2 and
4.2.7.1 for the system’s sonar testing
results). The Navy’s acoustic analyses
predict that less than 0.0001 percent of
the endangered north Pacific right
whale stock and 0.00 percent of the
stocks of all other marine mammal
species may be exposed to levels of
sound that could potentially result in
Level A harassment (i.e., exposures at
180 dB re: 1 mPa or greater).
Quantitatively, the Navy’s request
translates into take estimates of zero
animals for any species including the
endangered north Pacific right whale.
However, because the probability of
detection by the active sonar system
within the SURTASS LFA sonar
mitigation zone is not 100 percent, we
will include a small number of Level A
harassment takes for marine mammals
over the course of the five-year
regulations based on qualitative
analyses.
Reviewing the Navy’s historical data
on visual alerts that have triggered a
suspension of SURTASS LFA sonar
transmissions, the data indicate that the
largest grouping of mysticetes or
odontocetes that triggered a shutdown
outside of the SURTASS LFA sonar
mitigation zone and within the buffer
zone is three and two respectively.
Based on this, we analyzed the take of
no more than six mysticetes (total),
across all species requested in the
Navy’s application by Level A
harassment; no more than 25
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odontocetes (across all species) by Level
A harassment; and no more than 25
pinnipeds (across all species) by Level
A harassment over the course of the 5year regulations. These are the only
quantitative adjustments that we have
made to the requested takes from the
Navy’s modeled exposure results.
Again, we note that over the course of
the previous two rulemakings, the Navy
has reported no incidents of injury to or
mortality of any marine mammal. As
with the 2002 and 2007 Rules, the Navy
will limit operation of SURTASS LFA
sonar to ensure that no more than 12
percent of any marine mammal stock
would be taken by Level B harassment
annually, over the course of the fiveyear regulations. This annual per-stock
cap applies regardless of the number of
SURTASS LFA sonar vessels operating.
Also, the Navy will use the 12 percent
cap to guide its mission planning and
annual LOA applications. We have
made no other changes to this section in
the final rule.
Analysis and Negligible Impact
Determination
Our proposed rule for SURTASS LFA
sonar operations included a section that
addressed the analysis and negligible
impact determination of the Navy’s
activities on the affected species or
stocks (77 FR 842; January 6, 2012;
pages 884–887). The Navy has described
its specified activities based on best
estimates of the number of hours that
the Navy will conduct SURTASS LFA
sonar operations. The exact number of
transmission hours may vary from year
to year, but will not exceed 432 hours
(18 days) annually for each vessel.
Taking all of the previous discussions
into account, including the following:
• We anticipate no mortalities and
very few or more likely no injuries to
result from the action;
• We require the Navy to implement
mitigation and monitoring measures
including performing delay/shutdown
protocols of active SURTASS LFA sonar
transmissions when monitoring detects
a marine mammal; geographic
operational restrictions in coastal areas
and offshore areas of biological
importance for marine mammals;
• We anticipate a relatively small
number of SURTASS LFA sonar systems
deployed as well as a low number of
annual transmission hours;
• We anticipate no adverse effects on
annual rates of recruitment or survival
of the affected species or stock; and
• Our consideration of the following
sections discussed later in this
document.
We have determined that Navy
training, testing, and military operations
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utilizing SURTASS LFA sonar will have
a negligible impact on the marine
mammal species and stocks present in
operational areas in areas of the Pacific,
Atlantic, and Indian Oceans and the
Mediterranean Sea.
Behavioral Harassment
As discussed in the Potential Effects
of Exposure to SURTASS LFA Sonar
Operations section in the proposed rule
(77 FR 842; January 6, 2012; page 865–
871), marine mammals may respond to
SURTASS LFA sonar operations in
many different ways, a subset of which
qualifies as behavioral harassment. One
thing that the take estimates do not take
into account is the fact that marine
mammals will most likely avoid strong
sound sources to one extent or another.
Although an animal that avoids the
sound source will still be taken in some
instances (such as if the avoidance
results in a missed opportunity to feed,
interruption of reproductive behaviors,
etc.) in other cases avoidance may result
in fewer instances of take than were
estimated or in the takes resulting from
exposure to a lower received level than
was estimated, which could result in a
less severe response.
For SURTASS LFA sonar operations,
the Navy provided information (Tables
24–42 of the Navy’s application)
estimating numbers of total takes that
could occur within the proposed
operational areas. For reasons stated
previously in this document, the
specified activities associated with the
proposed SURTASS LFA sonar
operations will most likely fall within
the realm of Level B behavioral
harassment. We base this assessment on
a number of factors from the Navy’s
1997–98 Low Frequency Sound
Scientific Research Program.
The Navy designed the two-year study
to assess the potential impacts of
SURTASS LFA sonar on the behavior of
low-frequency hearing specialists, those
species believed to be at (potentially)
greatest risk. This field research
addressed three important behavioral
contexts for baleen whales: (1) Blue and
fin whales feeding in the southern
California Bight, (2) gray whales
migrating past the central California
coast, and (3) humpback whales
breeding off Hawaii. Taken together, the
results from the three phases of the LFS
SRP do not support the hypothesis that
most baleen whales exposed to received
levels near 140 dB re: 1 mPa would
exhibit disturbance behavior and avoid
the area. These experiments, which
exposed baleen whales to received
levels ranging from 120 to about 155 dB
re: 1 mPa, detected only minor, shortterm behavioral responses. However,
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short-term behavioral responses do not
necessarily constitute significant
changes in biologically important
behaviors.
Temporary Threshold Shift
Schlundt et al. (2000) documented
temporary threshold shift in trained
bottlenose dolphins and belugas after
exposure to intense 1-second signal
duration tones at 400 Hertz (Hz), and 3,
10, 20, and 75 kilohertz. We note that
at the low frequency band tones of 400
Hz, the researchers were unable to
induce temporary threshold shift in any
animal at levels up to 193 dB re: 1 mPa
at 1 m (the maximum level associated
with the experiment’s equipment). The
researchers implied that the temporary
threshold shift for a 100-second signal
would be approximately 184 dB (DoN,
2001; Table 1).
When SURTASS LFA sonar transmits,
there is a boundary that encloses a
volume of water where received levels
equal or exceed 180 dB re: 1 mPa (the
180–dB isopleth LFA sonar mitigation
zone) and a volume of water outside this
boundary where received levels are
below 180 dB re: 1 mPa. The level of risk
for temporary threshold shift for marine
mammals depends on their location in
relation to SURTASS LFA sonar.
However, the Navy’s standard protective
measures, captured in our regulation,
would ensure delay or suspension of
SURTASS LFA sonar transmissions if
any of the three monitoring measures
detect a marine mammal within 2 km
(1.2 mi; 1.1 nm) of the vessel. Thus, the
mitigation measures would allow the
Navy to reduce the number of marine
mammals exposed to received levels of
SURTASS LFA sonar or HF/M3 active
sonar sound that could result in
temporary threshold shift. For transient
sounds, the sound level necessary to
cause temporary threshold shift is
inversely related to the duration of the
sound. Again, in the case of SURTASS
LFA sonar, we do not expect animals to
be exposed to levels high enough or
durations long enough to result in
temporary threshold shift. In order to
receive more than one ‘‘ping’’ during a
normal vessel leg, an animal would
need to match the ship in speed and
course direction between pings.
Also, the Navy will conduct
SURTASS LFA sonar operations to
ensure that the sound field does not
exceed 180 dB re: 1 mPa within 22 km
(14 mi; 12 nm) of any coastline or
within 1-km (0.62 mi; 0.54 nm) of the
perimeter of any OBIA. These measures
offer protection to areas with higher
densities of marine mammals. Because
the Navy will operate for the most part
in waters that are not areas known for
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high concentrations of marine
mammals, few, if any, marine mammals
would be within the SURTASS LFA
sonar mitigation and buffer zones.
Because of the relatively short duty
cycle, the water depth of the
convergence zone ray path, the
movement of marine mammals in
relationship to the SURTASS LFA sonar
vessel, and the effectiveness of the
three-part mitigation program, few
marine mammals are likely to be
affected by temporary threshold shift.
Permanent Threshold Shift
In our 2002 and 2007 rules, we, along
with the Navy, based their estimate of
take by injury or the significant
potential for such take (Level A
harassment) on the criterion of 180–dB.
We continue to believe this is a
scientifically supportable and
conservative value for preventing
auditory injury or the significant
potential for such injury (Level A
harassment), as it represents a value less
than where the potential onset of a
minor temporary threshold shift in
hearing might occur based on Schlundt
et al.’s (2000) research (see the Navy’s
2007 Final Comprehensive Report
Tables 5 through 8).
This regulation requires the Navy to
ensure delay or suspension of SURTASS
LFA sonar transmissions if any of the
three monitoring protocols detect a
marine mammal either entering the LFA
sonar mitigation or buffer zone; (i.e.,
within approximately two km (1.2 mi;
1.1 nm)) of the SURTASS LFA sonar
transmit array or vessel. The mitigation
protocols would avoid exposing marine
mammals to received levels of
SURTASS LFA sonar or HF/M3 active
sonar sound that would result in injury
(Level A harassment). The sound
pressure level that is capable of
potentially causing injury to an animal
is within less than 1 km (0.62 mi; 0.54
nm) of the vessel. Implementing a
shutdown zone of approximately 2 km
(1.2 mi; 1.1 nm) around the SURTASS
LFA sonar array and vessel will ensure
that no marine mammals are exposed to
a sound pressure level greater than
approximately 175 dB re: 1 mPa
(received level). This is significantly
lower than the 180–dB re: 1 mPa
(received level) used for other acoustic
projects for protecting marine mammals
from injury. Serious injury is unlikely to
occur unless a marine mammal is well
within the 180–dB LFA sonar mitigation
zone and close to the source. The closer
the mammal is to the SURTASS LFA
sonar transmit array or the vessel, the
more likely that the Navy will detect the
animal with the three-part monitoring
protocols leading to the immediate
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delay or suspension of SURTASS LFA
sonar transmissions.
From 2003 to 2011, the Navy reported
a total of 12 visual sightings (including
two sightings during non-operational
periods and one sea turtle sighting), four
passive acoustic detections, and 130
HF/M3 active sonar system detections of
marine mammals, all leading to 139
suspensions/delays of transmissions in
accordance with mitigation protocols.
Because the HF/M3 active sonar system
is able to monitor large and medium
marine mammals out to an effective
range of 2 to 2.5 km (1.2 to 1.5 mi; 1.1
to 1.3 nm) from the vessel, it is unlikely
that the SURTASS LFA sonar operations
would expose marine mammals to a
sound pressure level greater than
approximately 175 dB re: 1 mPa. The
area between the 180–dB LFA sonar
mitigation zone and the additional 1-km
(0.62 mi; 0.54 nm) buffer zone proposed
by us (estimated to extend to
approximately the 175-dB re: 1 mPa
isopleth from the vessel) is an area
where marine mammals would
experience Level B harassment if
exposed to SURTASS LFA sonar
transmissions, in accordance with the
Navy’s risk analysis and acoustic
modeling (DoN, 2001; Subchapter 4.2.3).
Past results of the HF/M3 sonar system
tests provide confirmation that the
system has a demonstrated probability
of single-ping detection of 95 percent or
greater for single marine mammals, 10
m (32.8 ft) in length or larger, and a
probability approaching 100 percent for
multiple pings for any sized marine
mammal. Further, implementing a
shutdown zone of approximately 2 km
(1.2 mi; 1.1 nm) around the vessel will
ensure that no marine mammals are
exposed to a sound pressure level
greater than approximately 175 dB re: 1
mPa.
With three types of mitigation
monitoring for detecting marine
mammals, we believe it is unlikely that
any marine mammal would be exposed
to received levels of 180 dB re: 1 mPa
before detection and the resulting
SURTASS LFA sonar shutdown.
However, because the probability is not
zero, the Navy has requested and we
considered Level A harassment takes
incidental to SURTASS LFA sonar
operations.
Mortality
There is no empirical evidence of
strandings of marine mammals
associated with the employment of
SURTASS LFA sonar. Moreover, the
system acoustic characteristics differ
between low-frequency active sonar
addressed here and the mid-frequency
active sonars associated with strandings:
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Low frequency active sonars use
frequencies generally below 1,000 Hz,
with relatively long signals (pulses) on
the order of 60 seconds; while midfrequency active sonars use frequencies
greater than 1,000 Hz, with relatively
short signals on the order of 1 second.
We provided a summary of common
features shared by the strandings events
in Greece (1996), Bahamas (2000),
Madeira (2000), Canary Islands (2002),
Hanalei Bay (2004), and Spain (2006) in
the proposed rule (77 FR 842; January
6, 2012; pages 871–872). These included
operation of mid-frequency active sonar,
deep water close to land (such as
offshore canyons), presence of an
acoustic waveguide (surface duct
conditions), and periodic sequences of
transient pulses (i.e., rapid onset and
decay times) generated at depths less
than 32.8 ft (10 m) by sound sources
moving at speeds of 2.6 m/s (5.1 knots)
or more during sonar operations
(D’Spain, et al., 2006). None of these
features relate to SURTASS LFA sonar
operations.
In summary, based on these analyses,
the past nine years of SURTASS LFA
sonar operations, and results from the
LFS Scientific Research Program, we do
not anticipate that SURTASS LFA sonar
operations will likely have adverse
effects on annual rates of recruitment or
survival (i.e., population-level effects).
Further, in consideration of the fact that
the 22-km (14mi; 12 nm) coastal
standoff zone and designated OBIAs
restrict the use of SURTASS LFA sonar
in known areas of feeding, calving, and
breeding for marine mammals, we do
not expect the activity to have the sort
of energetic impacts on individuals that
would be likely to result in reduced
survivorship or reproductive success.
Accordingly we have determined that
the total taking over the 5-year period of
the regulations and related Letters of
Authorization for the Navy’s SURTASS
LFA sonar activities will have a
negligible impact on the affected species
or stocks in the Navy’s SURTASS LFA
sonar mission areas.
Subsistence Harvest of Marine
Mammals
We included a detailed discussion of
the potential effects of the Navy’s
SURTASS LFA sonar operations on
subsistence harvest (77 FR 842; January
6, 2012; pages 886–887). The
information contained in this section
has not changed from what was in the
proposed rule.
We have determined that the possible
future employment of SURTASS LFA
sonar will not lead to unmitigable
adverse impacts on the availability of
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marine mammal species or stocks for
subsistence uses in the Gulf of Alaska.
Should the Navy operate SURTASS
LFA sonar in the Gulf of Alaska, sonar
operation would adhere to the
shutdown in the mitigation and buffer
zones, as well as established geographic
restrictions, which include the coastal
standoff range (which dictates that the
sound field produced by the sonar must
be below 180 dB re: 1 mPa within 22 km
(14 mi; 12 nm) of any coastline) and at
1 km (0.62 mi; 054 nm) seaward of any
OBIA outer perimeter which includes
north Pacific right whale critical habitat.
Additionally, the Navy will continue to
keep Indian Tribal Governments
informed of the timeframes of any future
SURTASS LFA sonar exercises planned
for the Gulf of Alaska or offshore the
Washington or Oregon coasts.
Endangered Species Act
There are 15 marine mammal species
under our jurisdiction that are listed as
endangered or threatened under this Act
with confirmed or possible occurrence
in potential operational areas for
SURTASS LFA sonar: The blue, fin, sei
humpback, bowhead, north Atlantic
right, north Pacific right, southern right,
gray, and sperm whales as well as the
western and eastern distinct population
segments of the Steller sea lion,
Mediterranean monk seal, Hawaiian
monk seal, the eastern distinct
population segments of the Steller sea
lion; the Guadalupe fur seal and the
southern distinct population segments
of the spotted seal.
Pursuant to Section 7 of the
Endangered Species Act, the Navy has
consulted with NOAA Fisheries’ Office
of Protected Resources, Endangered
Species Act Interagency Cooperation
Division, on this action. We have also
consulted internally on the issuance of
regulations and annual LOAs under
section 101(a)(5)(A) of the Marine
Mammal Protection Act for this activity.
NMFS’ August 2012 Biological Opinion
concludes that the proposed SURTASS
LFA sonar operations and NMFS’
issuance of regulations and subsequent
LOAs to authorize incidental take of
marine mammals are not likely to
jeopardize the continued existence of
the threatened and endangered species
under NMFS’ jurisdiction and are not
likely to result in the destruction or
adverse modification of critical habitat.
National Environmental Policy Act
We have participated as a cooperating
agency on the Navy’s 2012 FSEIS/SOEIS
for employment of SURTASS LFA
sonar, published on June, 8, 2012. The
Navy has posted this document at
https://www.surtass-lfa-eis.com. We have
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adopted the Navy’s 2012 FSEIS/SOEIS
in connection with this Marine Mammal
Protection Act rulemaking and prepared
a Record of Decision.
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Determination
Based on the analyses contained here
and in the proposed rule (and other
related documents) of the likely effects
of the specified activity on marine
mammals and their habitat and
dependent upon the implementation of
the mitigation and monitoring measures,
we find that the Navy’s SURTASS LFA
sonar operations using active acoustic
sources (including the HF/M3 active
sonar system) over the five-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. We have issued
regulations for these activities 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 any
collection of information requirements
for purposes of the Paperwork
Reduction Act of 1980 (44 U.S.C. 3501
et seq.).
The Office of Management and Budget
has determined that this final rule is not
significant for purposes of Executive
Order 12866.
Pursuant to the Regulatory Flexibility
Act, the Chief Counsel for Regulation of
the Department of Commerce certified
to the Chief Counsel for Advocacy of the
Small Business Administration at the
proposed rule stage, that this rule, if
adopted, would not have a significant
economic impact on a substantial
number of small entities. We published
the certification in the Federal Register
notice of the proposed rulemaking on
January 6, 2012. We received no
comments about the certification.
Accordingly, a final regulatory
flexibility analysis is not required and
none has been prepared.
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. The Navy has a compelling
national policy reason to continue
military readiness activities without
interruption to the routine training and
testing as well as use of the SURTASS
LFA sonar system during military
operations.
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This rule making began shortly after
our receipt of the Navy’s application for
take authorization in August 2011.
During that year, Navy, with our
participation as a cooperating agency,
was preparing its FSEIS/SOEIS for
SURTASS LFA sonar. Both agencies
seriously considered all public
comments and worked together to
ensure an outcome that satisfied both
the Navy’s purpose and need and our
statutory responsibilities. In addition,
after the proposed rule was published in
the Federal Register in January 2012,
we undertook a review of Hoyt (2011),
a new edition of our key reference
document to identify OBIAs in the
world’s oceans, to ensure we had not
overlooked any other areas as potential
OBIAs. In addition to the considerable
time it took to review over 300 new
areas identified in Hoyt (2011), the
outcome of our review required us to
engage in additional analyses and
discussions both internally and with the
Navy to determine if any other areas
warranted OBIA consideration and
designation.
The current regulation expires on
August 15, 2012. The Navy has a
compelling national policy reason to
continue military readiness activities
without interruption to the routine
training and testing, and use of the
SURTASS LFA sonar system. Under
these circumstances, it was not possible
to finalize the MMPA rule making and
the NEPA obligations with sufficient
time to allow for the 30-day delay in
effectiveness date.
As discussed below, suspension/
interruption of the Navy’s ability to
conduct routine training and testing as
well as use of SURTASS LFA sonar
during military operations disrupts
adequate and realistic testing of military
equipment, weapons, and sensors for
proper operation and suitability for
combat essential to national security.
In order to meet its national security
objectives, the Navy must continually
maintain its ability to operate in a
challenging at-sea environment, conduct
military operations, control strategic
maritime transit routes and
international straits, and protect sea
lines of communications that support
international commerce. To meet these
objectives, the Navy must identify,
develop, and procure defense systems
by continually integrating test and
evaluation support throughout the
defense acquisition process and
providing essential information to
decision-makers. Such testing and
evaluation is critical in determining that
defense systems perform as expected
and whether these systems are
operationally effective, suitable,
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50315
survivable, and safe for their intended
use.
In order to effectively fulfill its
national security mission, the Navy has
a need to conduct routine training and
testing as well as use of the SURTASS
LFA sonar system during military
operations covered by this final rule as
soon as possible. The defense
acquisition process is structured to be
responsive and acquire quality products
that satisfy user needs with measurable
improvements on mission capability
and operational support in a timely
manner. Test and evaluation confirms
performance of platforms and systems
against documented capability needs
and adversary capabilities. Delays in
acquisition test and evaluation affect the
Navy’s need to meet its statutory
mission to deploy worldwide naval
forces equipped to meet existing and
emergent threats. The Navy would be
unable to plan to conduct activities
covered by this final rule in the
immediate future due to the
uncertainties in the planning process
and the fiscal and other consequences of
planning for, preparing for, and then
cancelling a major testing event. A 30day delay furthers the amount of time
the Navy is unable to plan for and
execute an activity covered by this rule.
Further, should an immediate national
security issue arise; the 30-day delay
would prevent the Navy from meeting
its mission, which would have adverse
national security consequences.
Waiver of the 30-day delay of the
effective date of the final rule will allow
the Navy to continue put SURTASS
LFA sonar capability into the hands of
U.S. Sailors quickly, while also ensuring
compliance with the MMPA.
List of Subjects in 50 CFR Part 218
Exports, Fish, Imports, Indians,
Labeling, Marine mammals, Penalties,
Reporting and recordkeeping
requirements, Seafood, Transportation.
Dated: August 13, 2012.
Alan D. Risenhoover,
Director, Office of Sustainable Fisheries,
performing the functions and duties of the
Deputy Assistant Administrator for
Regulatory Programs.
For reasons set forth in the preamble,
50 CFR part 218 is amended as follows:
PART 218–REGULATIONS
GOVERNING THE TAKING AND
IMPORTING OF MARINE MAMMALS
1. The authority citation for part 218
continues to read as follows:
■
Authority: 16 U.S.C. 1361 et seq.
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Subparts T through W [Added and
Reserved]
2. Reserved subparts T through W are
added.
■ 3. Subpart X is added to read as
follows:
■
Subpart X—Taking and Importing of Marine
Mammals; Navy Operations of Surveillance
Towed Array Sensor System Low
Frequency Active (SURTASS LFA) Sonar
Sec.
218.230 Specified activity, level of taking,
and species.
218.231 Effective dates.
218.232 Permissible methods of taking.
218.233 Prohibitions.
218.234 Mitigation.
218.235 Requirements for monitoring.
218.236 Requirements for reporting.
218.237 Applications for Letters of
Authorization.
218.238 Letters of Authorization.
218.239 Renewal of Letters of
Authorization.
218.240 Modifications to Letters of
Authorization.
218.241 Adaptive Management.
Subpart X—Taking and Importing of
Marine Mammals; Navy Operations of
Surveillance Towed Array Sensor
System Low Frequency Active
(SURTASS LFA) Sonar
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§ 218.230 Specified activity, level of taking,
and species.
Regulations in this subpart apply only
to the incidental taking of those marine
mammal species specified in paragraph
(b) of this section by the U.S. Navy,
Department of Defense, while engaged
in the operation of no more than four
SURTASS LFA sonar systems
conducting active sonar operations in
areas specified in paragraph (a) of this
section. The authorized activities, as
specified in a Letter of Authorization
issued under §§ 216.106 and 218.238,
include the transmission of low
frequency sounds from the SURTASS
LFA sonar system and the transmission
of high frequency sounds from the
mitigation sonar described in § 218.234
during routine training and testing as
well as during military operations.
(a) The incidental take, by Level A
and Level B harassment, of marine
mammals from the activity identified in
this section may be authorized in
certain areas of the Pacific, Atlantic, and
Indian Oceans and the Mediterranean
Sea, as specified in a Letter of
Authorization.
(b) The incidental take, by Level A
and Level B harassment, of marine
mammals from the activity identified in
this section is limited to the following
species and species groups:
(1) Mysticetes–blue whale
(Balaenoptera musculus), bowhead
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whale (Balaena mysticetus), Bryde’s
whale (Balaenoptera edeni), fin whale
(Balaenoptera physalus), gray whale
(Eschrichtius robustus), humpback
whale (Megaptera novaeangliae), minke
whale (Balaenoptera acutorostrata),
North Atlantic right whale (Eubalaena
glacialis), North Pacific right whale
(Eubalena japonica), pygmy right whale
(Caperamarginata), sei whale
(Balaenoptera borealis), southern right
whale (Eubalaena australis),
(2) Odontocetes–Andrew’s beaked
whale (Mesoplodon bowdoini),
Arnoux’s beaked whale (Berardius
arnuxii), Atlantic spotted dolphin
(Stenella frontalis), Atlantic white-sided
dolphin (Lagenorhynchus acutus),
Baird’s beaked whale (Berardius
bairdii), Beluga whale (Dephinapterus
leucas), Blainville’s beaked whale
(Mesoplodon densirostris), Chilean
dolphin (Cephalorhynchus eutropia),
Clymene dolphin (Stenella clymene),
Commerson’s dolphin
(Cephalorhynchus commersonii),
common bottlenose dolphin (Tursiops
truncatus), Cuvier’s beaked whale
(Ziphiuscavirostris), Dall’s porpoise
(Phocoenoides dalli), Dusky dolphin
(Lagenorhynchus obscurus), dwarf
sperm and pygmy sperm whales (Kogia
simus and K. breviceps), false killer
whale (Pseudorca crassidens), Fraser’s
dolphin (Lagenodelphis hosei), Gervais’
beaked whale (Mesoplodon europaeus),
ginkgo-toothed beaked whale
(Mesoplodon ginkgodens), Gray’s
beaked whale (Mesoplodon grayi),
Heaviside’s dolphin (Cephalorhynchus
heavisidii), Hector’s beaked whale
(Mesoplodon hectori), Hector’s dolphin
(Cephalorhynchus hectori); Hourglass
dolphin (Lagenorhynchus cruciger),
Hubbs’ beaked whale (Mesoplodon
carhubbsi), harbor porpoise (Phocoena
phocoena); Indo-Pacific bottlenose
dolphin (Tursiops aduncus), killer
whale (Orca orcinus), long-beaked
common dolphin (Delphinuscapensis),
long-finned pilot whale
(Globicephalamelas), Longman’s beaked
whale (Indopacetus pacificus), melonheaded whale (Peponocephala electra),
northern bottlenose whale (Hyperodon
ampullatus), northern right whale
dolphin (Lissodelphis borealis), Pacific
white-sided dolphin (Lagenorhynchus
obliquidens), pantropical spotted
dolphin (Stenella attenuata), Peale’s
dolphin (Lagenorhynchus australis),
Perrin’s beaked whale (Mesoplodon
perrini), pygmy beaked whale
(Mesoplodon peruvianus), pygmy killer
whale (Feresa attenuata), Risso’s
dolphin (Grampus griseus), roughtoothed dolphin (Steno bredanensis),
Shepherd’s beaked whale (Tasmacetus
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sheperdii), short-beaked common
dolphin (Delphinus delphis), shortfinned pilot whale (Globicephala
macrorhynchus), southern bottlenose
whale (Hyperodon planifrons), southern
right whale dolphin (Lissodelphis
peronii), Sowerby’s beaked whale
(Mesoplodon bidens), spade-toothed
beaked whale (Mesoplodon traversii),
spectacled porpoise (Phocoena
dioptrica), sperm whale (Physeter
macrocephalus), spinner dolphin
(Stenella longirostris), Stejneger’s
beaked whale (Mesoplodon stejnegeri),
strap-toothed beaked whale
(Mesoplodon layardii), striped dolphin
(Stenella coeruleoalba), True’s beaked
whale (Mesoplodon mirus), whitebeaked dolphin (Lagenorhynchus
albirostris),
(3) Pinnipeds–Australian sea lion
(Neophoca cinerea), California sea lion
(Zalophus californianus), Galapagos fur
seal (Arctocephalus galapagoensis),
Galapagos sea lion (Zalophus
wollebaeki), gray seal (Halichoerus
grypus), Guadalupe fur seal
(Arctocephalus townsendi), harbor seal
(Phoca vitulina), harp seal (Pagophilus
groenlandicus), Hawaiian monk seal
(Monachus schauinslandi), hooded seal
(Cystophora cristata), Juan Fernadez fur
seal (Arctocephalus philippi),
Mediterranean monk seal (Monachus
monachus), New Zealand fur seal
(Arctocephalus forsteri), New Zealand
fur seal (Phocarctos hookeri), northern
elephant seal (Mirounga angustirostris),
northern fur seal (Callorhinus ursinus),
ribbon seal (Phoca fasciata), South
African and Australian fur seals
(Arctocephalus pusillus), South
American fur seal (Arctocephalus
australis), South American sea lion
(Otaria flavescens), southern elephant
seal (Mirounga leonina), spotted seal
(Phoca largha), Steller sea lion
(Eumetopias jubatus), subantarctic fur
seal (Arctocephalus tropicalis).
§ 218.231
Effective dates.
Regulations are effective August 15,
2012 through August 15, 2017.
§ 218.232
Permissible methods of taking.
(a) Under Letters of Authorization
issued pursuant to §§ 216.106 and
218.238 of this chapter, the Holder of
the Letter of Authorization may
incidentally, but not intentionally, take
marine mammals by Level A and Level
B harassment within the areas described
in § 218.230(a), provided that the
activity is in compliance with all terms,
conditions, and requirements of these
regulations and the appropriate Letter of
Authorization.
(b) The Holder of the Letter of
Authorization must conduct the
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activities identified in § 218.230 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 § 218.230 is limited to the species
listed in § 218.230(b) by the method of
take indicated in paragraphs (c)(2)
through (5) of this section.
(1) The Navy must maintain a running
calculation/estimation of takes of each
species over the effective period of these
regulations.
(2) Level B harassment will not
exceed 12 percent of any marine
mammal stock listed in § 218.230(b)(1)
through (3) annually over the course of
the five-year regulations. This annual
per-stock cap of 12 percent applies
regardless of the number of SURTASS
LFA sonar vessels operating.
(3) Level A harassment of no more
than six mysticetes (total), of any of the
species listed in § 218.230(b)(1) over the
course of the five-year regulations.
(4) Level A harassment of no more
than 25 odontocetes (total), of any of the
species listed in § 218.230(b)(2) over the
course of the five-year regulations.
(5) Level A harassment of no more
than 25 pinnipeds (total), of any of the
species listed in § 218.230(b)(3) over the
course of the five-year regulations.
§ 218.233
Prohibitions.
No person in connection with the
activities described in § 218.230 may:
(a) Take any marine mammal not
specified in § 218.230(b);
(b) Take any marine mammal
specified in § 218.230 other than by
incidental take as specified in
§ 218.232(c)(2) through (5);
(c) Take any marine mammal
specified in § 218.230 if NMFS makes a
determination that 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, any
of the terms, conditions, or
requirements of these regulations or a
Letter of Authorization issued under
§§ 216.106 and 218.238 of this chapter.
§ 218.234
Mitigation.
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When conducting operations
identified in § 218.230, the mitigation
measures described in this section and
in any Letter of Authorization issued
under §§ 216.106 and 218.238 must be
implemented.
(a) Personnel Training—Lookouts: (1)
The Navy shall train the lookouts in the
most effective means to ensure quick
and effective communication within the
command structure in order to facilitate
implementation of protective measures
if they spot marine mammals.
(2) The Navy will hire one or more
marine mammal biologists qualified in
conducting at-sea marine mammal
visual monitoring from surface vessels
to train and qualify designated ship
personnel to conduct at-sea visual
monitoring.
(b) General Operating Procedures: (1)
Prior to SURTASS LFA sonar
operations, the Navy will promulgate
executive guidance for the
administration, execution, and
compliance with these regulations and
any Letters of Authorization issued.
(2) The Holder of a Letter of
Authorization will not transmit the
SURTASS LFA sonar signal at a
frequency greater than 500 Hertz (Hz).
(c) LFA Sonar Mitigation Zone and 1km Buffer Zone; Suspension and Delay:
(1) Prior to commencing and during
SURTASS LFA sonar transmissions, the
Holder of a Letter of Authorization will
determine the propagation of LFA sonar
signals in the ocean and the distance
from the SURTASS LFA sonar source to
the 180-decibel (dB) re: 1 mPa isopleth.
(2) The Holder of a Letter of
Authorization will establish a 180-dB
LFA sonar mitigation zone around the
surveillance vessel that is equal in size
to the 180-dB re: 1 mPa isopleth (i.e., the
volume subjected to sound pressure
levels of 180 dB or greater) as well as
a one-kilometer (1-km) buffer zone
around the LFA sonar mitigation zone.
(3) If a marine mammal is detected,
through monitoring required under
§ 218.235, within or about to enter the
LFA sonar mitigation zone plus the 1km buffer zone, the Holder of the Letter
of Authorization will immediately delay
or suspend SURTASS LFA sonar
transmissions.
(d) Resumption of SURTASS LFA
sonar transmissions: (1) The Holder of
a Letter of Authorization will not
resume SURTASS LFA sonar
transmissions earlier than 15 minutes
after:
(i) All marine mammals have left the
area of the SURTASS LFA sonar
mitigation and buffer zones; and
(ii) There is no further detection of
any marine mammal within the LFA
sonar mitigation and buffer zones as
determined by the visual, passive, and
high frequency monitoring described in
§ 218.235.
(e) Ramp-up Procedures for the highfrequency marine mammal monitoring
(HF/M3) sonar required under
§ 218.235: (1) The Holder of a Letter of
Authorization will ramp up the HF/M3
sonar power level beginning at a
maximum source sound pressure level
of 180 dB re: 1 mPa at 1 meter in 10-dB
increments to operating levels over a
period of no less than five minutes:
(i) At least 30 minutes prior to any
SURTASS LFA sonar transmissions;
(ii) Prior to any SURTASS LFA sonar
calibrations or testing that are not part
of regular SURTASS LFA sonar
transmissions described in § 218.230;
and
(iii) Anytime after the HF/M3 active
sonar source has been powered down
for more than two minutes.
(2) The Holder of a Letter of
Authorization will not increase the HF/
M3 active sonar system’s sound
pressure level once a marine mammal is
detected; ramp-up may resume once
marine mammals are no longer detected.
(f) Geographic Restrictions on the
SURTASS LFA Sonar Sound Field: (1)
The Holder of a Letter of Authorization
will not operate the SURTASS LFA
sonar such that:
(i) The SURTASS LFA sonar sound
field exceeds 180 dB re: 1 mPa (rms) at
a distance less than 12 nautical miles
(nm) (22 kilometers (km)) from any
coastline, including offshore islands;
(ii) The SURTASS LFA sonar sound
field exceeds 180 dB re: 1 mPa (rms) at
a distance less than 1 km (0.5 nm)
seaward of the outer perimeter of any
offshore biologically important area
designated in § 218.234(f)(2) during the
period specified.
(2) The Offshore Biologically
Important Areas (OBIAs) for marine
mammals (with specified periods) for
SURTASS LFA sonar operations are the
following:
Name of area
Location of area
(i) Georges Bank ............................................
40°00′ N, 72°30′ W; 39°37′ N, 72°09′ W; 39°54′ N,
71°43′ W; 40°02′ N, 71°20′ W; 40°08′ N, 71°01′
W; 40°04′ N, 70°44′ W; 40°00′ N, 69°24′ W;
40°16′ N, 68°27′ W; 40°34′ N, 67°13′ W; 41°00′
N, 66°24′ W; 41°52′ N, 65°47′ W; 42°20′ N,
66°06′ W; 42°18′ N, 67°23′ W.
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50317
Months of importance
Year-round.
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Name of area
Location of area
(ii) Roseway Basin Right Whale Conservation
Area.
(iii) Great South Channel, U.S. Gulf of Maine,
and Stellwagen Bank National Marine
Sanctuary (NMS).
43°05′ N, 65°40′ W; 43°05′ N, 65°03′ W; 42°45′ N,
65°40′ W; 42°45′ N, 65°03′ W.
41°00.000′ N, 69°05.000′ W; 42°09.000′ N,
67°08.400′ W; 42°53.436′ N, 67°43.873′ W;
44°12.541′ N, 67°16.847′ W; 44°14.911′ N,
67°08.936′ W; 44°21.538′ N, 67°03.663′ W;
44°26.736′ N, 67°09.596′ W; 44°16.805′ N,
67°27.394′ W; 44°11.118′ N, 67°56.398′ W;
43°59.240′ N, 68°08.263′ W; 43°36.800′ N,
68°46.496′ W; 43°33.925′ N, 69°19.455′ W;
43°32.008′ N, 69°44.504′ W; 43°21.922′ N,
70°06.257′ W; 43°04.084′ N, 70°21.418′ W;
42°51.982′ N, 70°31.965′ W; 42°45.187′ N,
70°23.396′ W; 42°39.068′ N, 70°30.188′ W;
42°32.892′ N, 70°35.873′ W; 42°07.748′ N,
70°28.257′ W; 42°05.592′ N, 70°02.136′ W;
42°03.664′ N, 69°44.000′ W; 41°40.000′ N,
69°45.000′ W.
Critical Habitat Boundaries are coastal waters between 31°15′ N and 30°15′ N from the coast out
15 nautical miles (nmi); and the coastal waters
between 30°15′ N and 28°00″ N from the coast
out 5 nmi. (50 CFR § 226.13(c));
OBIA Boundaries are coastal waters between
31°15″ N and 30°15″ N from 12 to 15 nmi..
57°03′ N, 153°00′ W; 57°18′ N, 151°30′ W; 57°00′
N, 151°30′ W; 56°45′ N, 153°00′ W.
(50 CFR § 226.215).
Silver Bank: .............................................................
20°38.899′ N, 69°23.640′ W; 20°55.706′ N,
69°57.984′ W; 20°25.221′ N, 70°00.387′ W;
20°12.833′ N, 69°40.604′ W; 20°13.918′ N,
69°31.518′ W; 20°28.680′ N, 69°31.900′ W
Navidad Bank:
20°15.596′ N, 68°47.967′ W; 20°11.971′ N,
68°54.810′ W; 19°52.514′ N, 69°00.443′ W;
19°54.957′ N, 68°51.430′ W; 19°51.513′ N,
68°41.399′ W.
An exclusion zone following the 500-m isobath extending from 3°31.055′ N, 9°12.226″ E in the
north offshore of Malabo southward to 8°57.470″
S, 12°55.873″ E offshore of Luanda
Between 200- and 2000-m isobaths and the following latitudes: 35°00″ S, 39°00″ S, 40°40″ S,
42°30″ S, 46°00″ S, 48°50″ S..
Coastal waters between 42°00″ S and 43°00″ S
from 12 to 15 nm including the enclosed bays of
Golfo Nuevo, Golfo San Jose, and San Matias.
Golfos San Jose and San Nuevo are within 22
km (14 mi; 12 nm) coastal exclusion zone
Single stratum boundary created from the Cordell
Bank (15 CFR 922.10), Gulf of the Farallones
(15 CFR 922.80), and Monterey Bay (15 CFR
922.30) NMS legal boundaries. Monterey Bay
NMS includes the Davidson Seamount Management Zone
30° E to 80° E, 45° S; 80° E to 150° E, 55° S;
150° E to 50° W, 60° S; 50° W to 30° E, 50° S.
(iv) Southeastern U.S. Right Whale Seasonal
Habitat.
(v) North Pacific Right Whale Critical Habitat
(vi) Silver Bank and Navidad Bank ................
(vii) Coastal waters of Gabon, Congo and
Equatorial Guinea.
(viii) Patagonian Shelf Break ..........................
(ix) Southern Right Whale Seasonal Habitat
(x) Central California National Marine Sanctuaries.
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(xi) Antarctic Convergence Zone ....................
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Months of importance
June through December, annually.
January 1 to November 14, annually.
November 15 to April 15, annually.
March through August, annually.
December through April, annually.
June through October, annually.
Year-round.
May through December, annually.
June through November, annually.
October through March, annually.
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Name of area
Location of area
(xii) Piltun and Chayvo offshore feeding
grounds in the Sea of Okhotsk.
54°09.436′ N, 143°47.408′ W; 54°09.436′ N,
143°17.354′ W; 54°01.161′ N, 143°17.354′ W;
53°53.580′ N, 143°13.398′ W; 53°26.963′ N,
143°28.230′ W; 53°07.013′ N, 143°35.481′ W;
52°48.705′ N, 143°38.447′ W; 52°32.077′ N,
143°37.788′ W; 52°21.605′ N, 143°34.163′ W;
52°09.470′ N, 143°26.582′ W; 51°57.686′ N,
143°30.208′ W; 51°36.033′ N, 143°42.794′ W;
51°08.082′ N, 143°51.301′ W; 51°08.082′ N,
144°16.742′ W; 51°24.514′ N, 144°11.139′ W;
51°48.116′ N, 144°10.809′ W; 52°03.194′ N,
144°20.363′ W; 52°23.235′ N, 144°10.150′ W;
52°28.674′ N, 144°12.787′ W; 52°42.523′ N,
144°10.150′ W; 53°12.972′ N, 143°55.648′ W;
53°18.505′ N, 143°56.637′ W; 53°23.041′ N,
143°53.011′ W; 53°28.250′ N, 143°53.341′ W;
53°44.039′ N, 143°49.056′ W; 53°53.207′ N,
143°50.045′ W; 53°59.819′ N, 143°48.067′ W.
16°03′55.04″ S, 50°27′12.59″ E; 16°12′23.03″ S,
51°03′37.38″ E; 24°30′45.06″ S, 48°26′00.94″ E;
24°15′28.07″ S, 47°46′51.16″ E; 22°18′00.74″ S,
48°14′13.52″ E; 20°52′24.12″ S, 48°43′13.49″ E;
19°22′33.24″ S, 49°15′45.47″ E; 18°29′46.08″ S,
49°37′32.25″ E; 17°38′27.89″ S, 49°44′27.17″ E;
17°24′39.12″ S, 49°39′17.03″ E; 17°19′35.34″ S,
49°54′23.82″ E; 16°45′41.71″ S, 50°15′56.35″ E.
25°55′20.00″ S, 44°05′15.45″ E; 25°46′31.36″ S,
47°22′35.90″ E; 27°02′37.71″ S, 48°03′31.08″ E;
35°13′51.37″ S, 46°26′19.98″ E; 35°14′28.59″ S,
42°35′49.20″ E; 31°36′57.96″ S, 42°37′49.35″ E;
27°41’11.21″ S, 44°30′11.01″ E.
42°50.271′ N, 06°31.883″ E; 42°55.603′ N,
06°43.418″ E; 43°04.374′ N, 06°52.165″ E;
43°12.600′ N, 07°10.440″ E; 43°21.720′ N,
07°19.380″ E; 43°30.600′ N, 07°32.220″ E;
43°33.900′ N, 07°49.920″ E; 43°36.420′ N,
08°05.580″ E; 43°42.600′ N, 08°22.140″ E;
43°50.880′ N, 08°34.500″ E; 43°58.560′ N,
08°47.700″ E; 43°59.040′ N, 08°56.040″ E;
43°57.047′ N, 09°03.540″ E; 43°52.260′ N,
09°08.520″ E; 43°47.580′ N, 09°13.500″ E;
43°36.060′ N, 09°16.620″ E; 43°28.440′ N,
09°05.820″ E; 43°21.360′ N, 09°02.100″ E;
43°16.020′ N, 08°57.240″ E; 43°04.440′ N,
08°47.580″ E; 42°54.900′ N, 08°35.400″ E;
42°45.900′ N, 08°27.540″ E; 42°36.060′ N,
08°22.020″ E; 42°22.620′ N, 08°15.849″ E;
42°07.202′ N, 08°17.174″ E; 41°52.800′ N,
08°15.720″ E; 41°39.780′ N, 08°05.280″ E;
41°28.200′ N, 08°51.600″ E; 42°57.060′ N,
06°19.860″ E.
21°10′02.179″
N,
157°30′58.217″
W;
21°09′46.815″
N,
157°30′22.367″
W;
21°06′39.882″
N,
157°31′00.778″
W;
21°02′51.976″
N,
157°30′30.049″
W;
20°59′52.725″
N,
157°29′28.591″
W;
20°58′05.174″
N,
157°27′35.919″
W;
20°55′49.456″
N,
157°30′58.217″
W;
20°50′44.729″
N,
157°42′42.418″
W;
20°51′02.654″
N,
157°44′45.333″
W;
20°53′56.784″
N,
157°46′04.716″
W;
20°56′32.988″
N,
157°45′33.987″
W;
21°01′27.472″
N,
157°43′10.586″
W;
21°05′20.499″
N,
157°39′27.802″
W;
21°10′02.179″ N, 157°30′58.217″ W.
Centered at 9°N and 88°W .....................................
(xiii) Coastal waters off Madagascar ..............
(xiv) Madagascar Plateau,
Ridge, and Walters Shoal.
Madagascar
(xv) Ligurian-Corsican-Provencal Basin and
Western Pelagos Sanctuary in the Mediterranean Sea.
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(xvi) Hawaiian Islands Humpback Whale
NMS and Penguin Bank.
(xvii) Costa Rica Dome ...................................
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50319
Months of importance
June through November, annually.
July through September, annually for humpback whale breeding and November
through December, annually for migrating
blue whales.
November through December, annually.
July to August, annually.
November through April, annually.
Year-round.
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Name of area
Location of area
(xviii) Great Barrier Reef Between 16° S and
21° S.
16°01.829″ S, 145°38.783″ E; 15°52.215″ S,
146°20.936″ E; 17°28.354″ S, 146°59.392″ E;
20°16.228″ S, 151°39.674″ E; 20°58.381″ S,
150°30.897″ E; 20°17.007″ S, 149°38.247″ E;
20°10.941″ S, 149°18.247″ E; 20°02.403″ S,
149°12.623″ E; 19°53.287″ S, 149°03.986″ E;
19°49.866″ S, 148°52.135″ E; 19°53.287″ S,
148°44.302″ E; 19°47.965″ S, 148°36.870″ E;
19°47.205″ S, 148°26.024″ E; 19°19.978″ S,
147°39.626″ E; 19°14.065″ S, 147°37.014″ E;
19°08.913″ S, 147°31.993″ E; 19°05.667″ S,
147°24.160″ E; 19°07.576″ S, 147°18.134″ E;
18°51.718″ S, 146°51.219″ E; 18°44.258″ S,
146°54.031″ E; 18°37.175″ S, 146°51.420″ E;
18°31.620″ S, 146°43.385″ E; 18°27.595″ S,
146°40.573″ E; 17°36.676″ S, 146°20.488″ E;
17°20.484″ S, 146°16.671″ E; 17°07.745″ S,
146°13.056″ E; 16°49.769″ S, 146°11.047″ E;
16°41.835″ S, 146°03.817″ E; 16°39.706″ S,
145°54.979″ E.
37°12′20.036″ S, 139°31′17.703″ E; 37°37′33.815″
S, 139°42′42.508″ E; 38°10′36.144″ S,
140°22′57.345″
E;
38°44′50.558″
S,
141°33′50.342″
E;
39°07′04.125″
S,
141°11′00.733″
E;
37°28′33.179″
S,
139°10′52.263″ E.
20°59.735′ N, 89°07.675″ E; 20°55.494′ N,
89°09.484″ E; 20°52.883′ N, 89°12.704″ E;
20°55.275′ N, 89°18.133″ E; 21°04.558′ N,
89°25.294″ E; 21°12.655′ N, 89°25.354″ E;
21°13.279′ N, 89°16.833″ E; 21°06.347′ N,
89°15.011″ E.
Boundaries within 23 nm (26.5 m; 42.6 km) of the
coast from 47°07′ N to 48°30′ N latitude.
48°30′01.995″
N,
125°58′38.786″
W;
48°16′55.605″
N,
125°38′52.052″
W;
48°23′07.353″
N,
125°17′10.935″
W;
48°12′38.241″
N,
125°16′42.339″
W;
47°58′20.361″
N,
125°31′14.517″
W;
47°58′20.361″
N,
126°06′16.322″
W;
48°09′46.665″ N, 126°25′48.758″ W.
16°35′34.909″
38°52′30.455″;
16°35′31.619″
38°43′41.069″; 16°40′00.131″ 37°23′52.492″;
19°30′59.069″ 37°23′52.446″; 19°30′59.974″
39°33′38.351″; 19°20′24.752″ 39°30′33.03″;
18°52′16.884″ 39°32′31.789″; 18°45′09.937″
39°32′27.709″; 18°30′59.345″ 39°30′59.669″;
18°27′28.985″ 39°30′13.453″; 18°17′30.429″
39°26′21.073″; 18°07′43.518″ 39°19′52.924″;
18°09′24.931″ 39°16′24.913″; 18°10′04.585″
39°12′30.425″; 18°10′20.682″ 38°39′06.185″;
18°08′50.404″ 38°35′00.059″; 18°06′05.466″
38°31′41.385″; 18°02′09.399″ 38°29′26.179″;
17°58′01.372″ 38°28′45.409″; 17°53′58.883″
38°29′34.612″; 16°48′58.768″ 38°55′23.768″;
16°43′15.682″ 38°53′40.007″.
(xix) Bonney Upwelling on the south coast of
Australia.
(xx) Northern Bay of Bengal and Head of
Swatch-of-No-Ground.
(xxi) Olympic Coast NMS and Prairie, Barkley Canyon, and Nitnat Canyon.
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(xxii) Abrolhos Bank ........................................
(g) Operational Exception for the
SURTASS LFA Sonar Sound Field.
During military operations SURTASS
LFA sonar transmissions may exceed
180 dB re: 1 mPa (rms) within the
boundaries of a SURTASS LFA sonar
OBIA when: operationally necessary to
continue tracking an existing
underwater contact; or operationally
necessary to detect a new underwater
contact within the OBIA. This exception
does not apply to routine training and
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Months of importance
testing with the SURTASS LFA sonar
systems.
§ 218.235
Requirements for monitoring.
(a) The Holder of a Letter of
Authorization issued pursuant to
§§ 216.106 and 218.238 must:
(1) Conduct visual monitoring from
the ship’s bridge during daylight hours
(30 minutes before sunrise until 30
minutes after sunset) during operations
that employ SURTASS LFA sonar in the
active mode. The SURTASS vessels
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May through September, annually.
December through May, annually.
Year-round.
Olympic NMS: December, January, March,
and May, annually.
The Prairie, Barkley Canyon, and Nitnat
Canyon: June through September, annually.
August through November, annually.
shall have lookouts to maintain a
topside watch with standard binoculars
(7x) and with the naked eye.
(2) Use low frequency passive
SURTASS sonar to listen for vocalizing
marine mammals; and
(3) Use the HF/M3 active sonar to
locate and track marine mammals in
relation to the SURTASS LFA sonar
vessel and the sound field produced by
the SURTASS LFA sonar source array,
subject to the ramp-up requirements in
§ 216.234(e).
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Federal Register / Vol. 77, No. 161 / Monday, August 20, 2012 / Rules and Regulations
(b) Monitoring under paragraph (a) of
this section must:
(1) Commence at least 30 minutes
before the first SURTASS LFA sonar
transmission;
(2) Continue between transmission
pings; and
(3) Continue either for at least 15
minutes after completion of the
SURTASS LFA sonar transmission
exercise or, if marine mammals are
exhibiting unusual changes in
behavioral patterns, for a period of time
until behavior patterns return to normal
or conditions prevent continued
observations.
(c) Holders of Letters of Authorization
for activities described in § 218.230 are
required to cooperate with the National
Marine Fisheries Service and any other
federal agency for monitoring the
impacts of the activity on marine
mammals.
(d) Holders of Letters of Authorization
must designate qualified on-site
individuals to conduct the mitigation,
monitoring and reporting activities
specified in the Letter of Authorization.
(e) Holders of Letters of Authorization
will continue to assess data from the
Marine Mammal Monitoring Program
and work toward making some portion
of that data, after appropriate security
reviews, available to scientists with
appropriate clearances. Any portions of
the analyses conducted by these
scientists based on these data that are
determined to be unclassified after
appropriate security reviews will be
made publically available.
(f) Holders of Letters of Authorization
will continue to explore the feasibility
of coordinating with other fleet assets
and/or range monitoring programs to
include the use of SURTASS towed
horizontal line arrays to augment the
collection of marine mammal
vocalizations before, during, and after
designated exercises.
(g) Holders of Letters of Authorization
will collect ambient noise data and will
explore the feasibility of declassifying
and archiving the ambient noise data for
incorporation into appropriate ocean
noise budget efforts.
(h) Holders of Letters of Authorization
will convene a Scientific Advisory
Group (SAG) to analyze different types
of monitoring/research that could
increase the understanding of the
potential effects of low-frequency active
sonar transmissions on beaked whales
and/or harbor porpoises.
(i) Holders of Letters of Authorization
must conduct all monitoring required
under the Letter of Authorization.
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§ 218.236
Requirements for reporting.
(a) The Holder of the Letter of
Authorization must submit classified
and unclassified quarterly mission
reports to the Director, Office of
Protected Resources, NMFS, no later
than 30 days after the end of each
quarter beginning on the date of
effectiveness of a Letter of Authorization
or as specified in the appropriate Letter
of Authorization. Each quarterly
mission report will include all activemode missions completed during that
quarter. At a minimum, each classified
mission report must contain the
following information:
(1) Dates, times, and location of each
vessel during each mission;
(2) Information on sonar
transmissions during each mission;
(3) Results of the marine mammal
monitoring program specified in the
Letter of Authorization; and
(4) Estimates of the percentages of
marine mammal species and stocks
affected (both for the quarter and
cumulatively for the year) covered by
the Letter of Authorization.
(b) The Holder of a Letter of
Authorization must submit an
unclassified annual report to the
Director, Office of Protected Resources,
NMFS, no later than 45 days after the
expiration of a Letter of Authorization.
The reports must contain all the
information required by the Letter of
Authorization.
(c) A final comprehensive report must
be submitted to the Director, Office of
Protected Resources, NMFS, at least 240
days prior to expiration of these
regulations. In addition to containing all
the information required by any final
year Letter of Authorization, this report
must contain an unclassified analysis of
new passive sonar technologies and an
assessment of whether such a system is
feasible as an alternative to SURTASS
LFA sonar.
(d) The Navy will continue to assess
the data collected by its undersea arrays
and work toward making some portion
of that data, after appropriate security
reviews, available to scientists with
appropriate clearances. Any portions of
the analyses conducted by these
scientists based on these data that are
determined to be unclassified after
appropriate security reviews will be
made publically available. The Navy
will provide a status update to NMFS
when they submit their annual
application.
(e) Following the Scientific Advisory
Group’s (SAG) submission of findings,
and assuming the SAG recommends
going forward with beaked whale and/
or harbor porpoise monitoring/research,
the Navy will either:
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50321
(1) Draft a plan of action outlining
their strategy for implementing the
SAG’s recommendations; or
(2) Describe in writing why none of
the SAG’s recommendations are feasible
and meet with NMFS to discuss any
other potential options.
§ 218.237 Applications for Letters of
Authorization.
(a) To incidentally take marine
mammals pursuant to these regulations,
the U.S. Navy authority conducting the
activity identified in § 218.230 must
apply for and obtain a Letter of
Authorization in accordance with
§ 216.106.
(b) The application for a Letter of
Authorization must be submitted to the
Director, Office of Protected Resources,
NMFS, at least 60 days before the date
that either the vessel is scheduled to
begin conducting SURTASS LFA sonar
operations or the previous Letter of
Authorization is scheduled to expire.
(c) All applications for a Letter of
Authorization must include the
following information:
(1) The date(s), duration, and the
area(s) where the vessel’s activity will
occur;
(2) The species and/or stock(s) of
marine mammals likely to be found
within each area;
(3) The type of incidental taking
authorization requested (i.e., take by
Level A and/or Level B harassment);
(4) The estimated percentage and
numbers of marine mammal species/
stocks potentially affected in each area
for the period of effectiveness of the
Letter of Authorization; and
(5) The means of accomplishing the
necessary monitoring and reporting that
will result in increased knowledge of
the species and the level of taking or
impacts on marine mammal
populations.
(d) The National Marine Fisheries
Service will review an application for a
Letter of Authorization in accordance
with § 216.104(b) and, if adequate and
complete, issue a Letter of
Authorization.
§ 218.238
Letters of Authorization.
(a) A Letter of Authorization, unless
suspended or revoked, will be valid for
a period of time not to exceed one year,
but may be renewed annually subject to
renewal conditions in § 218.239.
(b) Each Letter of Authorization will
set forth:
(1) Permissible methods of incidental
taking;
(2) Authorized geographic areas for
incidental takings;
(3) Means of effecting the least
practicable adverse impact on the
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Federal Register / Vol. 77, No. 161 / Monday, August 20, 2012 / Rules and Regulations
species of marine mammals authorized
for taking, their habitat, and the
availability of the species for
subsistence uses; and
(4) Requirements for monitoring and
reporting incidental take.
(c) Issuance of a letter of authorization
will be based on a determination that
the level of taking will be consistent
with the findings made for the total
taking allowable under these
regulations.
(d) Notice of issuance or denial of an
application for a Letter of Authorization
will be published in the Federal
Register within 30 days of a
determination.
§ 218.239 Renewal of Letters of
Authorization.
mstockstill on DSK4VPTVN1PROD with RULES3
(a) A Letter of Authorization issued
for the activity identified in § 218.230
may be renewed upon:
(1) Notification to NMFS that the
activity described in the application
submitted under § 218.237 will be
undertaken and that there will not be a
substantial modification to the
described activity, mitigation or
monitoring undertaken during the
upcoming period;
(2) Notification to NMFS of the
information identified in § 218.237(c);
(3) Timely receipt of the monitoring
reports required under § 218.236, which
have been reviewed by NMFS and
determined to be acceptable;
(4) A determination by NMFS that the
mitigation, monitoring and reporting
measures required under §§ 218.234,
218.235, and 218.236 and the previous
Letter of Authorization were undertaken
and will be undertaken during the
upcoming period of validity of a
renewed Letter of Authorization; and
(5) A determination by NMFS that the
level of taking will be consistent with
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17:06 Aug 17, 2012
Jkt 226001
the findings made for the total taking
allowable under these regulations.
(b) If a request for a renewal of a
Letter of Authorization indicates that a
substantial modification to the
described work, mitigation, or
monitoring will occur, or if NMFS
proposes a substantial modification to
the Letter of Authorization, NMFS will
provide a period of 30 days for public
review and comment on the proposed
modification. Amending the areas for
upcoming SURTASS LFA sonar
operations is not considered a
substantial modification to the 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 within 30 days of a
determination.
§ 218.240 Modifications to Letters of
Authorization.
(a) Except as provided in paragraph
(b) of this section, no substantial
modification (including withdrawal or
suspension) to a Letter of Authorization
subject to the provisions of this subpart
shall be made by NMFS until after
notification and an opportunity for
public comment has been provided. For
purposes of this paragraph, a renewal of
a Letter of Authorization, without
modification, except for the period of
validity and a listing of planned
operating areas, or for moving the
authorized SURTASS LFA sonar system
from one ship to another, is not
considered a substantial modification.
(b) If NMFS determines that an
emergency exists that poses a significant
risk to the well-being of the species or
stocks of marine mammals specified in
§ 218.230(b)(1), (2), or (3), NMFS may
modify a Letter of Authorization
PO 00000
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Fmt 4701
Sfmt 9990
without prior notice and opportunity for
public comment. Notification will be
published in the Federal Register
within 30 days of the action.
§ 218.241
Adaptive Management.
NMFS may modify (including through
addition or deletion) or augment the
existing mitigation or monitoring
measures (after consulting with the
Navy regarding the practicability of the
modifications) if doing so creates a
reasonable likelihood of more
effectively accomplishing the goals of
mitigation and monitoring set forth in
the preamble of these regulations.
NMFS will provide a period of 30 days
for public review and comment if such
modifications are substantial. NMFS
and the Navy will meet annually (if
deemed necessary by either agency) to
discuss the monitoring reports, Navy
research and development outcomes,
current science, and determine whether
mitigation or monitoring modifications
are appropriate. Below are some of the
possible sources of new data that could
contribute to the decision to modify the
mitigation or monitoring measures:
(a) Results from the Navy’s
monitoring from the previous year’s
operation of SURTASS LFA sonar.
(b) Compiled results of Navy-funded
research and development studies.
(c) Results from specific stranding
investigations.
(d) Results from general marine
mammal and sound research funded by
the Navy or other sponsors.
(e) Any information that reveals
marine mammals may have been taken
in a manner, extent or number not
anticipated by these regulations or
subsequent Letters of Authorization.
[FR Doc. 2012–20214 Filed 8–14–12; 4:15 pm]
BILLING CODE 3510–22–P
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Agencies
[Federal Register Volume 77, Number 161 (Monday, August 20, 2012)]
[Rules and Regulations]
[Pages 50289-50322]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-20214]
[[Page 50289]]
Vol. 77
Monday,
No. 161
August 20, 2012
Part IV
Department of Commerce
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National Oceanic and Atmospheric Administration
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50 CFR Part 218
Taking and Importing Marine Mammals: Taking Marine Mammals Incidental
to U.S. Navy Operations of Surveillance Towed Array Sensor System Low
Frequency Active Sonar; Final Rule
Federal Register / Vol. 77 , No. 161 / Monday, August 20, 2012 /
Rules and Regulations
[[Page 50290]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 218
[Docket No. 110808485-2148-02]
RIN 0648-BB14
Taking and Importing Marine Mammals: Taking Marine Mammals
Incidental to U.S. Navy Operations of Surveillance Towed Array Sensor
System Low Frequency Active Sonar
AGENCY: National Marine Fisheries Service, National Oceanic and
Atmospheric Administration, Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: Upon application from the U.S. Navy (Navy), we (the National
Marine Fisheries Service) are issuing regulations under the Marine
Mammal Protection Act to govern the unintentional taking of marine
mammals incidental to conducting operations of Surveillance Towed Array
Sensor System (SURTASS) Low Frequency Active (LFA) sonar on a maximum
of four naval surveillance vessels in areas of the Pacific, Atlantic,
and Indian Oceans and the Mediterranean Sea, from the period of August
15, 2012, through August 15, 2017. These regulations: allow us to issue
Letters of Authorization (LOA) for the incidental take of marine
mammals during the Navy's specified activities and timeframes; set
forth the permissible methods of taking; set forth other means of
effecting the least practicable adverse impact on marine mammal species
and their habitat; and set forth requirements pertaining to the
monitoring and reporting of the incidental take.
DATES: Effective August 15, 2012, through August 15, 2017.
ADDRESSES: To obtain an electronic copy of: the Navy's application
(which contains a list of the references within this document); our
Record of Decision; and other documents that we have cited in this
document, write to P. Michael Payne, Chief, Permits and Conservation
Division, Office of Protected Resources, National Marine Fisheries
Service, 1315 East-West Highway, Silver Spring, MD 20910-3225, or
download electronic copies at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm#applications or telephone the contact listed here (see
FOR FURTHER INFORMATION CONTACT).
The Navy released a Final Supplemental Environmental Impact
Statement/Supplemental Overseas Environmental Impact Statement (FSEIS/
SOEIS) for employment of SURTASS LFA sonar on June 8, 2012. The public
may view the document at: https://www.surtass-lfa-eis.com. We
participated in the development of this document as a cooperating
agency under the Council on Environmental Quality's regulations
implementing the National Environmental Policy Act of 1972.
FOR FURTHER INFORMATION CONTACT: Jeannine Cody, Office of Protected
Resources, NMFS, (301) 427-8401.
SUPPLEMENTARY INFORMATION:
Executive Summary
This regulation allows us to issue Letters of Authorization to the
Navy (upon their request) for the incidental take of marine mammals
during SURTASS LFA sonar operations. The SURTASS LFA sonar system is a
long-range, low frequency sonar that has both active and passive
acoustic components. The Navy will use the system for long-range
detection of quiet, hard-to-find submarines. The Navy's activities are
military readiness activities under the Marine Mammal Protection Act of
1972, as amended (MMPA; 16 U.S.C. 1631 et seq.) as defined by the
National Defense Authorization Act for Fiscal Year 2004 (NDAA; Pub. L.
108-136).
This is the third rule for SURTASS LFA sonar operations under the
Marine Mammal Protection Act. The 2007 regulations governing take
incidental to SURTASS LFA sonar activities expire on August 15, 2012.
We published the first rule, effective from August 2002 through August
2007, on July 16, 2002 (67 FR 46712), and published the second rule on
August 21, 2007 (72 FR 46846). For this five-year period (August 2012
through August 2017), covered under this regulation, the Navy is
proposing to conduct the same types of sonar activities as they have
conducted over the past nine years.
Purpose and Need for This Regulatory Action
In 2011, we received an application from the Navy requesting five-
year regulations and Letters of Authorizations to take marine mammals,
by harassment, incidental to conducting SURTASS LFA sonar operations in
areas of the world's oceans from August 2012 through August 2017. These
operations, which constitute a military readiness activity, have the
potential to cause behavioral disturbance and injury (if not mitigated)
to marine mammals.
Section 101(a)(5)(A) of the MMPA directs the Secretary of Commerce
(Secretary) to authorize, upon request, the incidental, but not
intentional, taking of marine mammals of a species or population stock,
by U.S. citizens who engage in a specified activity (other than
commercial fishing) within a specified geographical region if after
notice and public comment: (1) We make certain findings; and (2) issue
regulations.
Under this five-year regulation, the Navy will submit an annual
application to us for Letters of Authorizations for up to four vessels
to take marine mammals, incidental to conducting SURTASS LFA sonar
operations.
This regulation establishes a framework to authorize incidental
take through our issuing Letters of Authorizations to the Navy for
SURTASS LFA sonar operations and contains mitigation, monitoring, and
reporting requirements.
Legal Authority for the Regulatory Action
Section 101(a)(5)(A) of the Marine Mammal Protection Act and our
implementing regulations at 50 CFR part 216, subpart I provide the
legal basis for issuing the five-year regulations and Letters of
Authorization.
Summary of Major Provisions Within the Regulation
The following provides a summary of some of the major provisions
within this third rulemaking for SURTASS LFA sonar:
Required suspension/delay of SURTASS LFA sonar
transmissions if a marine mammal enters the 2-kilometer (km) (1.2-mile
(mi); 1.1 nautical mile (nm)) mitigation and buffer zones around the
vessel;
Required geographic restrictions in designated offshore
biologically important areas (OBIA) and within 22 km (14 mi; 12 nm) of
any coastline, including islands, for SURTASS LFA sonar operations to
protect marine mammals;
Required visual, passive acoustic and active acoustic
monitoring during routine training, testing and military operations of
SURTASS LFA sonar to support the implementation of mitigation measures
to protect marine mammals;
Required monitoring of ambient noise data for
incorporation into appropriate ocean noise budget efforts and analyses;
Required monitoring of marine mammal stranding incidents;
and
Required research on how marine mammals (including harbor
porpoises (Phocoena phocoena) and beaked whales (Mesoplodon spp.))
respond to
[[Page 50291]]
SURTASS LFA sonar as well as research on marine mammal vocalizations
before, during, and after designated exercises with SURTASS LFA sonar.
Cost and Benefits
This final rule, specific only to the Navy's SURTASS LFA sonar
operations, is not significant under Executive Order 12866, Regulatory
Planning and Review.
Availability of Supporting Information
We provided extensive SUPPLEMENTARY INFORMATION in the Notice of
the proposed rule for this activity in the Federal Register on Friday,
January 6, 2012 (77 FR 842). We did not reprint all of that information
here in its entirety; instead, we represent all sections from the
proposed rule in this document and provide either a summary of the
material presented in the proposed rule or a note referencing the
page(s) in the proposed rule where the public can find the information.
We address any information that has changed since the proposed rule in
this document. Additionally, this final rule contains a section that
responds to the public comments submitted during the 30-day public
comment period and the 15-day extension of the comment period for the
proposed rule.
Background
Section 101(a)(5)(A) of the MMPA directs the Secretary to
authorize, upon request, the incidental, but not intentional, taking of
small numbers of marine mammals of a species or population stock, by
U.S. citizens who engage in a specified activity (other than commercial
fishing) within a specified geographical region if, after notice and
public comment: (1) We make certain findings; and (2) we issue
regulations. We are required to grant authorization for the incidental
taking of marine mammals if we find that the total taking will have a
negligible impact on the species or stock(s); and will not have an
unmitigable adverse impact on the availability of the species or
stock(s) for subsistence uses (where relevant). We must also set forth
the permissible methods of taking; other means of effecting the least
practicable adverse impact on the species or stock and its habitat; and
requirements pertaining to the mitigation, monitoring, and reporting of
the takings.
Accordingly, this regulation, which governs our issuance of Letters
of Authorization (LOA) to the Navy, designates: (1) The permissible
methods of taking; (2) mitigation measures to minimize adverse impacts
to the lowest level practicable on marine mammal species and their
habitat; and (3) requirements for monitoring and reporting incidental
take.
We have defined negligible impact in 50 CFR 216.103 as ``* * * an
impact resulting from the specified activity that cannot be reasonably
expected to, and is not reasonably likely to, adversely affect the
species or stock through effects on annual rates of recruitment or
survival.''
The National Defense Authorization Act of 2004 amended section
101(a)(5)(A) of the MMPA by removing the small numbers and specified
geographic region provisions; revising the definition of harassment as
it applies to a military readiness activity; and explicitly requiring
that our determination of ``least practicable adverse impact'' include
consideration of: (1) Personnel safety; (2) the practicality of
implementation; and (3) impact on the effectiveness of the military
readiness activity.
With respect to military readiness activities, the MMPA defines
harassment as ``(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 August 17, 2011, we received an application from the Navy
requesting rulemaking and LOAs for the take of individuals of 94
species of marine mammals (70 cetaceans and 24 pinnipeds), by Level A
and Level B harassment, incidental to upcoming routine training and
testing and use of the SURTASS LFA sonar system during military
operations in areas of the Pacific, Atlantic, and Indian Oceans and the
Mediterranean Sea over the course of five years (2012-2017). The Navy
would use the sonar system on a maximum of four naval surveillance
vessels during military operations which they have designated as
military readiness activities.
The Navy states and we concur, that these military readiness
activities may incidentally take marine mammals present within the
Navy's mission areas by exposing them to sound from low-frequency
active sonar sources. The Navy requests authorization to take
individuals of these marine mammals by Level A and Level B harassment.
However, as we discuss later in this document, the Navy will likely
avoid Level A harassment by implementing required mitigation and
monitoring measures.
Please refer to Tables 9-27 (pages 123-140) of the Navy's
application for detailed information on the estimated percentages of
marine mammal stocks potentially affected by SURTASS LFA sonar
activities in areas of the Pacific, Atlantic, and Indian Oceans and the
Mediterranean Sea per year. This final rule does not specify the number
of marine mammals that may be taken in the proposed locations because
the Navy calculates the take estimates annually through various inputs
such as mission location, mission duration, and season of operation.
As with the 2002 and 2007 rules, the Navy will limit operation of
SURTASS LFA sonar to ensure that no more than 12 percent of any marine
mammal stock would be taken by Level B harassment, annually, over the
course of this rule. This annual, per-stock cap applies regardless of
the number of SURTASS LFA sonar vessels operating. The Navy will use
the 12 percent cap to guide its mission planning for selecting
potential operational areas within each annual authorization
application.
As a result of the required mitigation and monitoring measures and
standard operating procedures and the Navy's mission planning which, to
the greatest extent feasible considering national security tasking,
avoids conducting SURTASS LFA sonar operations in areas of high marine
animal densities, we believe that the incidental take of marine mammals
would likely be lower than the Navy's requested amount of incidental
take.
In the Navy's application, their acoustic analyses predict that
less than 0.0001 percent of the endangered north Pacific right whale
(Eubalaena japonica) population; less than 0.0001 of the northern
elephant seal (Mirounga angustirostris) population; and 0.00 percent of
the stocks of all other marine mammal species may be exposed to levels
of sound likely to result in Level A harassment. Quantitatively, the
Navy's request translates into take estimates of zero animals for any
species, including north Pacific right whales. However, because the
probability of detection by the Navy's active High-Frequency Marine
Mammal Monitoring (HF/M3) sonar system within the SURTASS LFA sonar
mitigation and buffer zones is not 100 percent, we will include a small
number of Level A harassment takes for marine mammals over the course
of the five-year regulations based on qualitative
[[Page 50292]]
analyses. These are the only quantitative adjustments that we have made
to the Navy's requested takes from their modeled exposure results.
Because the required mitigation measures will minimize any
potential risk for mortality and SURTASS LFA sonar has operated under
previous regulations for the last ten years without any reports of
mortality, we do not expect any mortality to occur as a result of the
Navy's SURTASS LFA sonar operations. Thus, we are not authorizing any
mortality incidental to the Navy's routine training and testing and
military operations of the SURTASS LFA sonar system.
Description of Specified Activities
The proposed rule included a complete description of the Navy's
specified activities covered by these final regulations (for which we
would authorize the associated incidental take of marine mammals in
annual LOAs and described the nature and levels of the use of the
SURTASS LFA sonar system (77 FR 842; January 6, 2012; page 843-846).
These military readiness activities for SURTASS LFA sonar consist of
routine training and testing as well as use of the system during
military operations which involves acoustic sources, including low
frequency active sonar and high-frequency active sonar components.
Below we summarize the description of the specified activities and one
small correction from the proposed rule.
Potential SURTASS LFA Sonar Operational Areas
Based on the Navy's current operational requirements, potential
operations for SURTASS LFA sonar vessels from August 2012 through
August 2017 would include areas located in the Pacific, Indian, and
Atlantic Oceans and Mediterranean Sea. The proposed rule provided a
list of the Navy's potential operating areas in Table 2 relevant to
U.S. national security interests (77 FR 842; January 6, 2012; page 843-
844). Use of the SURTASS LFA sonar system could occur on a maximum of
four naval surveillance vessels: the United States Naval Ship (USNS)
ABLE, the USNS EFFECTIVE, the USNS IMPECCABLE, and the USNS VICTORIOUS.
The Navy will not operate SURTASS LFA sonar in polar regions (i.e.,
Arctic and Antarctic waters) of the world. The Arctic Ocean, the Bering
Sea (including Bristol Bay and Norton Sound), portions of the
Norwegian, Greenland, and Barents Seas north of 72[deg] North (N)
latitude, plus Baffin Bay, Hudson Bay, and the Gulf of St. Lawrence are
non-operational areas for SURTASS LFA sonar. In the Antarctic, the Navy
will not conduct SURTASS LFA sonar operations in areas south of 60[deg]
South (S) latitude. The Navy has excluded polar waters from operational
planning because of the inherent inclement weather conditions and the
navigational and operational (equipment) danger that icebergs pose to
SURTASS LFA sonar vessels. Further, the Navy would operate SURTASS LFA
sonar such that the sound field does not exceed 180 decibels (dB) re: 1
[micro]Pa within the coastal standoff zone (i.e., 22 km; 14mi; 12 nm
from any coastline) or seaward of any OBIA boundary for SURTASS LFA
sonar operations, identified later in this document.
We have included additional operational restrictions beyond what
the Navy proposed in their application for SURTASS LFA sonar operations
within this rule. We are requiring: (1) An additional 1-km (0.62 mi;
054 nm) buffer around the Navy's 1-km (0.62 mi; 054 nm) LFA sonar
mitigation zone to protect marine mammals from entering the 180-
dBisopleth around the SURTASS LFA sonar vessel; and (2) an additional
1-km (0.62 mi; 054 nm) buffer seaward of the outer perimeter of any
OBIA.
Table 1 summarizes a projected annual deployment schedule for one
surveillance vessel using SURTASS LFA sonar.
Table 1--Example Annual Deployment Schedule for One Surveillance Vessel
Using SURTASS LFA Sonar
------------------------------------------------------------------------
On mission Days Off mission Days
------------------------------------------------------------------------
Transit........................ 54 In-Port Upkeep... 40
Active Transmissions...........
432 transmission hours based on 240 Regular Overhaul. 31
a 7.5% duty cycle..
----------- ----------
Total Days on Mission...... 294 Total Days off 71.
Mission.
------------------------------------------------------------------------
In the proposed rule, we incorrectly stated that a normal SURTASS
LFA sonar deployment schedule for a single vessel would involve 240
days of active sonar transmissions (77 FR 842; January 6, 2012; page
843). The correct statement is that the each vessel will perform up to
240 days of active operations and transmit SURTASS LFA sonar up to 432
hours.
Brief Background on Sound, Marine Mammal Hearing, and Vocalization
An understanding of the basic properties of underwater sound,
marine mammal hearing, and vocalization is necessary to comprehend many
of the concepts and analyses presented in this document. The proposed
rule contains a section that provides a brief background on the
principles of sound that are frequently referred to in this rulemaking
(77 FR 842; January 6, 2012; pages 857-859). 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 sound
metric used in our analysis (sound pressure level and single ping
equivalent). The information contained in the proposed rule has not
changed.
Acoustic stimuli (i.e., increased underwater sound) generated by
the SURTASS LFA sonar system's low-frequency acoustic transmissions
have the potential to cause take of marine mammals in the operational
areas. The operation of the SURTASS LFA sonar system during at-sea
operations would result in the generation of sound or pressure waves in
the water at or above levels that we have determined would result in
take. This is the principal means of marine mammal taking associated
with these military readiness activities. At no point do we expect the
Navy to have more than four SURTASS LFA sonar systems in use, and so
this rule analyzes the effects on marine mammals due to the deployment
of up to four SURTASS LFA sonar systems from 2012 through 2017.
Description of Marine Mammals in the Area of the Specified Activities
Ninety-four (94) marine mammal species or populations/stocks have
confirmed or possible occurrence within potential SURTASS LFA sonar
operational areas in the Pacific, Atlantic, and Indian Oceans and the
Mediterranean Sea. Twelve species of
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baleen whales (mysticetes), 58 species of toothed whales, dolphins, or
porpoises (odontocetes), and 24 species of seals or sea lions
(pinnipeds) could be affected by SURTASS LFA sonar operations.
Fifteen of the 94 marine mammal species are endangered and three of
the 94 marine mammal species are threatened under the Endangered
Species Act of 1973 (ESA; 16 U.S.C. 1531 et seq.). Marine mammal
species under our jurisdiction that are endangered include: the blue
whale (Balaenoptera musculus); fin whale (Balaenoptera physalus); sei
whale (Balaenoptera borealis); humpback whale (Megaptera novaeangliae);
bowhead whale (Balaena mysticetus); North Atlantic right whale
(Eubalaena glacialis); North Pacific right whale (Eubalena japonica);
southern right whale (Eubalaena australis); gray whale (Eschrichtius
robustus); sperm whale (Physeter macrocephalus); the Cook Inlet stock
of beluga whale (Delphinapterus leucas); the Southern Resident
population of Killer whale (Orca orcinus); the western distinct
population segment (DPS) of the Steller sea lion (Eumetopias jubatus);
Mediterranean monk seal (Monachus monachus); and Hawaiian monk seal
(Monachus schauinslandi). In addition, the Hawaiian insular distinct
population segment of false killer whale (Pseudorca crassidens) is a
candidate for proposed listing as endangered.
The three threatened marine mammal species under our jurisdiction
include: the eastern distinct population segment of the Steller sea
lion (currently proposed for delisting); the Guadalupe fur seal
(Arctocephalus townsendi) and the southern distinct population segment
of the spotted seal (Phoca largha).
The threatened and endangered marine mammal species mentioned
previously are also depleted under the Marine Mammal Protection Act.
Other species listed as depleted include: the western north Atlantic
coastal stock of bottlenose dolphin (Tursiops truncatus); the
northeastern offshore stock of the pantropical spotted dolphin
(Stenella attenuata); and the eastern stock of the spinner dolphin
(Stenella longirostris).
Ringed seals (Phoca hispida), bearded seals (Erignathus barbatus),
Chinese river dolphins (Lipotes vexillifer) and the vaquita (Phocoena
sinus) do not occur within the Navy's potential SURTASS LFA sonar
operational areas (see 77 FR 842; January 6, 2012; page 844).
The U.S. Fish and Wildlife Service is responsible for managing the
following marine mammal species: southern sea otter (Enhydra lutris),
polar bear (Ursus maritimus), walrus (Odobenus rosmarus), west African
manatee (Trichechus senegalensis), Amazonian manatee (Trichechus
inunguis), west Indian manatee (Trichechus manatus), and dugong (Dugong
dugon). None of these species occur in geographic areas that would
overlap with potential SURTASS LFA sonar operational areas.
The Description of Marine Mammals in the Area of the Specified
Activities section has not changed from what was in the proposed rule
(77 FR 842; January 6, 2012; pages 848-857). Tables 3 through 21 of the
proposed rule provided lists of marine mammal species known to occur or
potentially occur within the Navy's models of potential SURTASS LFA
sonar operational areas relevant to U.S. national security interests.
Tables 4.5 through 4.23 in the 2012 FSEIS/SOEIS also provide
information on the percentages of stocks potentially affected by
SURTASS LFA sonar operations. Although not repeated in this final rule,
we have reviewed these data, determined them to be the best available
scientific information for the purposes of the rulemaking, and consider
this information part of the administrative record for this action.
Potential Effects of the Specified Activity on Marine Mammals
For the purpose of MMPA authorizations, our effects assessments
serve four primary purposes:
(1) Identification of the permissible methods of taking, meaning
the nature of the take (e.g., resulting from anthropogenic noise versus
from ship strike, etc.); the regulatory level of take (i.e., mortality
versus Level A or Level B harassment); and the estimated amount of
take;
(2) Informing the prescription of means of effecting the least
practicable adverse impact on such species or stock and its habitat
(i.e., mitigation);
(3) Supporting the determination of 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); and
(4) Determining whether the specified activity will have an
unmitigable adverse impact on the availability of the species or
stock(s) for subsistence uses.
In the Potential Effects of the Specified Activity on Marine
Mammals section of the proposed rule, we included a qualitative
discussion of the different ways that SURTASS LFA sonar operations may
potentially affect marine mammals without consideration of mitigation
and monitoring measures (see 77 FR 842; January 6, 2012; pages 860-
874). Marine mammals may experience direct physiological effects (e.g.,
threshold shift and non-acoustic injury, acoustic masking, impaired
communication, stress responses, behavioral disturbance, stranding,
behavioral responses from vessel movement, and injury or death from
vessel collisions). The information contained in this section in the
proposed rule has not changed.
Later in the Estimated Take of Marine Mammals section in this
document, we relate and quantify the potential effects to marine
mammals from SURTASS LFA sonar operations discussed in this section to
the MMPA definitions of Level A and Level B harassment.
Anticipated Effects on Marine Mammal Habitat
We anticipate that the specified activity may result in marine
mammals avoiding certain areas due to temporary ensonification. This
impact is temporary and reversible, which we considered in proposed
rule as behavioral modification. The main impact associated with the
activity would be temporarily elevated noise levels and the associated
direct effects on marine mammals.
We included a detailed discussion of the potential effects of the
Navy's SURTASS LFA sonar operations on marine mammal habitat, including
critical habitat and marine mammal prey species (77 FR 842; January 6,
2012; pages 874-875). The information contained in the Anticipated
Effects on Marine Mammal Habitat section has not changed from what was
in the proposed rule.
Mitigation
In order to issue regulations and LOAs under section 101(a)(5)(A)
of the MMPA, we must set forth the ``permissible methods of taking
pursuant to such activity, and other means of effecting the least
practicable adverse impact on such species or stock and its habitat,
paying particular attention to rookeries, mating grounds, and areas of
similar significance.''
The National Defense Authorization Act for Fiscal Year 2004 amended
section 101(a)(5)(A) of the MMPA 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 routine training and testing as well as use
of the system during military operations described in the SURTASS
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LFA sonar application qualify as military readiness activities.
We have reviewed the Navy's proposed SURTASS LFA sonar activities
and the proposed mitigation measures in the Navy's application to
determine whether the resulting activities and mitigation measures
would effect the least practicable adverse impact on marine mammals
which includes a careful balancing of the likely degree to which the
measure is expected to minimize adverse impacts to marine mammals with
the likely effect of that measure on personnel safety, practicality of
implementation, and impact of the effectiveness of the military
readiness activity (i.e., minimizing adverse impacts to the lowest
level practicable with mitigation measures).
Any mitigation measure that we prescribe should be able to
accomplish, have a reasonable likelihood of accomplishing (based on
current science), or contribute to the accomplishment of one or more of
the general goals listed here:
Goal (a): Avoidance or minimization of injury or death of marine
mammals wherever possible (goals b, c, and d may contribute to this
goal).
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 SURTASS LFA sonar or other activities expected to
result in the take of marine mammals (this goal may contribute to goal
a or to reducing harassment takes only).
Goal (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 SURTASS LFA sonar or other activities
expected to result in the take of marine mammals (this goal may
contribute to goal a or to reducing harassment takes only).
Goal (d): A reduction in the intensity of exposures (either total
number or number at biologically important time or location) to
received levels of SURTASS LFA sonar or other activities expected to
result in the take of marine mammals (this goal may contribute to goal
a or to reducing the severity of harassment takes only).
Goal (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.
Goal (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.
We described the Navy's proposed mitigation measures, as well as
those that we added, in detail in the proposed rule (77 FR 842; January
6, 2012; pages 875-879). These required mitigation measures, which are
summarized below, have not changed with the exception of the addition
of one more OBIA. Following are the mitigation and monitoring measures
initially proposed by the Navy:
A 180-dB re:1 [micro]Pa isopleth SURTASS LFA sonar
mitigation zone around the vessel;
Delay or suspension of SURTASS LFA sonar transmissions if
the Navy detects a marine mammal entering or within the LFA sonar
mitigation zone (i.e., the 180-dB re: 1 [micro]Pa isopleth) by any of
the following detection methods;
(a) Visual monitoring;
(b) Passive acoustic monitoring; or
(c) Active acoustic monitoring;
Geographic and operational restrictions to avoid
generating sound levels above 180 dB re: 1 [micro]Pa in the following
areas:
(a) An OBIA; or
(b) Within coastal standoff zones (22 km; 14 mi; 12 nm of any
coastline).
In the proposed rule, we added the following mitigation
requirements:
An additional 1-km (0.62 mi; 054 nm) buffer zone around
the 180-dB re: 1 [micro]Pa isopleth SURTASS LFA sonar mitigation zone;
An additional 1-km (0.62 mi; 054 nm) buffer zone seaward
of any OBIA boundary.
Delay or suspension of SURTASS LFA sonar transmissions if
the Navy detects a marine mammal entering the 1-km (0.62 mi; 054 nm)
buffer zone around the SURTASS LFA sonar mitigation zone.
Within this final rule, we have added additional mitigation
measures based upon comments received during the public comment period
for the proposed rule (77 FR 842; January 6, 2012) and the Navy's 2011
Draft Supplemental Environmental Impact Statement/Overseas
Environmental Impact Statement.
Based on our evaluation of 367 potential areas within the Hoyt's
(2011) 2nd Edition of Marine Protected Areas for Whales, Dolphins and
Porpoises (see Appendix F of the Navy's 2012 FSEIS/SOEIS), we
identified three additional areas for consideration as OBIAs for marine
mammals. They were: (1) Abrolhos Bank in the southwest Atlantic Ocean;
(2) an area within the Southeast Shoal, Grand Bank in the northwest
Atlantic Ocean; and 3) an area within Dogger Bank in the North Sea.
Abrolhos Bank: For this rule, we have added the Abrolhos Bank as an
OBIA based on its importance for humpback whale breeding and calving.
The specified period of this OBIA would be effective August through
November. The Navy concurs with our recommendation to designate
Abrolhos Bank as an OBIA.
Southeast Shoal, Grand Bank: There is evidence from a single 1985
line transect survey that humpback whales foraged in this area in the
past; however, this information is almost 30 years old. We and the Navy
are continuing to gather information to determine whether this area
meets the OBIA criteria.
In the 2012 application for LOAs, the Navy states that it does not
plan to operate within the northwest Atlantic Ocean in the first year
of this rule. Utilizing the adaptive management framework, we and the
Navy will make a decision before issuing the second annual LOAs
regarding whether this area meets the OBIA criteria and, if so, can be
practicably implemented.
Dogger Bank: There is evidence from a single 2007 line transect
survey that minke whales aggregated on the slope of Dogger Bank to
forage on sandeels (de Boer, 2010). However, sandeels only emerge from
their sand burrows when oceanographic conditions are optimal (de Boer,
2010). There is not enough information to support this area as a
sustained and predictable foraging ground for minke whales at this
time. We will continue to monitor and re-evaluate this area as
researchers complete additional surveys on Dogger Bank within the next
few years. Utilizing the adaptive management framework, we and the Navy
will make a decision before issuing the second annual LOAs regarding
whether this area meets the OBIA criteria and, if so, can be
practicably implemented.
Operational Exception
We discussed the Navy's need for an operational exception for use
of the SURTASS LFA sonar system in the proposed rule (77 FR 842;
January 6, 2012; page 878). The information contained in this section
has not changed from what was in the proposed rule. Briefly, it may be
necessary for the Navy to operate in a manner that results in SURTASS
LFA sonar transmissions generating sound levels above 180 dB re: 1
[micro]Pa within an OBIA, or for Navy to operate within an OBIA: (1)
When it is operationally necessary for the Navy
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to continue tracking an existing underwater contact; or (2) when it is
operationally necessary for the Navy to detect a new underwater contact
within the area. This exception does not apply to routine training and
testing with the SURTASS LFA sonar systems.
Mitigation Conclusions
Based on our evaluation of the proposed measures and other measures
considered by us or recommended by the public, we have determined that
the required mitigation measures (including the Adaptive Management
component described later in this document) are means of effecting the
least practicable adverse impacts on marine mammal species or stocks
and their habitat, paying particular attention to rookeries, mating
grounds, and areas of similar significance, while also considering
personnel safety, practicality of implementation, and impact on the
effectiveness of the military readiness activity. The proposed rule
contains further support for this finding in the Mitigation Conclusion
section (77 FR 842; January 6, 2012; pages 878-879).
Research
We included a discussion of the Navy's proposed research that
increases the knowledge base about marine mammals and the potential
effects from underwater anthropogenic noise (77 FR 842; January 6,
2012; pages 879-880). The information contained in Research has not
changed from what was in the proposed rule.
Briefly, the Navy sponsors significant research and monitoring
projects for living marine resources to study the potential effects of
its activities on marine mammals. This ongoing marine mammal research
relates to hearing and hearing sensitivity, auditory effects, dive and
behavioral response models, noise impacts, beaked whale global
distribution, modeling of beaked whale hearing and response, tagging of
free-ranging marine animals at-sea, and radar-based detection of marine
mammals from ships. These research projects may not be specifically
related to SURTASS LFA sonar operations; however, they are crucial to
the overall knowledge base on marine mammals and the potential effects
from underwater anthropogenic noise.
Monitoring
Section 101(a)(5)(A) of the MMPA states that in order to issue an
Incidental Take Authorization for an activity, we must set forth
``requirements pertaining to the monitoring and reporting of such
taking.'' Our implementing regulations at 50 CFR 216.104 (a)(13)
indicate that requests for Letters of Authorization must include the
suggested means of accomplishing the necessary monitoring and reporting
that will result in increased knowledge of the species, the level of
taking, or impacts on populations of marine mammals that we expect to
be present.
We provided a detailed description of the general goals of
monitoring and the Navy's proposed monitoring measures in the proposed
rule (77 FR 842; January 6, 2012; page 880). Within this final rule, we
have added additional monitoring requirements for harbor porpoises and
beaked whales based upon comments received during the public comment
periods for the proposed rule. This additional monitoring would augment
the Navy's proposed monitoring efforts to increase our understanding of
how these species respond-behaviorally or physiologically-to SURTASS
LFA sonar.
Beaked Whale and Harbor Porpoise Monitoring
Within the first year of the five-year rule, the Navy will convene
a Scientific Advisory Group (SAG). Its goal will be to analyze
different types of monitoring and research that could increase the
understanding of the potential effects of low-frequency active sonar
transmissions on beaked whales and/or harbor porpoises.
The Navy will work closely with the SAG to characterize likely
available assets and resources to help them frame their analysis, in
order to identify monitoring/research options that would be most
feasible for the Navy to implement. SAG members will include recognized
marine biology and marine bio-acoustic scientific subject matter
experts. The results from the SAG meeting will be considered
independent scientific findings, fully accessible to the public.
The Navy's execution of any monitoring/research with beaked whales
or harbor porpoises recommended in the SAG's findings will necessarily
depend on the availability of scientists with the appropriate
background and experience to execute the field research, as well as the
availability of adequate resources to plan and conduct the research
project and to process, analyze, and report on the collected data.
Following the SAG's submission of findings, and assuming the SAG
recommends going forward with beaked whale and/or harbor porpoise
monitoring/research, the Navy will either: (1) Draft a plan of action
outlining their strategy for implementing the SAG's recommendations, or
(2) describe, in writing, why none of the SAG's recommendations are
feasible and meet with us to discuss any other potential options.
With the exception of the additional monitoring requirement for
harbor porpoises and beaked whales, the information on monitoring in
the proposed rule has not changed.
Adaptive Management
Our understanding of the potential effects of SURTASS LFA sonar on
marine mammals is continually evolving. Reflecting this, this final
regulation governing the take of marine mammals, incidental to the
Navy's SURTASS LFA sonar operations contains an adaptive management
component. We provided a description of the general framework for
adaptive management in the proposed rule (77 FR 842; January 6, 2012;
pages 880-881). The information contained in this section has not
changed from the proposed rule description.
This framework provides a mechanism for NMFS and the Navy to modify
(or add or delete) mitigation or monitoring measures, as appropriate,
based on new information.
The following are some of the possible sources of new data that
could contribute to our decision to modify mitigation or monitoring
measures:
Results from the Navy's monitoring from the previous
year's operation of SURTASS LFA sonar.
Compiled results of Navy-funded research and development
studies.
Results from specific stranding investigations.
Results from general marine mammal and sound research
funded by the Navy or other sponsors.
Any information that reveals marine mammals may have been
taken in a manner, extent or number not authorized by this regulation
or within subsequent Letters of Authorization.
We would add, modify or delete mitigation or monitoring measures in
consultation with the Navy if doing so creates a reasonable likelihood
of accomplishing the goals of mitigation and monitoring laid out in
this final rule. We and the Navy will meet annually (if deemed
necessary by either agency) to discuss the monitoring reports, Navy
research and development outcomes, current science, and determine
whether mitigation or monitoring modifications are appropriate.
[[Page 50296]]
Reporting
In order to issue an incidental take authorization for an activity,
section 101(a)(5)(A) of the MMPA states that we 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 the Letters of Authorization, and to provide us and the
Navy with data of the highest quality based on the required monitoring.
A subset of the monitoring reports' information may be classified and
thus not releasable to the public.
We provided a detailed description of the Navy's proposed reporting
requirements in the proposed rule (77 FR 842; January 6, 2012; pages
881-882). The information contained in the Reporting section has not
changed from the proposed rule description. Briefly, the reporting
measures require the Navy to provide: notification of injured or dead
marine mammals; notification of a ship strike; quarterly mitigation
monitoring reports; annual reports; and a five-year comprehensive
report.
Comments and Responses
On January 6, 2012, we published a proposed rule (77 FR 842) in
response to the Navy's request to take marine mammals, incidental to
conducting SURTASS LFA sonar operations in certain areas of the world's
oceans. We requested comments, information, and suggestions related to
the request. During the 30-day public comment period, we received
comments from the Marine Mammal Commission (Commission), the Natural
Resources Defense Council (NRDC), OceanCare, the Surfrider Foundation,
and 22 private citizens. We also received comments that appear to be
directed solely at the Navy's draft 2011 Supplemental Environmental
Impact Statement/Supplemental Overseas Environmental Impact Statement.
See the Navy's 2012 FSEIS/SOEIS, which we have adopted. We address the
comments here.
Marine Mammal Protection Act Concerns
Comment 1: Citing the broad scope of the Navy's application, the
complexity of the proposed rule, and the need for additional time for
public comment, the Natural Resources Defense Council requested that we
consider extending the public comment period for an additional 15 days.
Response: In response to the request, we extended the public
comment period by 15 extra days (77 FR 6771, February 9, 2012).
SURTASS LFA Sonar Activity Concerns
Comment 2: One commenter is concerned that the Navy seems to take
very few steps to reduce its use of sonar by using alternative
technologies and noted that the Navy could pursue the use of other
technologies for this action.
Response: The comment is beyond the scope of our rulemaking for
this action. The Navy's specified activity described in their
application for regulations is the use of SURTASS LFA sonar, not
alternatives to SURTASS LFA sonar.
However, the Navy reviewed and considered the use of non-acoustic
alternatives for underwater detection (i.e., radar, laser, magnetic,
infrared, electronic, electric, hydrodynamic, and biologic detection
systems) in the 2012 FSEIS/SOEIS (see subchapter 1.1.4).
Table 1 in this Federal Register notice summarizes a projected
annual deployment schedule for SURTASS LFA sonar which amounts to 432
hours (18 days) of active transmissions, annually, for one surveillance
vessel. The SURTASS LFA sonar has a relatively low duty cycle (i.e.,
the amount of time of active sonar transmissions divided by the amount
of time that the sonar is not transmitting) of 7.5 to 10 percent. Thus,
for an estimated 18-day mission period, SURTASS LFA sonar would be off
(quiet) for 90 to 92.5 percent of the time and adding no sound into the
water. On an annual basis, the Navy would limit each SURTASS LFA vessel
to transmitting no more than 4.9 percent of the time (i.e., 432 hours
within one year (8,760 hours)).
Threatened and Endangered Species
Comment 3: One commenter expressed concern that the Navy had
underestimated the full impact that sonar has on marine mammals,
particularly ones which are also listed under the Endangered Species
Act. They stated: ``The Navy's application for authorized use of
SURTASS LFA sonar states that the effects of sonar use will not be
greater on animals listed under the ESA than the effects on other
marine mammals (LOA Application at page 114.)''
Response: The commenter's statement is not accurate. First, the
Navy has analyzed the effects of SURTASS LFA sonar on marine mammals,
including those listed under the Endangered Species Act, in the 2001
Final Environmental Impact Statement (Don, 2001), the 2007 Final
Supplemental Environmental Impact Statement (DoN, 2007) and the
2012FSEIS/SOEIS. Specifically, the types of potential effects on marine
mammals from SURTASS LFA sonar operations presented include: (1) Non-
auditory injury; (2) permanent loss of hearing; (3) temporary loss of
hearing; (4) behavioral change; and (5) masking. We refer the commenter
to those documents for the Navy's analysis of the effects of SURTASS
LFA sonar on marine mammals.
Second, we also analyzed the effects of SURTASS LFA sonar on marine
mammals in the Potential Effects of the Specified Activity on Marine
Mammals section of the proposed rule (77 FR 842; January 6, 2012; pages
860-874). We included a qualitative discussion of the different ways
that unmitigated SURTASS LFA sonar operations may result in direct
physiological effects (e.g., threshold shift and non-acoustic injury,
acoustic masking, impaired communication, stress responses, behavioral
disturbance, stranding, and effects from vessel movement and vessel
collisions). We anticipate that actual effects to marine mammals
(including threatened and endangered species) would be in the form of
Level B harassment (behavioral), due to the required mitigation and
monitoring measures, and geographic restrictions. While marine mammals
could potentially be affected by the SURTASS LFA sonar sounds, we have
determined that these effects are not reasonably likely to adversely
affect the species or stock through effects on annual rates of
recruitment or survival.
Finally, previous Endangered Species Act section 7 consultations
(NMFS, 2002, 2003, 2004, 2005, 2006, 2007, 2008, 2009, 2010, and 2011)
and the section 7 consultation for this rule have analyzed the effects
of SURTASS LFA sonar operations on threatened and endangered marine
mammals and concluded that the operation of the SURTASS LFA sonar was
not likely to jeopardize the continued existence of any endangered or
threatened species under our jurisdiction and would not result in the
destruction or adverse modification of critical habitat.
Comment 4: One commenter stated: ``The LOA application states that
the Jacksonville training would occur in the winter, yet the winter
months are the time when this area is listed as an OBIA (LOA
Application at 11-13). Will the Navy be conducting SURTASS LFA training
here during calving months? If yes, what will the impact be on the
young whales? The diminished population of North Atlantic Right Whales
should not have to compete with the Navy for this area. The proper time
to conduct training here would be in the summer months when the whales
[[Page 50297]]
return to the New England and Canadian coast.''
Response: First, the Navy's application states that the Western
Atlantic/Jacksonville Operational Area is a potential area for SURTASS
LFA sonar operations; it does not state that training would occur in
the area in the winter. This area is one of 19 potential sites that
they modeled and analyzed during the winter to assess potential impacts
to marine mammals for the rule and the Letter of Authorization
application process.
We have designated the U.S. Right Whale Seasonal Habitat as an OBIA
specifically to mitigate effects on north Atlantic right whales and
their calves during the winter months. Moreover, because we are also
requiring the Navy to implement an additional 1-km (0.62 mi; 054 nm)
buffer zone seaward of the outer perimeter of this OBIA, these
mitigation measures ensure that sound levels within the area do not
exceed approximately 175dB re: 1 [micro]Pa from November 15 through
April 15, the calving months.
If the Navy were to operate within the greater Jacksonville
Operational Area outside of the U.S. Right Whale Seasonal Habitat OBIA,
the rule requires the Navy to conduct visual, passive acoustic, and
active acoustic monitoring and suspend/delay SURTASS LFA sonar
transmissions if a marine mammal enters the 2-km (1.2-mi; 1.1-nm) LFA
mitigation and buffer zones around the vessel.
In each annual application, the Navy will include information if it
plans to operate (or not operate) within the Western Atlantic/
Jacksonville Operational Area. Thus, at this time we cannot say if the
Navy intends to operate in the Western Atlantic/Jacksonville
Operational Area during the period of November through January (i.e.,
calving months) with the exception of the first year of SURTASS LFA
sonar operations, where the Navy has stated in its application, that it
does not intend to operate in this area.
To clarify, Table 21 in the Navy's application presents estimates
of the percentage of marine mammal stocks potentially affected by
SURTASS LFA sonar in the proposed mission area of the Western Atlantic/
Jacksonville Operational Area. The Navy has modeled potential effects
to all marine mammals in the Western Atlantic/Jacksonville Operational
Area during the winter in the 2012 FSEIS/SOEIS (see Tables 4-17 and C-
29). If the Navy conducted SURTASS LFA operations in the winter, the
Navy's risk estimates predict that 0.12 percent of the north Atlantic
right whale population could be potentially exposed to sound levels
that may lead to Level B harassment.
Comment 5: A commenter discussed the Navy's estimates of the
percentage of marine mammal stocks potentially affected by SURTASS LFA
sonar in the proposed mission area of the Sea of Japan operating area.
He stated: ``The summer feeding grounds of Western Gray [whales] is
located in the Sea of Okhotsk and is part of an OBIA which restricts
the Navy from training there. The migratory patterns and route of these
whales is largely unknown but is presumed to take them south to Korea.
If this is the case then the whales will be migrating through the Sea
of Japan during the spring and fall, the modeled season for training.''
Response: Based upon the best available information, we found few
data to support designating an area within the Sea of Japan as a
migration corridor (i.e., an OBIA for SURTASS LFA sonar). However, any
western Pacific gray whales transiting through the Sea of Japan will be
protected from exposure to sound pressure levels greater than
approximately 175dB re: 1 [micro]Pa by the Navy's three-part monitoring
protocols and required mitigation measures contained in this
regulation.
Comment 6: The same commenter as in Comment 5 also stated: ``There
are many other marine mammal populations that are listed under the ESA
that occupy areas close to proposed SURTASS LFA training areas. Due to
the fragile nature of these populations, the Navy should afford these
animals extra protection to maximize their chance of survival and
recovery. The SURTASS training in this area could affect the whale's
navigation or migration patterns and these populations will not be able
to recover from endangered levels when human interactions affect their
behavior. The Navy should make a concerted effort to ensure that sonar
is not used in areas where ESA species are currently migrating,
calving, and feeding.''
Response: See response to Comment 3. We are unclear as to which
area or species the commenter referred. We designated OBIAs based on
certain criteria and the best available information we had for marine
mammals to determine if any areas met the criteria. In some cases, we
designated an OBIA because a species listed under the Endangered
Species Act has designated critical habitat, breeds, calves, migrates,
or forages in a particular area. For example, we designated four OBIAs
for north Atlantic right whales, one OBIA each for north Pacific right
and fin whales, 10 OBIAs for humpback whales, and six OBIAs for blue
whales. Beyond that, the standard mitigation and monitoring measures
that apply wherever the Navy operates SURTASS LFA sonar will ensure
that marine mammals are not exposed to sound levels that exceed
approximately 175 dB re: 1 [micro]Pa. Finally, the Navy will
perform mission planning for annual Letters of Authorization
applications and would limit operation of SURTASS LFA sonar to ensure
that no more than 12 percent of any marine mammal stock would be taken
by Level B harassment annually, over the course of this five-year
regulation.
We anticipate that effects to marine mammals (including threatened
and endangered species) would be in the form of Level B harassment
(behavioral), due to the required mitigation measures, geographic
restrictions, and sporadic nature of the SURTASS LFA sonar operations.
While marine mammals may be affected by the SURTASS LFA sonar sounds,
we have determined that these effects are not reasonably likely to
adversely affect the species or stock through effects on annual rates
of recruitment or survival.
Comment 7: One commenter stated: ``There exists significant risk to
Southern Resident Killer Whales (SRKW), who are listed as an endangered
distinct species population [distinct population segment] under the
ESA, in addition to being protected under the MMPA. The critical
habitat for these animals is near the San Juan Archipelago in
Washington State, near the U.S.-Canadian Border. If sonar use causes
mass strandings similar to the incident in the Bahamas in 2000, it
could have permanent negative consequences on the long-term survival of
this species. While the application and proposed NMFS ruling say
harassment is the only foreseen consequence, the mass stranding event
in the Bahamas strongly suggests at least the possibility of
significant mortality occurring. Additionally J Pod, one of the three
SRKW pods, has already had a brush with Navy sonar, along with multiple
other marine mammals in the area. While the Navy claims there were no
adverse effects from the Sonar output of the USS Shoup in May of 2003,
local scientists disagree, and NMFS' own findings were inconclusive.
Such uncertain or dissenting expert opinions should create enough doubt
in any educated mind and the benefit of this doubt should be given to
the whales, not the Navy.
This application should be reconsidered. If an Unusual Mortality
Event (UME) were to occur in the San Juan Islands, this would have a
ripple effect on the entire ecosystem not just
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the various marine mammals in the area. Furthermore, if a UME were to
occur involving the SRKW population, this would have a serious
detriment on the local tourism economy of the San Juan Islands,
creating a direct harm on local citizens and the local economy in
addition to the ecological concerns already mentioned.''
Response: Based on the best available information, SURTASS LFA
sonar is not associated with strandings of marine mammals. SURTASS LFA
sonar has operated subject to our regulations for the last nine years
without any reports of strandings since the Navy began using the system
operationally in the early 2000s. The Stranding and Mortality section
in the proposed rule (77 FR 842; January 6, 2012; pages 871-872)
presented information on the potential for stranding from SURTASS LFA
sonar as well as information on strandings associated with mid-
frequency active sonar use.
Over the past 12 years, there have been five stranding events
coincident with military mid-frequency active sonar use in which
exposure to sonar is believed (by NMFS and the Navy) to have been a
contributing factor to strandings, including the Bahamas (2000). We
refer the reader to Cox et al. (2006) for a summary of the Bahamas
strandings event.
We have also provided a summary of the Navy's acoustic modeling
scenarios and risk analysis methods in the proposed rule (77 FR 842;
January 6, 2012; pages 859-860). Based upon the best available
scientific information, while marine mammals may be potentially
affected by the SURTASS LFA sonar sounds, we have determined that these
effects are not reasonably likely to adversely affect the species or
stock through effects on annual rates of recruitment or survival.
Second, there are three areas designated as critical habitat for
the Southern Resident killer whale: the Summer Core Area in Haro Strait
and waters around the San Juan Islands; Puget Sound; and the Strait of
Juan de Fuca (71 FR 69054, November 29, 2006). These areas are within
22 km (14 mi; 12 nm) of the Washington coastline and thus under our
criteria are not OBIAs, but rather fall within the coastal exclusion
zone, where sound pressure levels will not exceed 180 dB re: 1
[micro]Pa. We also note that sound pressure levels will not exceed
approximately 175 dB re: 1 [micro]Pa at 1 km (0.62 mi; 054 nm) seaward
of the boundary of the OBIA for the Olympic Coast National Marine
Sanctuary, the Prairie, Barkley Canyon, and Nitnat Canyon.
NMFS' final rule designating critical habitat for the Southern
Resident killer whale (71 FR 69054, November 29, 2006) did not
recognize any offshore areas (where the Navy could potentially operate
SURTASS LFA sonar) that might qualify as an OBIA for the Southern
Resident killer whales. Further, if the Navy were to operate in
offshore areas, where individuals of this species are present, they
would be protected from sound pressure levels in excess of
approximately 175 dB re: 1 [micro]Pa via the Navy's three-part
monitoring and shutdown/delay protocols.
Finally, the reporting measures in this regulation require the Navy
to provide us with a notification that includes reports of injured or
dead marine mammals as well as notification of a ship strike.
Comment 8: One commenter stated: ``The Administrative Procedure Act
requires agencies such as NMFS to give a reasonable explanation of
their decisions. This is to prevent agency decisions from being
``arbitrary and capricious.'' In this case, part of the Navy's LOA
application, and part of the reasoning of NMFS, is that: (1) ESA
species won't be additionally affected, and (2) it is unlikely these
effects will rise past mere harassment. However, as discussed in this
comment, there is evidence contradicting both of those statements. We
believe that when an agency fails to at least address contradictory
evidence in its decision making, those decisions will likely be too
arbitrary and capricious to satisfy the APA.''
Response: See our responses to Comments 3, 4, and 5. While
threatened and endangered marine mammals may be potentially affected by
the SURTASS LFA sonar sounds, we have determined that these effects
will be limited to Level B behavioral harassment and are not reasonably
likely to adversely affect the species or stock through effects on
annual rates of recruitment or survival, NMFS has also determined this
action is not likely to jeopardize the continued existence of any
endangered or threatened species under our jurisdiction or result in
the destruction or adverse modification of critical habitat.
We included a detailed discussion of the potential effects of the
Navy's SURTASS LFA sonar operations on marine mammals (including
threatened and endangered species), marine mammal habitat, critical
habitat, compliance with maritime laws, marine protected areas, and
potential physiological and behavioral effects on marine mammals in the
Federal Register notice of the proposed rule (77 FR 842; January 6,
2012). We have explained the basis for our findings under 16 U.S.C.
1371(a)(5)(A) and our implementing regulations to support issuance of
the final rule and Letters of Authorization to the Navy. We disagree
that our findings in this rulemaking are arbitrary and capricious.
Acoustic Thresholds for Threshold Shift
Comment 9: One commenter noted that although the Navy is restricted
from testing sonar within 22 kilometers of shore and within any
Offshore Biologically Important Area, the Navy estimates that sonar
waves can retain an intensity of 140 decibels from as far away as 300
miles (NRDC, Lethal Sounds).
Response: We refer the commenter to Appendix C of the 2012 FSEIS/
SOEIS for more detailed information on the Navy's modeling of sonar
sound waves.
Richardson et al. (1995) stated that it would be unlikely that any
marine mammal would remain for long in areas where there was continuous
underwater noise exceeding 140 dB re: 1 [mu]Pa. In fact, the Navy's Low
Frequency Sonar Scientific Research Program, which assessed the
potential impacts of SURTASS LFA sonar on the behavior of low-frequency
hearing specialists, noted no reduction in sighting rates and no
reduction in acoustic detection within the vicinity of the SURTASS LFA
sonar source vessel during the studies which lasted for several weeks
(DoN, 2001). In all three phases of the Program (Clark et al., 2001),
most animals showed little to no response to SURTASS LFA sonar signals
at received levels up to 155 dB re: 1 [mu]Pa, and those individuals
that did show a response resumed normal activities within tens of
minutes. Thus, av