Takes of Marine Mammals Incidental to Specified Activities; U.S. Navy Missile Launches From San Nicolas Island, California, 32678-32686 [2014-13084]
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instruction 21.g., ‘‘Revising paragraph
(c)(13)(i)(B) to read as set forth below;’’
is corrected to read, ‘‘Adding paragraph
(c)(13)(i)(B) to read as set forth below;’’.
FOR FURTHER INFORMATION CONTACT:
Dated: June 2, 2014.
Tina A. Campbell,
Chief, Division of Policy and Directives
Management, U.S. Fish and Wildlife Service.
Background
Section 101(a)(5)(A) of the MMPA (16
U.S.C 1361 et seq.) directs the Secretary
of Commerce to allow, upon request, the
incidental, but not intentional, taking of
small numbers of marine mammals by
U.S. citizens who engage in a specified
activity (other than commercial fishing)
within a specified geographical region if
certain findings are made and either
regulations are issued or, if the taking is
limited to harassment, a notice of a
proposed authorization is provided to
the public for review.
Authorization for incidental takings
shall be granted if NMFS finds that the
taking will have a negligible impact on
the species or stock(s), will not have an
unmitigable adverse impact on the
availability of the species or stock(s) for
subsistence uses (where relevant), and if
the permissible methods of taking and
requirements pertaining to the
mitigation, monitoring, and reporting of
such takings are set forth. NMFS has
defined ‘‘negligible impact’’ in 50 CFR
216.103 as ‘‘an impact resulting from
the specified activity that cannot be
reasonably expected to, and is not
reasonably likely to, adversely affect the
species or stock through effects on
annual rates of recruitment or survival.’’
The National Defense Authorization
Act of 2004 (NDAA) (Pub. L. 108–136)
removed the ‘‘small numbers’’ and
‘‘specified geographical region’’
limitations indicated above and
amended the definition of ‘‘harassment’’
as it applies to a ‘‘military readiness
activity’’ to read as follows (Section
3(18)(B) of the MMPA): (i) Any act that
injures or has the significant potential to
injure a marine mammal or marine
mammal stock in the wild [Level A
Harassment]; or (ii) Any act that
disturbs or is likely to disturb a marine
mammal or marine mammal stock in the
wild by causing disruption of natural
behavioral patterns, to a point where
such behavioral patterns are abandoned
or significantly altered [Level B
Harassment].
[FR Doc. 2014–13144 Filed 6–5–14; 8:45 am]
BILLING CODE 4310–55–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 217
[Docket No. 131120978–4452–02]
RIN 0648–BD80
Takes of Marine Mammals Incidental to
Specified Activities; U.S. Navy Missile
Launches From San Nicolas Island,
California
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
Upon application from the
U.S. Navy (Navy), Naval Air Warfare
Center Weapons Division (NAWCWD),
we (the National Marine Fisheries
Service) are issuing regulations under
the Marine Mammal Protection Act
(MMPA) to govern the unintentional
taking of marine mammals incidental to
missile launches from San Nicolas
Island (SNI) from June 2014 through
June 2019. These regulations allows us
to issue a Letter 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 or stocks and their
habitat, and set forth requirements
pertaining to the monitoring and
reporting of the incidental take.
DATES: Effective June 3, 2014, through
June 3, 2019.
ADDRESSES: To obtain an electronic
copy of the Navy’s application or other
referenced documents, visit the internet
at: https://www.nmfs.noaa.gov/pr/
permits/incidental.htm#applications.
Documents cited in this notice may also
be viewed, by appointment, during
regular business hours, at the Office of
Protected Resources, National Marine
Fisheries Service, 1315 East-West
Highway, Silver Spring, MD 20910.
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SUMMARY:
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John
Fiorentino, Office of Protected
Resources, NMFS, (301) 427–8401.
SUPPLEMENTARY INFORMATION:
Summary of Request
On July 24, 2013, NMFS received an
application from the Navy for the taking
of marine mammals incidental to
missile launches from San Nicolas
Island (SNI), California. NMFS
determined that the application was
adequate and complete on November
18, 2013.
The Navy proposed to continue a
launch program for missiles and targets
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from several launch sites on SNI
between June 2014 and June 2019.
These activities are considered military
readiness activities. Marine mammals
hauled out on SNI may be exposed to
sound from missile launches. The Navy
requests authorization to take three
marine mammal species by Level B
harassment: northern elephant seal
(Mirounga angustirostris), Pacific harbor
seal (Phoca vitulina), and California sea
lion (Zalophus californianus).
The Navy is currently operating under
an authorization to take marine
mammals incidental to missile launches
from SNI, which expires June 3, 2014
(74 FR 26587).
Description of the Specified Activity
Overview
The Navy is continuing a launch
program for missiles and targets from
several launch sites on SNI. Missiles
vary from tactical and developmental
weapons to target missiles used to test
defensive strategies and other weapons
systems. Some launch events involve a
single missile, while others involve the
launch of multiple missiles either in
quick succession or at intervals of a few
hours. Up to 200 missiles (40 missiles
per year) may be launched over the
5-year period, but the number and type
of launch varies depending on
operational needs.
The purpose of these launches is to
support testing and training activities
associated with operations on the
NAWCWD Point Mugu Sea Range. The
Sea Range is used by the U.S. and allied
military services to test and evaluate
sea, land, and air weapon systems; to
provide realistic training opportunities;
and to maintain operational readiness of
these forces. Some of the launches are
used for practicing defensive drills
against the types of weapons simulated
by these missiles and some launches are
conducted for the related purpose of
testing new types of targets.
Dates and Duration
Launches of this type have been
occurring at SNI for many years and are
expected to continue indefinitely into
the future. NMFS is issuing a 5-year
Letter of Authorization for missile
launches taking place between June
2014 and June 2019. The timing of these
launches is variable and subject to
testing and training requirements and
meteorological and logistical
limitations. To meet the Navy’s
operational testing and training
requirements, launches may be required
at any time of year and any time of day.
Up to 200 missiles (40 missiles per year)
may be launched over the 5-year period
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and the Navy is proposing that up to 10
launches per year may occur at night.
Given the launch acceleration and flight
speed of the missiles, most launch
events are of extremely short duration.
Strong launch sounds are typically
detectable near the surrounding beaches
for no more than a few seconds per
launch (Holst et al., 2005a, 2008, 2011).
Specified Geographic Region
SNI is one of the eight Channel
Islands in the Southern California Bight,
located about 105 kilometers (km)
southwest of Point Mugu. Missile
launches will occur from the western
part of SNI (see Figure 2 in the Navy’s
LOA application). The missiles fly
generally westward through the Point
Mugu Sea Range. The primary launch
locations are the Alpha Launch
Complex, which is located on the westcentral part of SNI, and Building 807
Launch Complex, which is located at
the western end of SNI. Other launch
pads are located nearby.
Detailed Description of Activities
Missiles included in the Navy’s
request range from relatively small and
quieter missiles like the Rolling
Airframe Missile to larger and louder
missiles like the Terrier Black-Brant.
While other missiles may be launched
in the future, the largest missile
analyzed here is 23,000 kilograms (kg).
A description of the types of missiles
that may be launched at SNI during the
5-year period and their sound
characteristics was provided in the
proposed rule (79 FR 13022, March 7,
2014) and includes, in summary: the
Rolling Airframe Missile (RAM), GQM–
163A ‘‘Coyote,’’ Multi-stage Sea
Skimming Target (MSST), Terrier (Black
Brant, Lynx, and Orion), and RIM–161
Standard Missile 3 (SM–3).
General Launch Operations—Aircraft
and helicopter flights between the Point
Mugu airfield on the mainland, the
airfield on SNI, and the target sites in
the Sea Range are a routine part of a
planned launch operation. These flights
generally do not pass at low level over
the beaches where pinnipeds are
expected to be hauled out. Therefore,
these flights are not further considered
in this document.
Movements of personnel are restricted
near the launch sites at least several
hours prior to a launch for safety
reasons. No personnel are allowed on
the western end of SNI during launches.
Movements of personnel or missiles
near the island’s beaches are also
restricted at other times of the year for
purposes of environmental protection
and preservation of cultural resource
sites. Launch monitoring equipment
would be deployed and activated prior
to the launches.
Comments and Responses
On March 7, 2014 (79 FR 13022),
NMFS published a proposed rule to
authorize the taking of marine mammals
incidental to missile launches at SNI.
During the 45-day public comment
period, NMFS received comments from
the Marine Mammal Commission
(Commission) and a private citizen. The
Commission’s comment is specific to
section 101(a)(5)(A) of the MMPA and
NMFS’ analysis of impacts to marine
mammals and is summarized and
addressed below and throughout the
final rule.
Comment 1: The Commission
recommended that NMFS require the
Navy to estimate the number of sea lion
takes based on the greatest mean
number of takes that has been estimated
in any previous monitoring year
multiplied by 40.
Response: NMFS agrees that the
potential number of annual launches
(40) should be considered when
estimating take in order to ensure that
the Navy remains in compliance with
the MMPA. NMFS reassessed the take
estimates for California sea lion by
calculating the annual average number
of takes per launch and multiplying
each average by 40. This total (24,360)
is the number of California sea lions
takes NMFS is authorizing over the 5year rule (an average of 4,872 takes per
year). This is the maximum number of
takes expected, considering the Navy
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only conducted 42 launches over the
past 5 years.
Comment 2: A private citizen
recommended that the Navy submit
annual reports describing noncompliance, if any, with required
mitigation measures—including
frequency of occurrence, date of
occurrence, and reason for occurrence of
non-compliance.
Response: It is standard practice for
the Navy to include this type of
information in their summary of
implementation of mitigation measures
in the annual interim technical reports
and comprehensive technical reports
submitted to NMFS. These reports are
available on the NMFS Office of
Protected Resources Web site at https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications.
Description of Marine Mammals in the
Area of the Specified Activity
There are seven species of marine
mammals with possible or confirmed
occurrence in the area of the specified
activity: Northern elephant seals, harbor
seals, California sea lions, northern fur
seals (Callorhinus ursinus), Guadalupe
fur seal (Arctocephalus townsendi),
Steller sea lions (Eumetopias jubatus),
and southern sea otters (Enhydra lutris
nereis). The northern fur seal is
considered depleted under the MMPA;
the Guadalupe fur seal is listed as
threatened under the Endangered
Species Act (ESA) and depleted under
the MMPA; and the eastern distinct
population segment of Steller sea lion
was delisted under the ESA in 2013.
The northern fur seal, Guadalupe fur
seal, and Steller sea lion are considered
rare at SNI and takes of these species
have not been observed under the
Navy’s current MMPA authorization.
Therefore, these three species were not
considered further. The southern sea
otter is managed by the U.S. Fish and
Wildlife Service and was also not
considered further. Table 1 includes
species-specific information on the
three species likely to occur in the area
of the specified activity.
TABLE 1—SPECIES INFORMATION ON THE MARINE MAMMALS LIKELY TO OCCUR IN THE AREA OF THE SPECIFIED ACTIVITY
Scientific name
Status
Occurrence
Seasonality
Range
Northern elephant sea ........
Harbor seal .........................
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Common name
Mirounga angustirostris .....
Phoca vitulina ....................
.............
.............
Common ......
Common ......
Year-round ..
Year-round ..
California sea lion ...............
Zalophus californianus .......
.............
Common ......
Year-round ..
Mexico to Alaska ...............
Baja California to Aleutian
Islands.
Mexico to Canada ..............
Further information on the biology
and local distribution of these species
can be found in the Navy’s application
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(see ADDRESSES), and the NMFS Marine
Mammal Stock Assessment Reports,
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Abundance
124,000
30,196
296,750
which are available online at: https://
www.nmfs.noaa.gov/pr/species/.
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Potential Effects of the Specified
Activity on Marine Mammals
This section of the proposed
Incidental Harassment Authorization
(IHA) (79 FR 13022, March 7, 2014)
included a summary and discussion of
the ways that the types of stressors
associated with the specified activity
(e.g., missile launch noise) have been
observed to impact marine mammals.
The ‘‘Estimated Take by Incidental
Harassment’’ section later in this
document will include a quantitative
analysis of the number of individuals
that are expected to be taken by this
activity. The ‘‘Negligible Impact
Analysis’’ section will include the
analysis of how this specific activity
will impact marine mammals and will
consider the content of this section, the
‘‘Estimated Take by Incidental
Harassment’’ section, the ‘‘Proposed
Mitigation’’ section, and the
‘‘Anticipated Effects on Marine Mammal
Habitat’’ section to draw conclusions
regarding the likely impacts of this
activity on the reproductive success or
survivorship of individuals and from
that on the affected marine mammal
populations or stocks.
In summary, potential effects of the
specified activity on marine mammals
involve both acoustic and non-acoustic
effects. Acoustic effects are related to
sound produced by the engines of all
launch vehicles, and, in some cases,
their booster rockets. Potential nonacoustic effects could result from the
physical presence of personnel during
placement of video and acoustical
monitoring equipment. However,
careful deployment of monitoring
equipment is not expected to result in
any disturbance to pinnipeds hauled out
nearby. Any visual disturbance caused
by passage of a vehicle overhead is
likely to be minor and brief as the
launch vehicles are relatively small and
move at great speed. Detailed
information on each potential effect
(acoustic impacts, behavioral reactions
of pinnipeds to missile launches,
stampede-related injury or mortality
from missile launches) was provided in
the proposed rule (79 FR 13022, March
7, 2014) and that information has not
changed.
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Anticipated Effects on Marine Mammal
Habitat
Three species of pinnipeds use
various beaches around SNI as places to
rest, molt, and breed. These beaches
consist of sand, rock ledges, and rocky
cobble. Pinnipeds continue to use
beaches around the western end of SNI,
and are expanding their use of some
beaches, despite ongoing launch
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activities for many years. Similarly, it
appears that sounds from prior launches
have not affected use of coastal areas at
Vandenberg Air Force Base where
similar missile launches occur.
Pinnipeds do not feed when hauled
out on these beaches and the airborne
launch sounds will not persist in the
water near the island for more than a
few seconds. Therefore, it is not
expected that the launch activities will
have any impact on the food or feeding
success of these pinnipeds.
Boosters from missiles may be
jettisoned shortly after launch and fall
on the island, but are not expected to
impact beaches. Fuel contained in these
boosters is consumed rapidly and
completely, so there would be no risk of
contamination even in the very unlikely
event that a booster did land on a beach.
Therefore, launch activities are not
expected to have any long-term,
significant effects on marine mammal
habitat.
Mitigation
In order to issue an incidental take
authorization (ITA) under section
101(a)(5)(A) of the MMPA, NMFS must
set forth the permissible methods of
taking pursuant to such activity, and
other means of effecting the least
practicable impact on such species or
stock and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance, and on
the availability of such species or stock
for taking for certain subsistence uses
(where relevant).
The NDAA of 2004 amended the
MMPA as it relates to military-readiness
activities and the ITA process such that
‘‘least practicable adverse impact’’ shall
include consideration of personnel
safety, practicality of implementation,
and impact of the effectiveness of the
‘‘military readiness activity.’’ The
activities described in the Navy’s
application are considered military
readiness activities.
As during launches conducted under
previous regulations, where practicable,
the Navy will implement the following
mitigation measures, provided that
doing so will not compromise
operational safety, human safety,
national security, or other requirements
or mission goals:
(1) Limit activities near the beaches in
advance of launches;
(2) Avoid launch activities during
harbor seal pupping season (February
through April);
(3) Limit launch activities during
other pinniped pupping seasons;
(4) Not launch missiles from the
Alpha Complex at low elevation (less
than 305 m) on launch azimuths that
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pass close to pinniped haul-out sites
when occupied;
(5) Avoid launching multiple missiles
in quick succession over haul-out sites,
especially when young pups are
present; and
(6) Maintain a minimum altitude of
305 m from pinniped haul-outs and
rookeries for aircraft and helicopter
flight paths during missile launch
operations, except in emergencies or for
real-time security incidents (e.g., searchand-rescue, fire-fighting, adverse
weather conditions), which may require
approaching pinniped haul-outs and
rookeries closer than 305 m.
Mitigation Conclusions
NMFS has carefully evaluated the
applicant’s proposed mitigation
measures and considered a range of
other measures in the context of
ensuring that NMFS prescribes the
means of effecting the least practicable
impact on the affected marine mammal
species and stocks and their habitat. No
additional mitigation measures were
recommended during the public
comment period on the proposed rule.
Our evaluation of potential measures
included consideration of the following
factors in relation to one another:
• The manner in which, and the
degree to which, the successful
implementation of the measure is
expected to minimize adverse impacts
to marine mammals;
• The proven or likely efficacy of the
specific measure to minimize adverse
impacts as planned; and
• The practicability of the measure
for applicant implementation, including
consideration of personnel safety,
practicality of implementation, and
impact on the effectiveness of the
military readiness activity.
Any mitigation measure(s) prescribed
by NMFS should be able to accomplish,
have a reasonable likelihood of
accomplishing (based on current
science), or contribute to the
accomplishment of one or more of the
general goals listed below:
1. Avoidance or minimization of
injury or death of marine mammals
wherever possible (goals 2, 3, and 4 may
contribute to this goal).
2. A reduction in the numbers of
marine mammals (total number or
number at biologically important time
or location) exposed to received levels
of noise, or other activities expected to
result in the take of marine mammals
(this goal may contribute to 1, above, or
to reducing harassment takes only).
3. A reduction in the number of times
(total number or number at biologically
important time or location) individuals
would be exposed to received levels of
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noise, or other activities expected to
result in the take of marine mammals
(this goal may contribute to 1, above, or
to reducing harassment takes only).
4. A reduction in the intensity of
exposures (either total number or
number at biologically important time
or location) to received levels of noise,
or other activities expected to result in
the take of marine mammals (this goal
may contribute to 1, above, or to
reducing the severity of harassment
takes only).
5. Avoidance or minimization of
adverse effects to marine mammal
habitat, paying special attention to the
food base, activities that block or limit
passage to or from biologically
important areas, permanent destruction
of habitat, or temporary destruction/
disturbance of habitat during a
biologically important time.
6. For monitoring directly related to
mitigation—an increase in the
probability of detecting marine
mammals, thus allowing for more
effective implementation of the
mitigation.
Based on our evaluation of the
applicant’s proposed measures, as well
as other measures considered by NMFS,
NMFS has determined that the proposed
mitigation measures provide the means
of effecting the least practicable impact
on marine mammal species or stocks
and their habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance, while
also considering personnel safety,
practicality of implementation, and
impact on the effectiveness of the
military readiness activity.
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Monitoring and Reporting
In order to issue an ITA for an
activity, section 101(a)(5)(A) of the
MMPA states that NMFS must set forth,
‘‘requirements pertaining to the
monitoring and reporting of such
taking.’’ The MMPA implementing
regulations at 50 CFR 216.104 (a)(13)
indicate that requests for ITAs must
include the suggested means of
accomplishing the necessary monitoring
and reporting that will result in
increased knowledge of the species and
of the level of taking or impacts on
populations of marine mammals that are
expected to be present in the proposed
action area. The Navy submitted a
marine mammal monitoring plan as part
of their application. It can be found in
section 13 of their application. NMFS
did not receive any comments
suggesting a modification or
supplementation to the proposed
monitoring plan during the public
comment period.
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Monitoring measures prescribed by
NMFS should accomplish one or more
of the following general goals:
1. An increase in the probability of
detecting marine mammals, both within
the mitigation zone (thus allowing for
more effective implementation of the
mitigation) and in general to generate
more data to contribute to the analyses
mentioned below.
2. An increase in our understanding
of how many marine mammals are
likely to be exposed to levels of noise
that we associate with specific adverse
effects, such as behavioral harassment,
TTS, or PTS.
3. An increase in our understanding
of how marine mammals respond to
stimuli expected to result in take and
how anticipated adverse effects on
individuals (in different ways and to
varying degrees) may impact the
population, species, or stock
(specifically through effects on annual
rates of recruitment or survival) through
any of the following methods:
a. Behavioral observations in the
presence of stimuli compared to
observations in the absence of stimuli
(need to be able to accurately predict
received level, distance from source,
and other pertinent information).
b. Physiological measurements in the
presence of stimuli compared to
observations in the absence of stimuli
(need to be able to accurately predict
received level, distance from source,
and other pertinent information).
c. Distribution and/or abundance
comparisons in times or areas with
concentrated stimuli versus times or
areas without stimuli.
4. An increased knowledge of the
affected species.
5. An increase in our understanding
of the effectiveness of certain mitigation
and monitoring measures.
Monitoring Measures
The Navy will conduct the following
monitoring measures, which are further
detailed in section 13 of their
application:
• The Navy will continue a standard,
ongoing, land-based monitoring
program to assess effects on harbor
seals, northern elephant seals, and
California sea lions on SNI. This
monitoring will occur at up to three
sites at different distances from the
launch site before, during, and after
each launch, depending upon presence
of pinnipeds during each launch. The
monitoring will be via autonomous
video or Forward Looking Infrared
(FLIR) cameras. Pinniped behavior on
the beach will be documented prior to
the planned launch operations, during
the launch, and following the launch.
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Northern elephant seals will not be
specifically targeted for monitoring,
though may be present in the field of
view when monitoring other species.
• During each launch, the Navy will
obtain calibrated recordings of the
sounds of the launches as received at
different distances from the missile’s
flightline. The Navy anticipates that
acoustic data will be acquired at each
video monitoring location, to estimate
sounds received by pinnipeds, and at
the launch site to estimate maximum
potential sound received. These
recordings will provide for a thorough
description of launch sounds as
received at different locations on
western SNI, and of the factors that
affect received sound levels. By analysis
of the paired data on behavioral
observations and received sound levels,
the Navy will further characterize the
relationship between the two. If there is
a clear correlation, the Navy will
determine the ‘‘dose-response’’
relationship.
Visual Monitoring—The Navy will
conduct marine mammal and acoustic
monitoring during launches from SNI,
using simultaneous video recording of
pinniped behavior and audio recording
of launch sounds. The land-based
monitoring will provide data required to
characterize the extent and nature of the
takes. In particular, the monitoring will
provide the information needed to
document the occurrence, nature,
frequency, and duration of any changes
in pinniped behavior that might result
from missile launches. Components of
this documentation will include the
following:
• Identify and document any change
in behavior or movements that may
occur at the time of the launch;
• Compare received levels of launch
sound with pinniped responses, based
on acoustic and behavioral data from up
to three monitoring sites at different
distances from the launch site and
missile path during each launch and
attempt to establish the dose-response
relationship for launch sounds under
different launch conditions;
• Ascertain periods or launch
conditions when pinnipeds are most
and least responsive to launch activities;
and
• Document take by harassment and,
although unlikely, any mortality or
injury.
The launch monitoring program will
include remote video recordings before,
during, and after launches when
pinnipeds are present in the area of
potential impact, and visual assessment
by trained observers before and after the
launch. Remote cameras are essential
during launches because safety rules
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prevent personnel from being present in
most of the areas of interest. In addition,
video techniques will allow
simultaneous observations at up to three
different locations, and will provide a
permanent record that could be
reviewed in detail. No specific effort
will be made to monitor elephant seals,
though they may be present in mixed
groups when monitoring other species.
Acoustical Monitoring—The Navy
will take acoustical recordings during
each monitored launch. These
recordings should be suitable for
quantitative analysis of the levels and
characteristics of the received launch
sounds. The Navy will use up to four
autonomous audio recorders to make
acoustical measurements. During each
launch, these will be located as close as
practical to monitored pinniped haulout sites and near the launch pad itself.
The monitored haul-out sites will
typically include one site as close as
possible to the missile’s planned flight
path and one or two locations farther
from the flight path within the area of
potential impact with pinnipeds
present.
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Reporting Measures
The Navy will submit annual interim
technical reports to NMFS no later than
December 31 for the duration of the
regulations. These reports will provide
full documentation of methods, results,
and interpretation pertaining to all
monitoring tasks for launches during
each calendar year. However, only
preliminary information will be
included for any launches during the
60-day period immediately preceding
submission.
The Navy will submit a draft
comprehensive technical report to
NMFS 180 days prior to the expiration
of the regulations, providing full
documentation of the methods, results,
and interpretation of all monitoring
tasks for launches to date. A revised
final comprehensive technical report,
including all monitoring results during
the entire period of the regulations will
be due 90 days after the regulations
expire.
The Navy will ensure that NMFS is
notified immediately if an injured or
dead marine mammal is judged to result
from launch activities at any time.
Monitoring Results From Previously
Authorized Activities
Between 2001 and 2012, a maximum
of 1,990 California sea lions, 395 harbor
seals, and 130 northern elephant seals
were estimated to have been potentially
harassed in any single monitoring year
incidental to missile launches at SNI
(Holst et al., 2008, 2010, 2011; Ugoretz
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and Greene, 2012). These numbers may
represent multiple exposures of single
animals, as beaches were monitored
repeatedly over the course of the year
during numerous launches. However,
some animals that displayed behavioral
reactions may have been missed, as not
all areas can be monitored during the
launches. Pinnipeds that were
potentially affected left the haul-out site
in response to the launch, left the water
at a vigorous pace, or exhibited
prolonged movement or behavioral
changes relative to their behavior
immediately prior to the launch.
Estimated Take by Incidental
Harassment
The NDAA of 2004 (Pub. L. 103–136)
removed the ‘‘small numbers’’ and
‘‘specified geographical region’’
limitations indicated above and
amended the definition of ‘‘harassment’’
as it applies to a ‘‘military readiness
activity’’ to read as follows (section
3(18)(B) of the MMPA): (i) Any act that
injures or has the significant potential to
injure a marine mammal or marine
mammal stock in the wild [Level A
Harassment]; or (ii) Any act that
disturbs or is likely to disturb a marine
mammal or marine mammal stock in the
wild by causing disruption of natural
behavioral patterns, including, but not
limited to, migration, surfacing, nursing,
breeding, feeding, or sheltering, to a
point where such behavioral patterns
are abandoned or significantly altered
[Level B Harassment].
Any takes of marine mammals are
most likely to result from operational
noise as launch missiles pass near haulout sites, and/or associated visual cues.
This section estimates maximum
potential take and the likely annual take
of marine mammal species during
missile launches at SNI.
The launch sounds could be received
for several seconds and, to be
conservative, are considered to be
prolonged rather than transient sounds.
Given the variety of responses
documented previously for the sounds
of man-made activities lasting several
seconds, a sound exposure level of 100
dB re 20 microPascals 2 per second is
considered appropriate as a disturbance
criterion for pinnipeds hauled out at the
west end of SNI, particularly for
California sea lions and northern
elephant seals. Some pinnipeds that
haul-out on the western end of SNI are
expected to be within the area where
sound exposure levels exceed 100 dB.
Far fewer pinnipeds are expected to
occur within this area and none of the
recorded sound exposure levels appear
to be high enough to induce TTS.
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Based on the reaction criterion, the
distance to which it is assumed to
extend, and the estimated numbers of
pinnipeds exposed to sound exposure
levels at or above 100 dB, the Navy
estimated the number of pinnipeds on
the west end of SNI that might be taken.
The Navy made an additional
adjustment for harbor seals, as they are
known to sometimes react strongly to
sound exposure levels below 100 dB.
The Navy considered the percentage of
animals that actually responded to
launch noise in previous monitoring
years in order to estimate the number of
animals potentially harassed. Recorded
sound exposure levels in different areas
of SNI were compared to ground-based
census data of pinnipeds. These
censuses were typically conducted
seasonally when maximum numbers of
pinnipeds were known to occur on land.
Northern Elephant Seal
To estimate the potential maximum
numbers of northern elephant seals that
might be exposed to sound levels at or
above 100 dB in 2014, the highest pup
counts within map areas K, L, and M
(see Figure 16 of the Navy’s application)
in any year between 2000 and 2010
were used (yielding a total of 1,854),
and a continuing growth rate of 7.3
percent since 2010 was applied. This
results in a maximum potential pup
count of 2,458 for those map areas in
2014. Based on data collected from 1988
to 2010, the total count of all age classes
expected to be hauled out is
approximately twice the number of
pups hauled out. Therefore, the
maximum number hauled out in areas
of potential impact for 2014 was
approximated by doubling the
maximum potential calculated pup
count. Thus, the maximum expected
number of elephant seals that may be
exposed to sound levels at or above 100
dB during 2014 is estimated to be 4,916.
In the absence of any contrary data, it
is assumed that elephant seals exhibit
high site fidelity when they return to
shore, and that the 4,916 elephant seals
calculated above represent the
maximum total number that might be
exposed to ‘‘strong’’ (at or above 100 dB)
sounds during the year, assuming
missiles are launched when all animals
are hauled out and all beaches within
the area receive strong sounds. If some
seals haul out on different beaches at
various times during the year,
sometimes within and sometimes
outside the area exposed to levels at or
above 100 dB, then the number of times
an individual elephant seal might be
exposed to strong launch sounds would
be reduced. However, the total number
of individuals that would be exposed at
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least once over the course of the year
would probably be increased.
Movements from one beach to another
may be more likely for juveniles than for
older seals, given that this has been
observed in other pinniped species
(such as for harbor seal pups; Thompson
et al. 1994).
Published studies and results from the
2001–2012 monitoring at SNI indicate
that elephant seals are more tolerant of
transient noise and other forms of
disturbance than are California sea lions
or harbor seals. If so, the actual impact
zone is smaller than assumed here, and
the number of elephant seals that might
be taken by harassment would be
substantially lower than the number of
seals present within the area where
sound levels are at or above 100 dB. For
example, during the 2001–2012 launch
program, the majority of northern
elephant seals did not exhibit more than
brief startle reactions in response to
launches (Holst et al. 2005, 2008, 2010,
2011; Ugoretz and Greene, 2012). Most
individuals merely raised their heads
briefly upon hearing the launch sounds
and then quickly returned to their
previous activity pattern (usually
sleeping). During some launches, a
small proportion (typically much less
than 10 percent) of northern elephant
seals moved a short distance (<10 m)
away from their resting site, but settled
within minutes. Elephant seals rarely
moved or reacted more than this.
Therefore, the Navy estimates that up
to 10 percent of 4,916 elephant seals (or
492 seals) might be taken by Level B
harassment during each year of planned
launch operations.
Harbor Seals
To determine the potential numbers
of harbor seals that might be taken by
harassment, the Navy used the
maximum total harbor seal count for
SNI (858) and assumed that the
population has remained relatively
stable. Previous monitoring from 2001–
2012 showed that most monitored
harbor seals entered the water in
response to launches. Previous
monitoring also indicates that about 70
percent of harbor seals that haul out on
SNI use the beaches within areas K, L,
and M. The Navy conservatively
estimates that 80 percent of harbor seals
on SNI may be impacted by missile
launches. Therefore, the Navy estimates
that a maximum of 686 harbor seals
might be taken by Level B harassment
during a 1-year period.
California Sea Lion
To estimate the maximum potential
number of sea lions that might be
hauled out within areas exposed to
sound levels at or above 100 dB, the
Navy calculated the maximum number
of sea lions occurring within map areas
K, L, and M (Figure 16 of the Navy’s
application) in any year from 2001–
2011. The Navy adjusted this maximum,
14,963 sea lions, for a population
growth rate of 5.6 percent per year,
which results in a maximum of 20,749
sea lions of all ages and sexes that might
be hauled out within the areas exposed
to sound levels at or above 100 dB in a
single year. For most of the year, only
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females and pups are expected to be
ashore, so the number of animals
exposed to these sound levels from any
one launch is likely less than the
estimated total number.
Based on past monitoring, the Navy
concluded that approximately 10
percent of the California sea lions
exposed to launch sounds during each
year of launch activity might exhibit
behavioral disturbance. Therefore, the
Navy estimated that a maximum of
2,740 California sea lions on SNI might
be taken by Level B harassment during
a 1-year period. However, based on the
Commission’s comment during the
proposed rule public comment period,
NMFS agreed that the maximum
number of annual launches (40) should
also be a factor when estimating take.
NMFS used the Navy’s draft
comprehensive monitoring report to
calculate the annual average of potential
takes per launch. Then, each average
was multiplied by 40 and summed to
get 24,360 takes over a 5-year period.
NMFS estimates that an average of 4,872
takes of California sea lions may occur
each year.
Summary
NMFS is authorizing take according to
the Navy’s estimates and also
considering monitoring results from the
past 5 years and the potential for up to
40 launches to occur each year. The
estimated take numbers are provided in
Table 2 below for each marine mammal
species. These take estimates do not
take mitigation measures into
consideration.
TABLE 2—ESTIMATED AND AUTHORIZED TAKE OF MARINE MAMMALS ON AN ANNUAL BASIS
Estimated
take by
Level B
harassment
Common species name
Northern elephant seal ............................................................................................................................
Harbor seal ..............................................................................................................................................
California sea lion ....................................................................................................................................
Analysis and Preliminary
Determinations
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Negligible Impact
Negligible impact is ‘‘an impact
resulting from the specified activity that
cannot be reasonably expected to, and is
not reasonably likely to, adversely affect
the species or stock through effects on
annual rates of recruitment or survival
(50 CFR 216.103). A negligible impact
finding is based on the lack of likely
adverse effects on annual rates of
recruitment or survival (i.e., populationlevel effects). An estimate of the number
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of Level B harassment takes, alone, is
not enough information on which to
base an impact determination. In
addition to considering estimates of the
number of marine mammals that might
be ‘‘taken’’ through behavioral
harassment, NMFS must consider other
factors, such as the likely nature of any
responses (their intensity, duration,
etc.), the context of any responses
(critical reproductive time or location,
migration, etc.), as well as the number
and nature of estimated Level A
harassment takes, the number of
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Abundance
of stock
Population
trend
492
686
4,872
124,000
30,196
296,750
Unknown.
Stable.
Increasing.
estimated mortalities, and effects on
habitat.
NMFS has determined that target and
missile launch activities and aircraft
and helicopter operations from SNI, as
described in this document and in the
Navy’s application, will result in no
more than Level B harassment of
northern elephant seals, harbor seals,
and California sea lions. The effects of
these military readiness activities will
be limited to short-term, localized
changes in behavior, including
temporarily vacating haul-outs, and
possible temporary threshold shift in
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the hearing of any pinnipeds that are in
close proximity to a launch pad at the
time of a launch. These effects are not
likely to have a significant or long-term
impact on feeding, breeding, or other
important biological functions. No take
by injury or mortality is anticipated, and
the potential for permanent hearing
impairment is unlikely. Furthermore,
during 5 years of monitoring under the
Navy’s current authorization, there was
no evidence of injury, mortality, pup
abandonment, or other significant
impact beyond behavioral harassment
during or immediately succeeding any
of the 33 launches. No known pinniped
injuries or mortalities have occurred
since monitoring began in 2001, and
few, if any, pinnipeds are believed to
have received sound levels strong
enough to elicit TTS.
Based on the analysis contained
herein of the likely effects of the
specified activity on marine mammals
and their habitat, and taking into
consideration the implementation of the
required monitoring and mitigation
measures, NMFS finds that the total
marine mammal take from the Navy’s
missile launches will have a negligible
impact on the affected marine mammal
species or stocks.
Impact on Availability of Affected
Species for Taking for Subsistence Uses
There are no relevant subsistence uses
of marine mammals implicated by this
action. Therefore, NMFS has
determined that the total taking of
affected species or stocks will not have
any unmitigable adverse impact on the
availability of such species or stocks for
taking for subsistence purposes.
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Endangered Species Act (ESA)
No species listed under the ESA are
expected to be affected by these
activities. Therefore, NMFS has
determined that a section 7 consultation
under the ESA is not required.
National Environmental Policy Act
(NEPA)
NMFS prepared an Environmental
Assessment (EA) analyzing the potential
issuance of regulations and an LOA to
the Navy for the period 2014–2019. The
final EA was prepared in May 2014 and
NMFS issued a Finding of No
Significant Impact for this action. These
documents are available on our Web site
at https://www.nmfs.noaa.gov/pr/
permits/incidental.htm#applications.
NMFS determined that issuance of the
rulemaking and subsequent LOA will
not significantly impact the quality of
the human environment and that
preparation of an Environmental Impact
Statement is not required.
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Classification
The Office of Management and Budget
has determined that this proposed rule
is not significant for purposes of
Executive Order 12866.
Pursuant to the Regulatory Flexibility
Act (RFA), 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 action will not have a
significant economic impact on a
substantial number of small entities.
NMFS did not receive any public
comments addressing this certification.
Therefore, a Final Initial 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 the effective
date of the measures contained in the
final rule. The existing regulations for
SNI expire June 3, 2014 and launches
may be scheduled soon after. Any delay
of enacting the final rule would result
in the Navy’s non-compliance with the
MMPA (should the Navy conduct
missile launches without an LOA),
thereby resulting in the potential for
unauthorized takes of marine mammals.
Moreover, the Navy is ready to
implement the rule immediately. For
these reasons, the Assistant
Administrator finds good cause to waive
the 30-day delay in the effective date.
List of Subjects in 50 CFR Part 217
Exports, Fish, Imports, Incidental
take, Indians, Labeling, Marine
mammals, Navy, Penalties, Reporting
and recordkeeping requirements,
Seafood, Sonar, Transportation.
Dated: June 2, 2014.
Eileen Sobeck,
Assistant Administrator for Fisheries,
National Marine Fisheries Service.
For reasons set forth in the preamble,
50 CFR part 217 is amended as follows:
PART 217—REGULATIONS
GOVERNING THE TAKE OF MARINE
MAMMALS INCIDENTAL TO
SPECIFIED ACTIVITIES
1. The authority citation for part 217
continues to read as follows:
■
Authority: 16 U.S.C. 1361 et seq.
2. Subpart F is added to part 217 to
read as follows:
■
Subpart F—Taking of Marine Mammals
Incidental To Target and Missile Launch
Activities From San Nicolas Island, CA
Sec.
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217.50 Specified activity and specified
geographical region.
217.51 Effective dates.
217.52 Permissible methods of taking.
217.53 Prohibitions.
217.54 Mitigation.
217.55 Requirements for monitoring and
reporting.
217.56 Applications for Letters of
Authorization.
217.57 Letters of Authorization.
217.58 Renewal and modifications of
Letters of Authorization.
Subpart F—Taking of Marine Mammals
Incidental To Target and Missile
Launch Activities From San Nicolas
Island, CA
§ 217.50 Specified activity and specified
geographical region.
(a) Regulations in this subpart apply
only to the incidental taking of marine
mammals specified in paragraph (b) of
this section by the Naval Air Warfare
Center Weapons Division, U.S. Navy,
and those persons it authorizes to
engage in target missile launch activities
and associated aircraft and helicopter
operations at the Naval Air Warfare
Center Weapons Division facilities on
San Nicolas Island, California.
(b) The incidental take of marine
mammals under the activity identified
in paragraph (a) of this section is limited
to the following species: Northern
elephant seals (Mirounga angustirostris),
harbor seals (Phoca vitulina), and
California sea lions (Zalophus
californianus).
(c) This Authorization is valid only
for activities associated with the
launching of a total of 40 vehicles (e.g.,
RAM, Coyote, MSST, Terrier, SM–3, or
similar) from Alpha Launch Complex
and smaller missiles and targets from
Building 807 on San Nicolas Island,
California.
§ 217.51
Effective dates.
Regulations in this subpart are
effective from June 3, 2014, through
June 3, 2019.
§ 217.52
Permissible methods of taking.
(a) Under Letters of Authorization
issued pursuant to § 216.106 and 217.57
of this chapter, the Holder of the Letter
of Authorization may incidentally, but
not intentionally, take marine mammals
by harassment, within the area
described in § 217.50, provided the
activity is in compliance with all terms,
conditions, and requirements of the
regulations and the appropriate Letter of
Authorization.
(b) The activities identified in
§ 217.50 must be conducted in a manner
that minimizes, to the greatest extent
practicable, any adverse impacts on
marine mammals and their habitat.
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(c) The incidental take of marine
mammals is authorized for the species
listed in § 217.50(b) and is limited to
Level B Harassment.
§ 217.53
Prohibitions.
Notwithstanding takings
contemplated in § 217.50 and
authorized by a Letter of Authorization
issued under §§ 216.106 and 217.57 of
this chapter, no person in connection
with the activities described in § 217.50
may:
(a) Take any marine mammal not
specified in § 217.50(b);
(b) Take any marine mammal
specified in § 217.50(b) other than by
incidental, unintentional harassment;
(c) Take a marine mammal specified
in § 217.50(b) if such taking results in
more than a negligible impact on the
species or stocks of such marine
mammal; or
(d) Violate, or fail to comply with, the
terms, conditions, and requirements of
this subpart or a Letter of Authorization
issued under §§ 216.106 and 217.57 of
this chapter.
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§ 217.54
Mitigation.
(a) When conducting operations
identified in § 217.50(c), the mitigation
measures contained in the Letter of
Authorization issued under §§ 216.106
and 217.57 must be implemented. These
mitigation measures include, but are not
limited to:
(1) The holder of the Letter of
Authorization must not enter pinniped
haul-out sites below the missile’s
predicted flight path for 2 hours prior to
planned missile launches.
(2) The holder of the Letter of
Authorization must avoid, whenever
possible, launch activities during harbor
seal pupping season (February to April),
unless constrained by factors including,
but not limited to, human safety,
national security, or for vehicle launch
trajectory necessary to meet mission
objectives.
(3) The holder of the Letter of
Authorization must limit, whenever
possible, launch activities during other
pinniped pupping seasons, unless
constrained by factors including, but not
limited to, human safety, national
security, or for vehicle launch trajectory
necessary to meet mission objectives.
(4) The holder of the Letter of
Authorization must not launch vehicles
from the Alpha Complex at low
elevation (less than 1,000 feet (305 m))
on launch azimuths that pass close to
pinniped haul-out sites when occupied.
(5) The holder of the Letter of
Authorization must avoid, where
practicable, launching multiple target
missiles in quick succession over haul-
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out sites, especially when young pups
are present.
(6) The holder of the Letter of
Authorization must limit launch
activities during nighttime hours, except
when required by the test objectives.
(7) Aircraft and helicopter flight paths
must maintain a minimum altitude of
1,000 feet (305 m) from pinniped haulouts and rookeries, except in
emergencies or for real-time security
incidents (e.g., search-and-rescue, firefighting), which may require
approaching pinniped haul-outs and
rookeries closer than 1,000 feet (305 m).
(8) If post-launch surveys determine
that an injurious or lethal take of a
marine mammal has occurred or there is
an indication that the distribution, size,
or productivity of the potentially
affected pinniped populations has been
affected, the launch procedure and the
monitoring methods must be reviewed,
in cooperation with NMFS, and, if
necessary, appropriate changes must be
made through modification to a Letter of
Authorization, prior to conducting the
next launch of the same vehicle under
that Letter of Authorization.
(9) Additional mitigation measures as
contained in a Letter of Authorization.
(b) [Reserved]
§ 217.55 Requirements for monitoring and
reporting.
(a) Unless specified otherwise in the
Letter of Authorization, the Holder of
the Letter of Authorization must notify
the Administrator, West Coast Region,
NMFS, by letter or telephone, at least 2
weeks prior to activities possibly
involving the taking of marine
mammals. If the authorized activity
identified in § 217.50 is thought to have
resulted in the mortality or injury of any
marine mammals or in any take of
marine mammals not identified in
§ 217.50(b), then the Holder of the Letter
of Authorization must notify the
Director, Office of Protected Resources,
NMFS, or designee, by telephone (301–
427–8401), and the Administrator, West
Coast Region, NMFS, or designee, by
telephone (562–980–3232), within 48
hours of the discovery of the injured or
dead animal.
(b) The National Marine Fisheries
Service must be informed immediately
of any changes or deletions to any
portions of the proposed monitoring
plan submitted, in accordance with the
Letter of Authorization.
(c) The holder of the Letter of
Authorization must designate
biologically trained, on-site
individual(s), approved in advance by
NMFS, to record the effects of the
launch activities and the resulting noise
on pinnipeds.
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32685
(d) The holder of the Letter of
Authorization must implement the
following monitoring measures:
(1) Visual land-based monitoring. (i)
Prior to each missile launch, an
observer(s) will place three autonomous
digital video cameras overlooking
chosen haul-out sites located varying
distances from the missile launch site.
Each video camera will be set to record
a focal subgroup within the larger haulout aggregation for a maximum of 4
hours or as permitted by the videotape
capacity.
(ii) Systematic visual observations, by
those individuals, described in
paragraph (c) of this section, of
pinniped presence and activity will be
conducted and recorded in a field
logbook a minimum of 2 hours prior to
the estimated launch time and for no
less than 1 hour immediately following
the launch of target missiles.
(iii) Systematic visual observations,
by those individuals, described in
paragraph (c) of this section, of
pinniped presence and activity will be
conducted and recorded in a field
logbook a minimum of 2 hours prior to
launch, during launch, and for no less
than 1 hour after the launch of the
BQM–34, BQM–74, Tomahawk, RAM
target and similar types of missiles.
(iv) Documentation, both via
autonomous video camera and human
observer, will consist of:
(A) Numbers and sexes of each age
class in focal subgroups;
(B) Description and timing of launch
activities or other disruptive event(s);
(C) Movements of pinnipeds,
including number and proportion
moving, direction and distance moved,
and pace of movement;
(D) Description of reactions;
(E) Minimum distances between
interacting and reacting pinnipeds;
(F) Study location;
(G) Local time;
(H) Substratum type;
(I) Substratum slope;
(J) Weather condition;
(K) Horizontal visibility; and
(L) Tide state.
(2) Acoustic monitoring. (i) During all
target missile launches, calibrated
recordings of the levels and
characteristics of the received launch
sounds will be obtained from three
different locations of varying distances
from the target missile’s flight path. To
the extent practicable, these acoustic
recording locations will correspond
with the haul-out sites where video and
human observer monitoring is done.
(ii) Acoustic recordings will be
supplemented by the use of radar and
telemetry systems to obtain the
trajectory of target missiles in three
dimensions.
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(iii) Acoustic equipment used to
record launch sounds will be suitable
for collecting a wide range of
parameters, including the magnitude,
characteristics, and duration of each
target missile.
(e) The holder of the Letter of
Authorization must implement the
following reporting requirements:
(1) For each target missile launch, the
lead contractor or lead observer for the
holder of the Letter of Authorization
must provide a status report to NMFS,
West Coast Regional Office, providing
reporting items found under the Letter
of Authorization, unless other
arrangements for monitoring are agreed
upon in writing.
(2) The Navy shall submit an annual
report describing their activities and
including the following information:
(i) Timing, number, and nature of
launch operations;
(ii) Summary of mitigation and
monitoring implementation;
(iii) Summary of pinniped behavioral
observations; and
(iv) Estimate of the amount and nature
of all takes by harassment or by other
means.
(3) The Navy shall submit a draft
comprehensive technical report to the
Office of Protected Resources and West
Coast Regional Office, NMFS, 180 days
prior to the expiration of the regulations
in this subpart, providing full
documentation of the methods, results,
and interpretation of all monitoring
tasks for launches to date plus
preliminary information for missile
launches during the first 6 months of
the regulations.
(4) A revised final comprehensive
technical report, including all
monitoring results during the entire
period of validity of the Letter of
Authorization, will be due 90 days after
the end of the period of effectiveness of
the regulations in this subpart.
(5) The final report will be subject to
review and comment by NMFS. Any
recommendations made by NMFS must
be addressed in the final comprehensive
technical report prior to acceptance by
NMFS.
(f) Activities related to the monitoring
described in paragraphs (c) and (d) of
this section, or in the Letter of
Authorization issued under §§ 216.106
and 217.57 of this chapter, including the
retention of marine mammals, may be
conducted without the need for a
separate scientific research permit.
(g) In coordination and compliance
with appropriate Navy regulations, the
VerDate Mar<15>2010
13:35 Jun 05, 2014
Jkt 232001
NMFS may, at its discretion, place an
observer on San Nicolas Island for any
activity involved in marine mammal
monitoring either prior to, during, or
after a missile launch in order to
monitor the impact on marine
mammals.
§ 217.56 Applications for Letters of
Authorization.
To incidentally take marine mammals
pursuant to the regulations in this
subpart, the U.S. citizen (as defined by
§ 216.6 of this chapter) conducting the
activity identified in § 217.50 (the U.S.
Navy) must apply for and obtain either
an initial LOA in accordance with
§ 217.57 or a renewal under § 217.58.
§ 217.57
Letters of Authorization.
(a) A Letter of Authorization, unless
suspended or revoked, will be valid for
a period of time not to exceed the period
of validity of this subpart.
(b) Each Letter of Authorization will
set forth:
(1) Permissible methods of incidental
taking;
(2) Means of effecting the least
practicable adverse impact on the
species, its habitat, and on the
availability of the species for
subsistence uses (i.e., mitigation); and
(3) Requirements for mitigation,
monitoring, and reporting.
(c) Issuance and renewal of the Letter
of Authorization will be based on a
determination that the total number of
marine mammals taken by the activity
as a whole will have no more than a
negligible impact on the affected species
or stock of marine mammal(s).
§ 217.58 Renewals and Modifications of
Letters of Authorization.
(a) A Letter of Authorization issued
under §§ 216.106 and 217.57 of this
chapter for the activity identified in
§ 217.50 will be renewed or modified
upon request of the applicant, provided
that:
(1) The proposed specified activity
and mitigation, monitoring, and
reporting measures as well as the
anticipated impacts, are the same as
those described and analyzed for these
regulations (excluding changes made
pursuant to the adaptive management
provision of this chapter), and;
(2) NMFS determines that the
mitigation, monitoring, and reporting
measures required by the previous LOA
under these regulations were
implemented.
(b) For LOA modification or renewal
requests by the applicant that include
PO 00000
Frm 00054
Fmt 4700
Sfmt 9990
changes to the activity or the mitigation,
monitoring, or reporting measures
(excluding changes made pursuant to
the adaptive management provision of
this chapter) that do not change the
findings made for the regulations or
result in no more than a minor change
in the total estimated number of takes
(or distribution by species or years),
NMFS may publish a notice of proposed
LOA in the Federal Register, including
the associated analysis illustrating the
change, and solicit public comments
before issuing the LOA.
(c) An LOA issued under §§ 216.106
and 217.57 of this chapter for the
activity identified in § 217.50 may be
modified by NMFS under the following
circumstances:
(1) Adaptive management. NMFS may
modify (including augment) the existing
mitigation, monitoring, or reporting
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
the mitigation and monitoring set forth
in the preamble for these regulations.
(i) Possible sources of data could
contribute to the decision to modify the
mitigation, monitoring, and reporting
measures in an LOA:
(A) Results from the Navy’s
monitoring from the previous year(s);
(B) Results from other marine
mammal and/or sound research or
studies; or
(C) Any information that reveals
marine mammals may have been taken
in a manner, extent, or number not
authorized by these regulations or
subsequent LOAs.
(ii) If, through adaptive management,
the modifications to the mitigation,
monitoring, or reporting measures are
substantial, NMFS will publish a notice
of proposed LOA in the Federal
Register and solicit public comment.
(2) Emergencies. 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 § 217.50(b), a Letter of
Authorization may be modified without
prior notice or opportunity for public
comment. Notice would be published in
the Federal Register within 30 days of
the action.
[FR Doc. 2014–13084 Filed 6–2–14; 4:15 pm]
BILLING CODE 3510–22–P
E:\FR\FM\06JNR1.SGM
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Agencies
[Federal Register Volume 79, Number 109 (Friday, June 6, 2014)]
[Rules and Regulations]
[Pages 32678-32686]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2014-13084]
=======================================================================
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 217
[Docket No. 131120978-4452-02]
RIN 0648-BD80
Takes of Marine Mammals Incidental to Specified Activities; U.S.
Navy Missile Launches From San Nicolas Island, California
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: Upon application from the U.S. Navy (Navy), Naval Air Warfare
Center Weapons Division (NAWCWD), we (the National Marine Fisheries
Service) are issuing regulations under the Marine Mammal Protection Act
(MMPA) to govern the unintentional taking of marine mammals incidental
to missile launches from San Nicolas Island (SNI) from June 2014
through June 2019. These regulations allows us to issue a Letter 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 or stocks and
their habitat, and set forth requirements pertaining to the monitoring
and reporting of the incidental take.
DATES: Effective June 3, 2014, through June 3, 2019.
ADDRESSES: To obtain an electronic copy of the Navy's application or
other referenced documents, visit the internet at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm#applications. Documents
cited in this notice may also be viewed, by appointment, during regular
business hours, at the Office of Protected Resources, National Marine
Fisheries Service, 1315 East-West Highway, Silver Spring, MD 20910.
FOR FURTHER INFORMATION CONTACT: John Fiorentino, Office of Protected
Resources, NMFS, (301) 427-8401.
SUPPLEMENTARY INFORMATION:
Background
Section 101(a)(5)(A) of the MMPA (16 U.S.C 1361 et seq.) directs
the Secretary of Commerce to allow, upon request, the incidental, but
not intentional, taking of small numbers of marine mammals by U.S.
citizens who engage in a specified activity (other than commercial
fishing) within a specified geographical region if certain findings are
made and either regulations are issued or, if the taking is limited to
harassment, a notice of a proposed authorization is provided to the
public for review.
Authorization for incidental takings shall be granted if NMFS finds
that the taking will have a negligible impact on the species or
stock(s), will not have an unmitigable adverse impact on the
availability of the species or stock(s) for subsistence uses (where
relevant), and if the permissible methods of taking and requirements
pertaining to the mitigation, monitoring, and reporting of such takings
are set forth. NMFS has defined ``negligible impact'' in 50 CFR 216.103
as ``an impact resulting from the specified activity that cannot be
reasonably expected to, and is not reasonably likely to, adversely
affect the species or stock through effects on annual rates of
recruitment or survival.''
The National Defense Authorization Act of 2004 (NDAA) (Pub. L. 108-
136) removed the ``small numbers'' and ``specified geographical
region'' limitations indicated above and amended the definition of
``harassment'' as it applies to a ``military readiness activity'' to
read as follows (Section 3(18)(B) of the MMPA): (i) Any act that
injures or has the significant potential to injure a marine mammal or
marine mammal stock in the wild [Level A Harassment]; or (ii) Any act
that disturbs or is likely to disturb a marine mammal or marine mammal
stock in the wild by causing disruption of natural behavioral patterns,
to a point where such behavioral patterns are abandoned or
significantly altered [Level B Harassment].
Summary of Request
On July 24, 2013, NMFS received an application from the Navy for
the taking of marine mammals incidental to missile launches from San
Nicolas Island (SNI), California. NMFS determined that the application
was adequate and complete on November 18, 2013.
The Navy proposed to continue a launch program for missiles and
targets from several launch sites on SNI between June 2014 and June
2019. These activities are considered military readiness activities.
Marine mammals hauled out on SNI may be exposed to sound from missile
launches. The Navy requests authorization to take three marine mammal
species by Level B harassment: northern elephant seal (Mirounga
angustirostris), Pacific harbor seal (Phoca vitulina), and California
sea lion (Zalophus californianus).
The Navy is currently operating under an authorization to take
marine mammals incidental to missile launches from SNI, which expires
June 3, 2014 (74 FR 26587).
Description of the Specified Activity
Overview
The Navy is continuing a launch program for missiles and targets
from several launch sites on SNI. Missiles vary from tactical and
developmental weapons to target missiles used to test defensive
strategies and other weapons systems. Some launch events involve a
single missile, while others involve the launch of multiple missiles
either in quick succession or at intervals of a few hours. Up to 200
missiles (40 missiles per year) may be launched over the 5-year period,
but the number and type of launch varies depending on operational
needs.
The purpose of these launches is to support testing and training
activities associated with operations on the NAWCWD Point Mugu Sea
Range. The Sea Range is used by the U.S. and allied military services
to test and evaluate sea, land, and air weapon systems; to provide
realistic training opportunities; and to maintain operational readiness
of these forces. Some of the launches are used for practicing defensive
drills against the types of weapons simulated by these missiles and
some launches are conducted for the related purpose of testing new
types of targets.
Dates and Duration
Launches of this type have been occurring at SNI for many years and
are expected to continue indefinitely into the future. NMFS is issuing
a 5-year Letter of Authorization for missile launches taking place
between June 2014 and June 2019. The timing of these launches is
variable and subject to testing and training requirements and
meteorological and logistical limitations. To meet the Navy's
operational testing and training requirements, launches may be required
at any time of year and any time of day. Up to 200 missiles (40
missiles per year) may be launched over the 5-year period
[[Page 32679]]
and the Navy is proposing that up to 10 launches per year may occur at
night. Given the launch acceleration and flight speed of the missiles,
most launch events are of extremely short duration. Strong launch
sounds are typically detectable near the surrounding beaches for no
more than a few seconds per launch (Holst et al., 2005a, 2008, 2011).
Specified Geographic Region
SNI is one of the eight Channel Islands in the Southern California
Bight, located about 105 kilometers (km) southwest of Point Mugu.
Missile launches will occur from the western part of SNI (see Figure 2
in the Navy's LOA application). The missiles fly generally westward
through the Point Mugu Sea Range. The primary launch locations are the
Alpha Launch Complex, which is located on the west-central part of SNI,
and Building 807 Launch Complex, which is located at the western end of
SNI. Other launch pads are located nearby.
Detailed Description of Activities
Missiles included in the Navy's request range from relatively small
and quieter missiles like the Rolling Airframe Missile to larger and
louder missiles like the Terrier Black-Brant. While other missiles may
be launched in the future, the largest missile analyzed here is 23,000
kilograms (kg). A description of the types of missiles that may be
launched at SNI during the 5-year period and their sound
characteristics was provided in the proposed rule (79 FR 13022, March
7, 2014) and includes, in summary: the Rolling Airframe Missile (RAM),
GQM-163A ``Coyote,'' Multi-stage Sea Skimming Target (MSST), Terrier
(Black Brant, Lynx, and Orion), and RIM-161 Standard Missile 3 (SM-3).
General Launch Operations--Aircraft and helicopter flights between
the Point Mugu airfield on the mainland, the airfield on SNI, and the
target sites in the Sea Range are a routine part of a planned launch
operation. These flights generally do not pass at low level over the
beaches where pinnipeds are expected to be hauled out. Therefore, these
flights are not further considered in this document.
Movements of personnel are restricted near the launch sites at
least several hours prior to a launch for safety reasons. No personnel
are allowed on the western end of SNI during launches. Movements of
personnel or missiles near the island's beaches are also restricted at
other times of the year for purposes of environmental protection and
preservation of cultural resource sites. Launch monitoring equipment
would be deployed and activated prior to the launches.
Comments and Responses
On March 7, 2014 (79 FR 13022), NMFS published a proposed rule to
authorize the taking of marine mammals incidental to missile launches
at SNI. During the 45-day public comment period, NMFS received comments
from the Marine Mammal Commission (Commission) and a private citizen.
The Commission's comment is specific to section 101(a)(5)(A) of the
MMPA and NMFS' analysis of impacts to marine mammals and is summarized
and addressed below and throughout the final rule.
Comment 1: The Commission recommended that NMFS require the Navy to
estimate the number of sea lion takes based on the greatest mean number
of takes that has been estimated in any previous monitoring year
multiplied by 40.
Response: NMFS agrees that the potential number of annual launches
(40) should be considered when estimating take in order to ensure that
the Navy remains in compliance with the MMPA. NMFS reassessed the take
estimates for California sea lion by calculating the annual average
number of takes per launch and multiplying each average by 40. This
total (24,360) is the number of California sea lions takes NMFS is
authorizing over the 5-year rule (an average of 4,872 takes per year).
This is the maximum number of takes expected, considering the Navy only
conducted 42 launches over the past 5 years.
Comment 2: A private citizen recommended that the Navy submit
annual reports describing non-compliance, if any, with required
mitigation measures--including frequency of occurrence, date of
occurrence, and reason for occurrence of non-compliance.
Response: It is standard practice for the Navy to include this type
of information in their summary of implementation of mitigation
measures in the annual interim technical reports and comprehensive
technical reports submitted to NMFS. These reports are available on the
NMFS Office of Protected Resources Web site at https://www.nmfs.noaa.gov/pr/permits/incidental.htm#applications.
Description of Marine Mammals in the Area of the Specified Activity
There are seven species of marine mammals with possible or
confirmed occurrence in the area of the specified activity: Northern
elephant seals, harbor seals, California sea lions, northern fur seals
(Callorhinus ursinus), Guadalupe fur seal (Arctocephalus townsendi),
Steller sea lions (Eumetopias jubatus), and southern sea otters
(Enhydra lutris nereis). The northern fur seal is considered depleted
under the MMPA; the Guadalupe fur seal is listed as threatened under
the Endangered Species Act (ESA) and depleted under the MMPA; and the
eastern distinct population segment of Steller sea lion was delisted
under the ESA in 2013. The northern fur seal, Guadalupe fur seal, and
Steller sea lion are considered rare at SNI and takes of these species
have not been observed under the Navy's current MMPA authorization.
Therefore, these three species were not considered further. The
southern sea otter is managed by the U.S. Fish and Wildlife Service and
was also not considered further. Table 1 includes species-specific
information on the three species likely to occur in the area of the
specified activity.
Table 1--Species Information on the Marine Mammals Likely To Occur in the Area of the Specified Activity
--------------------------------------------------------------------------------------------------------------------------------------------------------
Common name Scientific name Status Occurrence Seasonality Range Abundance
--------------------------------------------------------------------------------------------------------------------------------------------------------
Northern elephant sea............ Mirounga ............... Common............... Year-round........... Mexico to Alaska... 124,000
angustirostris.
Harbor seal...................... Phoca vitulina...... ............... Common............... Year-round........... Baja California to 30,196
Aleutian Islands.
California sea lion.............. Zalophus ............... Common............... Year-round........... Mexico to Canada... 296,750
californianus.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Further information on the biology and local distribution of these
species can be found in the Navy's application (see ADDRESSES), and the
NMFS Marine Mammal Stock Assessment Reports, which are available online
at: https://www.nmfs.noaa.gov/pr/species/.
[[Page 32680]]
Potential Effects of the Specified Activity on Marine Mammals
This section of the proposed Incidental Harassment Authorization
(IHA) (79 FR 13022, March 7, 2014) included a summary and discussion of
the ways that the types of stressors associated with the specified
activity (e.g., missile launch noise) have been observed to impact
marine mammals. The ``Estimated Take by Incidental Harassment'' section
later in this document will include a quantitative analysis of the
number of individuals that are expected to be taken by this activity.
The ``Negligible Impact Analysis'' section will include the analysis of
how this specific activity will impact marine mammals and will consider
the content of this section, the ``Estimated Take by Incidental
Harassment'' section, the ``Proposed Mitigation'' section, and the
``Anticipated Effects on Marine Mammal Habitat'' section to draw
conclusions regarding the likely impacts of this activity on the
reproductive success or survivorship of individuals and from that on
the affected marine mammal populations or stocks.
In summary, potential effects of the specified activity on marine
mammals involve both acoustic and non-acoustic effects. Acoustic
effects are related to sound produced by the engines of all launch
vehicles, and, in some cases, their booster rockets. Potential non-
acoustic effects could result from the physical presence of personnel
during placement of video and acoustical monitoring equipment. However,
careful deployment of monitoring equipment is not expected to result in
any disturbance to pinnipeds hauled out nearby. Any visual disturbance
caused by passage of a vehicle overhead is likely to be minor and brief
as the launch vehicles are relatively small and move at great speed.
Detailed information on each potential effect (acoustic impacts,
behavioral reactions of pinnipeds to missile launches, stampede-related
injury or mortality from missile launches) was provided in the proposed
rule (79 FR 13022, March 7, 2014) and that information has not changed.
Anticipated Effects on Marine Mammal Habitat
Three species of pinnipeds use various beaches around SNI as places
to rest, molt, and breed. These beaches consist of sand, rock ledges,
and rocky cobble. Pinnipeds continue to use beaches around the western
end of SNI, and are expanding their use of some beaches, despite
ongoing launch activities for many years. Similarly, it appears that
sounds from prior launches have not affected use of coastal areas at
Vandenberg Air Force Base where similar missile launches occur.
Pinnipeds do not feed when hauled out on these beaches and the
airborne launch sounds will not persist in the water near the island
for more than a few seconds. Therefore, it is not expected that the
launch activities will have any impact on the food or feeding success
of these pinnipeds.
Boosters from missiles may be jettisoned shortly after launch and
fall on the island, but are not expected to impact beaches. Fuel
contained in these boosters is consumed rapidly and completely, so
there would be no risk of contamination even in the very unlikely event
that a booster did land on a beach. Therefore, launch activities are
not expected to have any long-term, significant effects on marine
mammal habitat.
Mitigation
In order to issue an incidental take authorization (ITA) under
section 101(a)(5)(A) of the MMPA, NMFS must set forth the permissible
methods of taking pursuant to such activity, and other means of
effecting the least practicable impact on such species or stock and its
habitat, paying particular attention to rookeries, mating grounds, and
areas of similar significance, and on the availability of such species
or stock for taking for certain subsistence uses (where relevant).
The NDAA of 2004 amended the MMPA as it relates to military-
readiness activities and the ITA process such that ``least practicable
adverse impact'' shall include consideration of personnel safety,
practicality of implementation, and impact of the effectiveness of the
``military readiness activity.'' The activities described in the Navy's
application are considered military readiness activities.
As during launches conducted under previous regulations, where
practicable, the Navy will implement the following mitigation measures,
provided that doing so will not compromise operational safety, human
safety, national security, or other requirements or mission goals:
(1) Limit activities near the beaches in advance of launches;
(2) Avoid launch activities during harbor seal pupping season
(February through April);
(3) Limit launch activities during other pinniped pupping seasons;
(4) Not launch missiles from the Alpha Complex at low elevation
(less than 305 m) on launch azimuths that pass close to pinniped haul-
out sites when occupied;
(5) Avoid launching multiple missiles in quick succession over
haul-out sites, especially when young pups are present; and
(6) Maintain a minimum altitude of 305 m from pinniped haul-outs
and rookeries for aircraft and helicopter flight paths during missile
launch operations, except in emergencies or for real-time security
incidents (e.g., search-and-rescue, fire-fighting, adverse weather
conditions), which may require approaching pinniped haul-outs and
rookeries closer than 305 m.
Mitigation Conclusions
NMFS has carefully evaluated the applicant's proposed mitigation
measures and considered a range of other measures in the context of
ensuring that NMFS prescribes the means of effecting the least
practicable impact on the affected marine mammal species and stocks and
their habitat. No additional mitigation measures were recommended
during the public comment period on the proposed rule. Our evaluation
of potential measures included consideration of the following factors
in relation to one another:
The manner in which, and the degree to which, the
successful implementation of the measure is expected to minimize
adverse impacts to marine mammals;
The proven or likely efficacy of the specific measure to
minimize adverse impacts as planned; and
The practicability of the measure for applicant
implementation, including consideration of personnel safety,
practicality of implementation, and impact on the effectiveness of the
military readiness activity.
Any mitigation measure(s) prescribed by NMFS should be able to
accomplish, have a reasonable likelihood of accomplishing (based on
current science), or contribute to the accomplishment of one or more of
the general goals listed below:
1. Avoidance or minimization of injury or death of marine mammals
wherever possible (goals 2, 3, and 4 may contribute to this goal).
2. A reduction in the numbers of marine mammals (total number or
number at biologically important time or location) exposed to received
levels of noise, or other activities expected to result in the take of
marine mammals (this goal may contribute to 1, above, or to reducing
harassment takes only).
3. A reduction in the number of times (total number or number at
biologically important time or location) individuals would be exposed
to received levels of
[[Page 32681]]
noise, or other activities expected to result in the take of marine
mammals (this goal may contribute to 1, above, or to reducing
harassment takes only).
4. A reduction in the intensity of exposures (either total number
or number at biologically important time or location) to received
levels of noise, or other activities expected to result in the take of
marine mammals (this goal may contribute to 1, above, or to reducing
the severity of harassment takes only).
5. Avoidance or minimization of adverse effects to marine mammal
habitat, paying special attention to the food base, activities that
block or limit passage to or from biologically important areas,
permanent destruction of habitat, or temporary destruction/disturbance
of habitat during a biologically important time.
6. For monitoring directly related to mitigation--an increase in
the probability of detecting marine mammals, thus allowing for more
effective implementation of the mitigation.
Based on our evaluation of the applicant's proposed measures, as
well as other measures considered by NMFS, NMFS has determined that the
proposed mitigation measures provide the means of effecting the least
practicable impact on marine mammal species or stocks and their
habitat, paying particular attention to rookeries, mating grounds, and
areas of similar significance, while also considering personnel safety,
practicality of implementation, and impact on the effectiveness of the
military readiness activity.
Monitoring and Reporting
In order to issue an ITA for an activity, section 101(a)(5)(A) of
the MMPA states that NMFS must set forth, ``requirements pertaining to
the monitoring and reporting of such taking.'' The MMPA implementing
regulations at 50 CFR 216.104 (a)(13) indicate that requests for ITAs
must include the suggested means of accomplishing the necessary
monitoring and reporting that will result in increased knowledge of the
species and of the level of taking or impacts on populations of marine
mammals that are expected to be present in the proposed action area.
The Navy submitted a marine mammal monitoring plan as part of their
application. It can be found in section 13 of their application. NMFS
did not receive any comments suggesting a modification or
supplementation to the proposed monitoring plan during the public
comment period.
Monitoring measures prescribed by NMFS should accomplish one or
more of the following general goals:
1. An increase in the probability of detecting marine mammals, both
within the mitigation zone (thus allowing for more effective
implementation of the mitigation) and in general to generate more data
to contribute to the analyses mentioned below.
2. An increase in our understanding of how many marine mammals are
likely to be exposed to levels of noise that we associate with specific
adverse effects, such as behavioral harassment, TTS, or PTS.
3. An increase in our understanding of how marine mammals respond
to stimuli expected to result in take and how anticipated adverse
effects on individuals (in different ways and to varying degrees) may
impact the population, species, or stock (specifically through effects
on annual rates of recruitment or survival) through any of the
following methods:
a. Behavioral observations in the presence of stimuli compared to
observations in the absence of stimuli (need to be able to accurately
predict received level, distance from source, and other pertinent
information).
b. Physiological measurements in the presence of stimuli compared
to observations in the absence of stimuli (need to be able to
accurately predict received level, distance from source, and other
pertinent information).
c. Distribution and/or abundance comparisons in times or areas with
concentrated stimuli versus times or areas without stimuli.
4. An increased knowledge of the affected species.
5. An increase in our understanding of the effectiveness of certain
mitigation and monitoring measures.
Monitoring Measures
The Navy will conduct the following monitoring measures, which are
further detailed in section 13 of their application:
The Navy will continue a standard, ongoing, land-based
monitoring program to assess effects on harbor seals, northern elephant
seals, and California sea lions on SNI. This monitoring will occur at
up to three sites at different distances from the launch site before,
during, and after each launch, depending upon presence of pinnipeds
during each launch. The monitoring will be via autonomous video or
Forward Looking Infrared (FLIR) cameras. Pinniped behavior on the beach
will be documented prior to the planned launch operations, during the
launch, and following the launch. Northern elephant seals will not be
specifically targeted for monitoring, though may be present in the
field of view when monitoring other species.
During each launch, the Navy will obtain calibrated
recordings of the sounds of the launches as received at different
distances from the missile's flightline. The Navy anticipates that
acoustic data will be acquired at each video monitoring location, to
estimate sounds received by pinnipeds, and at the launch site to
estimate maximum potential sound received. These recordings will
provide for a thorough description of launch sounds as received at
different locations on western SNI, and of the factors that affect
received sound levels. By analysis of the paired data on behavioral
observations and received sound levels, the Navy will further
characterize the relationship between the two. If there is a clear
correlation, the Navy will determine the ``dose-response''
relationship.
Visual Monitoring--The Navy will conduct marine mammal and acoustic
monitoring during launches from SNI, using simultaneous video recording
of pinniped behavior and audio recording of launch sounds. The land-
based monitoring will provide data required to characterize the extent
and nature of the takes. In particular, the monitoring will provide the
information needed to document the occurrence, nature, frequency, and
duration of any changes in pinniped behavior that might result from
missile launches. Components of this documentation will include the
following:
Identify and document any change in behavior or movements
that may occur at the time of the launch;
Compare received levels of launch sound with pinniped
responses, based on acoustic and behavioral data from up to three
monitoring sites at different distances from the launch site and
missile path during each launch and attempt to establish the dose-
response relationship for launch sounds under different launch
conditions;
Ascertain periods or launch conditions when pinnipeds are
most and least responsive to launch activities; and
Document take by harassment and, although unlikely, any
mortality or injury.
The launch monitoring program will include remote video recordings
before, during, and after launches when pinnipeds are present in the
area of potential impact, and visual assessment by trained observers
before and after the launch. Remote cameras are essential during
launches because safety rules
[[Page 32682]]
prevent personnel from being present in most of the areas of interest.
In addition, video techniques will allow simultaneous observations at
up to three different locations, and will provide a permanent record
that could be reviewed in detail. No specific effort will be made to
monitor elephant seals, though they may be present in mixed groups when
monitoring other species.
Acoustical Monitoring--The Navy will take acoustical recordings
during each monitored launch. These recordings should be suitable for
quantitative analysis of the levels and characteristics of the received
launch sounds. The Navy will use up to four autonomous audio recorders
to make acoustical measurements. During each launch, these will be
located as close as practical to monitored pinniped haul-out sites and
near the launch pad itself. The monitored haul-out sites will typically
include one site as close as possible to the missile's planned flight
path and one or two locations farther from the flight path within the
area of potential impact with pinnipeds present.
Reporting Measures
The Navy will submit annual interim technical reports to NMFS no
later than December 31 for the duration of the regulations. These
reports will provide full documentation of methods, results, and
interpretation pertaining to all monitoring tasks for launches during
each calendar year. However, only preliminary information will be
included for any launches during the 60-day period immediately
preceding submission.
The Navy will submit a draft comprehensive technical report to NMFS
180 days prior to the expiration of the regulations, providing full
documentation of the methods, results, and interpretation of all
monitoring tasks for launches to date. A revised final comprehensive
technical report, including all monitoring results during the entire
period of the regulations will be due 90 days after the regulations
expire.
The Navy will ensure that NMFS is notified immediately if an
injured or dead marine mammal is judged to result from launch
activities at any time.
Monitoring Results From Previously Authorized Activities
Between 2001 and 2012, a maximum of 1,990 California sea lions, 395
harbor seals, and 130 northern elephant seals were estimated to have
been potentially harassed in any single monitoring year incidental to
missile launches at SNI (Holst et al., 2008, 2010, 2011; Ugoretz and
Greene, 2012). These numbers may represent multiple exposures of single
animals, as beaches were monitored repeatedly over the course of the
year during numerous launches. However, some animals that displayed
behavioral reactions may have been missed, as not all areas can be
monitored during the launches. Pinnipeds that were potentially affected
left the haul-out site in response to the launch, left the water at a
vigorous pace, or exhibited prolonged movement or behavioral changes
relative to their behavior immediately prior to the launch.
Estimated Take by Incidental Harassment
The NDAA of 2004 (Pub. L. 103-136) removed the ``small numbers''
and ``specified geographical region'' limitations indicated above and
amended the definition of ``harassment'' as it applies to a ``military
readiness activity'' to read as follows (section 3(18)(B) of the MMPA):
(i) Any act that injures or has the significant potential to injure a
marine mammal or marine mammal stock in the wild [Level A Harassment];
or (ii) Any act that disturbs or is likely to disturb a marine mammal
or marine mammal stock in the wild by causing disruption of natural
behavioral patterns, including, but not limited to, migration,
surfacing, nursing, breeding, feeding, or sheltering, to a point where
such behavioral patterns are abandoned or significantly altered [Level
B Harassment].
Any takes of marine mammals are most likely to result from
operational noise as launch missiles pass near haul-out sites, and/or
associated visual cues. This section estimates maximum potential take
and the likely annual take of marine mammal species during missile
launches at SNI.
The launch sounds could be received for several seconds and, to be
conservative, are considered to be prolonged rather than transient
sounds. Given the variety of responses documented previously for the
sounds of man-made activities lasting several seconds, a sound exposure
level of 100 dB re 20 microPascals \2\ per second is considered
appropriate as a disturbance criterion for pinnipeds hauled out at the
west end of SNI, particularly for California sea lions and northern
elephant seals. Some pinnipeds that haul-out on the western end of SNI
are expected to be within the area where sound exposure levels exceed
100 dB. Far fewer pinnipeds are expected to occur within this area and
none of the recorded sound exposure levels appear to be high enough to
induce TTS.
Based on the reaction criterion, the distance to which it is
assumed to extend, and the estimated numbers of pinnipeds exposed to
sound exposure levels at or above 100 dB, the Navy estimated the number
of pinnipeds on the west end of SNI that might be taken. The Navy made
an additional adjustment for harbor seals, as they are known to
sometimes react strongly to sound exposure levels below 100 dB. The
Navy considered the percentage of animals that actually responded to
launch noise in previous monitoring years in order to estimate the
number of animals potentially harassed. Recorded sound exposure levels
in different areas of SNI were compared to ground-based census data of
pinnipeds. These censuses were typically conducted seasonally when
maximum numbers of pinnipeds were known to occur on land.
Northern Elephant Seal
To estimate the potential maximum numbers of northern elephant
seals that might be exposed to sound levels at or above 100 dB in 2014,
the highest pup counts within map areas K, L, and M (see Figure 16 of
the Navy's application) in any year between 2000 and 2010 were used
(yielding a total of 1,854), and a continuing growth rate of 7.3
percent since 2010 was applied. This results in a maximum potential pup
count of 2,458 for those map areas in 2014. Based on data collected
from 1988 to 2010, the total count of all age classes expected to be
hauled out is approximately twice the number of pups hauled out.
Therefore, the maximum number hauled out in areas of potential impact
for 2014 was approximated by doubling the maximum potential calculated
pup count. Thus, the maximum expected number of elephant seals that may
be exposed to sound levels at or above 100 dB during 2014 is estimated
to be 4,916.
In the absence of any contrary data, it is assumed that elephant
seals exhibit high site fidelity when they return to shore, and that
the 4,916 elephant seals calculated above represent the maximum total
number that might be exposed to ``strong'' (at or above 100 dB) sounds
during the year, assuming missiles are launched when all animals are
hauled out and all beaches within the area receive strong sounds. If
some seals haul out on different beaches at various times during the
year, sometimes within and sometimes outside the area exposed to levels
at or above 100 dB, then the number of times an individual elephant
seal might be exposed to strong launch sounds would be reduced.
However, the total number of individuals that would be exposed at
[[Page 32683]]
least once over the course of the year would probably be increased.
Movements from one beach to another may be more likely for juveniles
than for older seals, given that this has been observed in other
pinniped species (such as for harbor seal pups; Thompson et al. 1994).
Published studies and results from the 2001-2012 monitoring at SNI
indicate that elephant seals are more tolerant of transient noise and
other forms of disturbance than are California sea lions or harbor
seals. If so, the actual impact zone is smaller than assumed here, and
the number of elephant seals that might be taken by harassment would be
substantially lower than the number of seals present within the area
where sound levels are at or above 100 dB. For example, during the
2001-2012 launch program, the majority of northern elephant seals did
not exhibit more than brief startle reactions in response to launches
(Holst et al. 2005, 2008, 2010, 2011; Ugoretz and Greene, 2012). Most
individuals merely raised their heads briefly upon hearing the launch
sounds and then quickly returned to their previous activity pattern
(usually sleeping). During some launches, a small proportion (typically
much less than 10 percent) of northern elephant seals moved a short
distance (<10 m) away from their resting site, but settled within
minutes. Elephant seals rarely moved or reacted more than this.
Therefore, the Navy estimates that up to 10 percent of 4,916
elephant seals (or 492 seals) might be taken by Level B harassment
during each year of planned launch operations.
Harbor Seals
To determine the potential numbers of harbor seals that might be
taken by harassment, the Navy used the maximum total harbor seal count
for SNI (858) and assumed that the population has remained relatively
stable. Previous monitoring from 2001-2012 showed that most monitored
harbor seals entered the water in response to launches. Previous
monitoring also indicates that about 70 percent of harbor seals that
haul out on SNI use the beaches within areas K, L, and M. The Navy
conservatively estimates that 80 percent of harbor seals on SNI may be
impacted by missile launches. Therefore, the Navy estimates that a
maximum of 686 harbor seals might be taken by Level B harassment during
a 1-year period.
California Sea Lion
To estimate the maximum potential number of sea lions that might be
hauled out within areas exposed to sound levels at or above 100 dB, the
Navy calculated the maximum number of sea lions occurring within map
areas K, L, and M (Figure 16 of the Navy's application) in any year
from 2001-2011. The Navy adjusted this maximum, 14,963 sea lions, for a
population growth rate of 5.6 percent per year, which results in a
maximum of 20,749 sea lions of all ages and sexes that might be hauled
out within the areas exposed to sound levels at or above 100 dB in a
single year. For most of the year, only females and pups are expected
to be ashore, so the number of animals exposed to these sound levels
from any one launch is likely less than the estimated total number.
Based on past monitoring, the Navy concluded that approximately 10
percent of the California sea lions exposed to launch sounds during
each year of launch activity might exhibit behavioral disturbance.
Therefore, the Navy estimated that a maximum of 2,740 California sea
lions on SNI might be taken by Level B harassment during a 1-year
period. However, based on the Commission's comment during the proposed
rule public comment period, NMFS agreed that the maximum number of
annual launches (40) should also be a factor when estimating take. NMFS
used the Navy's draft comprehensive monitoring report to calculate the
annual average of potential takes per launch. Then, each average was
multiplied by 40 and summed to get 24,360 takes over a 5-year period.
NMFS estimates that an average of 4,872 takes of California sea lions
may occur each year.
Summary
NMFS is authorizing take according to the Navy's estimates and also
considering monitoring results from the past 5 years and the potential
for up to 40 launches to occur each year. The estimated take numbers
are provided in Table 2 below for each marine mammal species. These
take estimates do not take mitigation measures into consideration.
Table 2--Estimated and Authorized Take of Marine Mammals on an Annual
Basis
------------------------------------------------------------------------
Estimated
take by Abundance Population
Common species name Level B of stock trend
harassment
------------------------------------------------------------------------
Northern elephant seal....... 492 124,000 Unknown.
Harbor seal.................. 686 30,196 Stable.
California sea lion.......... 4,872 296,750 Increasing.
------------------------------------------------------------------------
Analysis and Preliminary Determinations
Negligible Impact
Negligible impact is ``an impact resulting from the specified
activity that cannot be reasonably expected to, and is not reasonably
likely to, adversely affect the species or stock through effects on
annual rates of recruitment or survival (50 CFR 216.103). A negligible
impact finding is based on the lack of likely adverse effects on annual
rates of recruitment or survival (i.e., population-level effects). An
estimate of the number of Level B harassment takes, alone, is not
enough information on which to base an impact determination. In
addition to considering estimates of the number of marine mammals that
might be ``taken'' through behavioral harassment, NMFS must consider
other factors, such as the likely nature of any responses (their
intensity, duration, etc.), the context of any responses (critical
reproductive time or location, migration, etc.), as well as the number
and nature of estimated Level A harassment takes, the number of
estimated mortalities, and effects on habitat.
NMFS has determined that target and missile launch activities and
aircraft and helicopter operations from SNI, as described in this
document and in the Navy's application, will result in no more than
Level B harassment of northern elephant seals, harbor seals, and
California sea lions. The effects of these military readiness
activities will be limited to short-term, localized changes in
behavior, including temporarily vacating haul-outs, and possible
temporary threshold shift in
[[Page 32684]]
the hearing of any pinnipeds that are in close proximity to a launch
pad at the time of a launch. These effects are not likely to have a
significant or long-term impact on feeding, breeding, or other
important biological functions. No take by injury or mortality is
anticipated, and the potential for permanent hearing impairment is
unlikely. Furthermore, during 5 years of monitoring under the Navy's
current authorization, there was no evidence of injury, mortality, pup
abandonment, or other significant impact beyond behavioral harassment
during or immediately succeeding any of the 33 launches. No known
pinniped injuries or mortalities have occurred since monitoring began
in 2001, and few, if any, pinnipeds are believed to have received sound
levels strong enough to elicit TTS.
Based on the analysis contained herein of the likely effects of the
specified activity on marine mammals and their habitat, and taking into
consideration the implementation of the required monitoring and
mitigation measures, NMFS finds that the total marine mammal take from
the Navy's missile launches will have a negligible impact on the
affected marine mammal species or stocks.
Impact on Availability of Affected Species for Taking for Subsistence
Uses
There are no relevant subsistence uses of marine mammals implicated
by this action. Therefore, NMFS has determined that the total taking of
affected species or stocks will not have any unmitigable adverse impact
on the availability of such species or stocks for taking for
subsistence purposes.
Endangered Species Act (ESA)
No species listed under the ESA are expected to be affected by
these activities. Therefore, NMFS has determined that a section 7
consultation under the ESA is not required.
National Environmental Policy Act (NEPA)
NMFS prepared an Environmental Assessment (EA) analyzing the
potential issuance of regulations and an LOA to the Navy for the period
2014-2019. The final EA was prepared in May 2014 and NMFS issued a
Finding of No Significant Impact for this action. These documents are
available on our Web site at https://www.nmfs.noaa.gov/pr/permits/incidental.htm#applications. NMFS determined that issuance of the
rulemaking and subsequent LOA will not significantly impact the quality
of the human environment and that preparation of an Environmental
Impact Statement is not required.
Classification
The Office of Management and Budget has determined that this
proposed rule is not significant for purposes of Executive Order 12866.
Pursuant to the Regulatory Flexibility Act (RFA), 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 action will not have a significant
economic impact on a substantial number of small entities. NMFS did not
receive any public comments addressing this certification. Therefore, a
Final Initial 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 the effective date of the
measures contained in the final rule. The existing regulations for SNI
expire June 3, 2014 and launches may be scheduled soon after. Any delay
of enacting the final rule would result in the Navy's non-compliance
with the MMPA (should the Navy conduct missile launches without an
LOA), thereby resulting in the potential for unauthorized takes of
marine mammals. Moreover, the Navy is ready to implement the rule
immediately. For these reasons, the Assistant Administrator finds good
cause to waive the 30-day delay in the effective date.
List of Subjects in 50 CFR Part 217
Exports, Fish, Imports, Incidental take, Indians, Labeling, Marine
mammals, Navy, Penalties, Reporting and recordkeeping requirements,
Seafood, Sonar, Transportation.
Dated: June 2, 2014.
Eileen Sobeck,
Assistant Administrator for Fisheries, National Marine Fisheries
Service.
For reasons set forth in the preamble, 50 CFR part 217 is amended
as follows:
PART 217--REGULATIONS GOVERNING THE TAKE OF MARINE MAMMALS
INCIDENTAL TO SPECIFIED ACTIVITIES
0
1. The authority citation for part 217 continues to read as follows:
Authority: 16 U.S.C. 1361 et seq.
0
2. Subpart F is added to part 217 to read as follows:
Subpart F--Taking of Marine Mammals Incidental To Target and Missile
Launch Activities From San Nicolas Island, CA
Sec.
217.50 Specified activity and specified geographical region.
217.51 Effective dates.
217.52 Permissible methods of taking.
217.53 Prohibitions.
217.54 Mitigation.
217.55 Requirements for monitoring and reporting.
217.56 Applications for Letters of Authorization.
217.57 Letters of Authorization.
217.58 Renewal and modifications of Letters of Authorization.
Subpart F--Taking of Marine Mammals Incidental To Target and
Missile Launch Activities From San Nicolas Island, CA
Sec. 217.50 Specified activity and specified geographical region.
(a) Regulations in this subpart apply only to the incidental taking
of marine mammals specified in paragraph (b) of this section by the
Naval Air Warfare Center Weapons Division, U.S. Navy, and those persons
it authorizes to engage in target missile launch activities and
associated aircraft and helicopter operations at the Naval Air Warfare
Center Weapons Division facilities on San Nicolas Island, California.
(b) The incidental take of marine mammals under the activity
identified in paragraph (a) of this section is limited to the following
species: Northern elephant seals (Mirounga angustirostris), harbor
seals (Phoca vitulina), and California sea lions (Zalophus
californianus).
(c) This Authorization is valid only for activities associated with
the launching of a total of 40 vehicles (e.g., RAM, Coyote, MSST,
Terrier, SM-3, or similar) from Alpha Launch Complex and smaller
missiles and targets from Building 807 on San Nicolas Island,
California.
Sec. 217.51 Effective dates.
Regulations in this subpart are effective from June 3, 2014,
through June 3, 2019.
Sec. 217.52 Permissible methods of taking.
(a) Under Letters of Authorization issued pursuant to Sec. 216.106
and 217.57 of this chapter, the Holder of the Letter of Authorization
may incidentally, but not intentionally, take marine mammals by
harassment, within the area described in Sec. 217.50, provided the
activity is in compliance with all terms, conditions, and requirements
of the regulations and the appropriate Letter of Authorization.
(b) The activities identified in Sec. 217.50 must be conducted in
a manner that minimizes, to the greatest extent practicable, any
adverse impacts on marine mammals and their habitat.
[[Page 32685]]
(c) The incidental take of marine mammals is authorized for the
species listed in Sec. 217.50(b) and is limited to Level B Harassment.
Sec. 217.53 Prohibitions.
Notwithstanding takings contemplated in Sec. 217.50 and authorized
by a Letter of Authorization issued under Sec. Sec. 216.106 and 217.57
of this chapter, no person in connection with the activities described
in Sec. 217.50 may:
(a) Take any marine mammal not specified in Sec. 217.50(b);
(b) Take any marine mammal specified in Sec. 217.50(b) other than
by incidental, unintentional harassment;
(c) Take a marine mammal specified in Sec. 217.50(b) if such
taking results in more than a negligible impact on the species or
stocks of such marine mammal; or
(d) Violate, or fail to comply with, the terms, conditions, and
requirements of this subpart or a Letter of Authorization issued under
Sec. Sec. 216.106 and 217.57 of this chapter.
Sec. 217.54 Mitigation.
(a) When conducting operations identified in Sec. 217.50(c), the
mitigation measures contained in the Letter of Authorization issued
under Sec. Sec. 216.106 and 217.57 must be implemented. These
mitigation measures include, but are not limited to:
(1) The holder of the Letter of Authorization must not enter
pinniped haul-out sites below the missile's predicted flight path for 2
hours prior to planned missile launches.
(2) The holder of the Letter of Authorization must avoid, whenever
possible, launch activities during harbor seal pupping season (February
to April), unless constrained by factors including, but not limited to,
human safety, national security, or for vehicle launch trajectory
necessary to meet mission objectives.
(3) The holder of the Letter of Authorization must limit, whenever
possible, launch activities during other pinniped pupping seasons,
unless constrained by factors including, but not limited to, human
safety, national security, or for vehicle launch trajectory necessary
to meet mission objectives.
(4) The holder of the Letter of Authorization must not launch
vehicles from the Alpha Complex at low elevation (less than 1,000 feet
(305 m)) on launch azimuths that pass close to pinniped haul-out sites
when occupied.
(5) The holder of the Letter of Authorization must avoid, where
practicable, launching multiple target missiles in quick succession
over haul-out sites, especially when young pups are present.
(6) The holder of the Letter of Authorization must limit launch
activities during nighttime hours, except when required by the test
objectives.
(7) Aircraft and helicopter flight paths must maintain a minimum
altitude of 1,000 feet (305 m) from pinniped haul-outs and rookeries,
except in emergencies or for real-time security incidents (e.g.,
search-and-rescue, fire-fighting), which may require approaching
pinniped haul-outs and rookeries closer than 1,000 feet (305 m).
(8) If post-launch surveys determine that an injurious or lethal
take of a marine mammal has occurred or there is an indication that the
distribution, size, or productivity of the potentially affected
pinniped populations has been affected, the launch procedure and the
monitoring methods must be reviewed, in cooperation with NMFS, and, if
necessary, appropriate changes must be made through modification to a
Letter of Authorization, prior to conducting the next launch of the
same vehicle under that Letter of Authorization.
(9) Additional mitigation measures as contained in a Letter of
Authorization.
(b) [Reserved]
Sec. 217.55 Requirements for monitoring and reporting.
(a) Unless specified otherwise in the Letter of Authorization, the
Holder of the Letter of Authorization must notify the Administrator,
West Coast Region, NMFS, by letter or telephone, at least 2 weeks prior
to activities possibly involving the taking of marine mammals. If the
authorized activity identified in Sec. 217.50 is thought to have
resulted in the mortality or injury of any marine mammals or in any
take of marine mammals not identified in Sec. 217.50(b), then the
Holder of the Letter of Authorization must notify the Director, Office
of Protected Resources, NMFS, or designee, by telephone (301-427-8401),
and the Administrator, West Coast Region, NMFS, or designee, by
telephone (562-980-3232), within 48 hours of the discovery of the
injured or dead animal.
(b) The National Marine Fisheries Service must be informed
immediately of any changes or deletions to any portions of the proposed
monitoring plan submitted, in accordance with the Letter of
Authorization.
(c) The holder of the Letter of Authorization must designate
biologically trained, on-site individual(s), approved in advance by
NMFS, to record the effects of the launch activities and the resulting
noise on pinnipeds.
(d) The holder of the Letter of Authorization must implement the
following monitoring measures:
(1) Visual land-based monitoring. (i) Prior to each missile launch,
an observer(s) will place three autonomous digital video cameras
overlooking chosen haul-out sites located varying distances from the
missile launch site. Each video camera will be set to record a focal
subgroup within the larger haul-out aggregation for a maximum of 4
hours or as permitted by the videotape capacity.
(ii) Systematic visual observations, by those individuals,
described in paragraph (c) of this section, of pinniped presence and
activity will be conducted and recorded in a field logbook a minimum of
2 hours prior to the estimated launch time and for no less than 1 hour
immediately following the launch of target missiles.
(iii) Systematic visual observations, by those individuals,
described in paragraph (c) of this section, of pinniped presence and
activity will be conducted and recorded in a field logbook a minimum of
2 hours prior to launch, during launch, and for no less than 1 hour
after the launch of the BQM-34, BQM-74, Tomahawk, RAM target and
similar types of missiles.
(iv) Documentation, both via autonomous video camera and human
observer, will consist of:
(A) Numbers and sexes of each age class in focal subgroups;
(B) Description and timing of launch activities or other disruptive
event(s);
(C) Movements of pinnipeds, including number and proportion moving,
direction and distance moved, and pace of movement;
(D) Description of reactions;
(E) Minimum distances between interacting and reacting pinnipeds;
(F) Study location;
(G) Local time;
(H) Substratum type;
(I) Substratum slope;
(J) Weather condition;
(K) Horizontal visibility; and
(L) Tide state.
(2) Acoustic monitoring. (i) During all target missile launches,
calibrated recordings of the levels and characteristics of the received
launch sounds will be obtained from three different locations of
varying distances from the target missile's flight path. To the extent
practicable, these acoustic recording locations will correspond with
the haul-out sites where video and human observer monitoring is done.
(ii) Acoustic recordings will be supplemented by the use of radar
and telemetry systems to obtain the trajectory of target missiles in
three dimensions.
[[Page 32686]]
(iii) Acoustic equipment used to record launch sounds will be
suitable for collecting a wide range of parameters, including the
magnitude, characteristics, and duration of each target missile.
(e) The holder of the Letter of Authorization must implement the
following reporting requirements:
(1) For each target missile launch, the lead contractor or lead
observer for the holder of the Letter of Authorization must provide a
status report to NMFS, West Coast Regional Office, providing reporting
items found under the Letter of Authorization, unless other
arrangements for monitoring are agreed upon in writing.
(2) The Navy shall submit an annual report describing their
activities and including the following information:
(i) Timing, number, and nature of launch operations;
(ii) Summary of mitigation and monitoring implementation;
(iii) Summary of pinniped behavioral observations; and
(iv) Estimate of the amount and nature of all takes by harassment
or by other means.
(3) The Navy shall submit a draft comprehensive technical report to
the Office of Protected Resources and West Coast Regional Office, NMFS,
180 days prior to the expiration of the regulations in this subpart,
providing full documentation of the methods, results, and
interpretation of all monitoring tasks for launches to date plus
preliminary information for missile launches during the first 6 months
of the regulations.
(4) A revised final comprehensive technical report, including all
monitoring results during the entire period of validity of the Letter
of Authorization, will be due 90 days after the end of the period of
effectiveness of the regulations in this subpart.
(5) The final report will be subject to review and comment by NMFS.
Any recommendations made by NMFS must be addressed in the final
comprehensive technical report prior to acceptance by NMFS.
(f) Activities related to the monitoring described in paragraphs
(c) and (d) of this section, or in the Letter of Authorization issued
under Sec. Sec. 216.106 and 217.57 of this chapter, including the
retention of marine mammals, may be conducted without the need for a
separate scientific research permit.
(g) In coordination and compliance with appropriate Navy
regulations, the NMFS may, at its discretion, place an observer on San
Nicolas Island for any activity involved in marine mammal monitoring
either prior to, during, or after a missile launch in order to monitor
the impact on marine mammals.
Sec. 217.56 Applications for Letters of Authorization.
To incidentally take marine mammals pursuant to the regulations in
this subpart, the U.S. citizen (as defined by Sec. 216.6 of this
chapter) conducting the activity identified in Sec. 217.50 (the U.S.
Navy) must apply for and obtain either an initial LOA in accordance
with Sec. 217.57 or a renewal under Sec. 217.58.
Sec. 217.57 Letters of Authorization.
(a) A Letter of Authorization, unless suspended or revoked, will be
valid for a period of time not to exceed the period of validity of this
subpart.
(b) Each Letter of Authorization will set forth:
(1) Permissible methods of incidental taking;
(2) Means of effecting the least practicable adverse impact on the
species, its habitat, and on the availability of the species for
subsistence uses (i.e., mitigation); and
(3) Requirements for mitigation, monitoring, and reporting.
(c) Issuance and renewal of the Letter of Authorization will be
based on a determination that the total number of marine mammals taken
by the activity as a whole will have no more than a negligible impact
on the affected species or stock of marine mammal(s).
Sec. 217.58 Renewals and Modifications of Letters of Authorization.
(a) A Letter of Authorization issued under Sec. Sec. 216.106 and
217.57 of this chapter for the activity identified in Sec. 217.50 will
be renewed or modified upon request of the applicant, provided that:
(1) The proposed specified activity and mitigation, monitoring, and
reporting measures as well as the anticipated impacts, are the same as
those described and analyzed for these regulations (excluding changes
made pursuant to the adaptive management provision of this chapter),
and;
(2) NMFS determines that the mitigation, monitoring, and reporting
measures required by the previous LOA under these regulations were
implemented.
(b) For LOA modification or renewal requests by the applicant that
include changes to the activity or the mitigation, monitoring, or
reporting measures (excluding changes made pursuant to the adaptive
management provision of this chapter) that do not change the findings
made for the regulations or result in no more than a minor change in
the total estimated number of takes (or distribution by species or
years), NMFS may publish a notice of proposed LOA in the Federal
Register, including the associated analysis illustrating the change,
and solicit public comments before issuing the LOA.
(c) An LOA issued under Sec. Sec. 216.106 and 217.57 of this
chapter for the activity identified in Sec. 217.50 may be modified by
NMFS under the following circumstances:
(1) Adaptive management. NMFS may modify (including augment) the
existing mitigation, monitoring, or reporting 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 the mitigation and monitoring
set forth in the preamble for these regulations.
(i) Possible sources of data could contribute to the decision to
modify the mitigation, monitoring, and reporting measures in an LOA:
(A) Results from the Navy's monitoring from the previous year(s);
(B) Results from other marine mammal and/or sound research or
studies; or
(C) Any information that reveals marine mammals may have been taken
in a manner, extent, or number not authorized by these regulations or
subsequent LOAs.
(ii) If, through adaptive management, the modifications to the
mitigation, monitoring, or reporting measures are substantial, NMFS
will publish a notice of proposed LOA in the Federal Register and
solicit public comment.
(2) Emergencies. 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 Sec. 217.50(b), a Letter of Authorization
may be modified without prior notice or opportunity for public comment.
Notice would be published in the Federal Register within 30 days of the
action.
[FR Doc. 2014-13084 Filed 6-2-14; 4:15 pm]
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