Taking and Importing Marine Mammals; U.S. Navy Training in the Virginia Capes Range Complex, 28328-28349 [E9-13697]
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Federal Register / Vol. 74, No. 113 / Monday, June 15, 2009 / Rules and Regulations
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 218
RIN 0648–AW78
Taking and Importing Marine
Mammals; U.S. Navy Training in the
Virginia Capes Range Complex
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AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
SUMMARY: NMFS, upon application from
the U.S. Navy (Navy), is issuing
regulations to govern the unintentional
taking of marine mammals incidental to
activities conducted at the Virginia
Capes (VACAPES) Range Complex for
the period of June 2009 through June
2014. The Navy’s activities are
considered military readiness activities
pursuant to the Marine Mammal
Protection Act (MMPA), as amended by
the National Defense Authorization Act
for Fiscal Year 2004 (NDAA). These
regulations, which allow for the
issuance of ‘‘Letters of Authorization’’
(LOAs) for the incidental take of marine
mammals during the described activities
and specified timeframes, prescribe the
permissible methods of taking and other
means of effecting the least practicable
adverse impact on marine mammal
species and their habitat, as well as
requirements pertaining to the
monitoring and reporting of such taking.
DATES: Effective June 8, 2009 and is
applicable to the Navy on June 5, 2009
through June 4, 2014.
ADDRESSES: A copy of the Navy’s
application (which contains a list of the
references used in this document),
NMFS’ Record of Decision (ROD), and
other documents cited herein may be
obtained by writing to Michael Payne,
Chief, Permits, Conservation and
Education Division, Office of Protected
Resources, National Marine Fisheries
Service, 1315 East-West Highway, Silver
Spring, MD 20910–3225 or by telephone
via the contact listed here (see FOR
FURTHER INFORMATION CONTACT).
Additionally, the Navy’s LOA
application may be obtained by visiting
the Internet at: https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications.
FOR FURTHER INFORMATION CONTACT:
Shane Guan, Office of Protected
Resources, NMFS, (301) 713–2289, ext.
137.
SUPPLEMENTARY INFORMATION:
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Extensive Supplementary Information
was provided in the proposed rule for
this activity, which was published in
the Federal Register on Friday,
December 12, 2008 (73 FR 75631). This
information will not be reprinted here
in its entirety; rather, all sections from
the proposed rule will be represented
herein and will contain either a
summary of the material presented in
the proposed rule or a note referencing
the page(s) in the proposed rule where
the information may be found. Any
information that has changed since the
proposed rule was published will be
addressed herein. Additionally, this
final rule contains a section that
responds to the comments received
during the public comment period.
Background
Sections 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1361 et seq.) direct
the Secretary of Commerce (Secretary)
to allow, upon request, the incidental,
but not intentional taking of marine
mammals by U.S. citizens who engage
in a specified activity (other than
commercial fishing) during periods of
not more than five consecutive years
each if certain findings are made and
regulations are issued or, if the taking is
limited to harassment, notice of a
proposed authorization is provided to
the public for review.
Authorization shall be granted if
NMFS finds that the taking will have a
negligible impact on the species or
stock(s), will not have an unmitigable
adverse impact on the availability of the
species or stock(s) for subsistence uses,
and if the permissible methods of taking
and requirements pertaining to the
mitigation, monitoring and reporting of
such taking are set forth.
NMFS has defined ‘‘negligible
impact’’ in 50 CFR 216.103 as:
An impact resulting from the specified
activity that cannot be reasonably expected
to, and is not reasonably likely to, adversely
affect the species or stock through effects on
annual rates of recruitment or survival.
The NDAA (Pub. L. 108–136)
removed the ‘‘small numbers’’ and
‘‘specified geographical region’’
limitations and amended the definition
of ‘‘harassment’’ as it applies to a
‘‘military readiness activity’’ to read as
follows (Section 3(18)(B) of the MMPA):
(i) Any act that injures or has the
significant potential to injure a marine
mammal or marine mammal stock in the wild
[Level A Harassment]; or
(ii) Any act that disturbs or is likely to
disturb a marine mammal or marine mammal
stock in the wild by causing disruption of
natural behavioral patterns, including, but
not limited to, migration, surfacing, nursing,
breeding, feeding, or sheltering, to a point
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where such behavioral patterns are
abandoned or significantly altered [Level B
Harassment].
Summary of Request
On March 17, 2008, NMFS received
an application from the Navy requesting
authorization for the take of 13 cetacean
species incidental to the proposed
training activities in the VACAPES
Range Complex over the course of 5
years. These training activities are
classified as military readiness
activities. The Navy states that these
training activities may cause various
impacts to marine mammal species in
the proposed VACAPES Range Complex
area. The Navy requests an
authorization to take individuals of
these cetacean species by Level B
Harassment. Further, the Navy requests
authorization to take 1 individual
Atlantic spotted, 20 common, 1
pantropical spotted, and 3 striped
dolphins per year by injury, and 1
individual common dolphin per year by
mortality, as a result of the proposed
training activities in the VACAPES
Range Complex. Please refer to Table 29
of the LOA application for detailed
information of the potential exposures
from explosive ordnance (per year) for
marine mammals in the VACAPES
Range Complex. However, due to the
proposed mitigation and monitoring
measures, NMFS does not expect that
the proposed action would result in any
marine mammal mortality. Therefore,
no mortality would be authorized for
the Navy’s VACAPES Range Complex
training activities.
Background of Navy Request
The proposed rule contains a
description of the Navy’s mission, their
responsibilities pursuant to Title 10 of
the United States Code, and the specific
purpose and need for the activities for
which they requested incidental take
authorization. The description
contained in the proposed rule has not
changed (73 FR 75631; December 12,
2008).
Description of the Specified Activities
The proposed rule contains a
complete description of the Navy’s
specified activities that are covered by
these final regulations, and for which
the associated incidental take of marine
mammals will be authorized in the
related LOAs. The proposed rule
describes the nature and number of the
training activities. These training
activities consist of surface warfare
[Missile Exercise (MISSILEX) and Highspeed Anti-Radiation Missile Exercise
(HARMEX)], mine warfare [Mine
Exercises (MINEX)], amphibious warfare
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[Firing Exercise (FIREX)], strike warfare
[Bombing Exercise (BOMBEX)], and
vessel movement to, from and within
the VACAPES Range Complex Study
Area. The narrative description of the
action contained in the proposed rule
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has not changed. Table 1 summarizes
the nature and levels of these planned
activities.
TABLE 1—LEVELS OF TRAINING EVENTS INVOLVE EXPLOSIVES PLANNED IN THE VACAPES RANGE COMPLEX PER YEAR
Operation
Platform
System/ordnance
Number of events
Missile Exercise
(MISSILEX) (Air to Surface).
MH–60S, HH–60H ............
AGM–114 (Hellfire missile)
60 sorties (60 missiles) .....
1 hour.
F/A–18, P–3C, and P–8A
AGM–65 E/F (Maverick
missile).
MK–83/GBU–32 [1,000 lb
High Explosive (HE)
bomb].
AMNS ................................
20 lb charges ....................
5″ gun (IMPASS) ..............
20 sorties (20 missiles) .....
1 hour.
5 events (20 bombs, 4
bombs/event).
1 hour.
140 sorties (30 rounds) .....
24 events ..........................
22 events (858 HE rounds,
39 HE per event)).
1.5 hours.
6–8 hours.
8 hours.
Bombing Exercise
(BOMBEX) (Air-to-Surface, At-Sea).
Mine Neutralization ...........
FIREX with IMPASS .........
F/A–18 ...............................
MH–60S ............................
EOD ..................................
CG, DDG ...........................
VACAPES Range Complex
The VACAPES Range Complex
proposed rule contains a description of
the VACAPES Study Area along with a
description of the areas in which certain
types of activities will occur. Table 2,
included here, summarizes the areas in
which explosive events will occur and
Duration per event
their frequency of occurrence. The
description of the VACAPES Range
Complex Study Area in the proposed
rule has not changed.
TABLE 2—NUMBER OF EVENTS UTILIZING MUNITIONS WITHIN THE VACAPES RANGE COMPLEX
Ordnance
Winter
Spring
Summer
Fall
Annual
totals
MISSILEX ...............................................
Hellfire .....................................................
Hellfire .....................................................
Maverick .................................................
FIREX .....................................................
5″ rounds ................................................
5″ rounds ................................................
5″ rounds ................................................
MINEX ....................................................
5 LB* .......................................................
20 LB ......................................................
BOMBEX ................................................
MK–83** ..................................................
................
11.25
3.75
5
................
1.83
1.83
1.83
................
7.50
4.00
................
1.25
................
11.25
3.75
5
................
1.83
1.83
1.83
................
7.50
4.00
................
1.25
................
11.25
3.75
5
................
1.83
1.83
1.83
................
7.50
12.00
................
1.25
................
11.25
3.75
5
................
1.83
1.83
1.83
................
7.50
4.00
................
1.25
80
................
................
................
22
................
................
................
54
................
................
5
................
Sub-area
Air-K ........................................................
W–72A (2) ..............................................
Air-K ........................................................
5C/D ........................................................
7C/D and 8C/D .......................................
1C1/2 ......................................................
W–50 UNDET .........................................
W–50 UNDET .........................................
Air-K ........................................................
* The use of 3.24 lb charges during AMNS training were conservatively modeled as 5 lb charges.
** One event using the MK–83 bombs consists of 4 bombs being dropped in succession. For example, in VACAPES Air-K there are 5 MK–83
events, which mean that a total of 20 bombs will be dropped per year.
Description of Marine Mammals in the
Area of the Specified Activities
There are 34 marine mammal species
with possible or confirmed occurrence
in the VACAPES Range Complex. As
indicated in Table 3, there are 33
cetacean species (7 mysticetes and 26
odontocetes) and one pinniped species.
Table 6 also includes the federal status
of these marine mammal species. Six
marine mammal species listed as
federally endangered under the
Endangered Species Act (ESA) occur in
the VACAPES Range Complex: the
humpback whale, North Atlantic right
whale, sei whale, fin whale, blue whale,
and sperm whale. Although it is
possible that any of the 34 species of
marine mammals may occur in the
VACAPES Range Complex, only 24 of
those species are expected to occur
regularly in the region. The proposed
rule also includes a discussion of the
methods used to estimate marine
mammal density in the VACAPES Study
Area. The Description of Marine
Mammals in the Area of the Specified
Activities section has not changed from
what was in the proposed rule (73 FR
75631, pages 75635–75636).
TABLE 3—MARINE MAMMAL SPECIES FOUND IN THE VACAPES RANGE COMPLEX
Family and scientific name
Common name
Federal status
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Order Cetacea
Suborder Mysticeti (baleen whales)
Eubalaena glacialis ............................................
Megaptera novaeangliae ...................................
Balaenoptera acutorostrata ................................
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North Atlantic right whale .................................
Humpback whale ..............................................
Minke whale.
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Endangered.
Endangered.
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TABLE 3—MARINE MAMMAL SPECIES FOUND IN THE VACAPES RANGE COMPLEX—Continued
Family and scientific name
B.
B.
B.
B.
Common name
brydei .............................................................
borealis ..........................................................
physalus ........................................................
musculus .......................................................
Federal status
Bryde’s whale.
Sei whale ..........................................................
Fin whale ..........................................................
Blue whale ........................................................
Endangered.
Endangered.
Endangered.
Suborder Odontoceti (toothed whales)
Physeter macrocephalus ...................................
Kogia breviceps .................................................
K. sima ...............................................................
Ziphius cavirostris ..............................................
Mesoplodon minus .............................................
M. europaeus .....................................................
M. bidens ...........................................................
M. densirostris ....................................................
Steno bredanensis .............................................
Tursiops truncatus .............................................
Stenella attenuata ..............................................
S. frontalis ..........................................................
S. longirostris .....................................................
S. clymene .........................................................
S. coeruleoalba ..................................................
Delphinus delphis ...............................................
Lagenodephis hosei ...........................................
Lagenorhynchus acutus .....................................
Grampus griseus ................................................
Peponocephala electra ......................................
Feresa attenuata ................................................
Pseudorca crassidens ........................................
Orcinus orca .......................................................
Globicephala melas ...........................................
G. macrorhynchus ..............................................
Phocoena phocoena ..........................................
Sperm whale
Pygmy sperm whale.
Dwarf sperm whale.
Cuvier’s beaked whale.
True’s beaked whale.
Gervais’ beaked whale.
Sowerby’s beaked whale.
Blainville’s beaked whale.
Rough-toothed dolphin.
Bottlenose dolphin.
Pantropical spotted dolphin.
Atlantic spotted dolphin.
Spinner dolphin.
Clymene dolphin.
Striped dolphin.
Common dolphin.
Fraser’s dolphin.
Atlantic white-sided dolphin.
Risso’s dolphin.
Melon-headed whale.
Pygmy killer whale.
False killer whale.
Killer whale.
Long-finned pilot whale.
Short-finned pilot whale.
Harbor porpoise.
Endangered.
Order Carnivora
Suborder Pinnipedia
Phoca vitulina .....................................................
Harbor seal.
Suborder Sirenia
West Indian manatee.
Potential Impacts to Marine Mammal
Species
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Trichechus manatus ...........................................
determine whether the specified activity
will have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (however,
there are no subsistence communities in
the VACAPES study area); and (4) to
prescribe requirements pertaining to
monitoring and reporting.
In the Potential Impacts to Marine
Mammal Species section of the
proposed rule, NMFS included a
qualitative discussion of the different
ways that underwater explosive
detonations from MISSILEX, BOMBEX,
MINEX, and FIREX may potentially
affect marine mammals (some of which
NMFS would not classify as
harassment). See 73 FR 75631;
December 12, 2008; pages 75636–75646.
Marine mammals may experience direct
physiological effects (such as threshold
shift), acoustic masking, impaired
communications, stress responses, and
behavioral disturbance. The information
With respect to the MMPA, NMFS’
effects assessment serves four primary
purposes: (1) to prescribe the
permissible methods of taking (i.e.,
Level B Harassment (behavioral
harassment), Level A Harassment
(injury), or mortality, including an
identification of the number and types
of take that could occur by Level A or
B harassment or mortality) and to
prescribe other means of effecting the
least practicable adverse impact on such
species or stock and its habitat (i.e.,
mitigation); (2) to determine whether
the specified activity will have a
negligible impact on the affected species
or stocks of marine mammals (based on
the likelihood that the activity will
adversely affect the species or stock
through effects on annual rates of
recruitment or survival); (3) to
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contained in Potential Impacts to
Marine Mammal Species section from
MISSILEX, BOMBEX, MINEX, and
FIREX from the proposed rule has not
changed.
The information pertaining to
HARMEX has changed from the
Proposed Rule. Further analyses show
that HARMEX would have no effects on
marine mammals because these types of
missiles detonate 30–60 ft (9.1–18.3 m)
above the water surface. Therefore, they
are not included in the underwater
explosive exposure modeling in the
Final Rule since no marine mammal
exposures are anticipated.
Later, in the Estimated Take of Marine
Mammals Section, NMFS relates and
quantifies the potential effects to marine
mammals from underwater detonation
of explosives discussed here to the
MMPA definitions of Level A and Level
B Harassment. NMFS has also
considered the effects of mortality on
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these species, although mortality is
neither expected, nor will it be
authorized.
Additional analyses on potential
impacts to marine mammals from vessel
movement within the VACAPES Range
Complex Study Area are added below.
Vessel Movement
There are limited data concerning
marine mammal behavioral responses to
vessel traffic and vessel noise, and a
lack of consensus among scientists with
respect to what these responses mean or
whether they result in short-term or
long-term adverse effects. In those cases
where there is a busy shipping lane or
where there is large amount of vessel
traffic, marine mammals may
experience acoustic masking
(Hildebrand, 2005) if they are present in
the area (e.g., killer whales in Puget
Sound; Foote et al., 2004; Holt et al.,
2008). In cases where vessels actively
approach marine mammals (e.g., whale
watching or dolphin watching boats),
scientists have documented that animals
exhibit altered behavior such as
increased swimming speed, erratic
movement, and active avoidance
behavior (Bursk, 1983; Acevedo, 1991;
Baker and MacGibbon, 1991; Trites and
Bain, 2000; Williams et al., 2002;
Constantine et al., 2003), reduced blow
interval (Ritcher et al., 2003), disruption
of normal social behaviors (Lusseau,
2003; 2006), and the shift of behavioral
activities which may increase energetic
costs (Constantine et al., 2003; 2004)). A
detailed review of marine mammal
reactions to ships and boats is available
in Richardson et al. (1995). For each of
the marine mammals taxonomy groups,
Richardson et al. (1995) provided the
following assessment regarding cetacean
reactions to vessel traffic:
Toothed whales: ‘‘In summary,
toothed whales sometimes show no
avoidance reaction to vessels, or even
approach them. However, avoidance can
occur, especially in response to vessels
of types used to chase or hunt the
animals. This may cause temporary
displacement, but we know of no clear
evidence that toothed whales have
abandoned significant parts of their
range because of vessel traffic.’’
Baleen whales: ‘‘When baleen whales
receive low-level sounds from distant or
stationary vessels, the sounds often
seem to be ignored. Some whales
approach the sources of these sounds.
When vessels approach whales slowly
and nonaggressively, whales often
exhibit slow and inconspicuous
avoidance maneuvers. In response to
strong or rapidly changing vessel noise,
baleen whales often interrupt their
normal behavior and swim rapidly
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away. Avoidance is especially strong
when a boat heads directly toward the
whale.’’
It is important to recognize that
behavioral responses to stimuli are
complex and influenced to varying
degrees by a number of factors such as
species, behavioral contexts,
geographical regions, source
characteristics (moving or stationary,
speed, direction, etc.), prior experience
of the animal, and physical status of the
animal. For example, studies have
shown that beluga whales reacted
differently when exposed to vessel noise
¨
and traffic. In some cases, naıve beluga
whales exhibited rapid swimming from
ice-breaking vessels up to 80 km away,
and showed changes in surfacing,
breathing, diving, and group
composition in the Canadian high
Arctic where vessel traffic is rare (Finley
et al., 1990). In other cases, beluga
whales were more tolerant of vessels,
but differentially responsive by
reducing their calling rates, to certain
vessels and operating characteristics
(especially older animals) in the St.
Lawrence River where vessel traffic is
common (Blane and Jaakson, 1994). In
Bristol Bay, Alaska, beluga whales
continued to feed when surrounded by
fishing vessels and resisted dispersal
even when purposefully harassed (Fish
and Vania, 1971).
In reviewing more than 25 years of
whale observation data, Watkins (1986)
concluded that whale reactions to vessel
traffic were ‘‘modified by their previous
experience and current activity:
habituation often occurred rapidly,
attention to other stimuli or
preoccupation with other activities
sometimes overcame their interest or
wariness of stimuli.’’ Watkins noticed
that over the years of exposure to ships
in the Cape Cod area, minke whales
(Balaenoptera acutorostrata) changed
from frequent positive (such as
approaching vessels) interest to
generally uninterested reactions; finback
whales (B. physalus) changed from
mostly negative (such as avoidance) to
uninterested reactions; right whales
(Eubalaena glacialis) apparently
continued the same variety of responses
(negative, uninterested, and positive
responses) with little change; and
humpbacks (Megaptera novaeangliae)
dramatically changed from mixed
responses that were often negative to
often strongly positive reactions.
Watkins (1986) summarized that
‘‘whales near shore, even in regions
with low vessel traffic, generally have
become less wary of boats and their
noises, and they have appeared to be
less easily disturbed than previously. In
particular locations with intense
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shipping and repeated approaches by
boats (such as the whale-watching areas
of Stellwagen Bank), more and more
whales had P [positive] reactions to
familiar vessels, and they also
occasionally approached other boats
and yachts in the same ways.’’
In the case of the VACAPES Range
Complex, naval vessel traffic is expected
to be much lower than in areas where
there are large shipping lanes and large
numbers of fishing vessels and/or
recreational vessels. Nevertheless, the
proposed action area is well traveled by
a variety of commercial and recreational
vessels, so marine mammals in the area
are expected to be habituated to vessel
noise.
As described in the proposed rule,
operations involving vessel movements
occur intermittently and are variable in
duration, ranging from a few hours up
to 2 weeks. These operations are widely
dispersed throughout the VACAPES
Range Complex OPAREA, which is a
vast area encompassing 27,661 square
nautical miles (nm2) (an area
approximately the size of Indiana). The
Navy logs about 1,400 total vessel days
within the Study Area during a typical
year. Consequently, the density of ships
within the Study Area at any given time
is extremely low (i.e., less than 0.0004
ships/nm2).
Moreover, naval vessels transiting the
study area or engaging in the training
exercises will not actively or
intentionally approach a marine
mammal or change speed drastically.
Except under certain mitigation
measures that protect right whales and
other marine mammals from vessel
strike, all vessels transit to, from, and
within the range complexes will be
traveling at speeds generally ranging
from 10 to 14 knots.
The final rule contains additional
mitigation measures requiring Navy
vessels to keep at least 500 yards (460
m) away from any observed whale and
at least 200 yards (183 m) from marine
mammals other than whales, and avoid
approaching animals head-on. Although
the radiated sound from the vessels will
be audible to marine mammals over a
large distance, it is unlikely that animals
will respond behaviorally to low-level
distant shipping noise as the animals in
the area are likely to be habituated to
such noises (Nowacek et al., 2004). In
light of these facts, NMFS does not
expect the Navy’s vessel movements to
result in Level B harassment.
Mitigation
In order to issue an incidental take
authorization (ITA) under Section
101(a)(5)(A) of the MMPA, NMFS must
prescribe regulations setting forth the
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‘‘permissible methods of taking
pursuant to such activity, and other
means of effecting the least practicable
adverse impact on such species or stock
and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance.’’ The
NDAA amended the MMPA as it relates
to military readiness activities and the
incidental take authorization process
such that ‘‘least practicable adverse
impact’’ shall include consideration of
personnel safety, practicality of
implementation, and impact on the
effectiveness of the ‘‘military readiness
activity.’’ The VACAPES Range
Complex training activities described in
the proposed rule are considered
military readiness activities.
NMFS reviewed the Navy’s proposed
VACAPES Range Complex training
activities and the proposed VACAPES
Range Complex mitigation measures
presented in the Navy’s application to
determine whether the activities and
mitigation measures were capable of
achieving the least practicable adverse
effect on marine mammals.
Any mitigation measure prescribed by
NMFS should be known to accomplish,
have a reasonable likelihood of
accomplishing (based on current
science), or contribute to the
accomplishment of one or more of the
general goals listed below:
(1) Avoidance or minimization of
injury or death of marine mammals
wherever possible (goals b, c, and d 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 underwater
detonations or other activities expected
to result in the take of marine mammals
(this goal may contribute to a, above, or
to reducing harassment takes only).
(3) A reduction in the number of
times (total number or number at
biologically important time or location)
individuals would be exposed to
underwater detonations or other
activities expected to result in the take
of marine mammals (this goal may
contribute to a, above, or to reducing
harassment takes only).
(4) A reduction in the intensity of
exposures (either total number or
number at biologically important time
or location) to underwater detonations
or other activities expected to result in
the take of marine mammals (this goal
may contribute to a, above, or to
reducing the severity of harassment
takes only).
(5) A reduction in adverse effects to
marine mammal habitat, paying special
attention to the food base, activities that
block or limit passage to or from
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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 (shut-down zone, etc.).
NMFS reviewed the Navy’s proposed
mitigation measures, which included a
careful balancing of the likely benefit of
any particular measure to the marine
mammals with the likely effect of that
measure on personnel safety,
practicality of implementation, and
impact on the ‘‘military-readiness
activity.’’
The Navy’s proposed mitigation
measures were described in detail in the
proposed rule (73 FR 75631, pages
75646–75649). The Navy’s measures
address personnel training, lookout and
watchstander responsibilities, operating
procedures for training activities using
underwater detonations of explosives
and firing exercises, and mitigation
related to vessel traffic and the North
Atlantic right whale. No changes have
been made to the mitigation measures
described in the proposed rule except as
noted below.
Regarding nighttime monitoring in the
Personnel Training Lookouts section (73
FR 25631, page 25647), slight wording
changes have been made for Bullet 6 to
read: ‘‘At night, to increase
effectiveness, lookouts would not
continuously sweep the horizon with
their eyes. Instead, lookouts would scan
the horizon in a series of movements
that would allow their eyes to come to
periodic rests as they scan the sector.
When visually searching at night, they
would look a little to one side and out
of the corners of their eyes, paying
attention to the things on the outer
edges of their field of vision. Lookouts
will also have night vision devices
available for use.’’
For mitigation measures under FIREX
(73 FR 25631, page 25648), corrections
were made to reduce the buffer zone
from 640 yards (585 m) to 600 yards
(548 m). Therefore, Bullets 3 and 4 of
the FIREX mitigation measure read as:
3. ‘‘Big Eyes’’ on the ship will be used to
monitor a 600 yd (548 m) buffer zone around
the target area for marine mammals during
naval-gunfire events. Due to the distance
between the firing position and the buffer
zone, lookouts are only expected to visually
detect breaching whales, whale blows, and
large pods of dolphins and porpoises.
4. Ships will not fire on the target if marine
mammals are detected within or approaching
the 600 yd (548 m) buffer zone. If marine
mammals are present, operations would be
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suspended. Visual observation will occur for
approximately 45 minutes, or until the
animal has been observed to have cleared the
area and is heading away from the buffer
zone.
For mitigation measures under
MINEX (73 FR 25631, page 25649),
corrections were made to increase the
buffer zone from 656 yards (600 m) to
700 yards (640 m). Therefore, Bullet 2
of the MINEX mitigation measure reads
as:
2. Observers will survey the Zone of
Influence (ZOI), a 700 yd (640 m) radius from
detonation location, for marine mammals
from all participating vessels during the
entire operation. A survey of the ZOI
(minimum of 3 parallel tracklines 219 yd
[200 m] apart) using support craft will be
conducted at the detonation location 30
minutes prior through 30 minutes post
detonation. Aerial survey support will be
utilized whenever assets are available.
The buffer zones for FIREX and
MINEX activities were incorrectly
noticed in the proposed rule for the
VACAPES Range Complex. NMFS has
consulted with the Navy and the Navy
has stated that the buffer zones should
be corrected to ensure consistency for
all Navy FIREX and MINEX activities
across multiple range complexes. The
buffer zones identified in this final rule
are consistent with those established in
the Southern California Range Complex
final rule (74 FR 2882; January 21,
2009). NMFS does not believe that a
decrease in the FIREX buffer zone of 40
yards would affect, in any significant
way, the Navy’s ability to detect marine
mammals or provide adequate
protection to marine mammals that may
be in the vicinity of a FIREX activity.
Moreover, an increase in the MINEX
buffer zone will further minimize any
adverse effects that marine mammals
could experience as a result of the
MINEX activity.
In response to a comment from the
Marine Mammal Commission, NMFS
will require the Navy to suspend its
activities immediately if a marine
mammal is injured or killed as a result
of the proposed Navy training activities
(e.g., instances in which it is clear that
munitions explosions caused the injury
or death), the Navy shall suspend its
activities immediately and report such
incident to NMFS.
In addition, regarding the North
Atlantic right whale (NARW) vessel
collision measures, NMFS expanded the
final rule to include vessel collision
avoidance measures for the South
Atlantic and the Northeast Atlantic to be
consistent with the U.S. Navy’s Atlantic
Fleet Active Sonar Training (AFAST)
rule. Although the VACAPES Range
Complex is outside the South Atlantic
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and the Northeast Atlantic region, the
Navy is required to comply with the
same ship collision measures while
transiting and conducting exercises
within specific NARW areas along the
East Coast. The specific vessel collision
measures in the Northeast Atlantic
region are listed in the regulatory text of
the final rule.
NMFS has determined that these
mitigation measures (which include a
suite of measures that specifically
address vessel transit and the NARW)
are adequate means of effecting the least
practicable adverse impacts on marine
mammal species or stocks and their
habitat while also considering personnel
safety, practicality of implementation,
and impact on the effectiveness of the
military readiness activity.
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Monitoring
In order to issue an ITA for an
activity, Section 101(a)(5)(A) of the
MMPA states that NMFS must set forth
‘‘requirements pertaining to the
monitoring and reporting of such
taking.’’ The MMPA implementing
regulations at 50 CFR 216.104 (a)(13)
indicate that requests for LOAs must
include the suggested means of
accomplishing the necessary monitoring
and reporting that will result in
increased knowledge of the species and
of the level of taking or impacts on
populations of marine mammals that are
expected to be present.
Monitoring measures prescribed by
NMFS should accomplish one or more
of the following general goals:
(1) An increase in the probability of
detecting marine mammals, both within
the safety zone (thus allowing for more
effective implementation of the
mitigation) and in general to generate
more data to contribute to the effects
analyses.
(2) An increase in our understanding
of how many marine mammals are
likely to be exposed to levels of
underwater detonations or other stimuli
that we associate with specific adverse
effects, such as behavioral harassment,
temporary threshold shift of hearing
sensitivity (TTS), or permanent
threshold shift of hearing sensitivity
(PTS).
(3) An increase in our understanding
of how marine mammals respond
(behaviorally or physiologically) to
underwater detonations or other stimuli
expected to result in take and how
anticipated adverse effects on
individuals (in different ways and to
varying degrees) may impact the
population, species, or stock
(specifically through effects on annual
rates of recruitment or survival).
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(4) An increased knowledge of the
affected species.
(5) An increase in our understanding
of the effectiveness of certain mitigation
and monitoring measures.
(6) A better understanding and record
of the manner in which the authorized
entity complies with the incidental take
authorization.
Proposed Monitoring Plan for the
VACAPES Range Complex Study Area
As NMFS indicated in the proposed
rule, the Navy has (with input from
NMFS) fleshed out the details of and
made improvements to the VACAPES
Range Complex Monitoring Plan.
Additionally, NMFS and the Navy have
incorporated a suggestion from the
public, which recommended the Navy
hold a peer review workshop to discuss
the Navy’s Monitoring Plans for the
multiple range complexes and training
exercises in which the Navy would
receive ITAs (see Monitoring Workshop
section). The final VACAPES Range
Complex Monitoring Plan, which is
summarized below, may be viewed at
https://www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications. The Navy
plans to implement all of the
components of the Monitoring Plan;
however, only the marine mammal
components (not the sea turtle
components) will be required by the
MMPA regulations and associated
LOAs.
A summary of the monitoring
methods required for use during
training events in the VACAPES Range
Complex are described below. These
methods include a combination of
individual elements that are designed to
allow a comprehensive assessment.
I. Vessel or Aerial Surveys
(A) The Holder of this Authorization
shall visually survey a minimum of 2
explosive events per year, one of which
shall be a multiple detonation event.
One of the vessel or aerial surveys
should involve professionally trained
marine mammal observers (MMOs).
(B) If operationally feasible, for
specified training events, aerial or vessel
surveys shall be used 1–2 days prior to,
during (if reasonably safe), and 1–5 days
post detonation.
(C) Surveys shall include any
specified exclusion zone around a
particular detonation point plus 2,000
yards beyond the border of the
exclusion zone (i.e., the circumference
of the area from the border of the
exclusion zone extending 2,000 yards
outwards). For vessel based surveys a
passive acoustic system (hydrophone or
towed array) could be used to determine
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28333
if marine mammals are in the area
before and/or after a detonation event.
(D) When conducting a particular
survey, the survey team shall collect:
• Location of sighting;
• Species (if not possible, indicate
whale, dolphin or pinniped);
• Number of individuals;
• Whether calves were observed;
• Initial detection sensor;
• Length of time observers
maintained visual contact with marine
mammal;
• Wave height;
• Visibility;
• Whether sighting was before,
during, or after detonations/exercise,
and how many minutes before or after;
• Distance of marine mammal from
actual detonations (or target spot if not
yet detonated);
• Observed behavior—Watchstanders
will report, in plain language and
without trying to categorize in any way,
the observed behavior of the animal(s)
(such as animal closing to bow ride,
paralleling course/speed, floating on
surface and not swimming etc.),
including speed and direction;
• Resulting mitigation
implementation—Indicate whether
explosive detonations were delayed,
ceased, modified, or not modified due to
marine mammal presence and for how
long; and
• If observation occurs while
explosives are detonating in the water,
indicate munition type in use at time of
marine mammal detection (e.g., were
the 5-inch guns actually firing when the
animals were sighted? Did animals enter
an area 2 minutes after a huge explosion
went off?).
II. Passive Acoustic Monitoring
The Navy is required to conduct
passive acoustic monitoring when
operationally feasible.
(A) Any time a towed hydrophone
array is employed during shipboard
surveys the towed array shall be
deployed during daylight hours for each
of the days the ship is at sea.
(B) The towed hydrophone array shall
be used to supplement the ship-based
systematic line-transect surveys
(particularly for species such as beaked
whales that are rarely seen).
III. Marine Mammal Observers on Navy
Platforms
(A) Marine mammal observers
(MMOs) selected for aerial or vessel
survey shall be placed on a Navy
platform during one of the exercises
being monitored per year. The
remaining designated exercise(s) shall
be monitored by the Navy lookouts/
watchstanders.
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(B) The MMO must possess expertise
in species identification of regional
marine mammal species and experience
collecting behavioral data.
(C) MMOs shall not be placed aboard
Navy platforms for every Navy training
event or major exercise, but during
specifically identified opportunities
deemed appropriate for data collection
efforts. The events selected for MMO
participation shall take into account
safety, logistics, and operational
concerns.
(D) MMOs shall observe from the
same height above water as the
lookouts.
(E) The MMOs shall not be part of the
Navy’s formal reporting chain of
command during their data collection
efforts; Navy lookouts shall continue to
serve as the primary reporting means
within the Navy chain of command for
marine mammal sightings. The only
exception is that if an animal is
observed within the shutdown zone that
has not been observed by the lookout,
the MMO shall inform the lookout of the
sighting, and the lookout shall take the
appropriate action through the chain of
command.
(F) The MMOs shall collect species
identification, behavior, direction of
travel relative to the Navy platform, and
distance first observed. All MMO
sightings shall be conducted according
to a standard operating procedure.
Information collected by MMOs should
be the same as those collected by Navy
lookout/watchstanders described above.
The Monitoring Plan for VACAPES
Range Complex has been designed as a
collection of focused ‘‘studies’’
(described fully in the VACAPES
Monitoring Plan) to gather data that will
allow the Navy to address the following
questions:
(a) What are the behavioral responses
of marine mammals and sea turtles that
are exposed to explosives?
(b) Is the Navy’s suite of mitigation
measures effective at avoiding injury
and mortality of marine mammals and
sea turtles?
Data gathered in these studies will be
collected by qualified, professional
marine mammal biologists or trained
Navy lookouts/watchstanders that are
experts in their field. This monitoring
plan has been designed to gather data on
all species of marine mammals that are
observed in the VACAPES Range
Complex study area.
Monitoring Workshop
During the public comment period on
past proposed rules for Navy actions
(such as the Hawaii Range Complex
(HRC), and Southern California Range
Complex (SOCAL) proposed rules),
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NMFS received a recommendation that
a workshop or panel be convened to
solicit input on the monitoring plan
from researchers, experts, and other
interested parties. The VACAPES Range
Complex proposed rule included an
adaptive management component and
both NMFS and the Navy believe that a
workshop would provide a means for
Navy and NMFS to consider input from
participants in determining whether
(and if so, how) to modify monitoring
techniques to more effectively
accomplish the goals of monitoring set
forth earlier in the document. NMFS
and the Navy believe that this workshop
concept is valuable in relation to all of
the Range Complexes and major training
exercise rules and LOAs that NMFS is
working on with the Navy at this time,
and consequently this single Monitoring
Workshop will be included as a
component of all of the rules and LOAs
that NMFS will be processing for the
Navy in the next year or so.
The Navy, with guidance and support
from NMFS, will convene a Monitoring
Workshop, including marine mammal
and acoustic experts as well as other
interested parties, in 2011. The
Monitoring Workshop participants will
review the monitoring results from the
previous two years of monitoring
pursuant to the VACAPES Range
Complex rule as well as monitoring
results from other Navy rules and LOAs
(e.g., AFAST, SOCAL, HRC, and other
rules). The Monitoring Workshop
participants would provide their
individual recommendations to the
Navy and NMFS on the monitoring
plan(s) after also considering the current
science (including Navy research and
development) and working within the
framework of available resources and
feasibility of implementation. NMFS
and the Navy would then analyze the
input from the Monitoring Workshop
participants and determine the best way
forward from a national perspective.
Subsequent to the Monitoring
Workshop, modifications would be
applied to monitoring plans as
appropriate.
Integrated Comprehensive Monitoring
Program
In addition to the site-specific
Monitoring Plan for the VACAPES
Range Complex, the Navy will complete
the Integrated Comprehensive
Monitoring Program (ICMP) Plan by the
end of 2009. The ICMP is currently in
development by the Navy, with Chief of
Naval Operations Environmental
Readiness Division (CNO–N45) having
the lead. The program does not
duplicate the monitoring plans for
individual areas (e.g. AFAST, HRC,
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SOCAL); instead it is intended to
provide the overarching coordination
that will support compilation of data
from both range-specific monitoring
plans as well as Navy funded research
and development (R&D) studies. The
ICMP will coordinate the monitoring
program’s progress towards meeting its
goals and developing a data
management plan. A program review
board is also being considered to
provide additional guidance. The ICMP
will be evaluated annually to provide a
matrix for progress and goals for the
following year, and will make
recommendations on adaptive
management for refinement and analysis
of the monitoring methods.
The primary objectives of the ICMP
are to:
• Monitor and assess the effects of
Navy activities on protected species;
• Ensure that data collected at
multiple locations is collected in a
manner that allows comparison between
and among different geographic
locations;
• Assess the efficacy and practicality
of the monitoring and mitigation
techniques;
• Add to the overall knowledge-base
of marine species and the effects of
Navy activities on marine species.
The ICMP will be used both as: (1) A
planning tool to focus Navy monitoring
priorities (pursuant to ESA/MMPA
requirements) across Navy Range
Complexes and Exercises; and (2) an
adaptive management tool, through the
consolidation and analysis of the Navy’s
monitoring and watchstander data, as
well as new information from other
Navy programs (e.g., R&D), and other
appropriate newly published
information.
In combination with the 2011
Monitoring Workshop and the adaptive
management component of the
VACAPES Range Complex rule and the
other planned Navy rules (e.g.
Jacksonville Range Complex, Cherry
Point Range Complex, etc.), the ICMP
could potentially provide a framework
for restructuring the monitoring plans
and allocating monitoring effort based
on the value of particular specific
monitoring proposals (in terms of the
degree to which results would likely
contribute to stated monitoring goals, as
well as the likely technical success of
the monitoring based on a review of past
monitoring results) that have been
developed through the ICMP
framework, instead of allocating based
on maintaining an equal (or
commensurate to effects) distribution of
monitoring effort across range
complexes. For example, if careful
prioritization and planning through the
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ICMP (which would include a review of
both past monitoring results and current
scientific developments) were to show
that a large, intense monitoring effort in
Hawaii would likely provide extensive,
robust and much-needed data that could
be used to understand the effects of
sonar throughout different geographical
areas, it may be appropriate to have
other range complexes dedicate money,
resources, or staff to the specific
monitoring proposal identified as ‘‘high
priority’’ by the Navy and NMFS, in lieu
of focusing on smaller, lower priority
projects divided throughout their home
range complexes.
The ICMP will identify:
• A means by which NMFS and the
Navy would jointly consider prior years’
monitoring results and advancing
science to determine if modifications
are needed in mitigation or monitoring
measures to better effect the goals laid
out in the Mitigation and Monitoring
sections of the VACAPES Range
Complex rule.
• Guidelines for prioritizing
monitoring projects
• If, as a result of the workshop and
similar to the example described in the
paragraph above, the Navy and NMFS
decide it is appropriate to restructure
the monitoring plans for multiple ranges
such that they are no longer evenly
allocated (by rule), but rather focused on
priority monitoring projects that are not
necessarily tied to the geographic area
addressed in the rule, the ICMP will be
modified to include a very clear and
unclassified record-keeping system that
will allow NMFS and the public to see
how each range complex/project is
contributing to all of the ongoing
monitoring programs (resources, effort,
money, etc.).
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Adaptive Management
The final regulations governing the
take of marine mammals incidental to
Navy’s VACAPES Range Complex
exercises contain an adaptive
management component. The use of
adaptive management will give NMFS
the ability to consider new data from
different sources to determine (in
coordination with the Navy) on an
annual basis if mitigation or monitoring
measures should be modified or added
(or deleted) if new data suggests that
such modifications are appropriate (or
are not appropriate) for subsequent
annual LOAs.
The following are some of the
possible sources of applicable data:
• Results from the Navy’s monitoring
from the previous year (either from
VACAPES Range Complex or other
locations)
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• Findings of the Workshop that the
Navy will convene in 2011 to analyze
monitoring results to date, review
current science, and recommend
modifications, as appropriate to the
monitoring protocols to increase
monitoring effectiveness.
• Compiled results of Navy funded
research and development (R&D) studies
(presented pursuant to the ICMP, which
is discussed elsewhere in this
document)
• Results from specific stranding
investigations (either from VACAPES
Range Complex or other locations)
• Results from general marine
mammal and sound research (funded by
the Navy or otherwise)
• Any information which reveals that
marine mammals may have been taken
in a manner, extent or number not
authorized by these regulations or
subsequent Letters of Authorization
Mitigation measures could be
modified or added (or deleted) if new
data suggests that such modifications
would have (or do not have) a
reasonable likelihood of accomplishing
the goals of mitigation laid out in this
final rule and if the measures are
practicable. NMFS would also
coordinate with the Navy to modify or
add to (or delete) the existing
monitoring requirements if the new data
suggest that the addition of (or deletion
of) a particular measure would more
effectively accomplish the goals of
monitoring laid out in this final rule.
The reporting requirements associated
with this rule are designed to provide
NMFS with monitoring data from the
previous year to allow NMFS to
consider the data and issue annual
LOAs. NMFS and the Navy will meet
annually, prior to LOA issuance, to
discuss the monitoring reports, Navy
R&D developments, and current science
and whether mitigation or monitoring
modifications are appropriate.
Reporting
In order to issue an ITA for an
activity, Section 101(a)(5)(A) of the
MMPA states that NMFS must set forth
‘‘requirements pertaining to the
monitoring and reporting of such
taking’’. Effective reporting is critical to
ensure compliance with the terms and
conditions of a LOA, and to provide
NMFS and the Navy with data of the
highest quality based on the required
monitoring. As NMFS noted in its
proposed rule, additional detail has
been added to the reporting
requirements since they were outlined
in the proposed rule. The updated
reporting requirements are all included
below. A subset of the information
provided in the monitoring reports may
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28335
be classified and not releasable to the
public.
NMFS will work with the Navy to
develop tables that allow for efficient
submission of the information required
below.
General Notification of Injured or Dead
Marine Mammals
Navy personnel will ensure that
NMFS (regional stranding coordinator)
is notified immediately (or as soon as
operational security allows) if an
injured or dead marine mammal is
found during or shortly after, and in the
vicinity of, any Navy training exercise
utilizing underwater explosive
detonations or other activities. The
Navy will provide NMFS with species
or description of the animal(s), the
condition of the animal(s) (including
carcass condition if the animal is dead),
location, time of first discovery,
observed behaviors (if alive), and photo
or video (if available).
Annual VACAPES Range Complex
Monitoring Plan Report
The Navy shall submit a report
annually on March 1 describing the
implementation and results (through
January 1 of the same year) of the
VACAPES Range Complex Monitoring
Plan, described above. Data collection
methods will be standardized across
range complexes to allow for
comparison in different geographic
locations. Although additional
information will also be gathered, the
marine mammal observers (MMOs)
collecting marine mammal data
pursuant to the VACAPES Range
Complex Monitoring Plan shall, at a
minimum, provide the same marine
mammal observation data required in
the major range complex training
exercises section of the Annual
VACAPES Range Complex Exercise
Report referenced below.
The VACAPES Range Complex
Monitoring Plan Report may be
provided to NMFS within a larger report
that includes the required Monitoring
Plan Reports from multiple Range
Complexes.
Annual VACAPES Range Complex
Exercise Report
The Navy is in the process of
improving the methods used to track
explosives used to provide increased
granularity. The Navy will provide the
information described below for all of
their explosive exercises. Until the Navy
is able to report in full the information
below, they will provide an annual
update on the Navy’s explosive tracking
methods, including improvements from
the previous year.
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(i) Total annual number of each type
of explosive exercise (of those identified
as part of the ‘‘specified activity’’ in this
final rule) conducted in the VACAPES
Range Complex.
(ii) Total annual expended/detonated
rounds (missiles, bombs, etc.) for each
explosive type.
VACAPES Range Complex 5-yr
Comprehensive Report
The Navy shall submit to NMFS a
draft report that analyzes and
summarizes all of the multi-year marine
mammal information gathered during
the VACAPES Range Complex exercises
for which annual reports are required
(Annual VACAPES Range Complex
Exercise Reports and VACAPES Range
Complex Monitoring Plan Reports). This
report will be submitted at the end of
the fourth year of the rule (May 2013),
covering activities that have occurred
through December 1, 2012.
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Comments and Responses
On December 12, 2008, NMFS
published a proposed rule (73 FR
75631) in response to the Navy’s request
to take marine mammals incidental to
military readiness training in the
VACAPES Range Complex study area
and requested comments, information
and suggestions concerning the request.
During the 30-day public comment
period, NMFS received comments from
1 private citizen, comments from the
Marine Mammal Commission
(Commission), comments from the
Commonwealth of Virginia Department
of Environmental Quality (Virginia
DEQ, including the Department of Game
and Inland Fisheries (VDGIF) and the
Department of Conservation and
Recreation), comments from the
International Fund for Animal Welfare,
and comments from the Natural
Resources Defense Council (on behalf of
itself, The Humane Society of the
United States, Whale and Dolphin
Conservation Society, Cetacean Society
International, Ocean Futures Society,
Jean-Michel Cousteau). The comments
are summarized and sorted into general
topic areas and are addressed below.
Full copies of the comment letters may
be accessed at https://
www.regulations.gov.
MMPA Concerns
Comment 1: The Commission and
IFAW point out that there are
differences between the Navy’s and
NMFS’ estimates of maximum annual
takes for the proposed exercises in the
VACAPES range complex and that these
differences should be reconciled.
Response: NMFS does not believe
there are differences between the Navy’s
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and NMFS’ estimates of maximum
annual takes for the VACAPES Range
Complex training exercises. The
perceived differences the Commission
raised may be the differences between
the Navy’s initial LOA application and
its subsequent addendum. The Navy
states that further analyses on the
impacts from the proposed action and
the reduction of BOMBEX exercises are
the reason for the change of take
estimates. Specifically, the Navy states
that ‘‘HARM missile explodes no less
than 30 ft above the water, it is assumed
the amount of acoustic energy entering
the water would be negligible, so
exposures from that weapon should be
removed from the MISSILEX totals.
Secondly, the size of the BOMBEX
location was reduced to avoid important
fishing areas, the North Atlantic Right
Whale migratory corridor, and the
Norfolk Canyon area which lowered
potential exposures for certain species.’’
The amendment is posted on NMFS
incident take Web site at https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm.
Comment 2: The Commission
recommends that NMFS include in its
authorization the number of lethal takes
and takes by Level A harassment
requested by the Navy and regularly
confer with the Navy to monitor the
actual number of such takes to ensure
that they do not exceed the authorized
number.
Response: NMFS agrees with the
Commission. NMFS has, through this
final rule, included the authorized
numbers of marine mammal takes and
the manner of take (i.e., lethal, Level A
or Level B). In addition, monitoring and
reporting measures are prescribed to
ensure that all takes as a result of the
training activities are accounted for and
documented. The MMOs and Navy’s
lookouts/watchstanders will report any
sightings of marine mammals in the take
zone through the chain of command.
Furthermore, the Navy is required to
submit an Annual VACAPES Range
Complex Monitoring Plan Report. Prior
to issuing any subsequent LOAs, NMFS
will review the Navy’s monitoring
efforts and data from the previous year
to determine whether any new measures
will be necessary or a modification to
prior year’s measures.
Comment 3: The Virginia DEQ
recommends that NMFS develop the
regulations to reflect harbor seal, harp
seal, and gray seal as their occurrence in
the inshore and nearshore waters of the
mid-Atlantic region are becoming more
frequent in the fall and winter months.
Response: Based on the analyses by
the Navy and NMFS, there are 34
marine mammal species with possible
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or confirmed occurrence in the
VACAPES Range Complex. As indicated
in the proposed rule, there are 33
cetacean species and one pinniped
species (harbor seal). Harp and gray
seals occur primarily in the North
Atlantic, with the former species found
mostly in the Arctic region. Although
there have been increased anecdotal
sightings of these species in the midAtlantic coastal waters, their presence
in the mid-Atlantic region is still very
rare (Waring et al., 2008).
Comment 4: The VDGIF states that the
species take list appears to be accurate;
however, the number of animals
predicted to be affected for both Level
A and Level B harassment are probably
underestimated, because the species
density data from which take estimates
are derived are based on too few data.
Therefore, no marine mammal species
should be considered unlikely to be
affected just because there are no
density data available (e.g., beaked
whales). Since all of the species on the
list exist in the Virginia and North
Carolina Outer Banks stranding records,
collected and kept by the Virginia
Aquarium Stranding Response Program,
the VDGIF recommends that all species
on the take list should be considered
susceptible to Level B harassment year
round. The IFAW states that if one of
these animals not included in the
incidental take list is present in the area
of testing, there is a higher probability
that the animal will be struck, and that
the assumption that one third of the
cetacean species in the area will not be
exposed nor affected by noise represents
an oversight in the analysis of potential
takes.
Response: NMFS does not agree with
the VDGIF and IFAW’s assessment. The
most current stock assessment reports
(Waring et al., 2008) were used to
calculate density estimates. As
summarized in the proposed rule and
described more fully in the Navy’s FEIS,
the Navy used the best data and
methods available to calculate density,
including other literature as well as
habitat modeling that considered
bathymetry, distance from shelf break,
sea surface temperature, and
Chlorophyll a concentration. All spatial
models and density estimates were
reviewed by NMFS technical staff. The
Navy’s model utilizes uniform density,
but it also divides the east coast into
meaningful sections, such as on-shelf
and off-shelf and the different
OPAREAS.
Although stranding records indicate
that certain species may be found dead
or injured in the Virginia area, this does
not mean that these species are
normally distributed in this area.
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Rather, certain stranded species are
likely more common in other geographic
regions and due to their death or injury
in those areas, they may drift and wash
ashore in the Virginia area.
NMFS does not agree that all species
identified in a stranding list would be
affected by the proposed activity. As
noted above, NMFS relied on the best
available data to ascertain density
estimates. There are certain species for
which estimates are unavailable because
their presence in the VACAPES Range
Complex Study Area is rare (e.g.,
Bryde’s whale and false killer whale are
not reported in NMFS stock assessment
reports (SARs) for the U.S. Atlantic and
Gulf of Mexico regions for the stock
assessment). NMFS considers it unlikely
that species whose presence in the
action area is rare would be affected by
the proposed activities.
For species in which NMFS possesses
density data, the Navy conducted
modeling to calculate the potential takes
of these marine mammals. As described
in the proposed rule, estimating the take
that could result from the proposed
activities entails the following four
steps: propagation model estimates
animals exposed to sources at different
levels; further modeling determines the
number of exposures to levels indicated
in the criteria above (i.e., number of
takes); post-modeling corrections refine
estimates to make them more accurate;
mitigation is taken into consideration.
Detailed analyses regarding the models
used, the assumptions used in the
models, and the process of estimating
take is available in Appendix J of the
Navy’s EIS for the VACAPES Range
Complex. The Navy’s model revealed
that species such as blue whale, sei
whale, spinner dolphin, Fraser’s
dolphin, Atlantic white-sided dolphin,
harbor porpoise, and harbor seals would
not be taken by the proposed activities
because their presence in the VACAPES
Range Complex Study Area is rare.
Acoustic Impacts
Comment 5: The IFAW states that the
Navy failed to cite any scientific data to
support the claim that ‘‘explosive
ordnance and underwater detonations
would result in only short-term effects
to most individuals exposed.’’ The
IFAW also states that FIREX and
BOMBEX yield a novel situation for
impact analysis since they employ
multiple explosions, and that there is no
existing data on the impacts of multiple
explosions and therefore potential
impacts had to be extrapolated from
single explosion testing. The IFAW
further states that although a detailed
modeling system was developed, the
cumulative effect of multiple explosions
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may far exceed the sum of its parts.
Further research is needed before claims
can be made as to the impacts of
multiple explosions on marine
mammals.
Response: NMFS does not agree with
the IFAW’s assessment. Although few
scientific data are currently available on
the behavioral effects of explosive
ordnance on marine mammals, studies
of marine mammal reactions to intense
underwater sounds (Finneran et al.,
2000; Schlundt et al., 2000; Finneran
and Schlundt, 2004), studies of
underwater detonations on human
divers and territorial mammals (Gaspin,
1983; Goertner, 1982), studies on the
auditory anatomy of marine mammals
(Ketten, 1998), and studies on source
characterization of underwater
explosions (Cole, 1948; Gaspin and
Shuler, 1971; Rogers, 1977; Urick, 1983)
were reviewed. Based on the
conclusions of these studies in terms of
the impact ranges and levels from
different explosives and their acoustic
impacts, NMFS and the Navy
determined the use of explosive
ordnance and underwater detonations
in the Navy’s VACAPES Range Complex
(including implementation of mitigation
and monitoring measures), would result
in only short-term effects to most
individuals exposed. These analyses,
including the impact analyses on
multiple explosions, were described in
detail in Appendix A ‘‘Draft Technical
Risk Assessment for the Use of
Underwater Explosives in the Virginia
Capes (VACAPES) Range Complex’’ in
the Navy’s LOA application and were
referenced in the proposed rule (73 FR
75631; December 12, 2008).
Mitigation
Comment 6: The Commission
recommends that NMFS include in the
final rule a requirement that, in all but
emergency situations or where the need
for realistic training requires greater
speed or maneuverability, the Navy
abide by the seasonal restrictions
applicable to other vessels under NMFS’
ship-speed regulations (50 CFR 224.105)
to reduce the risk of ship collisions with
right whales.
Response: NMFS does not agree with
the Commission recommendation.
NMFS’ final rule on ship speed
restriction does not apply to vessels
operated by U.S. Federal agencies.
NMFS, in consultation with other
Federal agencies, has determined that
the national security, navigational, and
human safety missions of some agencies
may be compromised by mandatory
vessel speed restrictions. However, this
exemption will not relieve the Navy of
its obligations to consult, under section
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7 of the ESA, on how their activities
may affect listed species. NMFS
acknowledges that the Navy already
provides guidance to vessel operators
and fleets with regard to conservation
measures to protect right whales and
other endangered species, as well as
contribute to conservation efforts
generally.
For the proposed VACAPES Range
Complex training activities, the Navy
has developed a series of mitigation
measures that closely follow NMFS’
ship strike rule. These mitigation
measures are described in the Proposed
Mitigation Measures section of the
proposed rule (73 FR 76578; December
17, 2008). In addition, NMFS worked
with the Navy regarding their vessel
operations to determine where ESA
section 7 consultations would be
appropriate.
Comment 7: The Commission
recommends that if a serious injury or
death occurs and that injury or death
could have resulted from the authorized
Navy operations, NMFS and Navy
jointly investigate the circumstances
and steps needed to avoid similar
occurrences.
Response: NMFS concurs with the
Commission’s recommendation and will
work with the Navy to address such an
occurrence if and when it arises.
Comment 8: The Virginia DEQ and
IFAW state that they note that
mitigation measures for most training
exercises are largely comprised of
maintaining lookouts or watchstanders
to look for marine mammals, sea turtles,
rafts of sargassum grass and other
indicators of biological activity in the
buffer zones or zones of impact. As
such, most mitigation measures rely
entirely on the observers’ ability to
detect sea turtles, marine mammals, and
indicators of their presence such as
sargassum grass under all conditions
(e.g., high seas, after dark, storms, etc.).
The IFAW states that this mitigation
strategy is insufficient for detecting right
whales in the vicinity of Navy training
exercises.
Response: NMFS does not agree with
the Virginia DEQ and IFAW’s
assessment. Although visual monitoring
by lookouts or watchstanders is an
important component of monitoring
measures for the Navy’s VACAPES
Complex Range training exercises, it is
not the only mitigation measure for
most training exercises. Other
mitigation and monitoring measures are
also proposed to reduce any potential
impacts to marine mammals that would
result from the proposed training
activities. These include establishing
safety zones for all exercises involving
underwater detonations (FIREX,
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BOMBEX, MINEX, and MISSILEX),
aerial surveys of the action area,
limiting certain exercises (BOMBEX,
FIREX, and MINEX) to daylight hours,
etc. In addition, Navy lookouts or
watchstanders are specifically trained to
detect anomalies in the water around
the ship and both the safety of Navy
personnel and success in the training
exercise depend on the lookout being
able to detect objects (e.g., marine
mammals) effectively around the ship.
Additionally, NMFS has identified
ports located in the western Atlantic
Ocean, offshore of the southeastern
United States, where vessel transit
during right whale migration is of
highest concern for potential ship strike.
These ports include the Hampton Roads
entrance to the Chesapeake Bay, which
includes the concentration of Atlantic
Fleet vessels in Norfolk, Virginia. Navy
vessels are required to use extreme
caution and operate at a slow, safe
speed consistent with mission and
safety during the months of right whale
migration and within a 20 nm (37 km)
arc (except as noted) of the specified
reference points.
Comment 9: The VDGIF recommends
NMFS expand the ‘‘elevated time of
awareness’’ for right whales (Table 14 in
the proposed FR notice for the proposed
rule, 73 FR 75631; December 12, 2008)
to Oct–April (without excluding
January) or, at a minimum, Nov-March
(without excluding January) based on
strandings that have occurred in our
region throughout these months. The
VDGIF states that recent observations
have been made of new mothers as far
north as Wilmington, North Carolina
during the winter calving season (i.e.,
Nov. 15–April 15), which provides
further justification for expanding the
period of elevated awareness for
Virginia area and North Carolina.
Response: The ‘‘elevated time of
awareness’’ for right whales already
covers the months between October–
April in South Carolina and December–
April in North Carolina. Although
certain months were not covered in
areas north of North Carolina such as
the Chesapeake Bay, Delaware Bay, off
the coast of New York and New Jersey,
this is because right whales are
extremely rare in these waters during
those months. Regarding the recent
sighting (January 2009) of right whale
cows as far north as Wilmington, North
Carolina, this location and month are
covered under the current ‘‘elevated
time of awareness’’ for right whales.
Comment 10: The VDGIF states that
the proposed mitigation measures and
reporting requirement of the proposed
rule are acceptable. Therefore, the
VDGIF has no comments on them.
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Response: Comments noted.
Monitoring and Reporting
Comment 11: The Commission
recommends that NMFS work with the
Navy to design studies to collect and
analyze data necessary to characterize
the risk of collisions with right whales
by Navy vessels.
Response: Comment noted. The
reporting conditions for the Navy’s
training activities require the Navy to
report all marine mammal (right whale
included) sighting information during
exercises. This information includes the
location of sightings, species, number of
individuals, and calves observed, etc.
These data can later be analyzed to
characterize the risk of collisions with
marine mammals by Navy vessels. To
the extent resources exist, NMFS will
endeavor to work with the Navy to
develop more formal studies that would
allow each agency to obtain the
necessary data to characterize the risk of
Navy vessel collisions with right whales
and to take further steps to minimize the
probability of a vessel strike.
Comment 12: The Commission
recommends that NMFS work with the
Navy to sponsor a peer review of
existing risk analysis procedures and
the interpretation and use of survey or
other data in those analyses, and work
with the Navy to validate the
effectiveness of monitoring and
mitigation measures, preferably before
beginning or, if that is infeasible, in
conjunction with the Navy operations
subject to this incidental take
authorization.
Response: At this time, NMFS
concludes that the risk analyses for
naval activities and MMPA rulemakings
are appropriate. If necessary, NMFS and
the Navy will coordinate at some future
date to determine whether additional
consideration of the risk analysis
procedure is warranted. Regarding the
effectiveness of monitoring and
mitigation measures, this final rule
includes a requirement for the Navy to
convene a Monitoring Workshop in
2011 in which the participants will be
asked to review the Navy’s Monitoring
Plans and monitoring results and make
individual recommendations (to the
Navy and NMFS) of ways of improving
the Monitoring Plans. NMFS believes
that this type of workshop, with
participants including the Navy, NMFS,
researchers, invited experts, and other
interested parties, in combination with
an adaptive management plan that
allows for modification would provide a
means for the Navy to adjust the
Monitoring Plan as needed to more
effectively accomplish the goals of
monitoring set forth earlier. NMFS
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would incorporate any changes into
future LOAs and future rules as
necessary. NMFS has statutory
responsibility to prescribe regulations
pertaining to mitigation, monitoring,
and reporting, and will, in coordination
with the Navy, develop the most
effective and appropriate mitigation,
monitoring, and reporting protocols for
future authorizations.
In addition, NMFS has been working
with the Navy throughout the
rulemaking process to develop a series
of mitigation, monitoring, and reporting
protocols. NMFS believes that the
measures prescribed in this final rule
are practicable, effective and will afford
the necessary protection to marine
mammals.
NEPA
Comment 13: The Virginia DEQ
requests that the final Integrated
Comprehensive Monitoring Program
(ICMP) be included in the EIS if
possible.
Response: The ICMP will not be
completed until the summer of 2009,
therefore, it is not possible to include
the ICMP in the FEIS. However, the
Navy will include a comprehensive
monitoring plan and a summary of the
ICMP in the FEIS. In addition, the site
specific comprehensive monitoring plan
and a summary of the ICMP are
included in the Navy’s VACAPES Range
Complex final rule.
Miscellaneous Issues
Comment 14: The Virginia DEQ
requests that NMFS consider in the final
regulations that NMFS (1) coordinate
with the Virginia Department of Game
and Inland Fisheries and the U.S. Fish
and Wildlife Service for information
regarding the possible impacts to
protected species and to ensure
compliance with protected species
legislation, and (2) contact Rene Hypes
of the Virginia Department of
Conservation and Recreation Division of
Natural Heritage at (804) 371–2708 for
an update on natural heritage
information if a significant amount of
time passes before the proposed
activities are initiated since new and
updated information is continually
added to Biotics.
Response: NMFS published a
proposed rule for the VACAPES Range
Complex training exercises (73 FR
75631; December 12, 2008) that
included a detailed description of
protected marine mammal species
within the Range Complex. NMFS will
work with Virginia as necessary and
advise the State if there is any change
to the proposed action and updates on
natural resources information. With
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respect to other protected species such
as ESA listed turtles or fish, the Navy is
conducting a Section 7 consultation
with NMFS. The Navy has completed
consultation with Delaware, Maryland,
Virginia, and North Carolina under the
Coastal Zone Management Act. In
addition, NMFS is working to ensure
that the final rule for the proposed
action and the LOAs issued to the Navy
is in compliance with protected species
legislation through the ESA consultation
and the MMPA permitting review.
NMFS does not expect there will be
a significant amount of time that passes
between finalization of rule and the
commencement of naval exercises. To
the extent there is, NMFS will
coordinate, as appropriate, with the
State and FWS.
Comment 15: The NRDC commented
on the proposed rule with its earlier
comments on the NMFS’ proposed rule
for the Navy’s Atlantic Fleet Active
Sonar Training (AFAST) and the Navy’s
AFAST DEIS. Specifically, the NRDC
states that neither NMFS in its proposed
rule, nor the Navy in its EIS offers
sufficient measures to mitigate the
harmful impacts of high intensity sonar.
The NRDC further states that NMFS and
the Navy’s analysis substantially
understates the potential effects of sonar
on marine wildlife.
Response: NRDC’s comments are
inapplicable to the proposed Navy
training activities in the VACAPES
Range Complex. The Navy does not
intend, as part of its proposed action, to
conduct training with MFAS, HFAS,
and Improved Extended Echo Ranging
(IEER)/Advanced Extended Echo
Ranging (AEER). The Navy’s request for
a LOA for sonar related training was
addressed in the Final Rule and LOA for
AFAST which was issued by NMFS on
January 22, 2009, and published in the
Federal Register on February 19, 2009
(74 FR 4844).
Comment 16: One private citizen
expressed general opposition to Navy
activities and NMFS’ issuance of an
MMPA authorization because of the
danger of killing marine life.
Response: NMFS appreciates the
commenter’s concern for the marine
mammals that live in the area of the
proposed activities. However, the
MMPA allows individuals to take
marine mammals incidental to specified
activities if NMFS can make the
necessary findings required by law (i.e.,
negligible impact, unmitigable adverse
impact on subsistence users, etc.). As
explained throughout this rulemaking,
NMFS has made the necessary findings
under 16 U.S.C. 1371(a)(5)(A) to support
our issuance of the final rule.
Estimated Take of Marine Mammals
As mentioned previously, with
respect to the MMPA, NMFS’ effects
assessments serve four primary
purposes: (1) To prescribe the
permissible methods of taking (i.e.,
Level B Harassment (behavioral
harassment), Level A Harassment
(injury), or mortality, including an
identification of the number and types
of take that could occur by Level A or
B harassment or mortality)) and to
prescribe other means of effecting the
least practicable adverse impact on such
species or stock and its habitat (i.e.,
mitigation); (2) to determine whether
the specified activity will have a
negligible impact on the affected species
or stocks of marine mammals (based on
the likelihood that the activity will
adversely affect the species or stock
through effects on annual rates of
recruitment or survival); (3) to
determine whether the specified activity
will have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (however,
there are no subsistence communities in
the VACAPES Range Complex; thus,
there would be no affect to any
subsistence user); and (4) to prescribe
requirements pertaining to monitoring
and reporting.
In the Estimated Take of Marine
Mammals section of the proposed rule,
NMFS related the potential effects to
marine mammals from underwater
detonation of explosives to the MMPA
regulatory definitions of Level A and
Level B Harassment and assessed the
effects to marine mammals that could
result from the specific activities that
the Navy intends to conduct. The
subsections of this analysis are
discussed in the proposed rule (73 FR
75631; December 12, 2008) and have not
changed.
Acoustic Take Criteria
In the Acoustic Take Criteria section
of the proposed rule, NMFS described
the development and application of the
acoustic criteria for explosive
detonations (73 FR 76531; December 12,
2008). No changes have been made to
the discussion contained in this section
of the proposed rule.
Take Calculations
In the Take Calculation section of the
proposed rule, NMFS described in
detail how the take estimates were
calculated through modeling (73 FR
76531). No changes have been made to
the discussion contained in this section
of the proposed rule.
A summary of potential exposures
from ordnance (per year) for marine
mammals in the VACAPES Range
Complex is listed in Table 4 (these
exposure estimates are similar to those
presented in the proposed rule).
TABLE 4—SUMMARY OF POTENTIAL TAKES FROM EXPLOSIVE ORDNANCE (PER YEAR) FOR MARINE MAMMALS IN THE
VACAPES RANGE COMPLEX
Level B
harassment
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Species
Fin whale .........................................................................................................................................
Humpback whale .............................................................................................................................
North Atlantic right whale ................................................................................................................
Sperm whale ....................................................................................................................................
Atlantic spotted dolphin ...................................................................................................................
Beaked whales ................................................................................................................................
Bottlenose dolphin ...........................................................................................................................
Clymene dolphin ..............................................................................................................................
Common dolphin ..............................................................................................................................
Kogia sp. ..........................................................................................................................................
Pantropical spotted dolphin .............................................................................................................
Pilot whale .......................................................................................................................................
Risso’s dolphin .................................................................................................................................
Rough-toothed dolphin ....................................................................................................................
Striped dolphin .................................................................................................................................
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2
2
0
2
43
0
29
33
2,193
3
70
10
16
1
68
15JNR2
Level A
harassment
0
0
0
0
1
0
0
0
20
0
1
0
0
0
3
Mortality
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
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Effects on Marine Mammal Habitat
NMFS’ VACAPES Range Complex
proposed rule included a section that
addressed the effects of the Navy’s
activities on marine mammal habitat (73
FR 75631, page 75654). The Navy’s
proposed training exercises could
potentially affect marine mammal
habitat through underwater detonation
and the introduction of explosive sound
into the water column, and impacts to
the prey species of marine mammals.
These potential impacts are considered
in the VACAPES FEIS and were
determined by the Navy to have no
effect on marine mammal habitat. Based
on the information below and the
supporting information included in the
Navy’s FEIS, NMFS has determined that
the VACAPES Range Complex training
activities will not have adverse or longterm impacts on marine mammal
habitat.
Unless the sound source or explosive
detonation is stationary and/or
continuous over a long duration in one
area, the effects of underwater
detonation and its associated sound are
generally considered to have a less
severe impact on marine mammal
habitat than the physical alteration of
the habitat. Marine mammals may be
temporarily displaced from areas where
Navy training is occurring, but the area
will be utilized again after the activities
have ceased.
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Effects on Food Resources
There are currently no well
established thresholds for estimating
effects to fish from explosives other than
mortality models. Fish that are located
in the water column, in proximity to the
source of detonation could be injured,
killed, or disturbed by the impulsive
sound and possibly temporarily leave
the area. Continental Shelf Inc. (2004)
summarized a few studies conducted to
determine effects associated with
removal of offshore structures (e.g., oil
rigs) in the Gulf of Mexico. Their
findings revealed that at very close
range, underwater explosions are lethal
to most fish species regardless of size,
shape, or internal anatomy. For most
situations, cause of death in fishes has
been massive organ and tissue damage
and internal bleeding. At longer range,
species with gas-filled swimbladders
(e.g., snapper, cod, and striped bass) are
more susceptible than those without
swimbladders (e.g., flounders, eels).
Studies also suggest that larger fishes
are generally less susceptible to death or
injury than small fishes. Moreover,
elongated forms that are round in cross
section are less at risk than deep-bodied
forms; and orientation of fish relative to
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the shock wave may affect the extent of
injury. Open water pelagic fish (e.g.,
mackerel) also seem to be less affected
than reef fishes. The results of most
studies are dependent upon specific
biological, environmental, explosive,
and data recording factors.
The huge variations in the fish
population, including numbers, species,
sizes, and orientation and range from
the detonation point, make it very
difficult to accurately predict mortalities
at any specific site of detonation.
However, most fish species experience a
large number of natural mortalities,
especially during early life-stages, and
any small level of mortality caused by
the VACAPES Range Complex training
exercises involving explosives will
likely be insignificant to the population
as a whole.
Therefore, potential impacts to marine
mammal food resources within the
VACAPES Range Complex is negligible
given both the very geographic and
spatially limited scope of most Navy at
sea activities including underwater
detonations, and the high biological
productivity of these resources. No short
or long term effects to marine mammal
food resources from Navy activities are
anticipated within the VACAPES Range
Complex. There is no critical habitat for
marine mammals in the proposed
VACAPES Range Complex Study Area.
Analysis and Negligible Impact
Determination
Pursuant to NMFS’ regulations
implementing the MMPA, an applicant
is required to estimate the number of
animals that will be ‘‘taken’’ by the
specified activities (i.e., takes by
harassment only, or takes by
harassment, injury, and/or death). This
estimate informs the analysis that NMFS
must perform to determine whether the
activity will have a ‘‘negligible impact’’
on the species or stock. Level B
(behavioral) harassment occurs at the
level of the individual(s) and does not
assume any resulting population-level
consequences, though there are known
avenues through which behavioral
disturbance of individuals can result in
population-level effects. A negligible
impact finding is based on the lack of
likely adverse effects on annual rates of
recruitment or survival (i.e., populationlevel effects). An estimate of the number
of Level B harassment takes alone, is not
enough information on which to base an
impact determination.
In addition to considering estimates of
the number of marine mammals that
might be ‘‘taken’’ through behavioral
harassment, NMFS must consider other
factors, such as the likely nature of any
responses (their intensity, duration,
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etc.), the context of any responses
(critical reproductive time or location,
migration, etc.), as well as the number
and nature of estimated Level A takes,
the number of estimated mortalities, and
effects on habitat.
The Navy’s specified activities have
been described based on best estimates
of the planned detonation events the
Navy would conduct for the proposed
VACAPES Range Complex training
activities. The events are generally short
in duration, including a total of 115 1–
1.5–hour events and 46 6–8-hour events.
Taking the above into account, along
with the fact that NMFS anticipates no
mortalities (and few injuries) to result
from the action, the fact that there are
no specific areas of reproductive
importance for marine mammals
recognized within VACAPES, the
sections discussed below, and
dependent upon the implementation of
the proposed mitigation measures,
NMFS has determined that Navy
training exercises utilizing underwater
detonations will have a negligible
impact on the affected marine mammal
species and stocks present in the
VACAPES Range Complex Study Area.
NMFS’ analysis of potential
behavioral harassment, temporary
threshold shifts, permanent threshold
shifts, injury, and mortality to marine
mammals as a result of the VACAPES
Range Complex training activities was
provided in the proposed rule (73 FR
75631, pages 75636–75646) and is
described in more detail below.
Behavioral Harassment
The Navy plans a total of 80
MISSILEX training events (each lasting
for 1 hour), 22 FIREX training events
(each lasting for 8 hours), 5 BOMBEX
training events (each lasting for 1 hour),
30 MH–60S MINEX training events
(each lasting for 1.5 hours), and 24 EOD
MINEX training events (each lasting for
6–8 hours) annually. The total training
exercises proposed by the Navy in the
VACAPES Range Complex amount to
under 500 hours per year. These
detonation events are widely dispersed
throughout several of the designated
sites within the VACAPES Range
Complex Study Area. The probability
that detonation events will overlap in
time and space with marine mammals is
low, particularly given the densities of
marine mammals in the VACAPES
Range Complex Study Area and the
implementation of monitoring and
mitigation measures. Moreover, NMFS
does not expect animals to experience
repeat exposures to the same sound
source as animals will likely move away
from the source after being exposed. In
addition, these isolated exposures,
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when received at distances of Level B
behavioral harassment (i.e., 177 dB re 1
microPa2-sec), are expected to cause
brief startle reactions or short-term
behavioral modification by the animals.
These brief reactions and behavioral
changes are expected to disappear when
the exposures cease. Therefore, these
levels of received impulse noise from
detonation are not expected to affect
annual rates or recruitment or survival.
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TTS
NMFS and the Navy have estimated
that individuals of some species of
marine mammals may sustain some
level of temporarily threshold shift TTS
from underwater detonations. TTS can
last from a few minutes to days, be of
varying degree, and occur across various
frequency bandwidths. The TTS
sustained by an animal is primarily
classified by three characteristics:
• Frequency—Available data (of midfrequency hearing specialists exposed to
mid to high frequency sounds—Southall
et al., 2007) suggest that most TTS
occurs in the frequency range of the
source up to one octave higher than the
source (with the maximum TTS at 1⁄2
octave above).
• Degree of the shift (i.e., how many
dB is the sensitivity of the hearing
reduced by)—generally, both the degree
of TTS and the duration of TTS will be
greater if the marine mammal is exposed
to a higher level of energy (which would
occur when the peak dB level is higher
or the duration is longer). Since the
impulse from detonation is extremely
brief, an animal would have to approach
very close to the detonation site to
increase the received SEL. The
threshold for the onset of TTS for
detonations is a dual criteria: 182 dB re
1 microPa2-sec or 23 psi, which might
be received at distances from 345–2,863
m from the centers of detonation based
on the types of NEW involved to receive
the SEL that causes TTS compared to
similar source level with longer
durations (such as sonar signals).
• Duration of TTS (Recovery time)—
Of all TTS laboratory studies, some
using exposures of almost an hour in
duration or up to 217 SEL, almost all
recovered within 1 day (or less, often in
minutes), though in one study (Finneran
et al., 2007), recovery took 4 days.
• Although the degree of TTS
depends on the received noise levels
and exposure time, all studies show that
TTS is reversible and animals’
sensitivity is expected to recover fully
in minutes to hours. Therefore, NMFS
expects that TTS would not affect
annual rates of recruitment or survival.
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Acoustic Masking or Communication
Impairment
As discussed above, it is also possible
that anthropogenic sound could result
in masking of marine mammal
communication and navigation signals.
However, masking only occurs during
the time of the signal (and potential
secondary arrivals of indirect rays),
versus TTS, which occurs continuously
for its duration. Impulse sounds from
underwater detonation are extremely
brief and the majority of most animals’
vocalizations would not be masked.
Therefore, masking effects from
underwater detonation are expected to
be minimal and unlikely. If masking or
communication impairment were to
occur briefly, it would be in the
frequency ranges below 100 Hz, which
overlaps with some mysticete
vocalizations; however, it would likely
not mask the entirety of any particular
vocalization or communication series
because of the short impulse.
PTS, Injury, or Mortality
The Navy’s model estimated that 1
Atlantic spotted dolphin, 20 common
dolphins, 1 pantropical spotted dolphin,
and 3 striped dolphins could experience
50% tympanic membrane rupture or
slight lung injury (Level A harassment)
as a result of the training activities
utilizing underwater detonation in the
VACAPES Range Complex Study Area.
However, these estimates do not take
into consideration the proposed
mitigation and monitoring measures.
For underwater detonations, the animals
have to be within an area between
certain injury zones of influence (ZOI)
to experience Level A harassment. Such
injury ZOI varies from 0.02 km2 to 6.39
km2 (or at distances between 80 m to
1,426 m from the center of detonation)
depending on the types of munition
used and the season of the action.
Though it is possible that Navy
observers could fail to detect an animal
at a distance of more than 1 km (an
injury ZOI during BOMEX, which is
planned to have 5 events annually), all
injury ZOIs from other detonation
activities (FIREX, MISSILEX, and
MINEX) are smaller than 0.165 km2 (230
m in radius) and NMFS believes it is
unlikely that any marine mammal could
be detected by lookouts/watchstanders
or MMOs. As discussed previously, the
Navy plans to utilize aerial or vessel
surveys to detect marine mammals for
mitigation implementation and
indicated that they are capable of
effectively monitoring safety zones.
Based on these assessments, NMFS
determined that approximately 2
humpback whales, 2 fin whales, 2
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28341
sperm whales, 3 dwarf or pygmy sperm
whales, 1 rough-toothed dolphin, 29
bottlenose dolphins, 70 pantropical
spotted dolphins, 68 stripped dolphins,
33 Clymene dolphins, 43 Atlantic
spotted dolphins, 2,193 common
dolphins, 16 Risso’s dolphins, and 10
pilot whales could be affected by Level
B harassment (TTS and sub-TTS) as a
result of the proposed VACAPES Range
Complex training activities. These
numbers represent approximately
0.24%, 0.09%, 0.04%, 0.76%, 0.04%,
1.58%, 0.07%, 0.08%, 1.82%, 0.08%,
and 0.03% of humpback whales, fin
whales, sperm whales, dwarf or pygmy
sperm whales, bottlenose dolphins,
pantropical spotted dolphins, striped
dolphins, Clymene dolphins, Atlantic
spotted dolphins, common dolphins,
Risso’s dolphins, and pilot whales,
respectively in the vicinity of the
proposed VACAPES Range Complex
Study Area (calculation based on NMFS
2007 US Atlantic and Gulf of Mexico
Marine Mammal Stock Assessment).
Although the population estimates of
Clymene dolphins and rough-toothed
dolphins are unknown in the proposed
action area, NMFS believes that the take
of 33 individuals of Clymene dolphins
and 1 individual of rough-toothed
dolphin by Level B harassment would
have a negligible impact to this species
because most of their population exists
beyond the project area and because
they are widely distributed species in
the North Atlantic (Jefferson et al., 1993;
Reeves et al., 2002).
In addition, the Level A takes of 1
Atlantic spotted dolphin, 20 common
dolphins, 1 pantropical spotted dolphin,
and 3 striped dolphins represent
0.002%, 0.0166%, 0.0225%, and
0.0032% of these species, respectively,
in the vicinity of the proposed
VACAPES Range Complex Study Area
(calculation based on NMFS 2007 US
Atlantic and Gulf of Mexico Marine
Mammal Stock Assessment). Given
these very small percentages, NMFS
does not expect there to be any longterm adverse effect on the populations
of the aforementioned dolphin species.
No marine mammals are expected to be
killed as a result of these activities.
Additionally, the aforementioned take
estimates do not account for the
implementation of mitigation measures.
With the implementation of mitigation
and monitoring measures, NMFS
expects that the takes would be reduced
further. Coupled with the fact that these
impacts will likely not occur in areas
and times critical to reproduction,
NMFS has determined that the total
taking over the 5-year period of the
regulations and subsequent LOAs from
the Navy’s VACAPES Range Complex
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training activities will have a negligible
impact on the marine mammal species
and stocks present in the VACAPES
Range Complex Study Area.
Subsistence Harvest of Marine
Mammals
NMFS has determined that the
issuance of 5-year regulations and
subsequent LOAs (as warranted) for
Navy training exercises in the
VACAPES Range Complex would not
have an unmitigable adverse impact on
the availability of the affected species or
stocks for subsistence use since there
are no such uses in the specified area.
ESA
There are five marine mammal
species, three sea turtle species, and a
fish species that are listed as
endangered under the ESA with
confirmed or possible occurrence in the
study area and could be impacted by the
proposed action: Humpback whale,
North Atlantic right whale, blue whale,
fin whale, sperm whale, loggerhead sea
turtle, leatherback sea turtle, the Kemp’s
ridley sea turtle, and the shortnose
sturgeon.
Pursuant to Section 7 of the ESA, the
Navy has consulted with NMFS on this
action. NMFS has also consulted
internally on the issuance of regulations
under section 101(a)(5)(A) of the MMPA
for this activity. The Biological Opinion
concludes that the proposed training
activities are likely to adversely affect
but are not likely to jeopardize the
continued existence of these threatened
and endangered species under NMFS
jurisdiction.
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NEPA
NMFS participated as a cooperating
agency on the Navy’s Final
Environmental Impact Statement (FEIS)
for the VACAPES Range Complex.
NMFS subsequently adopted the Navy’s
EIS for the purpose of complying with
the MMPA.
Determination
Based on the analysis contained
herein and in the proposed rule (and
other related documents) of the likely
effects of the specified activity on
marine mammals and their habitat and
dependent upon the implementation of
the mitigation measures, NMFS finds
that the total taking from Navy
VACAPES Range Complex training
exercises utilizing underwater
explosives over the 5 year period will
have a negligible impact on the affected
species or stocks and will not result in
an unmitigable adverse impact on the
availability of marine mammal species
or stocks for taking for subsistence uses
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because no subsistence uses exist in the
VACAPES Range Complex study area.
NMFS has issued regulations for these
exercises that prescribe the means of
effecting the least practicable adverse
impact on marine mammals and their
habitat and set forth requirements
pertaining to the monitoring and
reporting of that taking.
Classification
This action does not contain a
collection of information requirement
for purposes of the Paperwork
Reduction Act.
Pursuant to Executive Order 12866,
the Office of Management and Budget
has determined that this rule is not
significant.
The Chief Counsel for Regulation of
the Department of Commerce certified at
the Proposed Rule stage that this action
will not have a significant economic
impact on a substantial number of small
entities. The Navy is the entity that will
be affected by this rulemaking, not a
small governmental jurisdiction, small
organization or small business, as
defined by the RFA. This rulemaking
authorizes the take of marine mammals
incidental to a specified activity. The
specified activity defined in the
proposed rule includes the use of
underwater detonations, which are only
used by the U.S. military, during
training activities that are only
conducted by the U.S. Navy.
Additionally, any requirements imposed
by a Letter of Authorization issued
pursuant to these regulations, and any
monitoring or reporting requirements
imposed by these regulations, will be
applicable only to the Navy. Because
this action, if adopted, would directly
affect the Navy and not a small entity,
NMFS concludes the action would not
result in a significant economic impact
on a substantial number of small
entities.
The Assistant Administrator for
Fisheries has determined that there is
good cause under the Administrative
Procedure Act (5 U.S.C. 553(d)(3)) to
waive the 30-day delay in effective date
of the measures contained in the final
rule. The U.S Navy has a compelling
national policy reason to continue
military readiness activities without
interruption in its East Coast Operating
Areas, i.e., the VACAPES Range
Complex. As discussed below,
suspension/interruption of the Navy’s
ability to train, for even a small number
of days, disrupts vital sequential
training and certification processes
essential to our national security.
In order to meet its national security
objectives, the Navy must continually
maintain its ability to operate in a
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challenging at-sea environment, conduct
military operations, control strategic
maritime transit routes and
international straits, and protect sea
lines of communications that support
international commerce. To meet these
objectives, the Navy must continually
train. Timely training is critical because
individual Navy units and Strike
Groups/Amphibious Readiness Groups
(ARG) currently operate in, or need to
quickly deploy to high risk geographic
areas. In addition, a Strike Group/ARG
is built around an aircraft carrier with
typically 5,300 personnel on board and
an amphibious assault ship that carries
a Marine Corps Expeditionary Unit, so
failure to adequately train risks
thousands of lives.
The training necessary to protect
American interests and the lives of
sailors and marines is complex. It
involves ensuring the warfighter can
accurately identify potential threats in a
variety of marine environments and
conditions, and it involves the
coordination of different vessels and
aircraft so that the group’s capabilities
are employed in the most tactically
effective manner. As with any
complicated coordinated effort, this
challenge requires routine practice, as
these skills are perishable.
In 10 U.S.C. 5062, Congress mandated
that the Chief of Naval Operations
(CNO) organize, train, and equip all
Naval forces for combat. In response, the
Fleet Response Training Plan (FRTP) is
a major initiative designed to ensure
Naval units receive required training
before they deploy. The FRTP is an
arduous sequential training cycle in
which unit level training (ULT) and
combat certification are followed by
major exercises that bring together
various warfare components so they
have the opportunity to practice as an
integrated whole and attain
certification. Accordingly, any delay in
coordinated training creates a
significant and unreasonable risk which
could result in a unit’s and/or Strike
Group’s inability to train, certify and
report as directed to an overseas theater
of operations.
A deployment certification exercise is
currently scheduled for June 2009 that
will encompass areas of the VACAPES
Range Complex. Lack of the appropriate
environmental regulatory coverage for
even a single day imperils completion of
this exercise, and risks deployment
certification. Essential ULT also occurs
in these OPAREAs. There is limited unit
level underway (at-sea) time available in
the FRTP to adjust the training dates.
These ULT training periods are driven
by sequential certification processes for
both inport and at-sea training.
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Scheduling constraints are further
complicated by the availability of Afloat
Training Groups (ATGs) that are
responsible for training all individual
units. ATGs have a limited number of
trainers available at any given time, and
their schedules must also be deconflicted, compounding the problem if
training schedules are not adhered to.
Waiver of the 30-day delay of the
effective date of the Final Rule will
allow Navy to finalize operational
procedures to ensure compliance with
required mitigation, monitoring, and
reporting requirements, and have
MMPA authorization in place prior to
Navy’s vital June 2009 exercise.
List of Subjects in 50 CFR Part 218
Exports, Fish, Imports, Incidental
take, Indians, Labeling, Marine
mammals, Navy, Penalties, Reporting
and recordkeeping requirements,
Seafood, Transportation.
Dated: June 5, 2009.
Samuel D. Rauch III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
For reasons set forth in the preamble,
50 CFR Chapter II is amended by adding
part 218 to read as follows:
■ 1. Part 218 is added to read as follows:
■
PART 218—REGULATIONS
GOVERNING THE TAKING AND
IMPORTING OF MARINE MAMMALS
Subpart A—Taking Marine Mammals
Incidental to U.S. Navy Training in the
Virginia Capes Range Complex (VACAPES
Range Complex)
Sec.
218.1 Specified activity, specified
geographical area and effective dates.
218.2 Permissible methods of taking.
218.3 Prohibitions.
218.4 Mitigation.
218.5 Requirements for monitoring and
reporting.
218.6 Applications for Letters of
Authorization.
218.7 Letters of Authorization.
218.8 Renewal of Letters of Authorization
and adaptive management.
218.9 Modifications to Letters of
Authorization.
Authority: 16 U.S.C. 1361 et seq.
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Subpart A—Taking Marine Mammals
Incidental to U.S. Navy Training in the
Virginia Capes Range Complex
(VACAPES Range Complex)
§ 218.1 Specified activity, specified
geographical area and effective dates.
(a) Regulations in this subpart apply
only to the U.S. Navy for the taking of
marine mammals that occurs in the area
outlined in paragraph (b) of this section
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and that occur incidental to the
activities described in paragraph (c) of
this section.
(b) The taking of marine mammals by
the Navy is only authorized if it occurs
within the VACAPES Range Complex
Operation Area (OPAREA), which is
located in the coastal and offshore
waters of the western North Atlantic
Ocean adjacent to Delaware, Maryland,
Virginia, and North Carolina. The
northernmost boundary of the
VACAPES Range Complex OPAREA is
located 37 nautical miles (nm) off the
entrance to Delaware Bay at latitude
38°45′ N, the farthest point of the
eastern boundary is 184 nm east of
Chesapeake Bay at longitude 72°41′ W,
and the southernmost point is 105 nm
southeast of Cape Hatteras, North
Carolina, at latitude of 34°19′ N. The
western boundary of the VACAPES
Range Complex OPAREA lies 3 nm from
the shoreline at the boundary separating
state and Federal waters.
(c) The taking of marine mammals by
the Navy is only authorized if it occurs
incidental to the following activities
within the designated amounts of use:
(1) The detonation of the underwater
explosives indicated in paragraph
(c)(1)(i) of this section conducted as part
of the training events indicated in
paragraph (c)(1)(ii) of this section:
(i) Underwater Explosives:
(A) AGM–114 (Hellfire missile)
(B) AGM–65 E/F (Maverick missile)
(C) MK–83/GBU–32 (1,000 lb High
Explosive bomb)
(D) Airgorne Mine Neutralization
system (AMNS)
(E) 20 lb NEW charges
(F) AGM–88 (HARM)
(G) 5″ Naval Gunfire
(ii) Training Events:
(A) Mine Exercise (MINEX) (Mine
Neutralization [AMNS])—up to 150
exercises over the course of 5 years (an
average of 30 per year);
(B) Mine Exercise (MINEX) (Mine
Neutralization [20 lb NEW charges])—
up to 120 exercises over the course of
5 years (an average of 24 per year);
(C) Bombing Exercise (BOMBEX) (Airto-Surface)—up to 100 exercises over
the course of 5 years (an average of 20
per year);
(D) Missile Exercise (MISSILEX) (Airto-Surface; Hellfire missile)—up to 300
exercises over the course of 5 years (an
average of 60 per year);
(E) Missile Exercise (MISSILEX) (Airto-Surface; Maverick, HE)—up to 100
exercises over the course of 5 years (an
average of 20 per year); and
(F) FIREX with IMPASS—up to 110
exercises over the course of 5 years (an
average of 22 per year).
(2) [Reserved]
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28343
(d) Regulations are effective June 8,
2009 and are applicable to the Navy on
June 5, 2009 through June 4, 2014.
§ 218.2
Permissible methods of taking.
(a) Under Letters of Authorization
issued pursuant to § 216.106 of this
chapter and § 218.7, the Holder of the
Letter of Authorization may
incidentally, but not intentionally, take
marine mammals within the area
described in § 218.1(b), provided the
activity is in compliance with all terms,
conditions, and requirements of this
subpart and the appropriate Letter of
Authorization.
(b) The activities identified in
§ 218.1(c) must be conducted in a
manner that minimizes, to the greatest
extent practicable, any adverse impacts
on marine mammals and their habitat.
(c) The incidental take of marine
mammals under the activities identified
in § 218.1(c) is limited to the following
species, by the indicated method of take
and the indicated number of times:
(1) Level B Harassment:
(i) Mysticetes:
(A) Humpback whale (Megaptera
novaeangliae)—10 (an average of 2
annually); and
(B) Fin whale (Balaenoptera
physalus)—10 (an average of 2
annually).
(ii) Odontocetes:
(A) Sperm whale (Physeter
macrocephalus)—10 (an average of 2
annually);
(B) Pygmy or dwarf sperm whales
(Kogia sp.)—15 (an average of 3
annually);
(C) Rough-toothed dolphin (Steno
bredanensis)—5 (an average of 1
annually);
(D) Bottlenose dolphin (Tursiops
truncatus)—145 (an average of 29
annually);
(E) Pantropical spotted dolphin
(Stenella attenuata)—350 (an average of
70 annually);
(F) Striped dolphin (S.
coeruleoalba)—340 (an average of 68
annually);
(G) Clymene dolphin (S. clymene)—
165 (an average of 33 annually);
(H) Atlantic spotted dolphin (S.
frontalis)—215 (an average of 43
annually);
(I) Common dolphin (Delphinus
delphis)—10,965 (an average of 2,193
annually);
(J) Risso’s dolphin (Grampus
griseus)—80 (an average of 16 annually);
and
(K) Pilot whales (Globicephala sp.)—
50 (an average of 10 annually).
(2) Level A Harassment (injury):
(i) Atlantic spotted dolphin—5 (an
average of 1 annually);
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(ii) Common dolphin—100 (an
average of 20 annually);
(iii) Pantropical spotted dolphin—5
(an average of 1 annually); and
(iv) Striped dolphin—15 (an average
of 3 annually).
§ 218.3
Prohibitions.
Notwithstanding takings
contemplated in § 218.2 and authorized
by a Letter of Authorization issued
under § 216.106 of this chapter and
§ 218.7, no person in connection with
the activities described in § 218.1 may:
(a) Take any marine mammal not
specified in § 218.2(c);
(b) Take any marine mammal
specified in § 218.2(c) other than by
incidental take as specified in
§ 218.2(c)(1) and (2);
(c) Take a marine mammal specified
in § 218.2(c) if such taking results in
more than a negligible impact on the
species or stocks of such marine
mammal; or
(d) Violate, or fail to comply with, the
terms, conditions, and requirements of
this Subpart or a Letter of Authorization
issued under § 216.106 of this chapter
and § 218.7.
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§ 218.4
Mitigation.
(a) When conducting training
activities identified in § 218.1(c), the
mitigation measures contained in the
Letter of Authorization issued under
§ 216.106 of this chapter and § 218.7
must be implemented. These mitigation
measures include, but are not limited to:
(1) General Maritime Measures:
(i) Personnel Training—Lookouts
(A) All bridge personnel,
Commanding Officers, Executive
Officers, officers standing watch on the
bridge, maritime patrol aircraft aircrews,
and Mine Warfare (MIW) helicopter
crews shall complete Marine Species
Awareness Training (MSAT).
(B) Navy lookouts shall undertake
extensive training to qualify as a
watchstander in accordance with the
Lookout Training Handbook
(NAVEDTRA 12968–D).
(C) Lookout training shall include onthe-job instruction under the
supervision of a qualified, experienced
watchstander. Following successful
completion of this supervised training
period, lookouts shall complete the
Personal Qualification Standard
Program, certifying that they have
demonstrated the necessary skills (such
as detection and reporting of partially
submerged objects).
(D) Lookouts shall be trained in the
most effective means to ensure quick
and effective communication within the
command structure to facilitate
implementation of protective measures
if marine species are spotted.
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(E) Surface lookouts shall scan the
water from the ship to the horizon and
be responsible for all contacts in their
sector. In searching the assigned sector,
the lookout shall always start at the
forward part of the sector and search aft
(toward the back). To search and scan,
the lookout shall hold the binoculars
steady so the horizon is in the top third
of the field of vision and direct the eyes
just below the horizon. The lookout
shall scan for approximately five
seconds in as many small steps as
possible across the field seen through
the binoculars. They shall search the
entire sector in approximately fivedegree steps, pausing between steps for
approximately five seconds to scan the
field of view. At the end of the sector
search, the glasses shall be lowered to
allow the eyes to rest for a few seconds,
and then the lookout shall search back
across the sector with the naked eye.
(F) At night, lookouts shall scan the
horizon in a series of movements that
would allow their eyes to come to
periodic rests as they scan the sector.
When visually searching at night, they
shall look a little to one side and out of
the corners of their eyes, paying
attention to the things on the outer
edges of their field of vision. Lookouts
shall also have night vision devices
available for use.
(ii) Operating Procedures and
Collision Avoidance:
(A) Prior to major exercises, a Letter
of Instruction, Mitigation Measures
Message or Environmental Annex to the
Operational Order shall be issued to
further disseminate the personnel
training requirement and general marine
species mitigation measures.
(B) Commanding Officers shall make
use of marine species detection cues
and information to limit interaction
with marine species to the maximum
extent possible consistent with safety of
the ship.
(C) While underway, surface vessels
shall have at least two lookouts with
binoculars; surfaced submarines shall
have at least one lookout with
binoculars. Lookouts already posted for
safety of navigation and man-overboard
precautions may be used to fill this
requirement. As part of their regular
duties, lookouts shall watch for and
report to the OOD the presence of
marine mammals.
(D) Personnel on lookout shall employ
visual search procedures employing a
scanning method in accordance with the
Lookout Training Handbook
(NAVEDTRA 12968–D).
(E) After sunset and prior to sunrise,
lookouts shall employ Night Lookouts
Techniques in accordance with the
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Lookout Training Handbook
(NAVEDTRA 12968–D).
(F) While in transit, naval vessels
shall be alert at all times, use extreme
caution, and proceed at a ‘‘safe speed’’
so that the vessel can take proper and
effective action to avoid a collision with
any marine animal and can be stopped
within a distance appropriate to the
prevailing circumstances and
conditions.
(G) When whales have been sighted in
the area, Navy vessels shall increase
vigilance and implement measures to
avoid collisions with marine mammals
and avoid activities that might result in
close interaction of naval assets and
marine mammals. Such measures shall
include changing speed and/or direction
and would be dictated by environmental
and other conditions (e.g., safety or
weather).
(H) Naval vessels shall maneuver to
keep at least 500 yds (460 m) away from
any observed whale and avoid
approaching whales head-on. This
requirement does not apply if a vessel’s
safety is threatened, such as when
change of course will create an
imminent and serious threat to a person,
vessel, or aircraft, and to the extent
vessels are restricted in their ability to
maneuver. Vessels shall take reasonable
steps to alert other vessels in the
vicinity of the whale.
(I) Where feasible and consistent with
mission and safety, vessels shall avoid
closing to within 200-yd (183 m) of
marine mammals other than whales
(whales addressed above).
(J) Navy aircraft participating in
exercises at sea shall conduct and
maintain, when operationally feasible
and safe, surveillance for marine species
of concern as long as it does not violate
safety constraints or interfere with the
accomplishment of primary operational
duties. Marine mammal detections shall
be immediately reported to assigned
Aircraft Control Unit for further
dissemination to ships in the vicinity of
the marine species as appropriate where
it is reasonable to conclude that the
course of the ship will likely result in
a closing of the distance to the detected
marine mammal.
(K) All vessels shall maintain logs and
records documenting training
operations should they be required for
event reconstruction purposes. Logs and
records shall be kept for a period of 30
days following completion of a major
training exercise.
(2) Coordination and Reporting
Requirements. (i) The Navy shall
coordinate with the local NMFS
Stranding Coordinator for any unusual
marine mammal behavior and any
stranding, beached live/dead, or floating
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marine mammals that may occur at any
time during or within 24 hours after
completion of training activities.
(ii) The Navy shall follow internal
chain of command reporting procedures
as promulgated through Navy
instructions and orders.
(3) Mitigation Measures Applicable to
Vessel Transit in the Mid-Atlantic
during North Atlantic Right Whale
Migration: The mitigation measures
apply to all Navy vessel transits,
including those vessels that would
transit to and from East Coast ports and
the VACAPES Range Complex.
(i) Mid-Atlantic, Offshore of the
Eastern United States:
(A) All Navy vessels are required to
use extreme caution and operate at a
slow, safe speed consistent with mission
and safety (at a speed that does not
compromise safety of navigation) during
the months indicated below and within
a 37 km (20 nm) arc (except as noted)
of the specified associated reference
points:
(1) South and East of Block Island (37
km (20 NM) seaward of line between
41–4.49° N. lat. 071–51.15° W. long. and
41–18.58° N. lat. 070–50.23° W. long):
Sept–Oct and Mar–Apr
(2) New York/New Jersey (40–30.64°
N. lat. 073–57.76° W. long.): Sep–Oct
and Feb–Apr.
(3) Delaware Bay (Philadelphia) (38–
52.13° N. lat. 075–1.93° W. long.): Oct–
Dec and Feb–Mar.
(4) Chesapeake Bay (Hampton Roads
and Baltimore) (37–1.11° N. lat. 075–
57.56° W. long.): Nov–Dec and Feb–Apr.
(5) North Carolina (34–41.54° N. lat.
076–40.20° W. long.): Dec–Apr.
(6) South Carolina (33–11.84° N. lat.
079–8.99° W. long. and 32–43.39° N. lat.
079–48.72° W. long.): Oct–Apr.
(B) During the months indicated in
paragraph (a)(3)(i)(A) of this section,
Navy vessels shall practice increased
vigilance with respect to avoidance of
vessel-whale interactions along the midAtlantic coast, including transits to and
from any mid-Atlantic ports not
specifically identified in paragraph
(a)(3)(i)(A) of this section.
(C) All surface units transiting within
56 km (30 NM) of the coast in the midAtlantic shall ensure at least two
watchstanders are posted, including at
least one lookout who has completed
required MSAT training.
(D) Navy vessels shall not knowingly
approach any whale head on and shall
maneuver to keep at least 457 m (1,500
ft) away from any observed whale,
consistent with vessel safety.
(ii) Southeast Atlantic, Offshore of the
Eastern United States—for the purposes
of the measures below (paragraphs
(a)(3)(ii)(A) & (B) of this section), the
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16:49 Jun 12, 2009
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‘‘southeast’’ encompasses sea space
from Charleston, South Carolina,
southward to Sebastian Inlet, Florida,
and from the coast seaward to 148 km
(80 NM) from shore. North Atlantic right
whale critical habitat is the area from
31–15° N. lat. to 30–15° N. lat.
extending from the coast out to 28 km
(15 NM), and the area from 28–00° N.
lat. to 30–15° N. lat. from the coast out
to 9 km (5 NM). All mitigation measures
described here that apply to the critical
habitat apply from November 15–April
15 and also apply to an associated area
of concern which extends 9 km (5 NM)
seaward of the designated critical
habitat boundaries.
(A) Prior to transiting or training in
the critical habitat or associated area of
concern, ships shall contact Fleet Area
Control and Surveillance Facility,
Jacksonville, to obtain latest whale
sighting and other information needed
to make informed decisions regarding
safe speed (the minimum speed at
which mission goals or safety will not
be compromised) and path of intended
movement. Subs shall contact
Commander, Submarine Group Ten for
similar information.
(B) The following specific mitigation
measures apply to activities occurring
within the North Atlantic right whale
critical habitat and an associated area of
concern which extends 9 km (5 NM)
seaward of the designated critical
habitat boundaries:
(1) When transiting within the critical
habitat or associated area of concern,
vessels shall exercise extreme caution
and proceed at a slow safe speed. The
speed shall be the slowest safe speed
that is consistent with mission, training
and operations.
(2) Speed reductions (adjustments) are
required when a whale is sighted by a
vessel or when the vessel is within 9 km
(5 NM) of a reported new sighting less
than 12 hours old. Circumstances could
arise where, in order to avoid North
Atlantic right whale(s), speed
reductions could mean vessels must
reduce speed to a minimum at which it
can safely keep on course or vessels
could come to an all stop.
(3) Vessels shall avoid head-on
approaches to North Atlantic right
whale(s) and shall maneuver to
maintain at least 457 m (500 yd) of
separation from any observed whale if
deemed safe to do so. These
requirements do not apply if a vessel’s
safety is threatened, such as when a
change of course would create an
imminent and serious threat to a person,
vessel, or aircraft, and to the extent
vessels are restricted in the ability to
maneuver.
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(4) During the North Atlantic right
whale calving season, north-south
transits through the critical habitat are
prohibited.
(5) Ships, surfaced subs, and aircraft
shall report any whale sightings to Fleet
Area Control and Surveillance Facility,
Jacksonville, by the quickest and most
practicable means. The sighting report
shall include the time, latitude/
longitude, direction of movement and
number and description of whale (i.e.,
adult/calf).
(iii) Northeast Atlantic, Offshore of
the Eastern United States:
(A) Prior to transiting the Great South
Channel or Cape Cod Bay critical habitat
areas, ships shall obtain the latest North
Atlantic right whale sightings and other
information needed to make informed
decisions regarding safe speed (the
minimum speed at which mission goals
or safety will not be compromised). The
Great South Channel critical habitat is
defined by the following coordinates:
41–00° N. lat., 69–05° W. long.; 41–45°
N. lat, 69–45° W. long; 42–10° N. lat.,
68–31° W. long.; 41–38° N. lat., 68–13°
W. long. The Cape Cod Bay critical
habitat is defined by the following
coordinates: 42–04.8° N. lat., 70–10° W.
long.; 42–12° N. lat., 70–15° W. long.;
42–12° N. lat., 70–30° W. long.; 41–46.8°
N. lat., 70–30° W. long.
(B) Ships, surfaced subs, and aircraft
shall report any North Atlantic right
whale sightings (if the whale is
identifiable as a right whale) off the
northeastern U.S. to Patrol and
Reconnaissance Wing
(COMPATRECONWING). The report
shall include the time of sighting, lat/
long, direction of movement (if
apparent) and number and description
of the whale(s).
(C) Vessels or aircraft that observe
whale carcasses shall record the
location and time of the sighting and
report this information as soon as
possible to the cognizant regional
environmental coordinator. All whale
strikes must be reported. This report
shall include the date, time, and
location of the strike; vessel course and
speed; operations being conducted by
the vessel; weather conditions,
visibility, and sea state; description of
the whale; narrative of incident; and
indication of whether photos/videos
were taken. Navy personnel are
encouraged to take photos whenever
possible.
(D) Specific mitigation measures
related to activities occurring within the
critical habitat include the following:
(1) Vessels shall avoid head-on
approaches to North Atlantic right
whale(s) and shall maneuver to
maintain at least 457 m (500 yd) of
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separation from any observed whale if
deemed safe to do so. These
requirements do not apply if a vessel’s
safety is threatened, such as when
change of course would create an
imminent and serious threat to person,
vessel, or aircraft, and to the extent
vessels are restricted in the ability to
maneuver.
(2) When transiting within the critical
habitat or associated area of concern,
vessels shall use extreme caution and
operate at a safe speed (the minimum
speed at which mission goals or safety
will not be compromised) so as to be
able to avoid collisions with North
Atlantic right whales and other marine
mammals, and stop within a distance
appropriate to the circumstances and
conditions.
(3) Speed reductions (adjustments) are
required when a whale is sighted by a
vessel or when the vessel is within 9 km
(5 NM) of a reported new sighting less
than one week old.
(4) Ships transiting in the Cape Cod
Bay and Great South Channel critical
habitats shall obtain information on
recent whale sightings in the vicinity of
the critical habitat. Any vessel operating
in the vicinity of a North Atlantic right
whale shall consider additional speed
reductions per Rule 6 of International
Navigational Rules.
(4) Mitigation Measures for Specific
At-sea Training Events—If a marine
mammal is killed as a result of the
proposed Navy training activities (e.g.,
instances in which it is clear that
munitions explosions caused the death),
the Navy shall suspend its activities
immediately and report the incident to
NMFS.
(i) Firing Exercise (FIREX) Using the
Integrated Maritime Portable Acoustic
Scoring System (IMPASS) (5-in.
Explosive Rounds):
(A) FIREX using IMPASS would only
be conducted in the four designated
areas specified in the Navy’s LOA
application in the VACAPES Range
Complex.
(B) Pre-exercise monitoring of the
target area shall be conducted with ‘‘Big
Eyes’’ prior to the event, during
deployment of the IMPASS sonobuoy
array, and during return to the firing
position. Ships shall be required to
maintain a lookout dedicated to visually
searching for marine mammals 180°
along the ship track line and 360° at
each buoy drop-off location.
(C) ‘‘Big Eyes’’ on the ship shall be
used to monitor a 600 yd (548 m) buffer
zone around the target area for marine
mammals during naval-gunfire events.
(D) Ships shall not fire on the target
if any marine mammals are detected
within or approaching the 600 yd (548
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16:49 Jun 12, 2009
Jkt 217001
m) buffer zone until the area is cleared.
If marine mammals are present,
operations shall be suspended. Visual
observation shall occur for
approximately 45 minutes, or until the
animal has been observed to have
cleared the area and is heading away
from the buffer zone.
(E) Post-exercise monitoring of the
entire target area shall take place with
‘‘Big Eyes’’ and the naked eye during the
retrieval of the IMPASS sonobuoy array
following each firing exercise.
(F) FIREX with IMPASS shall take
place during daylight hours only.
(G) FIREX with IMPASS shall only be
used in Beaufort Sea State three (3) or
less.
(H) The visibility must be such that
the fall of shot is visible from the firing
ship during the exercise.
(I) No firing shall occur if marine
mammals are detected within 70 yd (64
m) of the vessel.
(ii) Air-to-Surface At-Sea Bombing
Exercises (250-lbs to 2,000-lbs explosive
bombs):
(A) Aircraft shall visually survey the
target and buffer zone for marine
mammals prior to and during the
exercise. The survey of the impact area
shall be made by flying at 1,500 ft (457
m) altitude or lower, if safe to do so, and
at the slowest safe speed.
(B) A buffer zone of 5,100-yd (4,663
m) radius shall be established around
the intended target zone. The exercises
shall be conducted only when marine
mammals are observed to be outside the
buffer zone.
(C) At-sea BOMBEXs using live
ordnance shall occur during daylight
hours only.
(iii) Air-to-Surface Missile Exercises
(Explosive):
(A) Aircraft shall initially survey the
intended ordnance impact area for
marine mammals.
(B) During the actual firing of the
weapon, the aircraft involved must be
able to observe the intended ordnance
impact area to ensure the area is free of
marine mammal transiting the range.
(C) Visual inspection of the target area
shall be made by flying at 1,500 ft (457
m) altitude or lower, if safe to do so, and
at slowest safe speed.
(D) Explosive ordnance shall not be
targeted to impact within 1,800 yd
(1,646 m) of sighted marine mammals.
(iv) Mine Neutralization Training
Involving Underwater Detonations (up
to 20-lb charges):
(A) This activity shall only occur in
W–50 of the VACAPES Range Complex.
(B) Observers shall survey the Zone of
Influence (ZOI), a 700 yd (640 m) radius
from detonation location for marine
mammals from all participating vessels
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during the entire operation. A survey of
the ZOI (minimum of 3 parallel
tracklines 219 yd [200 m] apart) using
support craft shall be conducted at the
detonation location 30 minutes prior
through 30 minutes post detonation.
Aerial survey support shall be utilized
whenever assets are available.
(C) Detonation operations shall be
conducted during daylight hours only.
(D) If a marine mammal is sighted
within the ZOI, the animal shall be
allowed to leave of its own volition. The
Navy shall suspend detonation exercises
and ensure the area is clear of marine
mammals for a full 30 minutes prior to
detonation.
(E) Divers placing the charges on
mines and dive support vessel
personnel shall survey the area for
marine mammals and shall report any
sightings to the surface observers. These
animals shall be allowed to leave of
their own volition and the ZOI shall be
clear of marine mammals for 30 minutes
prior to detonation.
(F) No detonations shall take place
within 3.2 nm (6 km) of an estuarine
inlet (Chesapeake Bay Inlets).
(G) No detonations shall take place
within 1.6 nm (3 km) of shoreline.
(H) Personnel shall record any
protected species observations during
the exercise as well as measures taken
if species are detected within the ZOI.
(b) [Reserved]
§ 218.5 Requirements for monitoring and
reporting.
(a) The Holder of the Letter of
Authorization issued pursuant to
§ 216.106 of this chapter and § 218.7 for
activities described in § 218.1(c) is
required to cooperate with the NMFS
when monitoring the impacts of the
activity on marine mammals.
(b) The Holder of the Authorization
must notify NMFS immediately (or as
soon as clearance procedures allow) if
the specified activity identified in
§ 218.1(c) is thought to have resulted in
the mortality or serious injury of any
marine mammals, or in any take of
marine mammals not identified in
§ 218.2(c).
(c) The Navy must conduct all
monitoring and required reporting
under the Letter of Authorization,
including abiding by the VACAPES
Range Complex Monitoring Plan, which
is incorporated herein by reference, and
which requires the Navy to implement,
at a minimum, the monitoring activities
summarized below.
(1) Vessel or aerial surveys. (i) The
Holder of this Authorization shall
visually survey a minimum of 2
explosive events per year, one of which
shall be a multiple detonation event.
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One of the vessel or aerial surveys
should involve professionally trained
marine mammal observers (MMOs).
(ii) Where operationally feasible, for
specified training events, aerial or vessel
surveys shall be used 1–2 days prior to,
during (if reasonably safe), and 1–5 days
post detonation.
(iii) Surveys shall include any
specified exclusion zone around a
particular detonation point plus 2,000
yards beyond the border of the
exclusion zone (i.e., the circumference
of the area from the border of the
exclusion zone extending 2,000 yards
outwards). For vessel based surveys a
passive acoustic system (hydrophone or
towed array) could be used to determine
if marine mammals are in the area
before and/or after a detonation event.
(iv) When conducting a particular
survey, the survey team shall collect:
(A) Location of sighting;
(B) Species (if not possible, indicate
whale, dolphin or pinniped);
(C) Number of individuals;
(D) Whether calves were observed;
(E) Initial detection sensor;
(F) Length of time observers
maintained visual contact with marine
mammal;
(G) Wave height;
(H) Visibility;
(I) Whether sighting was before,
during, or after detonations/exercise,
and how many minutes before or after;
(J) Distance of marine mammal from
actual detonations (or target spot if not
yet detonated);
(K) Observed behavior—
Watchstanders shall report, in plain
language and without trying to
categorize in any way, the observed
behavior of the animal(s) (such as
animal closing to bow ride, paralleling
course/speed, floating on surface and
not swimming etc.), including speed
and direction;
(L) Resulting mitigation
implementation—Indicate whether
explosive detonations were delayed,
ceased, modified, or not modified due to
marine mammal presence and for how
long; and
(M) If observation occurs while
explosives are detonating in the water,
indicate munition type in use at time of
marine mammal detection.
(2) Passive acoustic monitoring—the
Navy shall conduct passive acoustic
monitoring when operationally feasible.
(i) Any time a towed hydrophone
array is employed during shipboard
surveys the towed array shall be
deployed during daylight hours for each
of the days the ship is at sea.
(ii) The towed hydrophone array shall
be used to supplement the ship-based
systematic line-transect surveys
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Jkt 217001
(particularly for species such as beaked
whales that are rarely seen).
(iii) The array shall have the
capability of detecting low frequency
vocalizations (<1,000 Hz) for baleen
whales and relatively high frequency
(up to 30 kHz) for odontocetes. The use
of two simultaneously deployed arrays
can also allow more accurate
localization and determination of diving
patterns.
(3) Marine mammal observers on
Navy platforms. (i) As required in
§ 218.5(c)(1), MMOs selected for aerial
or vessel survey shall be placed on a
Navy platform during one of the
explosive exercises being monitored per
year, the other designated exercise shall
be monitored by the Navy lookouts/
watchstanders.
(ii) The MMO must possess expertise
in species identification of regional
marine mammal species and experience
collecting behavioral data.
(iii) MMOs shall not be placed aboard
Navy platforms for every Navy training
event or major exercise, but during
specifically identified opportunities
deemed appropriate for data collection
efforts. The events selected for MMO
participation shall take into account
safety, logistics, and operational
concerns.
(iv) MMOs shall observe from the
same height above water as the
lookouts.
(v) The MMOs shall not be part of the
Navy’s formal reporting chain of
command during their data collection
efforts; Navy lookouts shall continue to
serve as the primary reporting means
within the Navy chain of command for
marine mammal sightings. The only
exception is that if an animal is
observed within the shutdown zone that
has not been observed by the lookout,
the MMO shall inform the lookout of the
sighting and the lookout shall take the
appropriate action through the chain of
command.
(vi) The MMOs shall collect species
identification, behavior, direction of
travel relative to the Navy platform, and
distance first observed. Information
collected by MMOs be the same as those
collected by Navy lookout/
watchstanders described in
§ 218.5(c)(1)(iv).
(d) The Navy shall complete an
Integrated Comprehensive Monitoring
Program (ICMP) Plan in 2009. This
planning and adaptive management tool
shall include:
(1) A method for prioritizing
monitoring projects that clearly
describes the characteristics of a
proposal that factor into its priority.
(2) A method for annually reviewing,
with NMFS, monitoring results, Navy
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28347
R&D, and current science to use for
potential modification of mitigation or
monitoring methods.
(3) A detailed description of the
Monitoring Workshop to be convened in
2011 and how and when Navy/NMFS
will subsequently utilize the findings of
the Monitoring Workshop to potentially
modify subsequent monitoring and
mitigation.
(4) An adaptive management plan.
(5) A method for standardizing data
collection for VACAPES Range Complex
and across range complexes.
(e) General Notification of Injured or
Dead Marine Mammals—Navy
personnel shall ensure that NMFS
(regional stranding coordinator) is
notified immediately (or as soon as
clearance procedures allow) if an
injured or dead marine mammal is
found during or shortly after, and in the
vicinity of, any Navy training exercise
utilizing underwater explosive
detonations. The Navy shall provide
NMFS with species or description of the
animal(s), the condition of the animal(s)
(including carcass condition if the
animal is dead), location, time of first
discovery, observed behaviors (if alive),
and photo or video (if available).
(f) Annual VACAPES Range Complex
Monitoring Plan Report—The Navy
shall submit a report annually on March
1 describing the implementation and
results (through January 1 of the same
year) of the VACAPES Range Complex
Monitoring Plan. Data collection
methods shall be standardized across
range complexes to allow for
comparison in different geographic
locations. Although additional
information will also be gathered, the
MMOs collecting marine mammal data
pursuant to the VACAPES Range
Complex Monitoring Plan shall, at a
minimum, provide the same marine
mammal observation data required in
the data required in § 218.5(g). The
VACAPES Range Complex Monitoring
Plan Report may be provided to NMFS
within a larger report that includes the
required Monitoring Plan Reports from
VACAPES Range Complex and multiple
range complexes.
(g) Annual VACAPES Range Complex
Exercise Report—The Navy shall
provide the information described
below for all of their explosive
exercises. Until the Navy is able to
report in full the information below,
they shall provide an annual update on
the Navy’s explosive tracking methods,
including improvements from the
previous year.
(1) Total annual number of each type
of explosive exercise (of those identified
as part of the ‘‘specified activity’’ in this
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final rule) conducted in the VACAPES
Range Complex.
(2) Total annual expended/detonated
rounds (missiles, bombs, etc.) for each
explosive type.
(h) VACAPES Range Complex 5-yr
Comprehensive Report—The Navy shall
submit to NMFS a draft report that
analyzes and summarizes all of the
multi-year marine mammal information
gathered during the VACAPES Range
Complex exercises for which annual
reports are required (Annual VACAPES
Range Complex Exercise Reports and
VACAPES Range Complex Monitoring
Plan Reports). This report shall be
submitted at the end of the fourth year
of the rule (May 2013), covering
activities that have occurred through
December 1, 2012.
(i) The Navy shall respond to NMFS’
comments and requests for additional
information or clarification on the
VACAPES Range Complex
Comprehensive Report, the Annual
VACAPES Range Complex Exercise
Report, or the Annual VACAPES Range
Complex Monitoring Plan Report (or the
multi-Range Complex Annual
Monitoring Plan Report, if that is how
the Navy chooses to submit the
information) if submitted within 3
months of receipt. These reports shall be
considered final after the Navy has
addressed NMFS’ comments or
provided the requested information, or
three months after the submittal of the
draft if NMFS does not comment by
then.
(j) In 2011, the Navy shall convene a
Monitoring Workshop in which the
Monitoring Workshop participants will
be asked to review the Navy’s
Monitoring Plans and monitoring results
and make individual recommendations
(to the Navy and NMFS) of ways of
improving the Monitoring Plans. The
recommendations shall be reviewed by
the Navy, in consultation with NMFS,
and modifications to the Monitoring
Plan shall be made, as appropriate.
§ 218.6 Applications for Letters of
Authorization.
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To incidentally take marine mammals
pursuant to these regulations in this
subpart, the U.S. citizen (as defined by
§ 216.103) conducting the activity
identified in § 218.1(c) (the U.S. Navy)
must apply for and obtain either an
initial Letter of Authorization in
accordance with § 218.7 or a renewal
under § 218.8.
§ 218.7
Letters of Authorization.
(a) A Letter of Authorization, unless
suspended or revoked, will be valid for
a period of time not to exceed the period
of validity of this subpart, but must be
VerDate Nov<24>2008
16:49 Jun 12, 2009
Jkt 217001
renewed annually subject to annual
renewal conditions in § 218.8.
(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).
§ 218.8 Renewal of Letters of
Authorization and adaptive management.
(a) A Letter of Authorization issued
under § 216.106 of this chapter and
§ 218.7 for the activity identified in
§ 218.1(c) will be renewed annually
upon:
(1) Notification to NMFS that the
activity described in the application
submitted under § 218.6 will be
undertaken and that there will not be a
substantial modification to the
described work, mitigation or
monitoring undertaken during the
upcoming 12 months;
(2) Timely receipt of the monitoring
reports required under § 218.5(c)
through (i); and
(3) A determination by NMFS that the
mitigation, monitoring and reporting
measures required under § 218.4 and the
Letter of Authorization issued under
§ 216.106 of this chapter and § 218.7,
were undertaken and will be undertaken
during the upcoming annual period of
validity of a renewed Letter of
Authorization.
(b) If a request for a renewal of a
Letter of Authorization issued under
§ 216.106 of this chapter and § 218.8
indicates that a substantial modification
to the described work, mitigation or
monitoring undertaken during the
upcoming season will occur, NMFS will
provide the public a period of 30 days
for review and comment on the request.
Review and comment on renewals of
Letters of Authorization are restricted
to:
(1) New cited information and data
indicating that the determinations made
in this document are in need of
reconsideration, and
(2) Proposed changes to the mitigation
and monitoring requirements contained
in these regulations or in the current
Letter of Authorization.
(c) A notice of issuance or denial of
a renewal of a Letter of Authorization
PO 00000
Frm 00022
Fmt 4701
Sfmt 4700
will be published in the Federal
Register.
(d) NMFS, in response to new
information and in consultation with
the Navy, may modify the mitigation or
monitoring measures in subsequent
LOAs if doing so creates a reasonable
likelihood of more effectively
accomplishing the goals of mitigation
and monitoring set forth in the preamble
of these regulations. Below are some of
the possible sources of new data that
could contribute to the decision to
modify the mitigation or monitoring
measures:
(1) Results from the Navy’s
monitoring from the previous year
(either from VACAPES Range Complex
or other locations).
(2) Findings of the Monitoring
Workshop that the Navy will convene in
2011 (§ 218.5(j)).
(3) Compiled results of Navy funded
research and development (R&D) studies
(presented pursuant to the ICMP
(§ 218.5(d)).
(4) Results from specific stranding
investigations (either from the VACAPE
Range Complex Study Area or other
locations, and involving coincident
explosives training or not involving
coincident use).
(5) Results from general marine
mammal and sound research (funded by
the Navy or otherwise).
(6) Any information which reveals
that marine mammals may have been
taken in a manner, extent or number not
authorized by these regulations or
subsequent Letters of Authorization.
§ 218.9 Modifications to Letters of
Authorization.
(a) Except as provided in paragraph
(b) of this section, no substantive
modification (including withdrawal or
suspension) to the Letter of
Authorization by NMFS, issued
pursuant to § 216.106 of this chapter
and § 218.7 and subject to the
provisions of this subpart shall be made
until after notification and an
opportunity for public comment has
been provided. For purposes of this
paragraph, a renewal of a Letter of
Authorization under § 218.8, without
modification (except for the period of
validity), is not considered a substantive
modification.
(b) If the Assistant Administrator
determines that an emergency exists
that poses a significant risk to the wellbeing of the species or stocks of marine
mammals specified in § 218.2(c), a
Letter of Authorization issued pursuant
to § 216.106 of this chapter and § 218.7
may be substantively modified without
prior notification and an opportunity for
public comment. Notification will be
E:\FR\FM\15JNR2.SGM
15JNR2
Federal Register / Vol. 74, No. 113 / Monday, June 15, 2009 / Rules and Regulations
published in the Federal Register
within 30 days subsequent to the action.
[FR Doc. E9–13697 Filed 6–8–09; 4:15 pm]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 218
RIN 0648–AW79
Taking and Importing Marine
Mammals; U.S. Navy Training in the
Jacksonville Range Complex
pwalker on PROD1PC71 with RULES2
AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
SUMMARY: NMFS, upon application from
the U.S. Navy (Navy), is issuing
regulations to govern the unintentional
taking of marine mammals incidental to
activities conducted off the Charleston/
Jacksonville (JAX) Range Complex for
the period of June 2009 through June
2014. The Navy’s activities are
considered military readiness activities
pursuant to the Marine Mammal
Protection Act (MMPA), as amended by
the National Defense Authorization Act
for Fiscal Year 2004 (NDAA). These
regulations, which allow for the
issuance of ‘‘Letters of Authorization’’
(LOAs) for the incidental take of marine
mammals during the described activities
and specified timeframes, prescribe the
permissible methods of taking and other
means of effecting the least practicable
adverse impact on marine mammal
species and their habitat, as well as
requirements pertaining to the
monitoring and reporting of such taking.
DATES: Effective June 8, 2009 and is
applicable to the Navy on June 5, 2009
through June 4, 2014.
ADDRESSES: A copy of the Navy’s
application (which contains a list of the
references used in this document),
NMFS’ Record of Decision (ROD), and
other documents cited herein may be
obtained by writing to Michael Payne,
Chief, Permits, Conservation and
Education Division, Office of Protected
Resources, National Marine Fisheries
Service, 1315 East-West Highway, Silver
Spring, MD 20910–3225 or by telephone
via the contact listed here (see FOR
FURTHER INFORMATION CONTACT).
FOR FURTHER INFORMATION CONTACT:
Shane Guan, Office of Protected
Resources, NMFS, (301) 713–2289, ext.
137.
VerDate Nov<24>2008
16:49 Jun 12, 2009
Jkt 217001
Extensive
supplementary information was
provided in the proposed rule for this
activity, which was published in the
Federal Register on Wednesday,
December 17, 2008 (73 FR 76578). This
information will not be reprinted here
in its entirety; rather, all sections from
the proposed rule will be represented
herein and will contain either a
summary of the material presented in
the proposed rule or a note referencing
the page(s) in the proposed rule where
the information may be found. Any
information that has changed since the
proposed rule was published will be
addressed herein. Additionally, this
final rule contains a section that
responds to the comments received
during the public comment period.
SUPPLEMENTARY INFORMATION:
Background
Sections 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1361 et seq.) direct
the Secretary of Commerce (Secretary)
to allow, upon request, the incidental,
but not intentional taking of marine
mammals by U.S. citizens who engage
in a specified activity (other than
commercial fishing) during periods of
not more than five consecutive years
each if certain findings are made and
regulations are issued or, if the taking is
limited to harassment and of no more
than 1 year, the Secretary shall issue a
notice of proposed authorization for
public review.
Authorization shall be granted if
NMFS finds that the taking will have a
negligible impact on the species or
stock(s), will not have an unmitigable
adverse impact on the availability of the
species or stock(s) for subsistence uses,
and if the permissible methods of taking
and requirements pertaining to the
mitigation, monitoring and reporting of
such taking are set forth.
NMFS has defined ‘‘negligible
impact’’ in 50 CFR 216.103 as:
An impact resulting from the specified
activity that cannot be reasonably expected
to, and is not reasonably likely to, adversely
affect the species or stock through effects on
annual rates of recruitment or survival.
The NDAA (Pub. L. 108–136)
removed the ‘‘small numbers’’ and
‘‘specified geographical region’’
limitations and amended the definition
of ‘‘harassment’’ as it applies to a
‘‘military readiness activity’’ to read as
follows (Section 3(18)(B) of the MMPA):
(i) Any act that injures or has the
significant potential to injure a marine
mammal or marine mammal stock in the wild
[Level A Harassment]; or (ii) any act that
disturbs or is likely to disturb a marine
mammal or marine mammal stock in the wild
by causing disruption of natural behavioral
patterns, including, but not limited to,
PO 00000
Frm 00023
Fmt 4701
Sfmt 4700
28349
migration, surfacing, nursing, breeding,
feeding, or sheltering, to a point where such
behavioral patterns are abandoned or
significantly altered [Level B Harassment].
Summary of Request
On March 17, 2008, NMFS received
an application from the Navy requesting
authorization for the take of six species
of cetaceans incidental to the proposed
training activities in the JAX Range
Complex over the course of 5 years. On
November 7, 2008, the Navy submitted
an Addendum with some modifications
and additional information to its
original request. These training
activities are classified as military
readiness activities. The Navy states that
these training activities may cause
various impacts to marine mammal
species in the proposed JAX Range
Complex area. The Navy requests an
authorization to take individuals of
these cetacean species by Level B
Harassment. Further, the Navy requests
authorization to take 2 individual
Atlantic spotted dolphins per year by
injury incidental to the proposed
training activities in the JAX Range
Complex. Please refer to Table 5 of this
document for detailed information of
the potential exposures from explosive
ordnance (per year) for marine
mammals in the JAX Range Complex.
However, due to the proposed
mitigation and monitoring measures,
NMFS does not expect the proposed
action would result in any marine
mammal mortality. Therefore, no
mortality would be authorized for the
Navy’s JAX Range Complex training
activities.
Background of Navy Request
The proposed rule contains a
description of the Navy’s mission, their
responsibilities pursuant to Title 10 of
the United States Code, and the specific
purpose and need for the activities for
which they requested incidental take
authorization. The description
contained in the proposed rule has not
changed (73 FR 76578; December 17,
2008).
Description of the Specified Activities
The proposed rule contains a
complete description of the Navy’s
specified activities that are covered by
these final regulations, and for which
the associated incidental take of marine
mammals will be authorized in the
related LOAs. The proposed rule
describes the nature and number of the
training activities. These training
activities consist of surface warfare
[Missile Exercise (MISSILEX)], mine
warfare [Mine Exercises (MINEX)],
amphibious warfare [Firing Exercise
E:\FR\FM\15JNR2.SGM
15JNR2
Agencies
[Federal Register Volume 74, Number 113 (Monday, June 15, 2009)]
[Rules and Regulations]
[Pages 28328-28349]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-13697]
[[Page 28327]]
-----------------------------------------------------------------------
Part II
Department of Commerce
-----------------------------------------------------------------------
National Oceanic and Atmospheric Administration
-----------------------------------------------------------------------
50 CFR Part 218
Taking and Importing Marine Mammals; U.S. Navy Training in the Virginia
Capes Range Complex, Taking and Importing Marine Mammals; U.S. Navy
Training in the Jacksonville Range Complex, Taking and Importing Marine
Mammals; U.S. Navy Training in the Cherry Point Range Complex; Final
Rules
Federal Register / Vol. 74 , No. 113 / Monday, June 15, 2009 / Rules
and Regulations
[[Page 28328]]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 218
RIN 0648-AW78
Taking and Importing Marine Mammals; U.S. Navy Training in the
Virginia Capes Range Complex
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS, upon application from the U.S. Navy (Navy), is issuing
regulations to govern the unintentional taking of marine mammals
incidental to activities conducted at the Virginia Capes (VACAPES)
Range Complex for the period of June 2009 through June 2014. The Navy's
activities are considered military readiness activities pursuant to the
Marine Mammal Protection Act (MMPA), as amended by the National Defense
Authorization Act for Fiscal Year 2004 (NDAA). These regulations, which
allow for the issuance of ``Letters of Authorization'' (LOAs) for the
incidental take of marine mammals during the described activities and
specified timeframes, prescribe the permissible methods of taking and
other means of effecting the least practicable adverse impact on marine
mammal species and their habitat, as well as requirements pertaining to
the monitoring and reporting of such taking.
DATES: Effective June 8, 2009 and is applicable to the Navy on June 5,
2009 through June 4, 2014.
ADDRESSES: A copy of the Navy's application (which contains a list of
the references used in this document), NMFS' Record of Decision (ROD),
and other documents cited herein may be obtained by writing to Michael
Payne, Chief, Permits, Conservation and Education Division, Office of
Protected Resources, National Marine Fisheries Service, 1315 East-West
Highway, Silver Spring, MD 20910-3225 or by telephone via the contact
listed here (see FOR FURTHER INFORMATION CONTACT). Additionally, the
Navy's LOA application may be obtained by visiting the Internet at:
https://www.nmfs.noaa.gov/pr/permits/incidental.htm#applications.
FOR FURTHER INFORMATION CONTACT: Shane Guan, Office of Protected
Resources, NMFS, (301) 713-2289, ext. 137.
SUPPLEMENTARY INFORMATION:
Extensive Supplementary Information was provided in the proposed
rule for this activity, which was published in the Federal Register on
Friday, December 12, 2008 (73 FR 75631). This information will not be
reprinted here in its entirety; rather, all sections from the proposed
rule will be represented herein and will contain either a summary of
the material presented in the proposed rule or a note referencing the
page(s) in the proposed rule where the information may be found. Any
information that has changed since the proposed rule was published will
be addressed herein. Additionally, this final rule contains a section
that responds to the comments received during the public comment
period.
Background
Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.)
direct the Secretary of Commerce (Secretary) to allow, upon request,
the incidental, but not intentional taking of marine mammals by U.S.
citizens who engage in a specified activity (other than commercial
fishing) during periods of not more than five consecutive years each if
certain findings are made and regulations are issued or, if the taking
is limited to harassment, notice of a proposed authorization is
provided to the public for review.
Authorization shall be granted if NMFS finds that the taking will
have a negligible impact on the species or stock(s), will not have an
unmitigable adverse impact on the availability of the species or
stock(s) for subsistence uses, and if the permissible methods of taking
and requirements pertaining to the mitigation, monitoring and reporting
of such taking are set forth.
NMFS has defined ``negligible impact'' in 50 CFR 216.103 as:
An impact resulting from the specified activity that cannot be
reasonably expected to, and is not reasonably likely to, adversely
affect the species or stock through effects on annual rates of
recruitment or survival.
The NDAA (Pub. L. 108-136) removed the ``small numbers'' and
``specified geographical region'' limitations and amended the
definition of ``harassment'' as it applies to a ``military readiness
activity'' to read as follows (Section 3(18)(B) of the MMPA):
(i) Any act that injures or has the significant potential to
injure a marine mammal or marine mammal stock in the wild [Level A
Harassment]; or
(ii) Any act that disturbs or is likely to disturb a marine
mammal or marine mammal stock in the wild by causing disruption of
natural behavioral patterns, including, but not limited to,
migration, surfacing, nursing, breeding, feeding, or sheltering, to
a point where such behavioral patterns are abandoned or
significantly altered [Level B Harassment].
Summary of Request
On March 17, 2008, NMFS received an application from the Navy
requesting authorization for the take of 13 cetacean species incidental
to the proposed training activities in the VACAPES Range Complex over
the course of 5 years. These training activities are classified as
military readiness activities. The Navy states that these training
activities may cause various impacts to marine mammal species in the
proposed VACAPES Range Complex area. The Navy requests an authorization
to take individuals of these cetacean species by Level B Harassment.
Further, the Navy requests authorization to take 1 individual Atlantic
spotted, 20 common, 1 pantropical spotted, and 3 striped dolphins per
year by injury, and 1 individual common dolphin per year by mortality,
as a result of the proposed training activities in the VACAPES Range
Complex. Please refer to Table 29 of the LOA application for detailed
information of the potential exposures from explosive ordnance (per
year) for marine mammals in the VACAPES Range Complex. However, due to
the proposed mitigation and monitoring measures, NMFS does not expect
that the proposed action would result in any marine mammal mortality.
Therefore, no mortality would be authorized for the Navy's VACAPES
Range Complex training activities.
Background of Navy Request
The proposed rule contains a description of the Navy's mission,
their responsibilities pursuant to Title 10 of the United States Code,
and the specific purpose and need for the activities for which they
requested incidental take authorization. The description contained in
the proposed rule has not changed (73 FR 75631; December 12, 2008).
Description of the Specified Activities
The proposed rule contains a complete description of the Navy's
specified activities that are covered by these final regulations, and
for which the associated incidental take of marine mammals will be
authorized in the related LOAs. The proposed rule describes the nature
and number of the training activities. These training activities
consist of surface warfare [Missile Exercise (MISSILEX) and High-speed
Anti-Radiation Missile Exercise (HARMEX)], mine warfare [Mine Exercises
(MINEX)], amphibious warfare
[[Page 28329]]
[Firing Exercise (FIREX)], strike warfare [Bombing Exercise (BOMBEX)],
and vessel movement to, from and within the VACAPES Range Complex Study
Area. The narrative description of the action contained in the proposed
rule has not changed. Table 1 summarizes the nature and levels of these
planned activities.
Table 1--Levels of Training Events Involve Explosives Planned in the VACAPES Range Complex Per Year
----------------------------------------------------------------------------------------------------------------
Operation Platform System/ordnance Number of events Duration per event
----------------------------------------------------------------------------------------------------------------
Missile Exercise (MISSILEX) (Air MH-60S, HH-60H.... AGM-114 (Hellfire 60 sorties (60 1 hour.
to Surface). missile). missiles).
F/A-18, P-3C, and AGM-65 E/F 20 sorties (20 1 hour.
P-8A. (Maverick missiles).
missile).
Bombing Exercise (BOMBEX) (Air- F/A-18............ MK-83/GBU-32 5 events (20 1 hour.
to-Surface, At-Sea). [1,000 lb High bombs, 4 bombs/
Explosive (HE) event).
bomb].
Mine Neutralization............. MH-60S............ AMNS.............. 140 sorties (30 1.5 hours.
rounds).
EOD............... 20 lb charges..... 24 events......... 6-8 hours.
FIREX with IMPASS............... CG, DDG........... 5'' gun (IMPASS).. 22 events (858 HE 8 hours.
rounds, 39 HE per
event)).
----------------------------------------------------------------------------------------------------------------
VACAPES Range Complex
The VACAPES Range Complex proposed rule contains a description of
the VACAPES Study Area along with a description of the areas in which
certain types of activities will occur. Table 2, included here,
summarizes the areas in which explosive events will occur and their
frequency of occurrence. The description of the VACAPES Range Complex
Study Area in the proposed rule has not changed.
Table 2--Number of Events Utilizing Munitions within the VACAPES Range Complex
----------------------------------------------------------------------------------------------------------------
Annual
Sub-area Ordnance Winter Spring Summer Fall totals
----------------------------------------------------------------------------------------------------------------
MISSILEX............. ......... ......... ......... ......... 80
Air-K............................. Hellfire............. 11.25 11.25 11.25 11.25 .........
W-72A (2)......................... Hellfire............. 3.75 3.75 3.75 3.75 .........
Air-K............................. Maverick............. 5 5 5 5 .........
FIREX................ ......... ......... ......... ......... 22
5C/D.............................. 5'' rounds........... 1.83 1.83 1.83 1.83 .........
7C/D and 8C/D..................... 5'' rounds........... 1.83 1.83 1.83 1.83 .........
1C1/2............................. 5'' rounds........... 1.83 1.83 1.83 1.83 .........
MINEX................ ......... ......... ......... ......... 54
W-50 UNDET........................ 5 LB*................ 7.50 7.50 7.50 7.50 .........
W-50 UNDET........................ 20 LB................ 4.00 4.00 12.00 4.00 .........
BOMBEX............... ......... ......... ......... ......... 5
Air-K............................. MK-83**.............. 1.25 1.25 1.25 1.25 .........
----------------------------------------------------------------------------------------------------------------
* The use of 3.24 lb charges during AMNS training were conservatively modeled as 5 lb charges.
** One event using the MK-83 bombs consists of 4 bombs being dropped in succession. For example, in VACAPES Air-
K there are 5 MK-83 events, which mean that a total of 20 bombs will be dropped per year.
Description of Marine Mammals in the Area of the Specified Activities
There are 34 marine mammal species with possible or confirmed
occurrence in the VACAPES Range Complex. As indicated in Table 3, there
are 33 cetacean species (7 mysticetes and 26 odontocetes) and one
pinniped species. Table 6 also includes the federal status of these
marine mammal species. Six marine mammal species listed as federally
endangered under the Endangered Species Act (ESA) occur in the VACAPES
Range Complex: the humpback whale, North Atlantic right whale, sei
whale, fin whale, blue whale, and sperm whale. Although it is possible
that any of the 34 species of marine mammals may occur in the VACAPES
Range Complex, only 24 of those species are expected to occur regularly
in the region. The proposed rule also includes a discussion of the
methods used to estimate marine mammal density in the VACAPES Study
Area. The Description of Marine Mammals in the Area of the Specified
Activities section has not changed from what was in the proposed rule
(73 FR 75631, pages 75635-75636).
Table 3--Marine Mammal Species Found in the VACAPES Range Complex
------------------------------------------------------------------------
Family and scientific name Common name Federal status
------------------------------------------------------------------------
Order Cetacea
------------------------------------------------------------------------
Suborder Mysticeti (baleen whales)
------------------------------------------------------------------------
Eubalaena glacialis............. North Atlantic Endangered.
right whale.
Megaptera novaeangliae.......... Humpback whale.... Endangered.
Balaenoptera acutorostrata...... Minke whale. ..................
[[Page 28330]]
B. brydei....................... Bryde's whale. ..................
B. borealis..................... Sei whale......... Endangered.
B. physalus..................... Fin whale......... Endangered.
B. musculus..................... Blue whale........ Endangered.
------------------------------------------------------------------------
Suborder Odontoceti (toothed whales)
------------------------------------------------------------------------
Physeter macrocephalus.......... Sperm whale Endangered.
Kogia breviceps................. Pygmy sperm whale. ..................
K. sima......................... Dwarf sperm whale. ..................
Ziphius cavirostris............. Cuvier's beaked ..................
whale.
Mesoplodon minus................ True's beaked ..................
whale.
M. europaeus.................... Gervais' beaked ..................
whale.
M. bidens....................... Sowerby's beaked ..................
whale.
M. densirostris................. Blainville's ..................
beaked whale.
Steno bredanensis............... Rough-toothed ..................
dolphin.
Tursiops truncatus.............. Bottlenose ..................
dolphin.
Stenella attenuata.............. Pantropical ..................
spotted dolphin.
S. frontalis.................... Atlantic spotted ..................
dolphin.
S. longirostris................. Spinner dolphin. ..................
S. clymene...................... Clymene dolphin. ..................
S. coeruleoalba................. Striped dolphin. ..................
Delphinus delphis............... Common dolphin. ..................
Lagenodephis hosei.............. Fraser's dolphin. ..................
Lagenorhynchus acutus........... Atlantic white- ..................
sided dolphin.
Grampus griseus................. Risso's dolphin. ..................
Peponocephala electra........... Melon-headed ..................
whale.
Feresa attenuata................ Pygmy killer ..................
whale.
Pseudorca crassidens............ False killer ..................
whale.
Orcinus orca.................... Killer whale. ..................
Globicephala melas.............. Long-finned pilot ..................
whale.
G. macrorhynchus................ Short-finned pilot ..................
whale.
Phocoena phocoena............... Harbor porpoise. ..................
------------------------------------------------------------------------
Order Carnivora
------------------------------------------------------------------------
Suborder Pinnipedia
------------------------------------------------------------------------
Phoca vitulina.................. Harbor seal. ..................
------------------------------------------------------------------------
Suborder Sirenia
------------------------------------------------------------------------
Trichechus manatus.............. West Indian ..................
manatee.
------------------------------------------------------------------------
Potential Impacts to Marine Mammal Species
With respect to the MMPA, NMFS' effects assessment serves four
primary purposes: (1) to prescribe the permissible methods of taking
(i.e., Level B Harassment (behavioral harassment), Level A Harassment
(injury), or mortality, including an identification of the number and
types of take that could occur by Level A or B harassment or mortality)
and to prescribe other means of effecting the least practicable adverse
impact on such species or stock and its habitat (i.e., mitigation); (2)
to determine whether the specified activity will have a negligible
impact on the affected species or stocks of marine mammals (based on
the likelihood that the activity will adversely affect the species or
stock through effects on annual rates of recruitment or survival); (3)
to determine whether the specified activity will have an unmitigable
adverse impact on the availability of the species or stock(s) for
subsistence uses (however, there are no subsistence communities in the
VACAPES study area); and (4) to prescribe requirements pertaining to
monitoring and reporting.
In the Potential Impacts to Marine Mammal Species section of the
proposed rule, NMFS included a qualitative discussion of the different
ways that underwater explosive detonations from MISSILEX, BOMBEX,
MINEX, and FIREX may potentially affect marine mammals (some of which
NMFS would not classify as harassment). See 73 FR 75631; December 12,
2008; pages 75636-75646. Marine mammals may experience direct
physiological effects (such as threshold shift), acoustic masking,
impaired communications, stress responses, and behavioral disturbance.
The information contained in Potential Impacts to Marine Mammal Species
section from MISSILEX, BOMBEX, MINEX, and FIREX from the proposed rule
has not changed.
The information pertaining to HARMEX has changed from the Proposed
Rule. Further analyses show that HARMEX would have no effects on marine
mammals because these types of missiles detonate 30-60 ft (9.1-18.3 m)
above the water surface. Therefore, they are not included in the
underwater explosive exposure modeling in the Final Rule since no
marine mammal exposures are anticipated.
Later, in the Estimated Take of Marine Mammals Section, NMFS
relates and quantifies the potential effects to marine mammals from
underwater detonation of explosives discussed here to the MMPA
definitions of Level A and Level B Harassment. NMFS has also considered
the effects of mortality on
[[Page 28331]]
these species, although mortality is neither expected, nor will it be
authorized.
Additional analyses on potential impacts to marine mammals from
vessel movement within the VACAPES Range Complex Study Area are added
below.
Vessel Movement
There are limited data concerning marine mammal behavioral
responses to vessel traffic and vessel noise, and a lack of consensus
among scientists with respect to what these responses mean or whether
they result in short-term or long-term adverse effects. In those cases
where there is a busy shipping lane or where there is large amount of
vessel traffic, marine mammals may experience acoustic masking
(Hildebrand, 2005) if they are present in the area (e.g., killer whales
in Puget Sound; Foote et al., 2004; Holt et al., 2008). In cases where
vessels actively approach marine mammals (e.g., whale watching or
dolphin watching boats), scientists have documented that animals
exhibit altered behavior such as increased swimming speed, erratic
movement, and active avoidance behavior (Bursk, 1983; Acevedo, 1991;
Baker and MacGibbon, 1991; Trites and Bain, 2000; Williams et al.,
2002; Constantine et al., 2003), reduced blow interval (Ritcher et al.,
2003), disruption of normal social behaviors (Lusseau, 2003; 2006), and
the shift of behavioral activities which may increase energetic costs
(Constantine et al., 2003; 2004)). A detailed review of marine mammal
reactions to ships and boats is available in Richardson et al. (1995).
For each of the marine mammals taxonomy groups, Richardson et al.
(1995) provided the following assessment regarding cetacean reactions
to vessel traffic:
Toothed whales: ``In summary, toothed whales sometimes show no
avoidance reaction to vessels, or even approach them. However,
avoidance can occur, especially in response to vessels of types used to
chase or hunt the animals. This may cause temporary displacement, but
we know of no clear evidence that toothed whales have abandoned
significant parts of their range because of vessel traffic.''
Baleen whales: ``When baleen whales receive low-level sounds from
distant or stationary vessels, the sounds often seem to be ignored.
Some whales approach the sources of these sounds. When vessels approach
whales slowly and nonaggressively, whales often exhibit slow and
inconspicuous avoidance maneuvers. In response to strong or rapidly
changing vessel noise, baleen whales often interrupt their normal
behavior and swim rapidly away. Avoidance is especially strong when a
boat heads directly toward the whale.''
It is important to recognize that behavioral responses to stimuli
are complex and influenced to varying degrees by a number of factors
such as species, behavioral contexts, geographical regions, source
characteristics (moving or stationary, speed, direction, etc.), prior
experience of the animal, and physical status of the animal. For
example, studies have shown that beluga whales reacted differently when
exposed to vessel noise and traffic. In some cases, na[iuml]ve beluga
whales exhibited rapid swimming from ice-breaking vessels up to 80 km
away, and showed changes in surfacing, breathing, diving, and group
composition in the Canadian high Arctic where vessel traffic is rare
(Finley et al., 1990). In other cases, beluga whales were more tolerant
of vessels, but differentially responsive by reducing their calling
rates, to certain vessels and operating characteristics (especially
older animals) in the St. Lawrence River where vessel traffic is common
(Blane and Jaakson, 1994). In Bristol Bay, Alaska, beluga whales
continued to feed when surrounded by fishing vessels and resisted
dispersal even when purposefully harassed (Fish and Vania, 1971).
In reviewing more than 25 years of whale observation data, Watkins
(1986) concluded that whale reactions to vessel traffic were ``modified
by their previous experience and current activity: habituation often
occurred rapidly, attention to other stimuli or preoccupation with
other activities sometimes overcame their interest or wariness of
stimuli.'' Watkins noticed that over the years of exposure to ships in
the Cape Cod area, minke whales (Balaenoptera acutorostrata) changed
from frequent positive (such as approaching vessels) interest to
generally uninterested reactions; finback whales (B. physalus) changed
from mostly negative (such as avoidance) to uninterested reactions;
right whales (Eubalaena glacialis) apparently continued the same
variety of responses (negative, uninterested, and positive responses)
with little change; and humpbacks (Megaptera novaeangliae) dramatically
changed from mixed responses that were often negative to often strongly
positive reactions. Watkins (1986) summarized that ``whales near shore,
even in regions with low vessel traffic, generally have become less
wary of boats and their noises, and they have appeared to be less
easily disturbed than previously. In particular locations with intense
shipping and repeated approaches by boats (such as the whale-watching
areas of Stellwagen Bank), more and more whales had P [positive]
reactions to familiar vessels, and they also occasionally approached
other boats and yachts in the same ways.''
In the case of the VACAPES Range Complex, naval vessel traffic is
expected to be much lower than in areas where there are large shipping
lanes and large numbers of fishing vessels and/or recreational vessels.
Nevertheless, the proposed action area is well traveled by a variety of
commercial and recreational vessels, so marine mammals in the area are
expected to be habituated to vessel noise.
As described in the proposed rule, operations involving vessel
movements occur intermittently and are variable in duration, ranging
from a few hours up to 2 weeks. These operations are widely dispersed
throughout the VACAPES Range Complex OPAREA, which is a vast area
encompassing 27,661 square nautical miles (nm\2\) (an area
approximately the size of Indiana). The Navy logs about 1,400 total
vessel days within the Study Area during a typical year. Consequently,
the density of ships within the Study Area at any given time is
extremely low (i.e., less than 0.0004 ships/nm\2\).
Moreover, naval vessels transiting the study area or engaging in
the training exercises will not actively or intentionally approach a
marine mammal or change speed drastically. Except under certain
mitigation measures that protect right whales and other marine mammals
from vessel strike, all vessels transit to, from, and within the range
complexes will be traveling at speeds generally ranging from 10 to 14
knots.
The final rule contains additional mitigation measures requiring
Navy vessels to keep at least 500 yards (460 m) away from any observed
whale and at least 200 yards (183 m) from marine mammals other than
whales, and avoid approaching animals head-on. Although the radiated
sound from the vessels will be audible to marine mammals over a large
distance, it is unlikely that animals will respond behaviorally to low-
level distant shipping noise as the animals in the area are likely to
be habituated to such noises (Nowacek et al., 2004). In light of these
facts, NMFS does not expect the Navy's vessel movements to result in
Level B harassment.
Mitigation
In order to issue an incidental take authorization (ITA) under
Section 101(a)(5)(A) of the MMPA, NMFS must prescribe regulations
setting forth the
[[Page 28332]]
``permissible methods of taking pursuant to such activity, and other
means of effecting the least practicable adverse impact on such species
or stock and its habitat, paying particular attention to rookeries,
mating grounds, and areas of similar significance.'' The NDAA amended
the MMPA as it relates to military readiness activities and the
incidental take authorization process such that ``least practicable
adverse impact'' shall include consideration of personnel safety,
practicality of implementation, and impact on the effectiveness of the
``military readiness activity.'' The VACAPES Range Complex training
activities described in the proposed rule are considered military
readiness activities.
NMFS reviewed the Navy's proposed VACAPES Range Complex training
activities and the proposed VACAPES Range Complex mitigation measures
presented in the Navy's application to determine whether the activities
and mitigation measures were capable of achieving the least practicable
adverse effect on marine mammals.
Any mitigation measure prescribed by NMFS should be known to
accomplish, have a reasonable likelihood of accomplishing (based on
current science), or contribute to the accomplishment of one or more of
the general goals listed below:
(1) Avoidance or minimization of injury or death of marine mammals
wherever possible (goals b, c, and d 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
underwater detonations or other activities expected to result in the
take of marine mammals (this goal may contribute to a, above, or to
reducing harassment takes only).
(3) A reduction in the number of times (total number or number at
biologically important time or location) individuals would be exposed
to underwater detonations or other activities expected to result in the
take of marine mammals (this goal may contribute to a, above, or to
reducing harassment takes only).
(4) A reduction in the intensity of exposures (either total number
or number at biologically important time or location) to underwater
detonations or other activities expected to result in the take of
marine mammals (this goal may contribute to a, above, or to reducing
the severity of harassment takes only).
(5) A reduction in adverse effects to marine mammal habitat, paying
special attention to the food base, activities that block or limit
passage to or from biologically important areas, permanent destruction
of habitat, or temporary destruction/disturbance of habitat during a
biologically important time.
(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 (shut-down zone, etc.).
NMFS reviewed the Navy's proposed mitigation measures, which
included a careful balancing of the likely benefit of any particular
measure to the marine mammals with the likely effect of that measure on
personnel safety, practicality of implementation, and impact on the
``military-readiness activity.''
The Navy's proposed mitigation measures were described in detail in
the proposed rule (73 FR 75631, pages 75646-75649). The Navy's measures
address personnel training, lookout and watchstander responsibilities,
operating procedures for training activities using underwater
detonations of explosives and firing exercises, and mitigation related
to vessel traffic and the North Atlantic right whale. No changes have
been made to the mitigation measures described in the proposed rule
except as noted below.
Regarding nighttime monitoring in the Personnel Training Lookouts
section (73 FR 25631, page 25647), slight wording changes have been
made for Bullet 6 to read: ``At night, to increase effectiveness,
lookouts would not continuously sweep the horizon with their eyes.
Instead, lookouts would scan the horizon in a series of movements that
would allow their eyes to come to periodic rests as they scan the
sector. When visually searching at night, they would look a little to
one side and out of the corners of their eyes, paying attention to the
things on the outer edges of their field of vision. Lookouts will also
have night vision devices available for use.''
For mitigation measures under FIREX (73 FR 25631, page 25648),
corrections were made to reduce the buffer zone from 640 yards (585 m)
to 600 yards (548 m). Therefore, Bullets 3 and 4 of the FIREX
mitigation measure read as:
3. ``Big Eyes'' on the ship will be used to monitor a 600 yd
(548 m) buffer zone around the target area for marine mammals during
naval-gunfire events. Due to the distance between the firing
position and the buffer zone, lookouts are only expected to visually
detect breaching whales, whale blows, and large pods of dolphins and
porpoises.
4. Ships will not fire on the target if marine mammals are
detected within or approaching the 600 yd (548 m) buffer zone. If
marine mammals are present, operations would be suspended. Visual
observation will occur for approximately 45 minutes, or until the
animal has been observed to have cleared the area and is heading
away from the buffer zone.
For mitigation measures under MINEX (73 FR 25631, page 25649),
corrections were made to increase the buffer zone from 656 yards (600
m) to 700 yards (640 m). Therefore, Bullet 2 of the MINEX mitigation
measure reads as:
2. Observers will survey the Zone of Influence (ZOI), a 700 yd
(640 m) radius from detonation location, for marine mammals from all
participating vessels during the entire operation. A survey of the
ZOI (minimum of 3 parallel tracklines 219 yd [200 m] apart) using
support craft will be conducted at the detonation location 30
minutes prior through 30 minutes post detonation. Aerial survey
support will be utilized whenever assets are available.
The buffer zones for FIREX and MINEX activities were incorrectly
noticed in the proposed rule for the VACAPES Range Complex. NMFS has
consulted with the Navy and the Navy has stated that the buffer zones
should be corrected to ensure consistency for all Navy FIREX and MINEX
activities across multiple range complexes. The buffer zones identified
in this final rule are consistent with those established in the
Southern California Range Complex final rule (74 FR 2882; January 21,
2009). NMFS does not believe that a decrease in the FIREX buffer zone
of 40 yards would affect, in any significant way, the Navy's ability to
detect marine mammals or provide adequate protection to marine mammals
that may be in the vicinity of a FIREX activity. Moreover, an increase
in the MINEX buffer zone will further minimize any adverse effects that
marine mammals could experience as a result of the MINEX activity.
In response to a comment from the Marine Mammal Commission, NMFS
will require the Navy to suspend its activities immediately if a marine
mammal is injured or killed as a result of the proposed Navy training
activities (e.g., instances in which it is clear that munitions
explosions caused the injury or death), the Navy shall suspend its
activities immediately and report such incident to NMFS.
In addition, regarding the North Atlantic right whale (NARW) vessel
collision measures, NMFS expanded the final rule to include vessel
collision avoidance measures for the South Atlantic and the Northeast
Atlantic to be consistent with the U.S. Navy's Atlantic Fleet Active
Sonar Training (AFAST) rule. Although the VACAPES Range Complex is
outside the South Atlantic
[[Page 28333]]
and the Northeast Atlantic region, the Navy is required to comply with
the same ship collision measures while transiting and conducting
exercises within specific NARW areas along the East Coast. The specific
vessel collision measures in the Northeast Atlantic region are listed
in the regulatory text of the final rule.
NMFS has determined that these mitigation measures (which include a
suite of measures that specifically address vessel transit and the
NARW) are adequate means of effecting the least practicable adverse
impacts on marine mammal species or stocks and their habitat while also
considering personnel safety, practicality of implementation, and
impact on the effectiveness of the military readiness activity.
Monitoring
In order to issue an ITA for an activity, Section 101(a)(5)(A) of
the MMPA states that NMFS must set forth ``requirements pertaining to
the monitoring and reporting of such taking.'' The MMPA implementing
regulations at 50 CFR 216.104 (a)(13) indicate that requests for LOAs
must include the suggested means of accomplishing the necessary
monitoring and reporting that will result in increased knowledge of the
species and of the level of taking or impacts on populations of marine
mammals that are expected to be present.
Monitoring measures prescribed by NMFS should accomplish one or
more of the following general goals:
(1) An increase in the probability of detecting marine mammals,
both within the safety zone (thus allowing for more effective
implementation of the mitigation) and in general to generate more data
to contribute to the effects analyses.
(2) An increase in our understanding of how many marine mammals are
likely to be exposed to levels of underwater detonations or other
stimuli that we associate with specific adverse effects, such as
behavioral harassment, temporary threshold shift of hearing sensitivity
(TTS), or permanent threshold shift of hearing sensitivity (PTS).
(3) An increase in our understanding of how marine mammals respond
(behaviorally or physiologically) to underwater detonations or other
stimuli expected to result in take and how anticipated adverse effects
on individuals (in different ways and to varying degrees) may impact
the population, species, or stock (specifically through effects on
annual rates of recruitment or survival).
(4) An increased knowledge of the affected species.
(5) An increase in our understanding of the effectiveness of
certain mitigation and monitoring measures.
(6) A better understanding and record of the manner in which the
authorized entity complies with the incidental take authorization.
Proposed Monitoring Plan for the VACAPES Range Complex Study Area
As NMFS indicated in the proposed rule, the Navy has (with input
from NMFS) fleshed out the details of and made improvements to the
VACAPES Range Complex Monitoring Plan. Additionally, NMFS and the Navy
have incorporated a suggestion from the public, which recommended the
Navy hold a peer review workshop to discuss the Navy's Monitoring Plans
for the multiple range complexes and training exercises in which the
Navy would receive ITAs (see Monitoring Workshop section). The final
VACAPES Range Complex Monitoring Plan, which is summarized below, may
be viewed at https://www.nmfs.noaa.gov/pr/permits/incidental.htm#applications. The Navy plans to implement all of the
components of the Monitoring Plan; however, only the marine mammal
components (not the sea turtle components) will be required by the MMPA
regulations and associated LOAs.
A summary of the monitoring methods required for use during
training events in the VACAPES Range Complex are described below. These
methods include a combination of individual elements that are designed
to allow a comprehensive assessment.
I. Vessel or Aerial Surveys
(A) The Holder of this Authorization shall visually survey a
minimum of 2 explosive events per year, one of which shall be a
multiple detonation event. One of the vessel or aerial surveys should
involve professionally trained marine mammal observers (MMOs).
(B) If operationally feasible, for specified training events,
aerial or vessel surveys shall be used 1-2 days prior to, during (if
reasonably safe), and 1-5 days post detonation.
(C) Surveys shall include any specified exclusion zone around a
particular detonation point plus 2,000 yards beyond the border of the
exclusion zone (i.e., the circumference of the area from the border of
the exclusion zone extending 2,000 yards outwards). For vessel based
surveys a passive acoustic system (hydrophone or towed array) could be
used to determine if marine mammals are in the area before and/or after
a detonation event.
(D) When conducting a particular survey, the survey team shall
collect:
Location of sighting;
Species (if not possible, indicate whale, dolphin or
pinniped);
Number of individuals;
Whether calves were observed;
Initial detection sensor;
Length of time observers maintained visual contact with
marine mammal;
Wave height;
Visibility;
Whether sighting was before, during, or after detonations/
exercise, and how many minutes before or after;
Distance of marine mammal from actual detonations (or
target spot if not yet detonated);
Observed behavior--Watchstanders will report, in plain
language and without trying to categorize in any way, the observed
behavior of the animal(s) (such as animal closing to bow ride,
paralleling course/speed, floating on surface and not swimming etc.),
including speed and direction;
Resulting mitigation implementation--Indicate whether
explosive detonations were delayed, ceased, modified, or not modified
due to marine mammal presence and for how long; and
If observation occurs while explosives are detonating in
the water, indicate munition type in use at time of marine mammal
detection (e.g., were the 5-inch guns actually firing when the animals
were sighted? Did animals enter an area 2 minutes after a huge
explosion went off?).
II. Passive Acoustic Monitoring
The Navy is required to conduct passive acoustic monitoring when
operationally feasible.
(A) Any time a towed hydrophone array is employed during shipboard
surveys the towed array shall be deployed during daylight hours for
each of the days the ship is at sea.
(B) The towed hydrophone array shall be used to supplement the
ship-based systematic line-transect surveys (particularly for species
such as beaked whales that are rarely seen).
III. Marine Mammal Observers on Navy Platforms
(A) Marine mammal observers (MMOs) selected for aerial or vessel
survey shall be placed on a Navy platform during one of the exercises
being monitored per year. The remaining designated exercise(s) shall be
monitored by the Navy lookouts/watchstanders.
[[Page 28334]]
(B) The MMO must possess expertise in species identification of
regional marine mammal species and experience collecting behavioral
data.
(C) MMOs shall not be placed aboard Navy platforms for every Navy
training event or major exercise, but during specifically identified
opportunities deemed appropriate for data collection efforts. The
events selected for MMO participation shall take into account safety,
logistics, and operational concerns.
(D) MMOs shall observe from the same height above water as the
lookouts.
(E) The MMOs shall not be part of the Navy's formal reporting chain
of command during their data collection efforts; Navy lookouts shall
continue to serve as the primary reporting means within the Navy chain
of command for marine mammal sightings. The only exception is that if
an animal is observed within the shutdown zone that has not been
observed by the lookout, the MMO shall inform the lookout of the
sighting, and the lookout shall take the appropriate action through the
chain of command.
(F) The MMOs shall collect species identification, behavior,
direction of travel relative to the Navy platform, and distance first
observed. All MMO sightings shall be conducted according to a standard
operating procedure. Information collected by MMOs should be the same
as those collected by Navy lookout/watchstanders described above.
The Monitoring Plan for VACAPES Range Complex has been designed as
a collection of focused ``studies'' (described fully in the VACAPES
Monitoring Plan) to gather data that will allow the Navy to address the
following questions:
(a) What are the behavioral responses of marine mammals and sea
turtles that are exposed to explosives?
(b) Is the Navy's suite of mitigation measures effective at
avoiding injury and mortality of marine mammals and sea turtles?
Data gathered in these studies will be collected by qualified,
professional marine mammal biologists or trained Navy lookouts/
watchstanders that are experts in their field. This monitoring plan has
been designed to gather data on all species of marine mammals that are
observed in the VACAPES Range Complex study area.
Monitoring Workshop
During the public comment period on past proposed rules for Navy
actions (such as the Hawaii Range Complex (HRC), and Southern
California Range Complex (SOCAL) proposed rules), NMFS received a
recommendation that a workshop or panel be convened to solicit input on
the monitoring plan from researchers, experts, and other interested
parties. The VACAPES Range Complex proposed rule included an adaptive
management component and both NMFS and the Navy believe that a workshop
would provide a means for Navy and NMFS to consider input from
participants in determining whether (and if so, how) to modify
monitoring techniques to more effectively accomplish the goals of
monitoring set forth earlier in the document. NMFS and the Navy believe
that this workshop concept is valuable in relation to all of the Range
Complexes and major training exercise rules and LOAs that NMFS is
working on with the Navy at this time, and consequently this single
Monitoring Workshop will be included as a component of all of the rules
and LOAs that NMFS will be processing for the Navy in the next year or
so.
The Navy, with guidance and support from NMFS, will convene a
Monitoring Workshop, including marine mammal and acoustic experts as
well as other interested parties, in 2011. The Monitoring Workshop
participants will review the monitoring results from the previous two
years of monitoring pursuant to the VACAPES Range Complex rule as well
as monitoring results from other Navy rules and LOAs (e.g., AFAST,
SOCAL, HRC, and other rules). The Monitoring Workshop participants
would provide their individual recommendations to the Navy and NMFS on
the monitoring plan(s) after also considering the current science
(including Navy research and development) and working within the
framework of available resources and feasibility of implementation.
NMFS and the Navy would then analyze the input from the Monitoring
Workshop participants and determine the best way forward from a
national perspective. Subsequent to the Monitoring Workshop,
modifications would be applied to monitoring plans as appropriate.
Integrated Comprehensive Monitoring Program
In addition to the site-specific Monitoring Plan for the VACAPES
Range Complex, the Navy will complete the Integrated Comprehensive
Monitoring Program (ICMP) Plan by the end of 2009. The ICMP is
currently in development by the Navy, with Chief of Naval Operations
Environmental Readiness Division (CNO-N45) having the lead. The program
does not duplicate the monitoring plans for individual areas (e.g.
AFAST, HRC, SOCAL); instead it is intended to provide the overarching
coordination that will support compilation of data from both range-
specific monitoring plans as well as Navy funded research and
development (R&D) studies. The ICMP will coordinate the monitoring
program's progress towards meeting its goals and developing a data
management plan. A program review board is also being considered to
provide additional guidance. The ICMP will be evaluated annually to
provide a matrix for progress and goals for the following year, and
will make recommendations on adaptive management for refinement and
analysis of the monitoring methods.
The primary objectives of the ICMP are to:
Monitor and assess the effects of Navy activities on
protected species;
Ensure that data collected at multiple locations is
collected in a manner that allows comparison between and among
different geographic locations;
Assess the efficacy and practicality of the monitoring and
mitigation techniques;
Add to the overall knowledge-base of marine species and
the effects of Navy activities on marine species.
The ICMP will be used both as: (1) A planning tool to focus Navy
monitoring priorities (pursuant to ESA/MMPA requirements) across Navy
Range Complexes and Exercises; and (2) an adaptive management tool,
through the consolidation and analysis of the Navy's monitoring and
watchstander data, as well as new information from other Navy programs
(e.g., R&D), and other appropriate newly published information.
In combination with the 2011 Monitoring Workshop and the adaptive
management component of the VACAPES Range Complex rule and the other
planned Navy rules (e.g. Jacksonville Range Complex, Cherry Point Range
Complex, etc.), the ICMP could potentially provide a framework for
restructuring the monitoring plans and allocating monitoring effort
based on the value of particular specific monitoring proposals (in
terms of the degree to which results would likely contribute to stated
monitoring goals, as well as the likely technical success of the
monitoring based on a review of past monitoring results) that have been
developed through the ICMP framework, instead of allocating based on
maintaining an equal (or commensurate to effects) distribution of
monitoring effort across range complexes. For example, if careful
prioritization and planning through the
[[Page 28335]]
ICMP (which would include a review of both past monitoring results and
current scientific developments) were to show that a large, intense
monitoring effort in Hawaii would likely provide extensive, robust and
much-needed data that could be used to understand the effects of sonar
throughout different geographical areas, it may be appropriate to have
other range complexes dedicate money, resources, or staff to the
specific monitoring proposal identified as ``high priority'' by the
Navy and NMFS, in lieu of focusing on smaller, lower priority projects
divided throughout their home range complexes.
The ICMP will identify:
A means by which NMFS and the Navy would jointly consider
prior years' monitoring results and advancing science to determine if
modifications are needed in mitigation or monitoring measures to better
effect the goals laid out in the Mitigation and Monitoring sections of
the VACAPES Range Complex rule.
Guidelines for prioritizing monitoring projects
If, as a result of the workshop and similar to the example
described in the paragraph above, the Navy and NMFS decide it is
appropriate to restructure the monitoring plans for multiple ranges
such that they are no longer evenly allocated (by rule), but rather
focused on priority monitoring projects that are not necessarily tied
to the geographic area addressed in the rule, the ICMP will be modified
to include a very clear and unclassified record-keeping system that
will allow NMFS and the public to see how each range complex/project is
contributing to all of the ongoing monitoring programs (resources,
effort, money, etc.).
Adaptive Management
The final regulations governing the take of marine mammals
incidental to Navy's VACAPES Range Complex exercises contain an
adaptive management component. The use of adaptive management will give
NMFS the ability to consider new data from different sources to
determine (in coordination with the Navy) on an annual basis if
mitigation or monitoring measures should be modified or added (or
deleted) if new data suggests that such modifications are appropriate
(or are not appropriate) for subsequent annual LOAs.
The following are some of the possible sources of applicable data:
Results from the Navy's monitoring from the previous year
(either from VACAPES Range Complex or other locations)
Findings of the Workshop that the Navy will convene in
2011 to analyze monitoring results to date, review current science, and
recommend modifications, as appropriate to the monitoring protocols to
increase monitoring effectiveness.
Compiled results of Navy funded research and development
(R&D) studies (presented pursuant to the ICMP, which is discussed
elsewhere in this document)
Results from specific stranding investigations (either
from VACAPES Range Complex or other locations)
Results from general marine mammal and sound research
(funded by the Navy or otherwise)
Any information which reveals that marine mammals may have
been taken in a manner, extent or number not authorized by these
regulations or subsequent Letters of Authorization
Mitigation measures could be modified or added (or deleted) if new
data suggests that such modifications would have (or do not have) a
reasonable likelihood of accomplishing the goals of mitigation laid out
in this final rule and if the measures are practicable. NMFS would also
coordinate with the Navy to modify or add to (or delete) the existing
monitoring requirements if the new data suggest that the addition of
(or deletion of) a particular measure would more effectively accomplish
the goals of monitoring laid out in this final rule. The reporting
requirements associated with this rule are designed to provide NMFS
with monitoring data from the previous year to allow NMFS to consider
the data and issue annual LOAs. NMFS and the Navy will meet annually,
prior to LOA issuance, to discuss the monitoring reports, Navy R&D
developments, and current science and whether mitigation or monitoring
modifications are appropriate.
Reporting
In order to issue an ITA for an activity, Section 101(a)(5)(A) of
the MMPA states that NMFS must set forth ``requirements pertaining to
the monitoring and reporting of such taking''. Effective reporting is
critical to ensure compliance with the terms and conditions of a LOA,
and to provide NMFS and the Navy with data of the highest quality based
on the required monitoring. As NMFS noted in its proposed rule,
additional detail has been added to the reporting requirements since
they were outlined in the proposed rule. The updated reporting
requirements are all included below. A subset of the information
provided in the monitoring reports may be classified and not releasable
to the public.
NMFS will work with the Navy to develop tables that allow for
efficient submission of the information required below.
General Notification of Injured or Dead Marine Mammals
Navy personnel will ensure that NMFS (regional stranding
coordinator) is notified immediately (or as soon as operational
security allows) if an injured or dead marine mammal is found during or
shortly after, and in the vicinity of, any Navy training exercise
utilizing underwater explosive detonations or other activities. The
Navy will provide NMFS with species or description of the animal(s),
the condition of the animal(s) (including carcass condition if the
animal is dead), location, time of first discovery, observed behaviors
(if alive), and photo or video (if available).
Annual VACAPES Range Complex Monitoring Plan Report
The Navy shall submit a report annually on March 1 describing the
implementation and results (through January 1 of the same year) of the
VACAPES Range Complex Monitoring Plan, described above. Data collection
methods will be standardized across range complexes to allow for
comparison in different geographic locations. Although additional
information will also be gathered, the marine mammal observers (MMOs)
collecting marine mammal data pursuant to the VACAPES Range Complex
Monitoring Plan shall, at a minimum, provide the same marine mammal
observation data required in the major range complex training exercises
section of the Annual VACAPES Range Complex Exercise Report referenced
below.
The VACAPES Range Complex Monitoring Plan Report may be provided to
NMFS within a larger report that includes the required Monitoring Plan
Reports from multiple Range Complexes.
Annual VACAPES Range Complex Exercise Report
The Navy is in the process of improving the methods used to track
explosives used to provide increased granularity. The Navy will provide
the information described below for all of their explosive exercises.
Until the Navy is able to report in full the information below, they
will provide an annual update on the Navy's explosive tracking methods,
including improvements from the previous year.
[[Page 28336]]
(i) Total annual number of each type of explosive exercise (of
those identified as part of the ``specified activity'' in this final
rule) conducted in the VACAPES Range Complex.
(ii) Total annual expended/detonated rounds (missiles, bombs, etc.)
for each explosive type.
VACAPES Range Complex 5-yr Comprehensive Report
The Navy shall submit to NMFS a draft report that analyzes and
summarizes all of the multi-year marine mammal information gathered
during the VACAPES Range Complex exercises for which annual reports are
required (Annual VACAPES Range Complex Exercise Reports and VACAPES
Range Complex Monitoring Plan Reports). This report will be submitted
at the end of the fourth year of the rule (May 2013), covering
activities that have occurred through December 1, 2012.
Comments and Responses
On December 12, 2008, NMFS published a proposed rule (73 FR 75631)
in response to the Navy's request to take marine mammals incidental to
military readiness training in the VACAPES Range Complex study area and
requested comments, information and suggestions concerning the request.
During the 30-day public comment period, NMFS received comments from 1
private citizen, comments from the Marine Mammal Commission
(Commission), comments from the Commonwealth of Virginia Department of
Environmental Quality (Virginia DEQ, including the Department of Game
and Inland Fisheries (VDGIF) and the Department of Conservation and
Recreation), comments from the International Fund for Animal Welfare,
and comments from the Natural Resources Defense Council (on behalf of
itself, The Humane Society of the United States, Whale and Dolphin
Conservation Society, Cetacean Society International, Ocean Futures
Society, Jean-Michel Cousteau). The comments are summarized and sorted
into general topic areas and are addressed below. Full copies of the
comment letters may be accessed at https://www.regulations.gov.
MMPA Concerns
Comment 1: The Commission and IFAW point out that there are
differences between the Navy's and NMFS' estimates of maximum annual
takes for the proposed exercises in the VACAPES range complex and that
these differences should be reconciled.
Response: NMFS does not believe there are differences between the
Navy's and NMFS' estimates of maximum annual takes for the VACAPES
Range Complex training exercises. The perceived differences the
Commission raised may be the differences between the Navy's initial LOA
application and its subsequent addendum. The Navy states that further
analyses on the impacts from the proposed action and the reduction of
BOMBEX exercises are the reason for the change of take estimates.
Specifically, the Navy states that ``HARM missile explodes no less than
30 ft above the water, it is assumed the amount of acoustic energy
entering the water would be negligible, so exposures from that weapon
should be removed from the MISSILEX totals. Secondly, the size of the
BOMBEX location was reduced to avoid important fishing areas, the North
Atlantic Right Whale migratory corridor, and the Norfolk Canyon area
which lowered potential exposures for certain species.'' The amendment
is posted on NMFS incident take Web site at https://www.nmfs.noaa.gov/pr/permits/incidental.htm.
Comment 2: The Commission recommends that NMFS include in its
authorization the number of lethal takes and takes by Level A
harassment requested by the Navy and regularly confer with the Navy to
monitor the actual number of such takes to ensure that they do not
exceed the authorized number.
Response: NMFS agrees with the Commission. NMFS has, through this
final rule, included the authorized numbers of marine mammal takes and
the manner of take (i.e., lethal, Level A or Level B). In addition,
monitoring and reporting measures are prescribed to ensure that all
takes as a result of the training activities are accounted for and
documented. The MMOs and Navy's lookouts/watchstanders will report any
sightings of marine mammals in the take zone through the chain of
command. Furthermore, the Navy is required to submit an Annual VACAPES
Range Complex Monitoring Plan Report. Prior to issuing any subsequent
LOAs, NMFS will review the Navy's monitoring efforts and data from the
previous year to determine whether any new measures will be necessary
or a modification to prior year's measures.
Comment 3: The Virginia DEQ recommends that NMFS develop the
regulations to reflect harbor seal, harp seal, and gray seal as their
occurrence in the inshore and nearshore waters of the mid-Atlantic
region are becoming more frequent in the fall and winter months.
Response: Based on the analyses by the Navy and NMFS, there are 34
marine mammal species with possible or confirmed occurrence in the
VACAPES Range Complex. As indicated in the proposed rule, there are 33
cetacean species and one pinniped species (harbor seal). Harp and gray
seals occur primarily in the North Atlantic, with the former species
found mostly in the Arctic region. Although there have been increased
anecdotal sightings of these species in the mid-Atlantic coastal
waters, their presence in the mid-Atlantic region is still very rare
(Waring et al., 2008).
Comment 4: The VDGIF states that the species take list appears to
be accurate; however, the number of animals predicted to be affected
for both Level A and Level B harassment are probably underestimated,
because the species density data from which take estimates are derived
are based on too few data. Therefore, no marine mammal species should
be considered unlikely to be affected just because there are no density
data available (e.g., beaked whales). Since all of the species on the
list exist in the Virginia and North Carolina Outer Banks stranding
records, collected and kept by the Virginia Aquarium Stranding Response
Program, the VDGIF recommends that all species on the take list should
be considered susceptible to Level B harassment year round. The IFAW
states that if one of these animals not included in the incidental take
list is present in the area of testing, there is a higher probability
that the animal will be struck, and that the assumption that one third
of the cetacean species in the area will not be exposed nor affected by
noise represents an oversight in the analysis of potential takes.
Response: NMFS does not agree with the VDGIF and IFAW's assessment.
The most current stock assessment reports (Waring et al., 2008) were
used to calculate density estimates. As summarized in the proposed rule
and described more fully in the Navy's FEIS, the Navy used the best
data and methods available to calculate density, including other
literature as well as habitat modeling that considered bathymetry,
distance from shelf break, sea surface temperature, and Chlorophyll a
concentration. All spatial models and density estimates were reviewed
by NMFS technical staff. The Navy's model utilizes uniform density, but
it also divides the east coast into meaning