Takes of Marine Mammals Incidental to Specified Activities; Taking Marine Mammals Incidental to the U.S. Air Force Conducting Maritime Weapon Systems Evaluation Program Operational Testing Within the Eglin Gulf Test and Training Range, 83209-83228 [2016-27881]

Agencies

• DEPARTMENT OF COMMERCE
• National Oceanic and Atmospheric Administration

[Federal Register Volume 81, Number 224 (Monday, November 21, 2016)]
[Notices]
[Pages 83209-83228]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2016-27881]


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DEPARTMENT OF COMMERCE

National Oceanic and Atmospheric Administration

RIN 0648-XE926


Takes of Marine Mammals Incidental to Specified Activities; 
Taking Marine Mammals Incidental to the U.S. Air Force Conducting 
Maritime Weapon Systems Evaluation Program Operational Testing Within 
the Eglin Gulf Test and Training Range

AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and 
Atmospheric Administration (NOAA), Commerce.

ACTION: Notice; proposed incidental harassment authorization; request 
for comments.

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SUMMARY: NMFS (hereinafter, ``we'') received an application from the 
U.S. Department of the Air Force, Headquarters 96th Air Base Wing (Air 
Force), Eglin Air Force Base (Eglin AFB), requesting an Incidental 
Harassment Authorization (IHA or Authorization) to take marine mammals, 
by harassment, incidental to a Maritime Weapon Systems Evaluation 
Program (Maritime WSEP) within a section of the Eglin Gulf Test and 
Training Range in the northern Gulf of Mexico.
    Eglin AFB's Maritime WSEP activities are military readiness 
activities per the Marine Mammal Protection Act (MMPA), as amended by 
the National Defense Authorization Act of 2004 (NDAA). Per the MMPA, 
NMFS requests comments on its proposal to issue an Authorization to 
Eglin AFB to incidentally take, by Level B and Level A harassment, two 
species of marine mammals, the Atlantic bottlenose dolphin (Tursiops 
truncatus) and Atlantic spotted dolphin (Stenella frontalis), during 
the specified activity.

DATES: NMFS must receive comments and information no later than 
December 21, 2016.

ADDRESSES: Address comments on the application to Jolie Harrison, 
Chief, Permits and Conservation Division, Office of Protected 
Resources, National Marine Fisheries Service, 1315 East-West Highway, 
Silver Spring, MD 20910. The mailbox address for providing email 
comments is ITP.Youngkin@noaa.gov. Please include RIN 0648-XE926 in the 
subject line. Comments sent via email to ITP.Youngkin@noaa.gov, 
including all attachments, must not exceed a 25-megabyte file size. 
NMFS is not responsible for email comments sent to addresses other than 
the one provided in this notice.
    Instructions: All submitted comments are a part of the public 
record, and generally we will post them to https://www.nmfs.noaa.gov/pr/permits/incidental/military.htm without change. All personal 
identifying information (for example, name, address, etc.) voluntarily 
submitted by the commenter may be publicly accessible. Do not submit 
confidential business information or otherwise sensitive or protected 
information.
    To obtain an electronic copy of Eglin AFB's application, a list of 
the references used in this document, and Eglin AFB's Environmental 
Assessment (EA) titled, ``Maritime Weapons System Evaluation Program,'' 
write to the previously mentioned address, telephone the contact listed 
here (see FOR FURTHER INFORMATION CONTACT), or visit the internet at: 
https://www.nmfs.noaa.gov/pr/permits/incidental/military.htm.

FOR FURTHER INFORMATION CONTACT: Dale Youngkin, Office of Protected 
Resources, NMFS, (301) 427-8401.

SUPPLEMENTARY INFORMATION:

Background

    Sections 101(a)(5)(A) and (D) of the Marine Mammal Protection Act 
of 1972, as amended (MMPA; 16 U.S.C. 1361 et seq.) direct the Secretary 
of Commerce to allow, upon request, the incidental, but not 
intentional, taking of small numbers of marine mammals of a species or 
population stock, by U.S. citizens who engage in a specified activity 
(other than commercial fishing) within a specified geographical region 
if, after NMFS provides a notice of a proposed authorization to the 
public for review and comment: (1) NMFS makes certain findings; and (2) 
the taking is limited to harassment.
    An Authorization for incidental takings for marine mammals shall be 
granted if NMFS finds that the taking will have a negligible impact on 
the species or stock(s), will not have an unmitigable adverse impact on 
the availability of the species or stock(s) for subsistence uses (where 
relevant), and if the permissible methods of taking and requirements 
pertaining to the mitigation, monitoring, and reporting of such 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 indicated earlier 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 February 4, 2016, we issued an Authorization to Eglin AFB to 
take marine mammals, by harassment, incidental to a Maritime Weapon 
Systems Evaluation Program (Maritime WSEP) within the Eglin Gulf Test 
and Training Range (EGTTR) in the Gulf of Mexico from February 4, 2016 
through February 3, 2017 (see 81 FR 7307; February 11, 2016). These 
proposed missions were very similar to previous Maritime WSEP mission 
activities for which incidental harassment

[[Page 83210]]

authorizations were issued the previous year (80 FR 17394). On 
September 19, 2016, we received a renewal request for an Authorization 
from Eglin AFB to continue the missions authorized in 2016. We 
considered the revised renewal request as adequate and complete on 
September 27, 2016.
    Due to the ongoing nature of these activities, as well as the fact 
that other mission activities are conducted within the EGTTR, we have 
discussed developing a rulemaking to encompass all mission activities 
in the EGTTR, and anticipate that the Maritime WSEP activities will be 
part of that future rulemaking. However, this IHA is being proposed due 
to timing constraints to ensure that these activities are in compliance 
with the Marine Mammal Protection Act (MMPA) while the future 
rulemaking is in process.
    Eglin AFB proposes to conduct Maritime WESP missions within the 
EGTTR airspace over the Gulf of Mexico within Warning Area 151 (W-151), 
specifically within sub-area W-151A (see Figure 2-1 of Eglin AFB's 
application and Figure 1 below). The proposed Maritime WSEP training 
activities are planned to occur during daylight hours in February and 
March 2017, however, the activities could occur between February 4, 
2017, and February 3, 2018.
    Eglin AFB proposes to use multiple types of live munitions (e.g., 
gunnery rounds, rockets, missiles, and bombs) against small boat 
targets in the EGTTR. These activities qualify as military readiness 
activities.
    The following aspects of the proposed Maritime WSEP training 
activities have the potential to take marine mammals: Exposure to 
impulsive noise and pressure waves generated by live ordnance 
detonation at or near the surface of the water. Take, by Level B 
harassment, of individuals of common bottlenose dolphin or Atlantic 
spotted dolphin could potentially result from the specified activity. 
Additionally, although NMFS does not expect it to occur, Eglin AFB has 
also requested authorization for Level A Harassment of up to three 
individuals of either common bottlenose dolphins or Atlantic spotted 
dolphins. Therefore, Eglin AFB has requested authorization to take 
individuals of two cetacean species by Level A and Level B harassment.
    Eglin AFB's Maritime WSEP training activities may potentially 
impact marine mammals at or near the water surface in the absence of 
mitigation. Marine mammals could potentially be harassed, injured, or 
killed by exploding and non-exploding projectiles, and falling debris. 
However, based on analyses provided in Eglin AFB's 2016 application, 
Eglin AFB's previous applications and Authorizations Eglin AFB's 2015 
Environmental Assessment (EA), and past monitoring reports for the 
authorized activities conducted in February and March 2016 and 2015, 
and for reasons discussed later in this document, we do not anticipate 
that Eglin AFB's Maritime WSEP activities would result in any serious 
injury or mortality to marine mammals.
    For Eglin AFB, this would be the third such Authorization, if 
issued, following the Authorization issued effective from February 4, 
2016, through February 3, 2017 (see 81 FR 7307; February 11, 2016). 
This IHA would be effective from February 4, 2017, through February 3, 
2018, if issued. The monitoring report associated with the 2016 
Authorization is available at www.nmfs.noaa.gov/pr/permits/incidental/military.htm and provides additional environmental information related 
to proposed issuance of this Authorization for public review and 
comment.

Description of the Specified Activity

Overview

    Eglin AFB proposes to conduct live ordnance testing and training in 
the Gulf of Mexico as part of the Maritime WSEP operational testing 
missions. The Maritime WSEP test objectives are to evaluate maritime 
deployment data, evaluate tactics, techniques and procedures, and to 
determine the impact of techniques and procedures on combat Air Force 
training. The need to conduct this type of testing has developed in 
response to increasing threats at sea posed by operations conducted 
from small boats, which can carry a variety of weapons, can form in 
large or small numbers, and may be difficult to locate, track, and 
engage in the marine environment. Because of limited Air Force aircraft 
and munitions testing on engaging and defeating small boat threats, 
Eglin AFB proposes to employ live munitions against boat targets in the 
EGTTR in order to continue development of techniques and procedures to 
train Air Force strike aircraft to counter small maneuvering surface 
vessels.

Dates and Duration

    Eglin AFB proposes to schedule up to eight Maritime WSEP training 
missions occurring during a one-week period in February 2017 and a one-
week period in March 2017. The proposed missions would occur for up to 
four hours each day during the morning hours, with multiple live 
munitions being released per day. However, the proposed Authorization, 
would be effective to cover those activities anytime during the period 
from February 4, 2017 through February 3, 2018.

Specified Geographic Region

    The specific planned mission location is approximately 17 miles 
(mi) (27.3 kilometers (km)) offshore from Santa Rosa Island, Florida, 
in nearshore waters of the continental shelf in the Gulf of Mexico. All 
activities would take place within the EGTTR, defined as the airspace 
over the Gulf of Mexico controlled by Eglin AFB, beginning at a point 
three nautical miles (nmi) (3.5 mi; 5.5 km) from shore. The EGTTR 
consists of subdivided blocks including Warning Area 151 (W-151) where 
the proposed activities would occur, specifically in sub-area W-151A 
(shown in Figure 1).
    W-151: The inshore and offshore boundaries of W-151 are roughly 
parallel to the shoreline contour. The shoreward boundary is three nmi 
(3.5 mi; 5.5 km) from shore, while the seaward boundary extends 
approximately 85 to 100 nmi (97.8 mi; 157.4 km to 115 mi; 185.2 km) 
offshore, depending on the specific location. W-151 covers a surface 
area of approximately 10,247 square nmi (nmi\2\) (13,570 square mi 
(mi\2\); 35,145 square km (km\2\)), and includes water depths ranging 
from about 20 to 700 meters (m) (65.6 to 2296.6 feet (ft)). This range 
of depth includes continental shelf and slope waters. Approximately 
half of W-151 lies over the shelf.
    W-151A: W-151A extends approximately 60 nmi (69.0 mi; 111.1 km) 
offshore and has a surface area of 2,565 nmi\2\ (3,396.8 mi\2\; 8,797 
km\2\). Water depths range from about 30 to 350 m (98.4 to 1148.2 ft) 
and include continental shelf and slope zones. However, most of W-151A 
occurs over the continental shelf, in water depths less than 250 m 
(820.2 ft). Maritime WSEP training missions will occur in the 
shallower, northern inshore portion of the sub-area, in a water depth 
of about 35 meters (114.8 ft).

[[Page 83211]]

[GRAPHIC] [TIFF OMITTED] TN21NO16.025

Detailed Description of Activities

    The Maritime WSEP training missions include the release of multiple 
types of inert and live munitions from fighter and bomber aircraft, 
unmanned aerial vehicles, and gunships against small, static, towed, 
and remotely-controlled boat targets. Munition types include bombs, 
missiles, rockets, and gunnery rounds (Table 1).

                                      Table 1--Live Munitions and Aircraft
----------------------------------------------------------------------------------------------------------------
                    Munitions                           Aircraft (not associated with  specific munitions)
----------------------------------------------------------------------------------------------------------------
GBU-10/-24/-31..................................  F-16C fighter aircraft.
GBU-49..........................................  F-16C+ fighter aircraft.
JASSM...........................................  F-15E fighter aircraft.
GBU-12 (PWII)/-54 (LJDAM)/-38/-32 (JDAM)........  A-10 fighter aircraft.
AGM-65 (Maverick)...............................  B-1B bomber aircraft.
CBU-105 (WCMD)..................................  B-52H bomber aircraft.
GBU-39 (Small Diameter Bomb)....................  MQ-1/9 unmanned aerial vehicle.
AGM-114 (Hellfire)..............................  AC-130 gunship.
AGM-176 (Griffin)...............................
2.75 Rockets/AGR-20A/B..........................
AIM-9X..........................................
PGU-12/B high explosive incendiary 30 mm rounds.
----------------------------------------------------------------------------------------------------------------
Key: AGM = air-to-ground missile; CBU = Cluster Bomb Unit; GBU = Guided Bomb Unit; LJDAM = Laser Joint Direct
  Attack Munition; Laser SDB = Laser Small Diameter Bomb; mm = millimeters; PGU = Projectile Gun Unit; WCMD =
  wind corrected munition dispenser.

    The proposed Maritime WSEP training activities involve detonations 
above the water, near the water surface, and under water within the 
EGTTR. However, because the tests will focus on weapons/target 
interaction, Eglin AFB will not specify a particular aircraft for a 
given test as long as it meets the delivery parameters.
    Eglin AFB would deploy the munitions against static, towed, and 
remotely-controlled boat targets within the W-151A. Eglin AFB would 
operate the remote-controlled boats from an

[[Page 83212]]

instrumentation barge (i.e., the Gulf Range Armament Test Vessel; 
GRATV) anchored on site within the test area. The GRATV would provide a 
platform for video cameras and weapons-tracking equipment.
    Table 2 lists the number, height, or depth of detonation, explosive 
material, and net explosive weight (NEW) in pounds (lbs) of each 
munition proposed for use during the Maritime WSEP activities.

                    Table 2--Maritime WSEP Munitions Proposed for Use in the W-151A Test Area
----------------------------------------------------------------------------------------------------------------
                                    Total number
         Type of munition              of live                 Detonation type              Net explosive weight
                                      munitions                                                 per munition
----------------------------------------------------------------------------------------------------------------
GBU-10/-24/-31...................               2  Subsurface (10-ft depth)..............  945 lbs.
GBU-49...........................               4  Surface...............................  500 lbs.
JASSM............................               4  Surface...............................  255 lbs.
GBU-12 (PWII)/-54 (LJDAM)/-38/-32               6  Subsurface (10-ft depth)..............  192 lbs.
 (JDAM).
AGM-65 (Maverick)................               8  Surface...............................  86 lbs.
CBU-105 (WCMD)...................               4  Airburst..............................  83 lbs.
GBU-39 (Small Diameter Bomb).....               4  Surface...............................  37 lbs.
AGM-114 (Hellfire)...............              20  Subsurface (10-ft depth)..............  20 lbs.
AGM-176 (Griffin)................              10  Surface...............................  13 lbs.
2.75 Rockets/AGR-20A/B...........             100  Surface...............................  12 lbs.
AIM-9X...........................               1  Surface...............................  7.9 lbs.
PGU-12/B high explosive                     1,000  Surface...............................  0.1 lbs.
 incendiary 30 mm rounds.
----------------------------------------------------------------------------------------------------------------
Key: AGL = above ground level; AGM = air-to-ground missile; CBU = Cluster Bomb Unit; GBU = Guided Bomb Unit;
  JDAM = Joint Direct Attack Munition; LJDAM = Laser Joint Direct Attack Munition; mm = millimeters; msec =
  millisecond; lbs = pounds; PGU = Projectile Gun Unit; HEI = high explosive incendiary.

    At least two ordnance delivery aircraft will participate in each 
live weapons release training mission, which lasts approximately four 
hours. Before delivering the ordnance, mission aircraft would make a 
dry run over the target area to ensure that it is clear of commercial 
and recreational boats. Jets will fly at a minimum air speed of 300 
knots (approximately 345 miles per hour, depending on atmospheric 
conditions) and at a minimum altitude of 305 m (1,000 ft). Due to the 
limited flyover duration and potentially high speed and altitude, the 
pilots would not participate in visual surveys for protected species. 
Eglin AFB's 2016 and 2015 Authorization renewal request, 2014 
application for the same activities, and 2015 EA and Finding of No 
Significant Impact (FONSI) contain additional detailed information on 
the Maritime WSEP training activities and are all available online 
(https://www.nmfs.noaa.gov/pr/permits/incidental/military.htm#af_eglinwsep2016).

Description of Marine Mammals in the Area of the Specified Activity

    Table 3 lists marine mammal species with potential or confirmed 
occurrence in the proposed activity area during the project timeframe 
and summarizes key information regarding stock status and abundance. 
Please see NMFS' 2015 and 2014 Stock Assessment Reports (SAR), 
available at www.nmfs.noaa.gov/pr/sars and Garrison et al., 2008; Navy, 
2007; Davis et al., 2000 for more detailed accounts of these stocks' 
status and abundance.

                                          Table 3--Marine Mammals That May Occur in the Proposed Activity Area
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                                                                                Regulatory status 1 2                             Relative occurrence in
               Species                              Stock name                                            Estimated abundance             W-151
--------------------------------------------------------------------------------------------------------------------------------------------------------
Common bottlenose dolphin...........  Choctawatchee Bay.....................  MMPA--S.................  179....................  Uncommon.
                                                                              ESA--NL.................  CV = 0.04 \3\..........
                                      Pensacola/East Bay....................  MMPA--S.................  33.....................  Uncommon.
                                                                              ESA--NL.................  CV = 0.80 \4\..........
                                      St. Andrew Bay........................  MMPA--S.................  124....................  Uncommon.
                                                                              ESA--NL.................  CV = 0.57 \4\..........
                                      Gulf of Mexico Northern Coastal.......  MMPA--S.................  7,185..................  Common.
                                                                              ESA--NL.................  CV = 0.21 \3\..........
                                      Northern Gulf of Mexico Continental     MMPA--NC................  51,192.................  Uncommon.
                                       Shelf.                                 ESA--NL.................  CV = 0.10 \3\..........
                                      Northern Gulf of Mexico Oceanic.......  MMPA--NC................  5,806..................  Uncommon.
                                                                              ESA--NL.................  CV = 0.39 \4\..........
Atlantic spotted dolphin............  Northern Gulf of Mexico...............  MMPA--NC................  37,611 \4\.............  Common.
                                                                              ESA--NL.................  CV = 0.28..............
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ MMPA: D = Depleted, S = Strategic, NC = Not Classified.
\2\ ESA: EN = Endangered, T = Threatened, DL = Delisted, NL = Not listed.
\3\ NMFS Draft 2015 SAR (Waring et al., 2015).
\4\ NMFS 2014 SAR (Waring et al., 2014).

    An additional 19 cetacean species could occur within the 
northeastern Gulf of Mexico, mainly occurring at or beyond the shelf 
break (i.e., water depth of approximately 200 m (656.2 ft)) located 
beyond the W-151A test area. NMFS and Eglin AFB consider these 19 
species to be rare or extralimital within the W-151A test location 
area. These

[[Page 83213]]

species are the Bryde's whale (Balaenoptera edeni), sperm whale 
(Physeter macrocephalus), dwarf sperm whale (Kogia sima), pygmy sperm 
whale (K. breviceps), pantropical spotted dolphin (Stenella attenuata), 
Clymene dolphin (S. clymene), spinner dolphin (S. longirostris), 
striped dolphin (S. coeruleoalba), Blainville's beaked whale 
(Mesoplodon densirostris), Gervais' beaked whale (M. europaeus), 
Cuvier's beaked whale (Ziphius cavirostris), killer whale (Orcinus 
orca), false killer whale (Pseudorca crassidens), pygmy killer whale 
(Feresa attenuata), Risso's dolphin (Grampus griseus), Fraser's dolphin 
(Lagenodelphis hosei), melon-headed whale (Peponocephala electra), 
rough-toothed dolphin (Steno bredanensis), and short-finned pilot whale 
(Globicephala macrorhynchus).
    Of these species, only the sperm whale is listed as endangered 
under the Endangered Species Act (ESA) and as depleted throughout its 
range under the MMPA. Sperm whale occurrence within W-151A is unlikely 
because almost all reported sightings have occurred in water depths 
greater than 200 m (656.2 ft).
    Because these species are unlikely to occur within the W-151A area, 
Eglin AFB has not requested and we are not proposing to authorize take 
for them. Thus, we do not consider these species further in this 
notice.
    We have reviewed Eglin AFB's species descriptions, including life 
history information, distribution, regional distribution, diving 
behavior, and acoustics and hearing, for accuracy and completeness. 
That information is contained in sections 3 and 4 of Eglin AFB's 2016 
Authorization application and to Chapter 3 in Eglin AFB's EA rather 
than reprinting the information here.

Other Marine Mammals in the Proposed Action Area

    The endangered West Indian manatee (Trichechus manatus) rarely 
occurs in the area (USAF 2014). The U.S. Fish and Wildlife Service has 
jurisdiction over the manatee; therefore, we would not include a 
proposed Authorization to harass manatees and do not discuss this 
species further in this notice.

Potential Effects of the Specified Activity on Marine Mammals and Their 
Habitat

    This section includes a summary and discussion of the ways that 
components (e.g., exposure to impulsive noise and pressure waves 
generated by live ordnance detonation at or near the surface of the 
water) of the specified activity, including mitigation may impact 
marine mammals and their habitat. The ``Estimated Take by Incidental 
Harassment'' section later in this document will include a quantitative 
analysis of the number of individuals that we expect Eglin AFB to take 
during this activity. The ``Negligible Impact Analysis'' section will 
include the analysis of how this specific activity would impact marine 
mammals. We will consider the content of the following sections: 
``Estimated Take by Incidental Harassment'' and ``Proposed Mitigation'' 
to draw conclusions regarding the likely impacts of these activities on 
the reproductive success or survivorship of individuals--and from that 
consideration--the likely impacts of this activity on the affected 
marine mammal populations or stocks.
    In the following discussion, we provide general background 
information on sound and marine mammal hearing before considering 
potential effects to marine mammals from sound produced by underwater 
detonations.

Brief Background on Sound and WSEP Sound Types

    Sound travels in waves, the basic components of which are 
frequency, wavelength, velocity, and amplitude. Frequency is the number 
of pressure waves that pass by a reference point per unit of time and 
is measured in hertz (Hz) or cycles per second. Wavelength is the 
distance between two peaks of a sound wave; lower frequency sounds have 
longer wavelengths than higher frequency sounds and attenuate 
(decrease) more rapidly in shallower water. Amplitude is the height of 
the sound pressure wave or the ``loudness'' of a sound and is typically 
measured using the decibel (dB) scale. A dB is the ratio between a 
measured pressure (with sound) and a reference pressure (sound at a 
constant pressure, established by scientific standards). It is a 
logarithmic unit that accounts for large variations in amplitude; 
therefore, relatively small changes in dB ratings correspond to large 
changes in sound pressure. When referring to sound pressure levels 
(SPLs; the sound force per unit area), sound is referenced in the 
context of underwater sound pressure to 1 microPascal ([mu]Pa). One 
pascal is the pressure resulting from a force of one newton exerted 
over an area of one square meter. The source level (SL) represents the 
sound level at a distance of 1 m from the source (referenced to 1 
[mu]Pa). The received level is the sound level at the listener's 
position. Note that we reference all underwater sound levels in this 
document to a pressure of 1 [mu]Pa.
    Root mean square (rms) is the quadratic mean sound pressure over 
the duration of an impulse. Acousticians calculate rms by squaring all 
of the sound amplitudes, averaging the squares, and then taking the 
square root of the average (Urick 1983). Rms accounts for both positive 
and negative values; squaring the pressures makes all values positive 
so that one can account for the values in the summation of pressure 
levels (Hastings and Popper 2005). Researchers often use this 
measurement in the context of discussing behavioral effects, in part 
because behavioral effects, which often result from auditory cues, may 
be better expressed through averaged units than by peak pressures.
    When underwater objects vibrate, or activity occurs, sound-pressure 
waves are created that alternately compress and decompress the water as 
the sound wave travels. These underwater sound waves radiate in all 
directions away from the source similar to ripples on the surface of a 
pond except in cases where the sound is directional. Aquatic life and 
underwater receptors such as hydrophones detect the changes in pressure 
associated with the compressions and decompressions of underwater sound 
waves as underwater sound or noise. Even in the absence of sound from 
the specified activity, the underwater environment has noise, or 
ambient sound, which is the environmental background sound levels 
lacking a single source or point (Richardson et. al., 1995). The sound 
level of a region is defined by the total acoustic energy being 
generated by known and unknown sources. These sources can be physical 
(e.g., waves, earthquakes, ice, or atmospheric sound); biological 
(e.g., sounds produced by marine mammals, fish, and invertebrates); and 
anthropogenic (e.g., vessels, dredging, aircraft, or construction).
    The sum of the various natural and anthropogenic sound sources at 
any given location and time comprising the ambient, or background, 
sound depends on the source levels (as determined by weather conditions 
and levels of biological and anthropogenic activities) and the ability 
of sounds to propagate through the environment. In turn, sound 
propagation is dependent on the spatially and temporally varying 
properties of the water column and sea floor, and is frequency-
dependent. As a result of the dependence on a large number of varying 
factors, ambient sound levels can be expected to vary widely over both 
coarse and fine spatial and temporal scales. Sound levels at a given 
frequency and location can vary by 10-20 dB from day to day (Richardson 
et. al., 1995). The result is

[[Page 83214]]

that, depending on the source type and its intensity, sound from the 
specified activity may be a negligible addition to the local 
environment or could form a distinctive signal that may affect marine 
mammals.
    Sounds fall into one of two general sound types: Impulsive (defined 
in the following paragraphs) and non-pulsed. The distinction between 
these two sound types is important because they have differing 
potential to cause physical effects, particularly with regard to 
hearing (e.g., Ward, 1997 in Southall et al., 2007). Please see 
Southall et al., (2007) for an in-depth discussion of these concepts. 
The sounds produced by the proposed WSEP activities are impulsive. 
Impulsive sound sources (e.g., explosions, gunshots, sonic booms, 
impact pile driving) produce signals that are brief (typically 
considered to be less than one second), broadband, atonal transients 
(ANSI, 1986; Harris, 1998; NIOSH, 1998; ISO, 2003; ANSI, 2005) and 
occur either as isolated events or repeated in some succession. These 
sounds have a relatively rapid rise from ambient pressure to a maximal 
pressure value followed by a rapid decay period that may include a 
period of diminishing, oscillating maximal and minimal pressures, and 
generally have an increased capacity to induce physical injury as 
compared with sounds that lack these features.

Marine Mammal Hearing

    When considering the influence of various kinds of sound on the 
marine environment, it is necessary to understand that different kinds 
of marine life are sensitive to different frequencies of sound. Current 
data indicate that not all marine mammal species have equal hearing 
capabilities (Richardson et al., 1995; Southall et al., 1997; Wartzok 
and Ketten 1999; Au and Hastings 2008).
    Animals are less sensitive to sounds at the outer edges of their 
functional hearing range and are more sensitive to a range of 
frequencies within the middle of their functional hearing range. For 
mid-frequency cetaceans, such the common bottlenose dolphin and the 
Atlantic spotted dolphin (the two marine mammal species with expected 
occurrence in the EGTTR WSEP mission area), functional hearing 
estimates occur between approximately 150 Hz and 160 kHz with best 
hearing estimated to occur between approximately 10 to less than 100 
kHz (Finneran et al., 2005 and 2009; Natchtigall et al., 2005 and 2008; 
Yuen et al., 2005; Popov et al., 2010 and 2011; and Schlundt et al., 
2011).
    On August 4, 2016, NMFS released its Technical Guidance for 
Assessing the Effects of Anthropogenic Sound on Marine Mammal Hearing 
(Technical Guidance)(NMFS 2016; 81 FR 51694). This new guidance 
established new thresholds for predicting onset of temporary (TTS) and 
permanent (PTS) threshold shifts for impulsive (e.g., explosives and 
impact pile drivers) and non-impulsive (e.g., vibratory pile drivers) 
sound sources. These acoustic thresholds are presented using dual 
metrics of cumulative sound exposure level (SELcum) and peak 
sound level (PK) for impulsive sounds and SELcum for non-
impulsive sounds. Eglin AFB used the new acoustic Technical Guidance to 
evaluate potential effects to marine mammals (more detailed information 
on PTS and TTS is provided below).
Common Bottlenose Dolphin Vocalization and Hearing
    Bottlenose dolphins can typically hear within a broad frequency 
range of 0.04 to 160 kHz (Au 1993; Turl 1993). Electrophysiological 
experiments suggest that the bottlenose dolphin brain has a dual 
analysis system: One specialized for ultrasonic clicks and another for 
lower-frequency sounds, such as whistles (Ridgway 2000). Scientists 
have reported a range of highest sensitivity between 25 and 70 kHz, 
with peaks in sensitivity at 25 and 50 kHz (Nachtigall et al., 2000). 
Research on the same individuals indicates that auditory thresholds 
obtained by electrophysiological methods correlate well with those 
obtained in behavior studies, except at lower (10 kHz) and higher (80 
and 100 kHz) frequencies (Finneran and Houser 2006).
    Sounds emitted by common bottlenose dolphins fall into two broad 
categories: Pulsed sounds (including clicks and burst-pulses) and 
narrow-band continuous sounds (whistles), which usually are frequency 
modulated. Clicks have a dominant frequency range of 110 to 130 kHz and 
a source level of 218 to 228 dB re: 1 [mu]Pa (peak-to-peak) (Au 1993) 
and 3.4 to 14.5 kHz at 125 to 173 dB re 1 [mu]Pa (peak-to-peak) (Ketten 
1998). Whistles are primarily associated with communication and can 
serve to identify specific individuals (i.e., signature whistles) 
(Caldwell and Caldwell 1965; Janik et al., 2006). Cook et al. (2004) 
classified up to 52 percent of whistles produced by bottlenose dolphin 
groups with mother-calf pairs as signature whistles. Sound production 
is also influenced by group type (single or multiple individuals), 
habitat, and behavior (Nowacek 2005). Bray calls (low-frequency 
vocalizations; majority of energy below 4 kHz), for example, are used 
when capturing fish, specifically sea trout (Salmo trutta) and Atlantic 
salmon (Salmo salar), in some regions (i.e., Moray Firth, Scotland) 
(Janik 2000). Additionally, whistle production has been observed to 
increase while feeding (Acevedo-Guti[eacute]rrez and Stienessen 2004; 
Cook et al., 2004).
Atlantic Spotted Dolphin Vocalization and Hearing
    Researchers have recorded a variety of sounds including whistles, 
echolocation clicks, squawks, barks, growls, and chirps for the 
Atlantic spotted dolphin. Whistles have dominant frequencies below 20 
kHz (range: 7.1 to 14.5 kHz) but multiple harmonics extend above 100 
kHz, while burst pulses consist of frequencies above 20 kHz (dominant 
frequency of approximately 40 kHz) (Lammers et al., 2003). Other 
sounds, such as squawks, barks, growls, and chirps, typically range in 
frequency from 0.1 to 8 kHz (Thomson and Richardson 1995). Recorded 
echolocation clicks had two dominant frequency ranges at 40 to 50 kHz 
and 110 to 130 kHz, depending on source level (i.e., lower source 
levels typically correspond to lower frequencies and higher frequencies 
to higher source levels (Au and Herzing 2003). Echolocation click 
source levels as high as 210 dB re 1 [mu]Pa-m peak-to-peak have been 
recorded (Au and Herzing 2003). Spotted dolphins in the Bahamas were 
frequently recorded during agonistic/aggressive interactions with 
bottlenose dolphins (and their own species) to produce squawks (0.2 to 
12 kHz broad band burst pulses; males and females), screams (5.8 to 9.4 
kHz whistles; males only), barks (0.2 to 20 kHz burst pulses; males 
only), and synchronized squawks (0.1-15 kHz burst pulses; males only in 
a coordinated group) (Herzing 1996). The hearing ability for the 
Atlantic spotted dolphin is unknown; however, odontocetes are generally 
adapted to hear high-frequencies (Ketten 1997).
    The Maritime WSEP training exercises proposed for the incidental 
take of marine mammals have the potential to take marine mammals by 
exposing them to impulsive noise and pressure waves generated by live 
ordnance detonation at or near the surface of the water. Exposure to 
energy, pressure, or direct strike by ordnance has the potential to 
result in non-lethal injury (Level A harassment), disturbance (Level B 
harassment), serious injury, and/or mortality. In addition, NMFS also 
considered the potential for harassment from vessel and aircraft 
operations.

[[Page 83215]]

Acoustic Effects, Underwater Detonations

    Underwater explosive detonations send a shock wave and sound energy 
through the water and can release gaseous by-products, create an 
oscillating bubble, or cause a plume of water to shoot up from the 
water surface. The shock wave and accompanying noise are of most 
concern to marine animals. Depending on the intensity of the shock wave 
and size, location, and depth of the animal, an animal can be injured, 
killed, suffer non-lethal physical effects, experience hearing related 
effects with or without behavioral responses, or exhibit temporary 
behavioral responses or tolerance from hearing the blast sound. 
Generally, exposures to higher levels of impulse and pressure levels 
would result in greater impacts to an individual animal.
    The effects of underwater detonations on marine mammals are 
dependent on several factors, including the size, type, and depth of 
the animal; the depth, intensity, and duration of the sound; the depth 
of the water column; the substrate of the habitat; the standoff 
distance between activities and the animal; and the sound propagation 
properties of the environment. Thus, we expect impacts to marine 
mammals from MaritimeWSEP activities to result primarily from acoustic 
pathways. As such, the degree of the effect relates to the received 
level and duration of the sound exposure, as influenced by the distance 
between the animal and the source. The further away from the source, 
the less intense the exposure should be.
    The potential effects of underwater detonations from the proposed 
Maritime WSEP training activities may include one or more of the 
following: Temporary or permanent hearing impairment; non-auditory 
physical or physiological effects; behavioral disturbance; and masking 
(Richardson et al., 1995; Gordon et al., 2004; Nowacek et al., 2007; 
Southall et al., 2007). However, the effects of noise on marine mammals 
are highly variable, often depending on species and contextual factors 
(based on Richardson et al., 1995).
    In the absence of mitigation, impacts to marine species could 
result from physiological and behavioral responses to both the type and 
strength of the acoustic signature (Viada et al., 2008). The type and 
severity of behavioral impacts are more difficult to define due to 
limited studies addressing the behavioral effects of impulsive sounds 
on marine mammals. Potential effects from impulsive sound sources can 
range in severity from effects such as behavioral disturbance or 
tactile perception to physical discomfort, slight injury of the 
internal organs and the auditory system, or mortality (Yelverton et 
al., 1973).

Hearing Impairment and Other Physical Effects

    Marine mammals exposed to high intensity sound repeatedly or for 
prolonged periods can experience hearing threshold shift (TS), which is 
the loss of hearing sensitivity at certain frequency ranges (Kastak et 
al., 1999; Schlundt et al., 2000; Finneran et al., 2002, 2005). TS can 
be permanent (PTS), in which case the loss of hearing sensitivity is 
not recoverable, or temporary (TTS), in which case the animal's hearing 
threshold would recover over time (Southall et al., 2007). Marine 
mammals depend on acoustic cues for vital biological functions, (e.g., 
orientation, communication, finding prey, avoiding predators) thus, TTS 
may result in reduced fitness in survival and reproduction. However, 
this depends on the frequency and duration of TTS, as well as the 
biological context in which it occurs. TTS of limited duration, 
occurring in a frequency range that does not coincide with that used 
for recognition of important acoustic cues, would have little to no 
effect on an animal's fitness. Repeated sound exposure that leads to 
TTS could cause PTS. PTS constitutes injury, but TTS does not (Southall 
et al., 2007). The following subsections provide a summary on the 
possibilities of TTS, PTS, and non-auditory physical effects.
Temporary Threshold Shift
    TTS is the mildest form of hearing impairment that can occur during 
exposure to a strong sound (Kryter 1985). While experiencing TTS, the 
hearing threshold rises, and a sound must be stronger in order to be 
heard. In terrestrial mammals, TTS can last from minutes or hours to 
days (in cases of strong TTS). For sound exposures at or somewhat above 
the TTS threshold, hearing sensitivity in both terrestrial and marine 
mammals recovers rapidly after exposure to the sound ends. Few data on 
sound levels and durations necessary to elicit mild TTS have been 
obtained for marine mammals. According to Finneran and Jenkins (2012) 
the TTS onset thresholds for mid-frequency cetaceans are based on TTS 
data from a beluga whale exposed to an underwater impulse produced from 
a seismic watergun. TTS thresholds also use a dual criterion, and in a 
given analysis the more conservative of the two criteria is applied. 
The TTS thresholds for bottlenose and Atlantic spotted dolphins consist 
of the SEL of an underwater blast weighted to the hearing sensitivity 
of mid-frequency cetaceans and a peak SPL measure of the same. The dual 
thresholds for TTS in mid-frequency cetaceans are:
     SEP (mid-frequency weighted) of 170 dB re 1 [mu]Pa\2\s
     Peak SPL (unweighted) of 224 dB re 1 [mu]Pa
Permanent Threshold Shift
    When PTS occurs, there is physical damage to the sound receptors in 
the ear. In severe cases, there can be total or partial deafness, while 
in other cases the animal has an impaired ability to hear sounds in 
specific frequency ranges (Kryter 1985). There is no specific evidence 
that exposure to pulses of sound can cause PTS in any marine mammal. 
However, given the possibility that mammals close to a sound source 
might incur TTS, there has been further speculation about the 
possibility that some individuals might incur PTS. Single or occasional 
occurrences of mild TTS are not indicative of permanent auditory 
damage, but repeated or (in some cases) single exposures to a level 
well above that causing TTS onset might elicit PTS.
    Relationships between TTS and PTS thresholds have not been studied 
in marine mammals, but they are assumed to be similar to those in 
humans and other terrestrial mammals. PTS might occur at a received 
sound level at least several dB above that inducing mild TTS if the 
animal were exposed to strong sound pulses with rapid rise time. There 
is no empirical data for onset of PTS in any marine mammal for ethical 
reasons and researchers must extrapolate PTS-onset based on hearing 
loss growth rates (i.e., rate of how quickly threshold shifts grow in 
relation to increases in decibel level; expressed in dB of TTS/dB of 
noise) from limited marine mammal TTS studies and more numerous 
terrestrial mammal TTS/PTS experiments. Typically, the magnitude of a 
threshold shift increases with increasing duration or level of 
exposure, until it becomes asymptotic (growth rate begins to level or 
the upper limit of TTS; Mills et al., 1979; Clark et al., 1987; Laroche 
et al., 1989; Yost 2007). Based on data from terrestrial mammals, a 
precautionary assumption is that the PTS threshold for impulse sounds 
is at least six dB higher than the TTS threshold on a peak-pressure 
basis and probably greater than six dB (Southall et al., 2007). Jenkins 
and Finneran (2012) define PTS thresholds differently for three groups 
of cetaceans based on their hearing sensitivity: Low-frequency, mid-

[[Page 83216]]

frequency; and high frequency. Bottlenose and Atlantic spotted dolphins 
(the subject of the Maritime WSEP acoustic impact analysis) both fall 
within the mid-frequency hearing category. The PTS thresholds use a 
dual criterion, one based on SEL and one based on SPL of an underwater 
blast. For a given analysis, the more conservative of the two is 
applied to afford the most protection to marine mammals. The mid-
frequency cetacean criteria for PTS are:
     SEL(mid-frequency weighted) of 185 dB re 1 [mu]Pa\2\s.
     Peak SPL (unweighted) of 230 dB re 1 [mu]Pa.
Non-Auditory Physiological Effects
    Non-auditory physiological effects or injuries that theoretically 
might occur in marine mammals exposed to strong underwater sound 
include stress and other types of organ or tissue damage (Cox et al., 
2006; Southall et al., 2007). While Eglin AFB's activities involve the 
use of explosives that are associated with these types of effects, 
severe injury to marine mammals is not anticipated from these 
activities.
Adverse Stress Responses
    An acoustic source is considered a potential stressor if, by its 
action on the animal, via auditory or non-auditory means, it may 
produce a stress response in the animal. Here, the stress response will 
refer to an increase in energetic expenditure that results from 
exposure to the stressor and which is predominantly characterized by 
either the stimulation of the sympathetic nervous system (SNS) or the 
hypothalamic-pituitary-adrenal (HPA) axis (Reeder and Kramer 2005). The 
SNS response to a stressor is immediate and acute and occurs by the 
release of the catecholamine neurohormones norepinephrine and 
epinephrine (i.e., adrenaline). These hormones produce elevations in 
the heart and respiration rate, increase awareness, and increase the 
availability of glucose and lipids for energy. The HPA response results 
in increases in the secretion of the glucocorticoid steroid hormones, 
predominantly cortisol in mammals. The presence and magnitude of a 
stress response in an animal depends on a number of factors. These 
include the animal's life history stage (e.g., neonate, juvenile, 
adult), the environmental conditions, reproductive or developmental 
state, and experience with the stressor. Not only will these factors be 
subject to individual variation, but they will also vary within an 
individual over time. The stress response may or may not result in a 
behavioral change, depending on the characteristics of the exposed 
animal. However, provided that a stress response occurs, we assume that 
some contribution is made to the animal's allostatic load. One can 
assume that any immediate effect of exposure that produces an injury 
also produce a stress response and contribute to the allostatic load. 
Allostasis is the ability of an animal to maintain stability through 
change by adjusting its physiology in response to both predictable and 
unpredictable events (McEwen and Wingfield 2003). If the animal does 
not perceive the sound, the acoustic source would not produce tissue 
effects and does not produce a stress response by any other means. 
Thus, we expect that the exposure does not contribute to the allostatic 
load.
Serious Injury/Mortality
    Elgin AFB proposes to use several types of explosive sources during 
its training exercises. Proposed detonations could be either in air, at 
the water surface, or underwater, depending on the mission and type of 
munition. Airburst detonations have little transfer of energy 
underwater, but surface and underwater detonations are of most concern 
regarding potential effects to marine mammals. The underwater 
explosions from these weapons would send a shock wave and blast noise 
through the water, release gaseous by-products, create an oscillating 
bubble, and cause a plume of water to shoot up from the water surface. 
The shock wave and blast noise are of most concern to marine animals. 
In general, potential impacts from explosive detonations can range from 
brief effects (such as short term behavioral disturbance), tactile 
perception, physical discomfort, slight injury of the internal organs, 
and death of the animal (Yelverton et al., 1973; O'Keeffe and Young 
1984; DoN 2001). The effects of an underwater explosion on a marine 
mammal depend on many factors, including: the size, type, and depth of 
both the animal and the explosive charge; the depth of the water 
column; and the standoff distance between the charge and the animal, as 
well as the sound propagation properties of the environment. Physical 
damage of tissues resulting from a shock wave (from an explosive 
detonation) constitutes an injury. Blast effects are greatest at the 
gas-liquid interface (Landsberg 2000) and gas containing organs, 
particularly the lungs and gastrointestinal tract, are especially 
susceptible to damage (Goertner 1982; Hill 1978; Yelverton et al., 
1973). Nasal sacs, larynx, pharynx, trachea, and lungs may be damaged 
by compression/expansion caused by the oscillations of the blast gas 
bubble (Reidenberg and Laitman 2003). Severe damage (from the shock 
wave) to the ears can include tympanic membrane rupture, fracture of 
the ossicles, cochlear damage, hemorrhage, and cerebrospinal fluid 
leakage into the middle ear.
    Non-lethal injury includes slight injury to internal organs and the 
auditory system, however, delayed lethality can be a result of 
individual or cumulative sublethal injuries (DoN, 2001). Immediate 
lethal injury would be a result of massive combined trauma to internal 
organs as a direct result of proximity to the point of detonation (DoN 
2001).
Disturbance Reactions
    Disturbance includes a variety of effects, including subtle changes 
in behavior, more conspicuous changes in activities, and displacement, 
or abandonment of habitat. Behavioral responses to sound are highly 
variable and context-specific and reactions, if any, depend on species, 
state of maturity, experience, current activity, reproductive state, 
auditory sensitivity, time of day, and many other factors (Richardson 
et al., 1995; Wartzok et al., 2003; Southall et al., 2007). Behavioral 
reactions can vary among individuals as well as within an individual, 
depending on previous experience with a sound source, context, and 
numerous other factors (Ellison et al., 2012). Behavioral reactions can 
also vary depending on the characteristics associated with the sound 
source (e.g., whether it is moving or stationary, the number of 
sources, etc).
Tolerance
    Studies on marine mammals' tolerance to sound in the natural 
environment are relatively rare. Richardson et al. (1995) defined 
tolerance as the occurrence of marine mammals in areas where they are 
exposed to human activities or manmade noise. In many cases, tolerance 
develops by the animal habituating to the stimulus (i.e., the gradual 
waning of responses to a repeated or ongoing stimulus) (Richardson, et 
al., 1995; Wartzok et al., 2003), but because of ecological or 
physiological requirements, many marine animals may need to remain in 
areas where they are exposed to chronic stimuli (Richardson, et al., 
1995). Animals are most likely to habituate to sounds that are 
predictable and unvarying.
    The opposite process is sensitization, when an unpleasant 
experience leads to subsequent responses, often in the form

[[Page 83217]]

of avoidance, at a lower level of exposure. Behavioral state may affect 
the type of response as well. For example, animals that are resting may 
show greater behavioral change in response to disturbing sound levels 
than animals that are highly motivated to remain in an area for feeding 
(Richardson et al., 1995; NRC, 2003; Wartzok et al., 2003).
    Numerous studies have shown that underwater sounds are often 
readily detectable by marine mammals in the water at distances of many 
kilometers. However, other studies have shown that marine mammals at 
distances more than a few kilometers away often show no apparent 
response to activities of various types (Miller et al., 2005). This is 
often true even in cases when the sounds must be readily audible to the 
animals based on measured received levels and the hearing sensitivity 
of that mammal group. Although various baleen whales, toothed whales, 
and (less frequently) pinnipeds have been shown to react behaviorally 
to underwater sound from impulsive sources such as airguns, at other 
times, mammals of all three types have shown no overt reactions (e.g., 
Malme et al., 1986; Richardson et al., 1995; Madsen and Mohl, 2000; 
Croll et al., 2001; Jacobs and Terhune 2002; Madsen et al., 2002; 
MacLean and Koski, 2005; Miller et al., 2005; Bain and Williams 2006).
    Controlled experiments with captive marine mammals showed 
pronounced behavioral reactions, including avoidance of loud sound 
sources (Ridgway et al., 1997; Finneran et al., 2003). Observed 
responses of wild marine mammals to loud pulsed sound sources 
(typically seismic guns or acoustic harassment devices) have been 
varied but often consist of avoidance behavior or other behavioral 
changes suggesting discomfort (Morton and Symonds, 2002; Thorson and 
Reyff, 2006; see also Gordon et al., 2004; Wartzok et al., 2003; 
Nowacek et al., 2007).
    Because the few available studies show wide variation in response 
to underwater sound, it is difficult to quantify exactly how sound from 
the Maritime WSEP operational testing would affect marine mammals. It 
is likely that the onset of underwater detonations could result in 
temporary, short term changes in an animal's typical behavior and/or 
avoidance of the affected area. These behavioral changes may include 
(Richardson et al., 1995): Changing durations of surfacing and dives, 
number of blows per surfacing, or moving direction and/or speed; 
reduced/increased vocal activities; changing/cessation of certain 
behavioral activities (such as socializing or feeding); visible startle 
response or aggressive behavior (such as tail/fluke slapping or jaw 
clapping); or avoidance of areas where sound sources are located.
    The biological significance of any of these behavioral disturbances 
is difficult to predict, especially if the detected disturbances appear 
minor. However generally, one could expect the consequences of 
behavioral modification to be biologically significant if the change 
affects growth, survival, or reproduction. Significant behavioral 
modifications that could potentially lead to effects on growth, 
survival, or reproduction include:
     Drastic changes in diving/surfacing patterns (such as 
those thought to cause beaked whale stranding due to exposure to 
military mid-frequency tactical sonar);
     Habitat abandonment due to loss of desirable acoustic 
environment; and
     Cessation of feeding or social interaction.
    The onset of behavioral disturbance from anthropogenic sound 
depends on both external factors (characteristics of sound sources and 
their paths) and the specific characteristics of the receiving animals 
(hearing, motivation, experience, demography) and is difficult to 
predict (Southall et al., 2007). However, Finneran and Schlundt (2004) 
and Schlundt et al., 2000 reported on observations of behavioral 
reactions in captive dolphins and belugas to pure tones (different type 
of noise than that produced from an underwater detonation). The 
behavioral impacts threshold for mid-frequency cetaceans exposed to 
multiple, successive detonations is 165 dB re 1 [micro]Pa\2\s SEL (mid-
frequency weighted).
Auditory Masking
    Natural and artificial sounds can disrupt behavior by masking, or 
interfering with, a marine mammal's ability to hear other sounds. 
Masking occurs when the receipt of a sound interferes with by another 
coincident sound at similar frequencies and at similar or higher levels 
(Clark et al., 2009). Chronic exposure to excessive, though not high-
intensity, sound could cause masking at particular frequencies for 
marine mammals, which utilize sound for vital biological functions. 
Masking can interfere with detection of acoustic signals such as 
communication calls, echolocation sounds, and environmental sounds 
important to marine mammals for other purposes such as navigation. 
Therefore, under certain circumstances, marine mammals whose acoustical 
sensors or environment are being severely masked could also be impaired 
from maximizing their performance fitness in survival and reproduction. 
If the coincident (masking) sound were man-made, it could be 
potentially harassing if it disrupted hearing-related behavior. It is 
important to distinguish TTS and PTS, which persist after the sound 
exposure, from masking, which occurs during the sound exposure. 
Introduced underwater sound may, through masking, more specifically 
reduce the effective communication distance of a marine mammal species 
if the frequency of the source is close to that used as a signal by the 
marine mammal, and if the anthropogenic sound is present for a 
significant fraction of the time (Richardson et al., 1995). Marine 
mammals are thought to be able to compensate for communication masking 
by adjusting their acoustic behavior through shifting call frequencies, 
increasing call volume, and increasing vocalization rates. For example 
in one study, blue whales increased call rates when exposed to noise 
from seismic surveys in the St. Lawrence Estuary (Di Iorio and Clark 
2010). Other studies reported that some North Atlantic right whales 
exposed to high shipping noise increased call frequency (Parks et al., 
2007) and some humpback whales responded to low-frequency active sonar 
playbacks by increasing song length (Miller et al., 2000). 
Additionally, beluga whales change their vocalizations in the presence 
of high background noise possibly to avoid masking calls (Au et al., 
1985; Lesage et al., 1999; Scheifele et al., 2005).
    While it may occur temporarily, we do not expect auditory masking 
to result in detrimental impacts to an individual's or population's 
survival, fitness, or reproductive success. Dolphin movement is not 
restricted within the W-151A test area, allowing for movement out of 
the area to avoid masking impacts and the sound resulting from the 
underwater detonations is short in duration. Also, masking is typically 
of greater concern for those marine mammals that utilize low frequency 
communications, such as baleen whales and, as such, is not likely to 
occur for marine mammals in the W-151A test area.

Vessel and Aircraft Presence

    The marine mammals most vulnerable to vessel strikes are slow-
moving and/or spend extended periods of time at the surface in order to 
restore oxygen levels within their tissues after deep dives (e.g., 
North Atlantic right whales (Eubalaena glacialis), fin whales 
(Balaenoptera physalus), and sperm

[[Page 83218]]

whales). Smaller marine mammals such as common bottlenose and Atlantic 
spotted dolphins (the species anticipated to occur in the area of Eglin 
AFB's activities) are agile and move more quickly through the water, 
making them less susceptible to ship strikes. NMFS and Eglin AFB are 
not aware of any vessel strikes of common bottlenose and Atlantic 
spotted dolphins within in W-151 during training operations and both 
parties do not anticipate that Eglin AFB vessels engaged in the 
specified activity would strike any marine mammals.
    Dolphins within the Gulf of Mexico are continually exposed to 
recreational, commercial, and military vessels. Behaviorally, marine 
mammals may or may not respond to the operation of vessels and 
associated noise. Responses to vessels vary widely among marine mammals 
in general, but also among different species of small cetaceans. 
Responses may include attraction to the vessel (Richardson et al., 
1995); altering travel patterns to avoid vessels (Constantine 2001; 
Nowacek et al., 2001; Lusseau 2003, 2006); relocating to other areas 
(Allen and Read, 2000); cessation of feeding, resting, and social 
interaction (Baker et al., 1983; Bauer and Herman 1986; Hall 1982; 
Krieger and Wing 1984; Lusseau 2003; Constantine et al., 2004); 
abandoning feeding, resting, and nursing areas (Jurasz and Jurasz 1979; 
Dean et al., 1985; Glockner-Ferrari and Ferrari 1985, 1990; Lusseau 
2005; Norris et al., 1985; Salden 1988; Forest 2001; Morton and Symonds 
2002; Courbis 2004; Bejder 2006); stress (Romano et al., 2004); and 
changes in acoustic behavior (Van Parijs and Corkeron 2001). However, 
in some studies marine mammals display no reaction to vessels (Watkins 
1986; Nowacek et al., 2003) and many odontocetes show considerable 
tolerance to vessel traffic (Richardson et al., 1995). Dolphins may 
actually reduce the energetic cost of traveling by riding the bow or 
stern waves of vessels (Williams et al., 1992; Richardson et al., 
1995).
    Aircraft produce noise at frequencies that are well within the 
frequency range of cetacean hearing and also produce visual signals 
such as the aircraft itself and its shadow (Richardson et al., 1995, 
Richardson and Wursig 1997). A major difference between aircraft noise 
and noise caused by other anthropogenic sources is that the sound is 
generated in the air, transmitted through the water surface and then 
propagates underwater to the receiver, diminishing the received levels 
significantly below what is heard above the water's surface. Sound 
transmission from air to water is greatest in a sound cone 26 degrees 
directly under the aircraft.
    There are fewer reports of reactions of odontocetes to aircraft 
than those of pinnipeds. Responses to aircraft include diving, slapping 
the water with pectoral fins or tail fluke, or swimming away from the 
track of the aircraft (Richardson et al., 1995). The nature and degree 
of the response, or the lack thereof, are dependent upon the nature of 
the flight (e.g., type of aircraft, altitude, straight vs. circular 
flight pattern). Wursig et al. (1998) assessed the responses of 
cetaceans to aerial surveys in the north central and western Gulf of 
Mexico using a DeHavilland Twin Otter fixed-wing airplane. The plane 
flew at an altitude of 229 m (751.3 ft) at 204 km/hr (126.7 mph) and 
maintained a minimum of 305 m (1,000 ft) straight line distance from 
the cetaceans. Water depth was 100 to 1,000 m (328 to 3,281 ft). 
Bottlenose dolphins most commonly responded by diving (48 percent), 
while 14 percent responded by moving away. Other species (e.g., beluga 
(Delphinapterus leucas) and sperm whales) show considerable variation 
in reactions to aircraft but diving or swimming away from the aircraft 
are the most common reactions to low flights (less than 500 m; 1,640 
ft).

Direct Strike by Ordnance

    Another potential risk to marine mammals is direct strike by 
ordnance, in which the ordnance physically hits an animal. While strike 
from an item falling through the water column is possible, the 
potential risk of a direct hit to an animal within the target area 
would be so low because objects sink slowly and most projectiles fired 
at targets usually hit those targets.

Anticipated Effects on Habitat

    Detonations of live ordnance would result in temporary changes to 
the water environment. Munitions could hit the targets and not explode 
in the water. However, because the targets are located over the water, 
in water explosions could occur. An underwater explosion from these 
weapons could send a shock wave and blast noise through the water, 
release gaseous by-products, create an oscillating bubble, and cause a 
plume of water to shoot up from the water surface. However, these 
effects would be temporary and not expected to last more than a few 
seconds.
    Similarly, Eglin AFB does not expect any long-term impacts with 
regard to hazardous constituents to occur. Eglin AFB considered the 
introduction of fuel, debris, ordnance, and chemical materials into the 
water column within its EA and determined the potential effects of each 
to be insignificant. We summarize Eglin AFB's analyses in the following 
paragraphs (for a complete discussion of potential effects, please 
refer to section 3.3 in Eglin AFB's EA).
    Metals typically used to construct bombs, missiles, and gunnery 
rounds include copper, aluminum, steel, and lead, among others. 
Aluminum is also present in some explosive materials. These materials 
would settle to the seafloor after munitions detonate. Metal ions would 
slowly leach into the substrate and the water column, causing elevated 
concentrations in a small area around the munitions fragments. Some of 
the metals, such as aluminum, occur naturally in the ocean at varying 
concentrations and would not necessarily impact the substrate or water 
column. Other metals, such as lead, could cause toxicity in microbial 
communities in the substrate. However, such effects would be localized 
to a very small distance around munitions fragments and would not 
significantly affect the overall habitat quality of sediments in the 
northeastern Gulf of Mexico. In addition, metal fragments would 
corrode, degrade, and become encrusted over time.
    Chemical materials include explosive byproducts and also fuel, oil, 
and other fluids associated with remotely controlled target boats. 
Explosive byproducts would be introduced into the water column through 
detonation of live munitions. Explosive materials would include 2,4,6-
trinitrotoluene (TNT) and Research Department Formula X (RDX), among 
others. Various byproducts are produced during and immediately after 
detonation of TNT and RDX. During the very brief time that a detonation 
is in progress, intermediate products may include carbon ions, nitrogen 
ions, oxygen ions, water, hydrogen cyanide, carbon monoxide, nitrogen 
gas, nitrous oxide, cyanic acid, and carbon dioxide (Becker 1995). 
However, reactions quickly occur between the intermediates, and the 
final products consist mainly of water, carbon monoxide, carbon 
dioxide, and nitrogen gas, although small amounts of other compounds 
are typically produced as well.
    Chemicals introduced into the water column would be quickly 
dispersed by waves, currents, and tidal action, and eventually become 
uniformly distributed. A portion of the carbon compounds such as carbon 
monoxide and carbon dioxide would likely become integrated into the 
carbonate system (alkalinity and pH buffering capacity of seawater). 
Some of the nitrogen and carbon compounds,

[[Page 83219]]

including petroleum products, would be metabolized or assimilated by 
phytoplankton and bacteria. Most of the gas products that do not react 
with the water or become assimilated by organisms would be released 
into the atmosphere. Due to dilution, mixing, and transformation, none 
of these chemicals are expected to have significant impacts on the 
marine environment.
    Explosive material that is not consumed in a detonation could sink 
to the substrate and bind to sediments. However, the quantity of such 
materials is expected to be inconsequential. When munitions function 
properly, nearly full combustion of the explosive materials will occur, 
and only extremely small amounts of raw material will remain. In 
addition, any remaining materials would be naturally degraded. TNT 
decomposes when exposed to sunlight (ultraviolet radiation), and is 
also degraded by microbial activity (Becker, 1995). Several types of 
microorganisms have been shown to metabolize TNT. Similarly, RDX 
decomposes by hydrolysis, ultraviolet radiation exposure, and 
biodegradation.
    While we anticipate that the specified activity may result in 
marine mammals avoiding certain areas due to temporary ensonification, 
this impact to habitat and prey resources would be temporary and 
reversible. The main impact associated with the proposed activity would 
be temporarily elevated noise levels and the associated direct effects 
on marine mammals, previously discussed in this notice. Marine mammals 
are anticipated to temporarily vacate the area of live fire events. 
However, these events usually do not last more than 90 to 120 minutes 
at a time, and animals are anticipated to return to the activity area 
during periods of non-activity. Thus, based on the preceding 
discussion, we do not anticipate that the proposed activity would have 
any habitat-related effects that could cause significant or long-term 
consequences for individual marine mammals or their populations.

Proposed Mitigation

    In order to issue an Authorization under section 101(a)(5)(D) of 
the MMPA, NMFS must set forth the permissible methods of taking 
pursuant to such activity, and other means of effecting the least 
practicable adverse impact on such species or stock and its habitat, 
paying particular attention to rookeries, mating grounds, and areas of 
similar significance, and the availability of such species or stock for 
taking for certain subsistence uses (where relevant).
    The NDAA of 2004 amended the MMPA as it relates to military-
readiness activities and the incidental take authorization process such 
that ``least practicable adverse impact'' shall include consideration 
of personnel safety, practicality of implementation, and impact on the 
effectiveness of the military readiness activity.
    NMFS and Eglin AFB have worked to identify potential practicable 
and effective mitigation measures, which include 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.'' We 
refer the reader to Section 11 of Eglin AFB's application for more 
detailed information on the proposed mitigation measures which include 
the following:

Vessel-Based Monitoring

    Eglin AFB would station a large number of range clearing boats 
(approximately 30 to 35) around the test site to prevent non-
participating vessels from entering the human safety zone. Based on the 
composite footprint, range clearing boats will be located approximately 
15.28 km (9.5 mi) from the detonation point (see Figure 11-1 in Eglin 
AFB's application). However, the actual distance will vary based on the 
size of the munition being deployed.
    Trained protected species observers (PSO) would be aboard five of 
these boats and will conduct protected species surveys before and after 
each test. The protected species survey vessels will be dedicated 
solely to observing for marine species during the pre-mission surveys 
while the remaining safety boats clear the area of non-authorized 
vessels. The protected species survey vessels will begin surveying the 
area at sunrise. The area to be surveyed will encompass the zone of 
influence (ZOI), which is discussed in more detail below.
    Because of human safety issues, observers will be required to leave 
the test area at least 30 minutes in advance of live weapon deployment 
and move to a position on the safety zone periphery, approximately 
15.28 km (9.5 mi) from the detonation point. Observers will continue to 
scan for marine mammals from the periphery. Animals that may enter the 
area after Eglin AFB has completed the pre-mission surveys and prior to 
detonation would not reach the predicted smaller slight lung injury 
and/or mortality zones.

Determination of the Zone of Influence

    Historically, Eglin AFB has conservatively used the number of live 
weapons deployed to estimate take of marine mammals. This method 
assumed a fresh population of marine mammals for each detonation to 
calculate the number taken. However, NMFS requested mission-day 
scenarios in order to be able to model accumulated energy. Therefore, 
each mission-day scenario is considered a separate event to model takes 
as opposed to modeling for each live detonation. Eglin developed three 
mission-day categories (Category A, which represents levels of 
activities considered a worst-case scenario consisting of ordnances 
with large explosive weights as well as surface and subsurface 
detonations; Category B, which represents a `typical' mission day based 
on levels of weapons releases during past Maritime WSEP activities; and 
Category C, which represents munitions with smaller explosive weights 
and surface detonations only), and estimated the number of days each 
category would be executed during the 2017 Maritime WSEP missions (See 
Table 1-3 in Eglin AFB's application for the Mission Day Scenarios). 
Table 4 below provides the categorization of mission days (Table 1-3 in 
Eglin AFB's application), and Table 5 provides the maximum range of 
effects for all criteria and thresholds for mission-day Categories A, 
B, and C. These ranges were calculated based on explosive acoustic 
characteristics, sound propagation, and sound transmission loss in the 
study area (which incorporates water depth, sediment type, wind speed, 
bathymetry, and temperature/salinity profiles). Refer to Appendix A of 
Eglin AFB's application for a complete description of the acoustic 
modeling methodology used in the analysis.

                                           Table 4--Live Munitions Categorized as Representative Mission Days
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                                                                                                 Total
           Mission  category                           Munition                NEW (lbs)        Detonation type       Munitions/    Mission   munitions/
                                                                                                                          day      days/year     year
--------------------------------------------------------------------------------------------------------------------------------------------------------
A......................................  GBU-10/-24/-31.....................         945  Subsurface (10' depth)....           1           2           2

[[Page 83220]]

 
                                         GBU-49.............................         500  Surface...................           2                       4
                                         JASSM..............................         255  Surface...................           2                       4
                                         GBU-12 (PWII)/-54 (LJDAM)/-38/-32           192  Subsurface (10' depth)....           3                       6
                                          (JDAM).
B......................................  AGM-65 (Maverick)..................          86  Surface...................           2           4           8
                                         CBU-105 (WCMD).....................          83  Airburst..................           1                       4
                                         GBU-39 (Small Diameter Bomb).......          37  Surface...................           1                       4
                                         AGM-114 (Hellfire).................          20  Subsurface (10' depth)....           5                      20
C......................................  AGM-176 (Griffin)..................          13  Surface...................           5           2          10
                                         2.75 rockets or AGR-20A/B..........          12  Surface...................          50                     100
                                         AIM-9X.............................         7.9  Surface...................           1                       2
                                         PGU-12 HEI 30 mm...................         0.1  Surface...................         500                   1,000
--------------------------------------------------------------------------------------------------------------------------------------------------------


           Table 5--Criteria and Threshold Radii (in Meters) for Maritime WSEP Mission-Day Categories
----------------------------------------------------------------------------------------------------------------
                                         Level A harassment                     Level B harassment
                                     ------------------------------------------------------------------------------
                                                PTS                                             Behavioral
        Mission-day category         -------------------------                        -----------------------------
                                                                         ITS                                   165
                                             185 dB SEL                                      170 dB SEP
                                                                                                               SEL
------------------------------------------------------------------------------------------------------------- -----
A...................................  945 m..................  4,666 m...............  7,479 m.
B...................................  248 m..................  2,225 m...............  3,959 m.
C...................................  286 m..................  1,128 m...............  1,863 m.
----------------------------------------------------------------------------------------------------------------

    Mortality and slight lung injury threshold ranges would extend from 
47 to 216 m and 84 to 595 m, respectively, depending on the mission-day 
category. These ranges would fall within the Level A harassment ranges. 
Based on the planned activities on a given mission day, and the ranges 
presented in Table 4, Eglin AFB would ensure that the area equating to 
the Level A harassment threshold range is free of protected species. By 
clearing the Level A harassment threshold range of protected species, 
animals that may enter the area after the completed pre-mission surveys 
but prior to detonation would not reach the smaller slight lung injury 
or mortality zones. Because of human safety issues, Eglin AFB would 
require observers to leave the test area at least 30 minutes in advance 
of live weapon deployment and move to a position on the safety zone 
periphery, approximately 15 km (9.5 mi) from the detonation point. 
Observers would continue to scan for marine mammals from the periphery, 
but effectiveness would be limited as the boat would remain at a 
designated station.
    Video Monitoring: In addition to vessel-based monitoring, Eglin AFB 
would position three high-definition video cameras on the GRATV 
anchored on-site, as described earlier, to allow for real-time 
monitoring for the duration of the mission. The camera configuration 
and actual number of cameras used would depend on specific mission 
requirements. In addition to monitoring the area for mission objective 
issues, the camera(s) would also monitor for the presence of protected 
species. A trained marine species observer from Eglin Natural Resources 
would be located in Eglin AFB's Central Control Facility, along with 
mission personnel, to view the video feed before and during test 
activities. The distance to which objects can be detected at the water 
surface by use of the cameras is considered generally comparable to 
that of the human eye.
    The GRATV will be located about 183 m (600 ft) from the target. The 
larger mortality threshold ranges correspond to the modified Goertner 
model adjusted for the weight of an Atlantic spotted dolphin calf, and 
extend from 0 to 216 m (0 to 709 ft) from the target, depending on the 
ordnance, and the Level A ranges for both common bottlenose and 
Atlantic spotted dolphins extend up to 945 m (3,100 ft) from the 
target, depending on the ordnance and harassment criterion. Given these 
distances, observers could reasonably be expected to view a substantial 
portion of the mortality zone in front of the camera, although a small 
portion would be behind or to the side of the camera view. Based on 
previous monitoring reports for this activity, the pre-training surveys 
for delphinids and other protected species within the mission area are 
effective. Observers can view some portion of the Level A harassment 
zone, although the view window would be less than that of the mortality 
zone (a large percentage would be behind or to the side of the camera 
view).
    In addition to the two types of visual monitoring discussed earlier 
in this section, Eglin AFB personnel are present within the mission 
area (on boats and the GRATV) on each day of testing well in advance of 
weapon deployment, typically near sunrise. They will perform a variety 
of tasks including target preparation, equipment checks, etc., and will 
opportunistically observe for marine mammals and indicators as feasible 
throughout test preparation. However, we consider these observations as 
supplemental to the proposed mitigation monitoring and would only occur 
as time and schedule permits. Eglin AFB personnel would relay 
information on these types of sightings to the Lead Biologist, as 
described in the following mitigation sections.

Pre-Mission Monitoring

    The purposes of pre-mission monitoring are to: (1) Evaluate the 
mission site for environmental suitability, and (2) verify that the ZOI 
is free of visually detectable marine mammals, as well as potential 
indicators of these species. On the morning of the mission, the Test 
Director and Safety Officer will confirm that there are no issues that 
would preclude mission execution and that weather is adequate to 
support mitigation measures.

[[Page 83221]]

Sunrise or Two Hours Prior to Mission

    Eglin AFB range clearing vessels and protected species survey 
vessels will be on site at least two hours prior to the mission. The 
Lead Biologist on board one survey vessel will assess the overall 
suitability of the mission site based on environmental conditions (sea 
state) and presence/absence of marine mammal indicators. Eglin AFB 
personnel will communicate this information to Tower Control and 
personnel will relay the information to the Safety Officer in Central 
Control Facility.

One and One-Half Hours Prior to Mission

    Vessel-based surveys will begin approximately one and one-half 
hours prior to live weapons deployment. Surface vessel observers will 
survey the ZOI and relay all marine species and indicator sightings, 
including the time of sighting, GPS location, and direction of travel, 
if known, to the Lead Biologist. The Lead Biologist will document all 
sighting information on report forms which he/she will submit to Eglin 
Natural Resources after each mission. Surveys would continue for 
approximately one hour. During this time, Eglin AFB personnel in the 
mission area will also observe for marine species as feasible. If 
marine mammals or indicators are observed within the ZOI for that day's 
mission activities, the range will be declared ``fouled,'' a term that 
signifies to mission personnel that conditions are such that a live 
ordnance drop cannot occur (e.g., protected species or civilian vessels 
are in the mission area). If there are no observations of marine 
mammals or indicators of marine mammals, Eglin AFB would declare the 
range clear of protected species.

One-Half Hour Prior to Mission

    At approximately 30 minutes prior to live weapon deployment, marine 
species observers will be instructed to leave the mission site and 
remain outside the safety zone, which on average will be 15.28 km (9.5 
mi) from the detonation point. The actual size is determined by weapon 
net explosive weight and method of delivery. The survey team will 
continue to monitor for protected species while leaving the area. As 
the survey vessels leave the area, marine species monitoring of the 
immediate target areas will continue at the Central Control Facility 
through the live video feed received from the high definition cameras 
on the GRATV. Once the survey vessels have arrived at the perimeter of 
the safety zone (approximately 30 minutes after leaving the area per 
instructions from Eglin AFB, depending on actual travel time), Eglin 
AFB will declare the range as ``green'' and the mission will proceed, 
assuming all non-participating vessels have left the safety zone as 
well.

Execution of Mission

    Immediately prior to live weapons drop, the Test Director and 
Safety Officer will communicate to confirm the results of marine mammal 
surveys and the appropriateness of proceeding with the mission. The 
Safety Officer will have final authority to proceed with, postpone, or 
cancel the mission. Eglin AFB would postpone the mission if:
     Any of the high-definition video cameras are not 
operational for any reason;
     Any marine mammal is visually detected within the ZOI. 
Postponement would continue until the animal(s) that caused the 
postponement is: (1) Confirmed to be outside of the ZOI on a heading 
away from the targets; or (2) not seen again for 30 minutes and 
presumed to be outside the ZOI due to the animal swimming out of the 
range;
     Any large schools of fish or large flocks of birds feeding 
at the surface are within the ZOI. Postponement would continue until 
Eglin AFB personnel confirm that these potential indicators are outside 
the ZOI:
     Any technical or mechanical issues related to the aircraft 
or target boats; or
     Any non-participating vessel enters the human safety zone 
prior to weapon release.
    In the event of a postponement, protected species monitoring would 
continue from the Central Control Facility through the live video feed. 
Observers would also continue to monitor from the vessels at the safety 
perimeter, with limited effectiveness due to the distance from the 
detonation site.

Post-Mission Monitoring

    Post-mission monitoring determines the effectiveness of pre-mission 
mitigation by reporting sightings of any marine mammals. Post-
detonation monitoring surveys will commence once the mission has ended 
or, if required, as soon as personnel declare the mission area safe. 
Vessels will move into the survey area from outside the safety zone and 
monitor for at least 30 minutes, concentrating on the area down-current 
of the test site. This area is easily identifiable because of the 
floating debris in the water from impacted targets. Up to 10 Eglin AFB 
support vessels will be cleaning debris and collecting damaged targets 
from this area thus spending several hours in the area once Eglin AFB 
completes the mission. Observers will document and report any marine 
mammal species, number, location, and behavior of any animals observed 
to Eglin Natural Resources.

Mission Delays Due to Weather

    Eglin AFB would delay or reschedule Maritime WSEP missions if the 
Beaufort sea state is greater than number 4 at the time of the testing 
activities. The Lead Biologist aboard one of the survey vessels will 
make the final determination of whether conditions are conducive for 
sighting protected species or not.
    We have carefully evaluated Eglin AFB's proposed mitigation 
measures in the context of ensuring that we prescribe the means of 
effecting the least practicable impact on the affected marine mammal 
species and stocks and their habitat. Our evaluation of potential 
measures included consideration of the following factors in relation to 
one another:
     The manner in which, and the degree to which, the 
successful implementation of the measure is expected to minimize 
adverse impacts;
     The proven or likely efficacy of the specific measure to 
minimize adverse impacts as planned; and
     The practicability of the measure for applicant 
implementation.
    Any mitigation measure(s) prescribed by NMFS should be able to 
accomplish, have a reasonable likelihood of accomplishing (based on 
current science), or contribute to the accomplishment of one or more of 
the general goals listed here:
    1. Avoidance or minimization of injury or death of marine mammals 
wherever possible (goals 2, 3, and 4 may contribute to this goal);
    2. A reduction in the numbers of marine mammals (total number or 
number at biologically important time or location) exposed to stimuli 
expected to result in incidental take (this goal may contribute to 1, 
above, or to reducing takes by behavioral harassment only);
    3. A reduction in the number of times (total number or number at 
biologically important time or location) individuals would be exposed 
to stimuli that we expect to result in the take of marine mammals (this 
goal may contribute to 1, above, or to reducing harassment takes only);
    4. A reduction in the intensity of exposures (either total number 
or number at biologically important time or location) to training 
exercises that we expect to result in the take of marine mammals (this 
goal may contribute to 1,

[[Page 83222]]

above, or to reducing the severity of harassment takes only);
    5. Avoidance or minimization of adverse effects to marine mammal 
habitat, paying special attention to the food base, activities that 
block or limit passage to or from biologically important areas, 
permanent destruction of habitat, or temporary destruction/disturbance 
of habitat during a biologically important time; and
    6. For monitoring directly related to mitigation--an increase in 
the probability of detecting marine mammals, thus allowing for more 
effective implementation of the mitigation.
    Based on our evaluation of Eglin AFB's proposed measures, as well 
as other measures that may be relevant to the specified activity, we 
have preliminarily determined that the proposed mitigation measures 
provide the means of effecting the least practicable impact on marine 
mammal species or stocks and their habitat, paying particular attention 
to rookeries, mating grounds, and areas of similar significance (while 
also considering personnel safety, practicality of implementation, and 
the impact of effectiveness of the military readiness activity).

Proposed Monitoring and Reporting

    In order to issue an Authorization for an activity, section 
101(a)(5)(D) of the MMPA states that we 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 an authorization must include the suggested means of 
accomplishing the necessary monitoring and reporting that will result 
in increased knowledge of the species and our expectations of the level 
of taking or impacts on populations of marine mammals present in the 
proposed action area.
    Eglin AFB submitted a marine mammal monitoring plan in their 
Authorization application. We may modify or supplement the plan based 
on comments or new information received from the public during the 
public comment period. Any monitoring requirement we prescribe should 
improve our understanding of one or more of the following:
     Occurrence of marine mammal species in action area (e.g., 
presence, abundance, distribution, density);
     Nature, scope, or context of likely marine mammal exposure 
to potential stressors/impacts (individual or cumulative, acute or 
chronic), through better understanding of: (1) Action or environment 
(e.g., source characterization, propagation, ambient noise); (2) 
Affected species (e.g., life history, dive patterns); (3) Co-occurrence 
of marine mammal species with the action; or (4) Biological or 
behavioral context of exposure (e.g., age, calving or feeding areas);
     Individual responses to acute stressors, or impacts of 
chronic exposures (behavioral or physiological);
     How anticipated responses to stressors impact either: (1) 
Long-term fitness and survival of an individual; or (2) Population, 
species, or stock;
     Effects on marine mammal habitat and resultant impacts to 
marine mammals; and
     Mitigation and monitoring effectiveness.
    NMFS proposes to include the following measures in the Maritime 
WSEP Authorization (if issued). They are:
    (1) Eglin AFB will track the use of the EGTTR for test firing 
missions and protected species observations, through the use of mission 
reporting forms;
    (2) Eglin AFB will submit a summary report of marine mammal 
observations and Maritime WSEP activities to the NMFS Southeast 
Regional Office (SERO) and the Office of Protected Resources 90 days 
after expiration of the current Authorization. This report must include 
the following information: (i) Date and time of each Maritime WSEP 
exercise; (ii) a complete description of the pre-exercise and post-
exercise activities related to mitigating and monitoring the effects of 
Maritime WSEP exercises on marine mammal populations; and (iii) results 
of the Maritime WSEP exercise monitoring, including number of marine 
mammals (by species) that may have been harassed due to presence within 
the activity zone;
    (3) Eglin AFB will monitor for marine mammals in the proposed 
action area. If Eglin AFB personnel observe or detect any dead or 
injured marine mammals prior to testing, or detects any injured or dead 
marine mammal during live fire exercises, Eglin AFB must cease 
operations and submit a report to NMFS within 24 hours and
    (4) Eglin AFB must immediately report any unauthorized takes of 
marine mammals (i.e., serious injury or mortality) to NMFS and to the 
respective Southeast Region stranding network representative. Eglin AFB 
must cease operations and submit a report to NMFS within 24 hours.

Monitoring Results From Previously Authorized Activities

    Eglin AFB complied with the mitigation and monitoring required 
under the previous Authorization for 2016 WSEP activities. Marine 
mammal monitoring occurred before, during, and after each Maritime WSEP 
mission. During the course of these activities, Eglin AFB's monitoring 
did not suggest that they had exceeded the take levels authorized under 
Authorization. In accordance with the 2015 Authorization, Eglin AFB 
submitted a monitoring report (available at: www.nmfs.noaa.gov/pr/permits/incidental/military.htm).
    Under the 2016 Authorization, Eglin AFB anticipated conducting 
Maritime WSEP training missions over approximately two to three weeks, 
but actually conducted a total of five mission days: February 11 and 
March 14-17 associated with live ordnance delivery. Due to weather 
conditions and high sea states, no live missions were conducted 
February 8-10. Munitions that were actually dropped accounted for only 
approximately 41 percent of what was authorized in the 2016 IHA.
    During the February 2016 mission, Eglin AFB released one AGM-65 
Maverick. The AGM-65 Maverick is a penetrating blast-fragment warhead 
that detonates at the surface, and has 86 lb NEW. Eglin AFB conducted 
the required monitoring for marine mammals or indicators of marine 
mammals (e.g., flocks of birds, baitfish schools, or large fish 
schools) before, during, and after each mission and observed a mixture 
of six bottlenose and spotted dolphins approximately seven miles 
outside of the largest ZOI, so no action was required. No protected 
species were observed within the ZOI during pre-mission surveys, 
mission activities, or during post-mission surveys. Therefore, the 
mission resulted in no acoustic impacts to marine mammals.
    During the March 2016 live fire missions, Eglin AFB expended two 
AGM-65 Mavericks and twelve AGM-114 Hellfire missiles. The NEW of the 
munitions that detonated at the water surface or up to 3 m (10 ft) 
below the surface are 86 lb for the AGM-65 Maverick missiles and 13 lb 
for the AGM-114 Hellfire missiles. Eglin AFB conducted the required 
monitoring for marine mammals or indicators of marine mammals (e.g., 
flocks of birds, baitfish schools, or large fish schools) before, 
during, and after each mission and observed two species of marine 
mammals: the common bottlenose dolphin and Atlantic spotted dolphin; 
one sea turtle; and two flocks of approximately 10-20 birds on two 
separate occasions (upon investigation, there was no evidence of 
protected species associated with either flock of birds). Eglin AFB 
confirmed that all

[[Page 83223]]

protected species observed were outside of the ZOI at the conclusion of 
each pre-mission survey.
    After each mission, Eglin AFB re-entered the ZOI to begin post-
mission surveys for marine mammals and debris-clean-up operations. 
Eglin AFB personnel did not observe reactions indicative of disturbance 
during the pre-mission surveys and did not observe any marine mammals 
during the post-mission surveys. In summary, Eglin AFB reports that no 
observable instances of take of marine mammals occurred incidental to 
the Maritime WSEP training activities under the 2016 Authorization.

Estimated Numbers of Marine Mammals Taken by Harassment

    The definition of harassment as it applies to a ``military 
readiness activity'' is: (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).
    NMFS' analysis identified the physiological responses, and 
behavioral responses that could potentially result from exposure to 
underwater explosive detonations. In this section, we will relate the 
potential effects to marine mammals from underwater detonation of 
explosives to the MMPA regulatory definitions of Level A and Level B 
harassment. This section will also quantify the effects that might 
occur from the proposed military readiness activities in W-151.
    At NMFS' recommendation, Eglin AFB updated the thresholds used for 
onset of temporary threshold shift (TTS; Level B Harassment) and onset 
of permanent threshold shift (PTS; Level A Harassment) to be consistent 
with the thresholds outlined in NMFS's new ``Technical Guidance for 
Assessing the Effects of Anthropogenic Sound on Marine Mammal Hearing'' 
(NMFS, 2016). NMFS believes that the thresholds outlined in the new 
Technical Guidance represent the best available science. The report is 
available on the internet at: https://www.nmfs.noaa.gov/pr/acoustics/Acoustic%20Guidance%20Files/opr-55_acoustic_guidance_tech_memo.pdf.

Level B Harassment

    Of the potential effects described earlier in this document, the 
following are the types of effects that fall into the Level B 
harassment category:
Behavioral Harassment
    Behavioral disturbance that rises to the level described in the 
above definition, when resulting from exposures to non-impulsive or 
impulsive sound, is Level B harassment. Some of the lower level 
physiological stress responses discussed earlier would also likely co-
occur with the predicted harassments, although these responses are more 
difficult to detect and fewer data exist relating these responses to 
specific received levels of sound. When predicting Level B harassment 
based on estimated behavioral responses, those takes may have a stress-
related physiological component.
Temporary Threshold Shift (TTS)
    As discussed previously, TTS can affect how an animal behaves in 
response to the environment, including conspecifics, predators, and 
prey. NMFS classifies TTS (when resulting from exposure to explosives 
and other impulsive sources) as Level B harassment, not Level A 
harassment (injury).

Level A Harassment

    Of the potential effects that were described earlier, the following 
are the types of effects that fall into the Level A Harassment 
category:
Permanent Threshold Shift (PTS)
    PTS (resulting either from exposure to explosive detonations) is 
irreversible and NMFS considers this to be an injury.
    Table 6 in this document outlines the acoustic thresholds used by 
NMFS for this Authorization when addressing noise impacts from 
explosives.

                        Table 6--Impulsive Sound Explosive Thresholds Used by Eglin AFB in its Current Acoustics Impacts Modeling
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                            Level B harassment                                Level A harassment
                                 ----------------------------------------------------------------------------------------------------
              Group                                                                            Gastro-intestinal                           Mortality
                                      Behavioral              TTS                 PTS                tract               Lung
--------------------------------------------------------------------------------------------------------------------------------------------------------
Mid-frequency Cetaceans.........  165 dB SEL........  170 dB SEL........  185 dB SEL........  237 dB SPL........  39.1 M\1/3\         91.4 M\1/3\ (1+DRm/
                                                                                                                   (1+[DRm/            10.081])\1/2\ Pa-
                                                                                                                   10.081])\1/2\ Pa-   sec
                                                                                                                   sec.               Where: M = mass of
                                                                                                                  Where: M = mass of   the animals in kg
                                                                                                                   the animals in kg. DRm = depth of the
                                                                                                                  DRm = depth of the   receiver (animal)
                                                                                                                   receiver (animal)   in meters.
                                                                                                                   in meters.
--------------------------------------------------------------------------------------------------------------------------------------------------------
TTS = temporary threshold shift; PTS = permanent threshold shift; dB = decibels; SEL = sound exposure level; SPL = sound pressure level.

    Table 7 provides the estimated maximum range or radius, from the 
detonation point to the various thresholds described in Tables 4-6 
(Note: for PTS and TTS dual metrics, the more conservative metric was 
used).

[[Page 83224]]



                                   Table 7--Distances (m) to Harassment Thresholds From Eglin AFB's Explosive Ordnance
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                  Mortality                            Level A harassment                               Level B  Harassment
                                                ---------------------------------------------------------------------------------------------------------------
                                                                                                           PTS                                     Behavioral
              Mission-day category                Modified     Slight               ------------------------------------------------            ---------------
                                                  goertner      lung      GI tract    Modified                                           TTS     170  224
                                                   model 1     injury      injury     goertner   237 dB SPL  185 dB SEL    230 dB                 dB   dB
                                                                                       model 2                            Peak SPL               SEL  SPL
----------------------------------------------------------------------------------------------------------------------------------------------- ---------------
                                                               Bottlenose Dolphin
--------------------------------------------------------------------------------------------------------------------------------------------------------
A..............................................         193         534         180         945         705       4,666       1,302       7,479
B..............................................         110         180         156         248         180       2,225         180       3,959
C..............................................          37          73          83         286         169       1,128         180       1,863
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                            Atlantic Spotted Dolphin
--------------------------------------------------------------------------------------------------------------------------------------------------------
A..............................................         216         595         180         945         705       4,666       1,302       7,479
B..............................................         136         180         156         248         180       2,225         180       3,959
C..............................................          47          84          83         286         169       1,128         180       1,863
--------------------------------------------------------------------------------------------------------------------------------------------------------
dB = decibels; GI = gastrointestinal; SEP = sound exposure level; SPL = sound pressure level; PTS = permanent threshold shift; TTS = temporary threshold
  shift.

    The ranges presented above were used to calculate the ZOI for each 
criterion/threshold. To eliminate double counting of `takes', impact 
areas from higher impact categories (e.g., PTS) were subtracted from 
areas associated with lower impact categories (e.g., TTS). The 
estimated number of marine mammals potentially exposed to the various 
impact thresholds was calculated with a two-dimensional approach using 
the product of the adjusted impact area, animal density, and annual 
number of events for each mission-day category. A `take' is considered 
to occur for SEL metrics if the received level is equal to or above the 
associated threshold within the appropriate frequency band of the sound 
received, adjusted for the appropriate weighting function value of that 
frequency band. Similarly, a `take' would occur for impulse and peak 
SPL metrics if the received level is equal to or above the associated 
threshold.

Density Estimation

    Density estimates for bottlenose dolphin and spotted dolphin were 
obtained from Duke University Marine Geospatial Ecology Lab Reports 
(Roberts et al., 2016). Raster data from Duke University were imported 
into ArcGIS and overlaid onto the Maritime WSEP mission area. Density 
values were provided in 100 km\2\ boxes. A 30-km by 30-km (900 km\2\) 
area centered on the Maritime WSEP mission location was selected, which 
consisted of nine 100-km\2\ blocks. Density values from those blocks 
were averaged and converted to number of animals per square kilometer 
to obtain average annual density estimates for the common bottlenose 
and Atlantic spotted dolphins used in this analysis (see Table 8 for 
the resultant densities for these species).

    Table 8--Marine Mammal Density Estimates Within Eglin AFB's EGTTR
------------------------------------------------------------------------
                                                              Density
                         Species                             (animals/
                                                              km\2\)
------------------------------------------------------------------------
Bottlenose dolphin......................................           0.433
Atlantic spotted dolphin................................           0.148
------------------------------------------------------------------------

Take Estimation

    Table 9 indicates the modeled potential for lethality, injury, and 
non-injurious harassment (including behavioral harassment) to marine 
mammals in the absence of mitigation measures. Eglin AFB and NMFS 
estimate that approximately three marine mammals could be exposed to 
injurious Level A harassment noise levels (187 dB SEL) and 
approximately 326 animals could be exposed to Level B harassment (TTS 
and Behavioral) noise levels in the absence of mitigation measures.

           Table 9--Modeled Number of Marine Mammals Potentially Affected by Maritime WSEP Operations
----------------------------------------------------------------------------------------------------------------
                                                                      Level A         Level B         Level B
                     Species                         Mortality      harassment      harassment      harassment
                                                                    (PTS only)         (TTS)       (behavioral)
----------------------------------------------------------------------------------------------------------------
Bottlenose dolphin..............................               0               2              87             157
Atlantic spotted dolphin........................               0               1              29              53
                                                 ---------------------------------------------------------------
    Total.......................................               0               3             116             210
----------------------------------------------------------------------------------------------------------------

    Based on the mortality exposure estimates calculated by the 
acoustic model and the anticipated effectiveness of mitigation 
measures, zero marine mammals are expected to be affected by pressure 
levels associated with mortality or serious injury. Zero marine mammals 
are expected to be exposed to pressure levels associated with slight 
lung injury or gastrointestinal tract injury.
    NMFS generally considers PTS to fall under the injury category 
(Level A Harassment). An animal would need to stay very close to the 
sound source for an extended amount of time to incur a serious degree 
of PTS, which could increase the probability of mortality. In this 
case, it would be highly unlikely for this scenario to unfold given the 
nature of any anticipated acoustic exposures that could potentially 
result from a mobile marine mammal that NMFS generally expects to 
exhibit avoidance

[[Page 83225]]

behavior to loud sounds within the EGTTR. NMFS concludes that 
possibility of minor PTS in the form of slight upward shift of hearing 
threshold at certain frequency bands by a few individuals of marine 
mammals is extremely low, but not unlikely. The majority of `takes' 
resulting from Eglin AFB's WSEP activities would constitute Level B 
harassment, such as TTS and behavioral harassment.

Negligible Impact Analysis and Preliminary Determinations

    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'' (i.e., population-level effects). An estimate 
of the number of Level B harassment takes alone is not enough 
information on which to base an impact determination. In addition to 
considering estimates of the number of marine mammals that might be 
``taken'' through behavioral harassment, we consider other factors, 
such as the likely nature of any responses (e.g., intensity, duration), 
the context of any responses (e.g., critical reproductive time or 
location, migration), as well as the number and nature of estimated 
Level A harassment takes, the number of estimated mortalities, and 
effects on habitat.
    To avoid repetition, the discussion below applies to each of the 
species for which we propose to authorize incidental take for Eglin 
AFB's activities, given that expected impacts are expected to be the 
same for both species.
    In making a negligible impact determination, we consider:
     The number of anticipated injuries, serious injuries, or 
mortalities;
     The number, nature, and intensity, and duration of Level B 
harassment;
     The context in which the takes occur (e.g., impacts to 
areas of significance, impacts to local populations, and cumulative 
impacts when taking into account successive/contemporaneous actions 
when added to baseline data);
     The status of stock or species of marine mammals (i.e., 
depleted, not depleted, decreasing, increasing, stable, impact relative 
to the size of the population);
     Impacts on habitat affecting rates of recruitment/
survival; and
     The effectiveness of monitoring and mitigation measures to 
reduce the number or severity of incidental take.
    For reasons stated previously in this document and based on the 
following factors, Eglin AFB's specified activities are not likely to 
cause long-term behavioral disturbance, serious injury, or death.
    The takes from Level B harassment would be due to potential 
behavioral disturbance and TTS. The takes from Level A harassment would 
be due to some, likely lesser, degree of PTS. Activities would only 
occur over a timeframe of two to three weeks in beginning in February 
2017, with one or two missions occurring per day. It is possible that 
some individuals may be taken more than once if those individuals are 
located in the exercise area on two different days when exercises are 
occurring.
    Noise-induced threshold shifts (TS, which includes PTS) are defined 
as increases in the threshold of audibility (i.e., the sound has to be 
louder to be detected) of the ear at a certain frequency or range of 
frequencies (ANSI 1995; Yost 2000). Several important factors relate to 
the magnitude of TS, such as level, duration, spectral content 
(frequency range), and temporal pattern (continuous, intermittent) of 
exposure (Yost 2000; Henderson et al., 2008). TS occurs in terms of 
frequency range (Hz or kHz), hearing threshold level (dB), or both 
frequency and hearing threshold level (CDC 2004).
    In addition, there are different degrees of PTS: ranging from 
slight/mild to moderate and from severe to profound (Clark 1981). 
Profound PTS or the complete loss of the ability to hear in one or both 
ears is commonly referred to as deafness (CDC 2004; WHO 2006). High-
frequency PTS, presumably as a normal process of aging that occurs in 
humans and other terrestrial mammals, has also been demonstrated in 
captive cetaceans (Ridgway and Carder 1997; Yuen et al., 2005; Finneran 
et al., 2005; Houser and Finneran 2006; Finneran et al., 2007; Schlundt 
et al., 2011) and in stranded individuals (Mann et al., 2010).
    In terms of what is analyzed for the potential PTS (Level A 
harassment) in marine mammals as a result of Eglin AFB's Maritime WSEP 
operations, if it occurs, NMFS has determined that the levels would be 
slight/mild because most cetaceans would be expected to show relatively 
high levels of avoidance. Further, it is uncommon to sight marine 
mammals within the target area, especially for prolonged durations. 
Results from monitoring programs associated other Eglin AFB activities 
and for Eglin AFB's 2016 Maritime WSEP activities have shown the 
absence of marine mammals within the EGTTR during and after maritime 
operations. Avoidance varies among individuals and depends on their 
activities or reasons for being in the area.
    NMFS' predicted estimates for Level A harassment take are likely 
overestimates of the likely injury that will occur. NMFS expects that 
successful implementation of the required vessel-based and video-based 
mitigation measures would avoid Level A take in some instances. Also, 
NMFS expects that some individuals would avoid the source at levels 
expected to result in injury. Nonetheless, although NMFS expects that 
Level A harassment is unlikely to occur at the numbers proposed to be 
authorized, because it is difficult to quantify the degree to which the 
mitigation and avoidance will reduce the number of animals that might 
incur PTS, we are proposing to authorize (and analyze) the modeled 
number of Level A takes (three), which does not take the mitigation or 
avoidance into consideration. However, we anticipate that any PTS 
incurred because of mitigation and the likely short duration of 
exposures, would be in the form of only a small degree of permanent 
threshold shift and not total deafness.
    While animals may be impacted in the immediate vicinity of the 
activity, because of the short duration of the actual individual 
explosions themselves (versus continual sound source operation) 
combined with the short duration of the Maritime WSEP operations, NMFS 
has preliminarily determined that there will not be a substantial 
impact on marine mammals or on the normal functioning of the nearshore 
or offshore Gulf of Mexico ecosystems. We do not expect that the 
proposed activity would impact rates of recruitment or survival of 
marine mammals since we do not expect mortality (which would remove 
individuals from the population) or serious injury to occur. In 
addition, the proposed activity would not occur in areas (and/or times) 
of significance for the marine mammal populations potentially affected 
by the exercises (e.g., feeding or resting areas, reproductive areas), 
and the activities would only occur in a small part of their overall 
range, so the impact of any potential temporary displacement would be 
negligible and animals would be expected to return to the area after 
the cessations of activities. Although the proposed activity could 
result in Level A (PTS only, not slight lung injury or gastrointestinal 
tract injury) and Level B (behavioral disturbance and TTS of lesser 
degree and shorter duration) harassment of marine mammals, the

[[Page 83226]]

level of harassment is not anticipated to impact rates of recruitment 
or survival of marine mammals because the number of exposed animals is 
expected to be low due to the short-term (i.e., four hours a day or 
less) and site-specific nature of the activity. We do not anticipate 
that the effects would be detrimental to rates of recruitment and 
survival because we do not expect serious of extended behavioral 
responses that would result in energetic effects at the level to impact 
fitness.
    Moreover, the mitigation and monitoring measures proposed for the 
Authorization (described earlier in this document) are expected to 
further minimize the potential for harassment. The protected species 
surveys would require Eglin AFB to search the area for marine mammals, 
and if any are found in the live fire area, then the exercise would be 
suspended until the animal(s) has left the area or relocated. Moreover, 
marine species observers located in the Eglin control tower would 
monitor the high-definition video feed from cameras located on the 
instrument barge anchored on-site for the presence of protected 
species. Furthermore, Maritime WSEP missions would be delayed or 
rescheduled if the sea state is greater than a 4 on the Beaufort Scale 
at the time of the test. In addition, Maritime WSEP missions would 
occur no earlier than two hours after sunrise and no later than two 
hours prior to sunset to ensure adequate daylight for pre- and post-
mission monitoring.
    Based on the preliminary analysis contained herein of the likely 
effects of the specified activity on marine mammals and their habitat, 
and taking into consideration the implementation of the mitigation and 
monitoring measures, NMFS finds that Eglin AFB's Maritime WSEP 
operations will result in the incidental take of marine mammals, by 
Level A and Level B harassment only, and that the taking from the 
Maritime WSEP exercises will not have an adverse effect on annual rates 
of recruitment or survival, and therefore will have a negligible impact 
on the affected species or stocks.

Impact on Availability of Affected Species or Stock for Taking for 
Subsistence Uses

    There are no relevant subsistence uses of marine mammals implicated 
by this action. Therefore, NMFS has preliminarily determined that the 
total taking of affected species or stocks would not have an 
unmitigable adverse impact on the availability of such species or 
stocks for taking for subsistence purposes.

Endangered Species Act (ESA)

    Due to the location of the activity and past experience with 
similar authorizations for these activities, no ESA-listed marine 
mammal species are likely to be affected. Therefore, NMFS has 
preliminarily determined that this proposed Authorization would have no 
effect on ESA-listed species. However, prior to the agency's decision 
on the issuance or denial of this Authorization, NMFS will make a final 
determination on whether additional consultation is necessary.

National Environmental Policy Act (NEPA)

    In 2015, Eglin AFB provided NMFS with an EA titled, Maritime Weapon 
Systems Evaluation Program (WSEP) Operational Testing in the Eglin Gulf 
Testing and Training Range (EGTTR), Florida. The EA analyzed the 
direct, indirect, and cumulative environmental impacts of the specified 
activities on marine mammals. NMFS, after review and evaluation of the 
Eglin AFB EA for consistency with the regulations published by the 
Council of Environmental Quality (CEQ) and NOAA Administrative Order 
216-6, Environmental Review Procedures for Implementing the National 
Environmental Policy Act, adopted the EA. After considering the EA, the 
information in the 2014 IHA application, and the Federal Register 
notice, as well as public comments, NMFS' issuance of the 2015 
Authorization and determination that the activity was not likely to 
result in significant impacts on the human environment, NMFS adopted 
Eglin AFB's EA under 40 CFR 1506.3; and issued a FONSI statement on 
issuance of an Authorization under section 101(a)(5) of the MMPA.
    In accordance with NOAA Administrative Order 216-6 (Environmental 
Review Procedures for Implementing the National Environmental Policy 
Act, May 20, 1999), NMFS will again review the information contained in 
Eglin AFB's EA and determine whether the EA accurately and completely 
describes the preferred action alternative and the potential impacts on 
marine mammals. Based on this review and analysis, NMFS may reaffirm 
the 2015 FONSI statement on issuance of an annual authorization under 
section 101(a)(5) of the MMPA or supplement the EA if necessary.

Proposed Authorization

    As a result of these preliminary determinations, we propose to 
issue an Authorization to Eglin AFB for conducting Maritime WSEP 
activities, for a period of one year from the date of issuance, 
provided the previously mentioned mitigation, monitoring, and reporting 
requirements are incorporated. The proposed Authorization language is 
provided in the next section. The wording contained in this section is 
proposed for inclusion in the Authorization (if issued).
    1. This Authorization is valid for a period of one year from 
February 4, 2017 through February 3, 2018.
    2. This Authorization is valid only for activities associated with 
the Maritime WSEP operations utilizing munitions identified in the 
Attachment.
    3. The incidental taking, by Level A and Level B harassment, is 
limited to: Atlantic bottlenose dolphin (Tursiops truncatus); and 
Atlantic spotted dolphin (Stenella frontalis) as specified in Table 1, 
below.

           Table 1--Modeled Number of Marine Mammals Potentially Affected by Maritime WSEP Operations.
----------------------------------------------------------------------------------------------------------------
                                                                      Level A         Level B         Level B
                     Species                         Mortality      harassment      harassment      harassment
                                                                    (PTS only)         (TTS)       (behavioral)
----------------------------------------------------------------------------------------------------------------
Bottlenose dolphin..............................               0               2              87             157
Atlantic spotted dolphin........................               0               1              29              53
Total...........................................               0               3             116             210
----------------------------------------------------------------------------------------------------------------

    The taking by serious injury or death of these species, the taking 
of these species in violation of the conditions of this Incidental 
Harassment Authorization, or the taking by harassment, serious injury 
or death of any other species of marine mammal is prohibited and may 
result in the

[[Page 83227]]

modification, suspension or revocation of this Authorization.
    4. Mitigation.
    When conducting this activity, the following mitigation measures 
must be undertaken:
     If daytime weather and/or sea conditions preclude adequate 
monitoring for detecting marine mammals and other marine life, maritime 
strike operations must be delayed until adequate sea conditions exist 
for monitoring to be undertaken. Daytime maritime strike exercises will 
be conducted only when sea surface conditions do not exceed Beaufort 
sea state 4 (i.e., wind speed 13-18 mph (11-16 knots); wave height 1 m 
(3.3 ft)), the visibility is 5.6 km (3 nm) or greater, and the ceiling 
is 305 m (1,000 ft) or greater;
     On the morning of the maritime strike mission, the test 
director and safety officer will confirm that there are no issues that 
would preclude mission execution and that the weather is adequate to 
support monitoring and mitigation measures.

Two Hours Prior to Mission

     Mission-related surface vessels will be stationed on site.
     Vessel-based observers on board at least one vessel will 
assess the overall suitability of the test site based on environmental 
conditions (e.g., sea state) and presence/absence of marine mammal or 
marine mammal indicators (e.g., large schools of fish, jellyfish, 
Sargassum rafts, and large flocks of birds feeding at the surface). 
Observers will relay this information to the safety officer.

One and One-half Hours Prior to Mission

     Vessel-based surveys and video camera surveillance will 
commence. Vessel-based observers will survey the zone of impact (ZOI) 
calculated for that day's mission category and relay all marine mammal 
and indicator sightings, including the time of sighting and direction 
of travel (if known) to the safety officer. Surveys will continue for 
approximately one hour.
     If marine mammals or marine mammal indicators are observed 
within the ZOI, the test range will be declared ``fouled,'' which will 
signify to mission personnel that conditions are such that a live 
ordnance drop cannot occur.
     If no marine mammals or marine mammal indicators are 
observed, the range will be declared ``green,'' which will signify to 
mission personnel that conditions are such that a live ordnance drop 
may occur.
One-half Hour Prior to Mission
     Approximately 30 minutes prior to live weapon deployment, 
vessel-based observers will be instructed to leave the test site and 
remain outside the safety zone, which will be approximately 9.5 miles 
from the detonation point (actual size will be determined by weapon net 
explosive weight (NEW) and method of delivery) during the conduct of 
the mission.
     Monitoring for marine mammals will continue from the 
periphery of the safety zone while the mission is in progress. Other 
safety boat crews will be instructed to observe for marine mammals 
during this time.
     After survey vessels have left the test site, marine 
species monitoring will continue for the Eglin control tower through 
the video feed received from the high definition cameras on the 
instrument barge.

Execution of Mission

     Immediately prior to live weapons drop, the Test Director 
and Safety Officer will communicate to confirm the results of the 
marine mammal survey and the appropriateness of proceeding with the 
mission. The Safety Ffficer will have final authority to proceed with, 
postpone, move, or cancel the mission.
     The mission will be postponed or moved if: Any marine 
mammal is visually detected within the ZOI, or large schools of fish, 
jellyfish, Sargassum rafts, or large flocks of birds feeding at the 
surface are observed within the ZOI. Postponement will continue until 
the animal(s) that caused the postponement is (1) confirmed to be 
outside of the ZOI due to swimming out of the range on a heading away 
from the targets; or (2) not seen again for 30 minutes and presumed to 
be outside the ZOI due to the animal swimming outside of the range. 
Postponement will continue until these potential indicators are 
confirmed to be outside the ZOI.
     In the event of a postponement, pre-mission monitoring 
will continue as long as weather and daylight hours allow (no later 
than two hours prior to sunset).

Post Mission

     Post-mission surveys will commence as soon as Explosive 
Ordnance Disposal (EOD) personnel declare the test area safe. These 
surveys will be conducted by the same vessel-based observers that 
conducted the pre-mission surveys.
     Survey vessels will move into the ZOI from outside the 
safety zone and monitor for at least 30 minutes, concentrating on the 
area down-current of the test site. Any marine mammals killed or 
injured as a result of the test will be documented and immediately 
reported to the National Marine Fisheries Service (NMFS) Southeast 
Region Marine Mammal Stranding Network at 877-433-8299 and the Florida 
Marine Mammal Stranding Hotline at 888-404-3922. The species, number, 
location, and behavior of any animals observed will be documented and 
reported.
     If post-mission surveys determine that an injury or lethal 
take of a marine mammal has occurred, the next maritime strike mission 
will be suspended until the test procedure and the monitoring methods 
have been reviewed with NMFS and appropriate changes made.
    5. Monitoring.
    The holder of this Authorization is required to cooperate with the 
National Marine Fisheries Service and any other Federal, state or local 
agency monitoring the impacts of the activity on marine mammals.
    The holder of this Authorization will track their use of the EGTTR 
for the Maritime WSEP missions and marine mammal observations, through 
the use of mission reporting forms.
    Maritime strike missions will coordinate with other activities 
conducted in the EGTTR (e.g., Precision Strike Weapon and Air-to-
Surface Gunnery missions) to provide supplemental post-mission 
observations of marine mammals in the operations area of the exercise.
    Any dead or injured marine mammals observed or detected prior to 
testing or injured or killed during live drops, must be immediately 
reported to the NMFS Southeast Region Marine Mammal Stranding Network 
at 877-433-8299 and the Florida Marine Mammal Stranding Hotline at 888-
404-3922.
    Any unauthorized impacts on marine mammals must be immediately 
reported to the National Marine Fisheries Service's Southeast Regional 
Administrator, at 727-842-5312, and the Chief of the Permits and 
Conservation Division, Office of Protected Resources, at 301-427-8401.
    The monitoring team will document any marine mammals that were 
killed or injured as a result of the test and, if practicable, 
coordinate with the local stranding network and NMFS to assist with 
recovery and examination of any dead animals, as needed.
    Activities related to the monitoring described in this 
Authorization, including the retention of marine mammals, do not 
require a separate scientific research permit issued under

[[Page 83228]]

Section 104 of the Marine Mammal Protection Act.
    6. Reporting.
    A draft report of marine mammal observations and Maritime WSEP 
mission activities must be submitted to the National Marine Fisheries 
Service's Southeast Regional Office, Protected Resources Division, 263 
13th Ave. South, St. Petersburg, FL 33701 and NMFS's Office of 
Protected Resources, 1315 East West Highway, Silver Spring, MD 20910. 
This draft report must include the following information:
     Date and time of each maritime strike mission;
     A complete description of the pre-exercise and post-
exercise activities related to mitigating and monitoring the effects of 
maritime strike missions on marine mammal populations;
     Results of the monitoring program, including numbers by 
species/stock of any marine mammals noted injured or killed as a result 
of the maritime strike mission and number of marine mammals (by species 
if possible) that may have been harassed due to presence within the 
ZOI; and
     A detailed assessment of the effectiveness of sensor based 
monitoring in detecting marine mammals in the area of Maritime WSEP 
operations.
    The draft report will be subject to review and comment by NMFS. Any 
recommendations made by NMFS must be addressed in the final report 
prior to acceptance by NMFS. The draft report will be considered the 
final report for this activity under this Authorization if NMFS has not 
provided comments and recommendations within 90 days of receipt of the 
draft report.
    7. Additional Conditions.
     The maritime strike mission monitoring team will 
participate in the marine mammal species observation training. 
Designated crew members will be selected to receive training as 
protected species observers (PSO). PSOs will receive training in 
protected species survey and identification techniques through a NMFS-
approved training program.
     The holder of this Authorization must inform the Director, 
Office of Protected Resources, National Marine Fisheries Service, (301-
427-8400) or designee (301-427-8401) prior to the initiation of any 
changes to the monitoring plan for a specified mission activity.
     A copy of this Authorization must be in the possession of 
the Safety Officer on duty each day that maritime strike missions are 
conducted.
     Failure to abide by the Terms and Conditions contained in 
this Incidental Harassment Authorization may result in a modification, 
suspension or revocation of the Authorization.

Request for Public Comments

    We request comment on our analysis, the draft authorization, and 
any other aspect of this Federal Register notice of proposed 
Authorization. Please include with your comments any supporting data or 
literature citations to help inform our final decision on Eglin AFB's 
renewal request for an MMPA authorization.

    Dated: November 15, 2016.
Donna S. Wieting,
Director, Office of Protected Resources, National Marine Fisheries 
Service.
[FR Doc. 2016-27881 Filed 11-18-16; 8:45 am]
 BILLING CODE 3510-22-P