Incidental Takes of Marine Mammals During Specified Activities; Marine Seismic Survey in the Arctic Ocean, August to September, 2010, 60174-60203 [2010-24335]
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Federal Register / Vol. 75, No. 188 / Wednesday, September 29, 2010 / Notices
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XW05
Incidental Takes of Marine Mammals
During Specified Activities; Marine
Seismic Survey in the Arctic Ocean,
August to September, 2010
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; issuance of an incidental
take authorization.
AGENCY:
In accordance with the
Marine Mammal Protection Act
(MMPA) regulations, notification is
hereby given that NMFS issued an
Incidental Harassment Authorization
(IHA) to the U.S. Geological Survey
(USGS) for the take of small numbers of
marine mammals, by Level B
harassment, incidental to conducting a
marine seismic survey in the Arctic
Ocean during August to September,
2010.
SUMMARY:
Effective August 11, 2010,
through October 21, 2010.
ADDRESSES: A copy of the IHA and
application are available by writing to P.
Michael Payne, Chief, Permits,
Conservation, and Education Division,
Office of Protected Resources, National
Marine Fisheries Service, 1315 EastWest Highway, Silver Spring, MD 20910
or by telephoning the contact listed
here.
A copy of the application containing
a list of the references used in this
document may be obtained by writing to
the address specified above, telephoning
the contact listed below (see FOR
FURTHER INFORMATION CONTACT), or
visiting the internet at: https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm. Documents cited in this
notice may be viewed, by appointment,
during regular business hours, at the
aforementioned address.
FOR FURTHER INFORMATION CONTACT:
Howard Goldstein or Jolie Harrison,
Office of Protected Resources, NMFS,
301–713–2289.
SUPPLEMENTARY INFORMATION:
DATES:
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Background
Sections 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1361 et seq.) direct
the Secretary of Commerce (Secretary)
to allow, upon request, the incidental,
but not intentional, taking of small
numbers of marine mammals by United
States (U.S.) citizens who engage in a
specified activity (other than
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commercial fishing) within a specified
geographical region if certain findings
are made and either regulations are
issued or, if the taking is limited to
harassment, a notice of a proposed
authorization is provided to the public
for review.
An authorization for incidental taking
of small numbers of 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, and if the permissible
methods of taking and requirements
pertaining to the mitigation, monitoring
and reporting of such takings are set
forth. NMFS has defined ‘‘negligible
impact’’ in 50 CFR 216.103 as ‘‘ * * * an
impact resulting from the specified
activity that cannot be reasonably
expected to, and is not reasonably likely
to, adversely affect the species or stock
through effects on annual rates of
recruitment or survival.’’
Section 101(a)(5)(D) of the MMPA
established an expedited process by
which citizens of the United States can
apply for an authorization not to exceed
one year to incidentally take small
numbers of marine mammals by
harassment. Except with respect to
certain activities not pertinent here, the
MMPA defines ‘‘harassment’’ as:
Any act of pursuit, torment, or annoyance
which (i) has the potential to injure a marine
mammal or marine mammal stock in the wild
[‘‘Level A harassment’’]; or (ii) has the
potential to disturb a marine mammal or
marine mammal stock in the wild by causing
disruption of behavioral patterns, including,
but not limited to, migration, breathing,
nursing, breeding, feeding, or sheltering
[‘‘Level B harassment’’].
16 U.S.C. 1362(18)
Section 101(a)(5)(D) establishes a 45day time limit for NMFS’ review of an
application followed by a 30-day public
notice and comment period for any
proposed authorizations for the
incidental harassment of marine
mammals. Within 45 days of the close
of the comment period, NMFS must
either issue or deny the authorization.
Summary of Request
On March 9, 2010, NMFS received an
IHA application and a draft
Environmental Assessment (EA) from
USGS for the taking, by Level B
harassment only, of small numbers of
several species of marine mammals
incidental to conducting a marine
seismic survey in the Arctic Ocean
during August to September, 2010.
NMFS received a revised IHA
application on June 1, 2010, and a final
EA on August 6, 2010.
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Description of the Specified Activity
USGS is conducting a marine
geophysical (seismic reflection/
refraction) and bathymetric survey in
the Arctic Ocean in August and
September, 2010 (see Tables 1 and 2,
and Figure 3 of the IHA application).
The survey is being conducted from the
Canadian Coast Guard (CCG) vessel
CCGS Louis S. St. Laurent (St. Laurent)
which will be accompanied by the U.S.
Coast Guard Cutter (USCGC) Healy, both
of which are polar-class icebreakers.
Descriptions of the vessels and their
specifications are presented in
Appendix A of the IHA application. The
two vessels operate in tandem in the
presence of ice but may diverge and
operate independently in open water.
Some minor deviation of the dates is
possible, depending on logistics and
weather (i.e., the cruise may depart
earlier or be extended due to poor
weather; there could be extra days of
seismic operations if collected data are
of sub-standard quality).
One CCG helicopter is available for
deployment from the St. Laurent for ice
reconnaissance and crew transfers
between the vessels during survey
operations. Helicopter transfer of crew
from the Healy is also planned for
approximately one day during a ship-toshore crew change at Barrow, Alaska at
the end of the survey. The helicopter
operations in Barrow will be conducted
under Department of Interior (DOI)
contract. Daily helicopter operations are
anticipated pending weather conditions.
Spot bathymetry will also be conducted
from the helicopter outside U.S. waters.
Acoustic sources onboard the St.
Laurent include an airgun array
comprised of three Sercel G-airguns and
a Knudsen 320BR ‘‘Chirp’’ pulse
echosounder operating at 12 kHz. The
St. Laurent also tows a 3 to 5 kHz subbottom profiler while in open water and
when not working with the Healy. The
airgun array consists of two 500 in3 and
one 150 in3 airguns for an overall
discharge of 1,150 in3. Table 2 of the
IHA application presents different
sound pressure level (SPL) radii of the
airgun array. Acoustic sources being
operated on the St. Laurent are
described in detail in Section VII and
Appendix B in the IHA application. The
seismic array and a hydrophone
streamer towed from the St. Laurent
operate under the provisions of a
Canadian authorization based on
Canada’s environmental assessment of
the proposed survey while in Canadian
or international waters, and under the
provisions of an IHA issued to the USGS
by NMFS in U.S. waters. NMFS cannot
issue an IHA directly to a non-U.S.
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citizen, however, the Geological Survey
of Canada (GSC) has written a
Categorical Declaration stating that
‘‘while in U.S. waters (i.e., the U.S. 200
mile Exclusive Economic Zone), the
GSC will comply with any and all
environmental mitigation measures
required by the U.S. NMFS and/or the
U.S. Fish and Wildlife Service.’’ The St.
Laurent follows the lead of the Healy.
The Healy breaks and clears ice
approximately 1.6 to 3.2 km (1 to 2
miles [mi]) in advance of the St.
Laurent. In situations where the array
(and hydrophone streamer) cannot be
towed safely due to ice cover, the St.
Laurent may escort the Healy. The
Healy uses a multi-beam echosounder
(Kongsberg EM122), a sub-bottom
profiler (Knudsen 3.5 kHz Chirp), and a
‘‘piloting’’ echosounder (ODEC 1500)
continuously when underway and
during the seismic profiling. Acoustic
Doppler current profilers (75 kHz and
150 kHz) may also be used on the Healy.
The Healy’s acoustic systems are
described in further detail in Section VII
and Appendix B of the IHA application.
In addition to the hydrophone
streamer, marine sonobuoys are
deployed to acquire wide angle
reflection and refraction data for
velocity determination to convert
seismic reflection travel time to depth.
Sonobuoys are deployed off the stern of
the St. Laurent approximately every
eight hours during seismic operations
with as many as three deployments per
day. The sonobuoy’s hydrophone
activates at a water depth of
approximately 60 m (196.9 ft) and
seismic signals are communicated via
radio to the St. Laurent. The sonobuoys
are pre-set to scuttle (i.e., deliberately
sink) eight hours after activation.
The program within U.S. waters
consists of approximately 806 km (500.8
mi) of survey transect line, not
including transits when the airguns are
not operating (see Figure 1 and Table 1
of the IHA application). U.S. priorities
include another 997 km (619.5 mi) of
survey lines north of the U.S. Exclusive
Economic Zone (EEZ), for a total of
1,804 km (1,121 mi) of tracklines of
interest to the U.S. Table 1 of the IHA
application lists all U.S. priority
tracklines; Figure 1 of the IHA
application includes all U.S. priority
tracks and the area of interest to Canada
near the proposed U.S. tracklines. Water
depths within the U.S. study area range
from approximately 1,900 to 4,000 m
(6,233.5 to 13,123.4 ft) (see Figure 1 of
the IHA application). There may be
additional seismic operations associated
with airgun testing, start-up, and repeat
coverage of any areas where initial data
quality is sub-standard. The tracklines
being surveyed in U.S. waters include
the southern 263.8 km (164 mi) of the
line that runs North-South in the
western EEZ, the southern 264.5 km
(164.4 mi) of the line that runs North—
South in the central EEZ, and 277.7 km
(172.6 mi) of trackline that connects the
two (see Table 1 here and in Figure 1
of the IHA application). The IHA
application requested the authorization
of incidental takes of marine mammals
for activities within U.S. waters. The
survey line nearest to shore in U.S.
waters is approximately 116 km (63
nmi) offshore at its closest point.
TABLE 1—U.S. PRIORITY TRACKLINES FOR USGS AND GEOLOGICAL SURVEY OF CANADA (GSC) 2010 EXTENDED
CONTINENTAL SHELF SURVEY IN THE NORTHERN BEAUFORT SEA AND ARCTIC OCEAN
Location
NS in central EEZ (south) .....
NS in central EEZ (north) ......
Central-western EEZ connector.
NS in western EEZ ................
South Northwind Ridge .........
Northwind Ridge connector ...
Mid-Northwind Ridge .............
Northwind Ridge connector ...
Mid-Northwind Ridge .............
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Totals ..............................
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Nautical mile
(nmi)
Time
(Hour [hr])
@ 4 nmi/hr
71.22° North; 145.17° West
72.27° North; 145.41° West
73.92° North; 145.30° West
72.27° North; 145.41° West
73.92° North; 145.30° West
71.84° North; 151.82° West
118
183
317
64
100
171
16
25
43
71.84°
74.32°
74.96°
76.30°
75.41°
76.57°
74.32°
74.96°
76.30°
75.41°
76.57°
76.49°
281
239
161
274
129
102
152
129
87
148
70
55
39
32
22
37
17
14
1,804
976
245
North;
North;
North;
North;
North;
North;
151.82°
150.30°
158.01°
155.88°
146.50°
146.82°
West
West
West
West
West
West
...............................................
The two vessels operate cooperatively
during the seismic survey. The St.
Laurent conducts seismic operations
using an airgun array and also operates
a 12 kHz Chirp echosounder. The St.
Laurent also operates a 3 to 5 kHz subbottom profiler in open water when not
working with the Healy. The Healy
normally escorts the St. Laurent in ice
cover, and continuously operates a
bathymetric multi-beam echosounder, a
3.5 kHz Chirp sub-bottom profiler, a
piloting echosounder, and two acoustic
Doppler current profilers.
The St. Laurent accessed the survey
area from Canada and rendezvoused
with the Healy on approximately
August 10, 2010; the Healy approached
the survey area from the Bering Straits.
The St. Laurent deploys a relatively
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(km)
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North;
North;
North;
North;
North;
North;
150.30°
158.01°
155.88°
146.50°
146.82°
150.73°
West
West
West
West
West
West
...............................................
small airgun array comprised of three
G-airguns and a single hydrophone
streamer approximately 300 m (984 ft)
in length. The airgun array consists of
two 500 in 3 and one 150 in 3 airguns for
an overall discharge of 1,150 in 3. The
St. Laurent follows the lead of the Healy
which operates approximately 1.9 to 3.8
km (1 to 2 nmi) ahead of the St. Laurent.
In ice conditions where seismic gear
cannot be safely towed, the St. Laurent
escorts the Healy to optimize multibeam bathymetry data collection. If
extended open-water conditions are
encountered, Healy and St. Laurent may
operate independently. After
completion of the survey the St. Laurent
will return to port in Canada, and the
Healy will change crew at Barrow via
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helicopter or surface conveyance before
continuing on another project.
Vessel Specifications
The CCGS St. Laurent was built in
1969 by Canadian Vickers Ltd. in
Montreal, Quebec, and underwent an
extensive modernization in Halifax,
Nova Scotia between 1988 to 1993. The
St. Laurent is based at CCG Base
Dartmouth in Dartmouth, Nova Scotia.
Current vessel activities involve
summer voyages to the Canadian Arctic
for sealifts to various coastal
communities and scientific expeditions.
A description of the St. Laurent with
vessel specifications is presented in
Appendix A of the IHA application and
is available online at: https://www.ccg-
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gcc.gc.ca/eng/Fleet/Vessels?id=1111
&info=5&subinfo.
The Healy is designed to conduct a
wide range of research activities,
providing more than 390.2 m 2 (4,200
ft 2) of scientific laboratory space,
numerous electronic sensor systems,
oceanographic winches, and
accommodations for up to 50 scientists.
The Healy is designed to break 1.4 m
(4.5 ft) of ice continuously at 5.6 km/
hour (three knots) and can operate in
temperatures as low as ¥45.6 C (¥50
degrees F). The Healy is a USCG
icebreaker, capable of traveling at 5.6
km/hour (three knots) through 1.4 m
(4.5 ft) of ice. A ‘‘Central Power Plant,’’
four Sultzer 12Z AU40S diesel
generators, provides electric power for
propulsion and ship’s services through
a 60 Hz, three-phase common bus
distribution system. Propulsion power
is provided by two electric AC
Synchronous, 11.2 MW drive motors,
fed from the common bus through a
Cycloconverter system, that turn two
fixed-pitch, four-bladed propellers.
The science community provided
invaluable input on lab lay-outs and
science capabilities during design and
construction of the ship. The Healy is
also a capable platform for supporting
other potential missions in the polar
regions, including logistics, search and
rescue, ship escort, environmental
protection, and enforcement of laws and
treaties, and will also serve as the
platform from which vessel-based
Protected Species Observers (PSOs) will
watch for marine mammals before and
during airgun operations. Other details
of the Healy can be found in Appendix
A of the IHA application.
NMFS believes that the realistic
possibility of a ship-strike of a marine
mammal by the vessel during research
operations and in-transit during the
proposed survey is discountable. The
probability of a ship strike resulting in
an injury or mortality of an animal has
been associated with ship speed;
however, it is highly unlikely that the
proposed seismic survey would increase
the rate of injury, serious injury, or
mortality given the St. Laurent and
Healy’s slow survey speed.
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Acoustic Source Specifications—
Seismic Airguns and Radii
The seismic source for the seismic
survey is comprised of three Sercel G-
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airguns with a total volume of 1,150 in 3.
The three-airgun array is comprised of
two 500 in 3 and one 150 in 3 G-airguns
in a triangular configuration (see Figure
B–1 in the IHA application). The single
150 in 3 G-airgun is used if a powerdown is necessary for mitigation. The Gairgun array is towed behind the St.
Laurent at a depth of approximately 11
m (36.1 ft) (see Figure B–2 in the IHA
application) along predetermined lines
in water depths ranging from 1,900 to
4,000 m (6,233.6 to 13,123.4 ft). One
streamer approximately 232 m (761.2 ft)
in length with a single hydrophone is
towed behind the airgun array at a
depth of approximately 9 to 30 m (29.5
to 98.4 ft).
A square wave trigger signal is
supplied to the firing system hardware
by a FEI–Zyfer GPStarplus Clock model
565, based on GPS time (typically at
approximately 14 to 20 sec intervals).
Vessel speed is approximately 10.2 km/
hour (5.5 knots) resulting in a shot
interval ranging from approximately 39
to 56 m (128 to 183.7 ft). G-airgun firing
and synchronization are controlled by a
RealTime Systems LongShot fire
controller, which sends a voltage to the
airgun solenoid to trigger firing with
approximately 54.8 ms delay between
trigger and fire point.
Pressurized air for the pneumatic Gairguns is supplied by two Hurricane
compressors, model 6T–276–44SB/
2500. These are air cooled,
containerized compressor systems. Each
compressor is powered by a C13
Caterpillar engine which turns a rotary
screw first stage compressor and a three
stage piston compressor capable of
developing a total air volume of 600
SCFM @ 2,500 pounds per square inch
(PSI). The seismic system is operated at
1,950 PSI and one compressor could
easily supply sufficient volume of air
under appropriate pressure.
Seismic acquisition requires a
watchkeeper in the seismic lab and
another in the compressor container.
The seismic lab watchkeeper is
responsible for data acquisition/
recording, watching over-the-side
equipment, airgun firing and log
keeping. A remote screen permits
monitoring of compressor pressures and
alerts, as well as communication with
the compressor watchkeeper. The
compressor watchkeeper is required to
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monitor the compressor for any
emergency shut-down and provide
general maintenance that might be
required during operations.
Sound level radii for the proposed
three airgun array were measured in
2009 during a seismic calibration
(Mosher et al., 2009; Roth and Schmidt,
2010). A transmission loss model was
then constructed assuming spherical
(20LogR) spreading and using the source
level estimate 235 dB re 1 μPa (rms) 0–
peak; 225 dB re 1 μPa (rms) from the
measurements. The use of 20LogR
spreading fit the data well out to
approximately 1 km (0.6 mi) where
variability in measured vales increased
(see Appendix B in the IHA application
for more details and a figure of the
transmission loss model compared to
the measurement data). Additionally,
the Gundalf modeling package was used
to model the airgun array and estimated
a source level output of 236.7 dB 0–peak
(226.7 dB [rms]). Using this slightly
stronger source level estimate and a
20LogR spreading the 180 and 190 dB
(rms) radii are estimated to be 216 m
(708.7 ft) and 68 m (223.1 ft),
respectively. As a conservative measure
for the proposed safety radii, the sound
level radii indicated by the empirical
data and source models have been
increased to 500 m (1,640.4 ft) for the
180 dB isopleths and to 100 m (328 ft)
of the 190 dB isopleths.
The rms received levels that are used
as impact criteria for marine mammals
are not directly comparable to the peak
or peak-to-peak values normally used to
characterize source levels of airguns.
The measurement units used above to
describe the airgun source, peak or
peak-to-peak dB, are always higher than
the rms dB referred to in much of the
biological literature. A measured
received level of 160 dB (rms) in the far
field would typically correspond to a
peak measurement of about 170 to 172
dB, at the same location (Greene, 1997;
McCauley et al., 1998, 2000). The
precise difference between rms and
peak or peak-to-peak values for a given
pulse depends on the frequency content
and duration of the pulse, among other
factors. However, the rms level is
always lower than the peak or peak-topeak level for an airgun-type source.
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TABLE 2—DISTANCES TO WHICH SOUND LEVELS GREATER THAN OR EQUAL TO 190, 180, AND 160 DB RE 1 μPA (RMS)
COULD BE RECEIVED IN DEEP (GREATER THAN 1,000 M) WATER DURING THE SURVEY IN THE ARCTIC OCEAN,
AUGUST 7, TO SEPTEMBER 3, 2010
Tow depth
(m)
ice/open
water
Source and volume
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Single Mitigation Airgun (150 in3) ...................................
Three G-airguns (1,150 in3) ............................................
Acoustic Source Specifications—
Multibeam Echosounders (MBES), SubBottom Profilers (SBP) and Acoustic
Doppler Current Profilers (ADCP)
Along with the airgun operations,
additional acoustic systems that are
operated during the cruise include a 12
kHz Chirp echosounder and a 3–5 kHz
SBP from the St. Laurent. The Healy
operates a 12 kHz Kongsberg MBES, a
Knudsen 320BR profiler, a piloting
echosounder, and two ADCPs. These
sources are operated throughout most of
the cruise to map bathymetry, as
necessary, to meet the geophysical
science objectives. During seismic
operations, these sources are deployed
from the St. Laurent and the Healy and
generally operate simultaneously with
the airgun array deployed from the St.
Laurent.
The Knudsen 320BR echosounder
provides information on depth and
bottom profile. The Knudsen 320BR is
a dual-frequency system with operating
frequencies of 3.5 and 12 kHz, however,
the unit functions at the higher
frequency, 12 kHz, because the 3.5 kHz
transducer is not installed.
While the Knudsen 320BR operates at
12 kHz, its calculated maximum source
level (downward) is 215 dB re μPa at 1
m. The pulse duration is typically 1.5 to
5 ms with a bandwidth of 3 kHz (FM
sweep from 3 kHz to 6 kHz). The
repetition rate is range dependent, but
the maximum is a one percent duty
cycle. Typical repetition rate is between
1⁄2 s (in shallow water) to 8 s in deep
water. A single 12 kHz transducer (subbottom) array, consisting of 16 elements
in a 4x4 array will be used for the
Knudsen 320BR. The 12 kHz transducer
(TC–12/34) emits a conical beam with a
width of 30°.
The 3–5 kHz chirp SBP is towed by
and operated from the St. Laurent in
open water when the St. Laurent is not
working in tandem with the Healy. The
SBP provides information about
sedimentary features and bottom
topography. The chirp system has a
maximum 7.2 kW transmit capacity into
the towed array. The energy from the
towed unit is directed downward by an
array of eight transducers in a conical
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11/6–7
11/6–7
Predicted received RMS distances (m)
Water depth
190 dB
Deep (>1,000 m) ................
Deep (>1,000 m) ................
beamwidth of 80 degrees. The interval
between pulses is no less than one pulse
per second. SBPs of that frequency can
produce sound levels 200 to 230 dB re
1 μPa at 1 m (Richardson et al., 1995).
The Kongsberg EM 122 MBES
operates at 10.5 to 13 (usually 12) kHz
and is hull-mounted on the Healy. The
transmitting beamwidth is 1° or 2° foreaft and 150° athwartship. The maximum
source level is 242 dB re 1 μPam (rms).
Each ‘‘ping’’ consists of eight (in water
greater than 1,000 m deep) or four (less
than 1,000 m) successive fan-shaped
transmissions, each ensonifying a sector
that extends 1° fore-aft. Continuouswave (CW) pulses increase from two to
15 ms long in water depths up to 2,600
m (8,530 ft), and FM chirp pulses up to
100 ms long are used in water greater
than 2,600 m (8,530 ft). The successive
transmissions span an overall crosstrack angular extent of about 150°, with
2 ms gaps between pulses for successive
sectors.
The Knudsen 320BR hydrographic
SBP provides information on
sedimentary layering, down to between
20 and 70 m (65.6 to 229.7 ft),
depending on bottom type and slope.
The Knudsen 320 BR is a dualfrequency system with operating
frequencies of 3.5 and 12 kHz; only the
low frequency is being used during this
survey. At 3.5 kHz, the maximum
output power into the transducer array,
as wired on the Healy (where the array
impedance is approximately 125 ohms),
is approximately 6,000 watts (electrical),
which results in a maximum source
level of 221 dB re 1 μPa at 1 m
downward. Pulse lengths range from 1.5
to 24 ms with a bandwidth of 3 kHz (FM
sweep from 3 kHz to 6 kHz). The
repetition rate is range dependent, but
the maximum is a one percent duty
cycle. Typical repetition rate is between
1⁄2 s (in shallow water) to 8 s in deep
water. The 3.5 kHz transducer array on
the Healy, consisting of 16 (TR109)
elements in a 4x4 array, is being used
for the Knudsen 320BR. At 3.5 kHz the
SBP emits a downward conical beam
with a width of approximately 26°.
The piloting echosounder on the
Healy is an Ocean Data Equipment
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30
100
180 dB
160 dB
75
500
750
2,500
Corporation (ODEC) Bathy–1500 that
provides information on water depth
below the vessel. The ODEC system has
a maximum 2 kW transmit capacity into
the transducer and has two operating
modes, single or interleaved dual
frequency, with available frequencies of
12, 24, 33, 40, 100, and 200 kHz.
The 150 kHz ADCP has a minimum
ping rate of 0.65 ms. There are four
beam sectors and each beamwidth is 3°.
The pointing angle for each beam is 30°
off from vertical with one each to port,
starboard, forward, and aft. The four
beams do not overlap. The 150 kHz
ADCP’s maximum depth range is 300 m
(984.3 ft).
The Ocean Surveyor 75 is an ADCP
operating at a frequency of 75 kHz,
producing a ping every 1.4 s. The
system is a four-beam phased array with
a beam angle of 30°. Each beam has a
width of 4° and there is no overlap.
Maximum output power is 1 kW with a
maximum depth range of 700 m (2,296.6
ft).
Acoustic Source Specifications—
Icebreaking
Icebreaking is considered by NMFS to
be a continuous sound and NMFS
estimates that harassment occurs when
marine mammals are exposed to
continuous sounds at a received sound
level of 120 dB SPL or above. Potential
takes of marine mammals may ensue
from icebreaking activity in which the
Healy is expected to engage outside of
U.S. waters, i.e., north of approximately
74.1° North. While breaking ice, the
noise from the ship, including impact
with ice, engine noise, and propeller
cavitation, will exceed 120 dB (rms)
continuously. If icebreaking does occur
in U.S. waters, USGS expects it will
occur during seismic operations. The
exclusion zone (EZ) for the marine
mammal Level B harassment threshold
during the proposed seismic activities is
greater than the calculated radius during
icebreaking. Therefore, if the Healy
breaks ice during seismic operations
within the U.S. waters, the greater
radius, i.e., that for seismic operations,
supersedes that for icebreaking, so no
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additional takes have been estimated
within U.S. waters.
Dates, Duration, and Specific
Geographic Area
The seismic survey is being
conducted for approximately 36 days
from approximately August 2 to
September 6, 2010. The approximately
806 km (501 mi) of tracklines within
U.S. waters will be surveyed first. These
survey lines are expected to be
completed by approximately August 19,
2010. The seismic vessel St. Laurent
departed from Kugluktuk, Nunavut,
Canada on August 6, 2010 and returned
to the same port on approximately
September 15, 2010. The Healy departed
from Dutch Harbor, Alaska on August 2,
2010, to meet the St. Laurent on August
10, 2010. After completion of this
survey, the Healy is changing crew
through Barrow via helicopter or surface
vessel on September 6, 2010 (see Table
3 of the IHA application). The entire
survey area will be bounded
approximately by 145° to 158° West
longitude and 71° to 84° North latitude
in water depths ranging from
approximately 1,900 to 4,000 m (6,234
to 13,123 ft) (see Figure 1 and Table 1
of the IHA application). Ice conditions
are expected to range from open water
to 10/10 ice cover. See Table 3 of the
IHA application for a synopsis of the
2010 St. Laurent and Healy Extended
Continental Shelf expeditions in the
Arctic Ocean, August 2 to September 15,
2010.
Icebreaking outside U.S. waters will
occur between the latitudes of
approximately 74° to 84° North. Vessel
operations and ice conditions from
similar survey activities and timing in
2008 and 2009 were used to estimate the
amount of icebreaking (in trackline km)
that is likely to occur in 2010. USGS
expects that the St. Laurent and the
Healy will be working in tandem
through the ice for a maximum of 23 to
25 days while outside of U.S. waters.
The average distance travelled in 2008
and 2009 when the Healy broke ice for
the St. Laurent was 135 km/day (83.9
mi/day). Based on the 23 to 25 day
period of icebreaking, USGS calculated
that, at most approximately 3,102 to
3,372 km (1,927.5 to 2,095.3 mi) of
vessel trackline may involve
icebreaking. This calculation is likely an
overestimation because icebreakers
often follow leads when they are
available and thus do not break ice at all
times.
TABLE 3—PROJECTED 2010 ICEBREAKING EFFORT FOR USGS/GSC 2010 EXTENDED CONTINENTAL SHELF SURVEY IN
THE NORTHERN BEAUFORT SEA AND ARCTIC OCEAN
Two-Ship
operations
(days)
2008 .............................................................................................................................................
2009 .............................................................................................................................................
Average 2008 to 2009 .................................................................................................................
Projected 2010 .............................................................................................................................
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Comments and Responses
A Notice of Receipt of the USGS
application and proposed IHA was
published in the Federal Register on
July 8, 2010 (75 FR 39336). During the
comment period, NMFS received
comments from the Marine Mammal
Commission (Commission), the North
Slope Borough (NSB) Office of the
Mayor, and the Alaska Eskimo Whaling
Commission (AEWC). The public
comments can be found online at:
https://www.nmfs.noaa.gov/pr/permits/
incidental.htm. The following are their
comments, and NMFS’s responses.
Comment 1: The Commission
recommends that NMFS approve the
requested IHA, provided NMFS
ascertain who will be responsible for
operating the Canadian vessel and the
airguns and other instruments deployed
from the St. Laurent and issue an IHA
for these activities only if a U.S. agency
or U.S. citizen(s) will be conducting
those operations.
Response: USGS’s EA has clarified the
roles and responsibilities of the
Canadian vessel St. Laurent while
operating within and outside U.S.
waters:
‘‘The activity that the USGS is funding
and undertaking in both the U.S. waters
(maritime zones) and the high seas is to
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collect multi-beam, associated chirp
sub-bottom data, and possibly sediment
and rock samples both within and
outside the 370.4 km (200 nmi) limit, as
well as to break ice for the St. Laurent
during operations in ice-covered area.
The St. Laurent is a vessel entitled to
sovereign immunity under international
law, operated by the CCG with a seismic
system owned and operated by Natural
Resources Canada, and therefore not
under the jurisdiction of U.S. laws or
regulations outside the U.S. maritime
zones where the U.S. has exclusive
rights and jurisdiction. The USGS is
acting as the responsible agency for
MMPA, ESA, and NEPA for the St.
Laurent while the St. Laurent is
collecting seismic data within the U.S.
EEZ. The operators of the seismic
equipment on the St. Laurent have
written a Categorical Declaration that,
for operations in U.S. waters (i.e., within
the U.S. EEZ), they will comply with
any and all environmental mitigation
measures required by NMFS and/or the
U.S. Fish and Wildlife Service (USFWS)
(see Appendix C of the EA). There are
no U.S. Federal funds that are
supporting the costs of operating St.
Laurent, or its seismic gear’’ (see p. 2 to
3 of the EA).
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19
27
23
23–25
Two-Ship
operations
(km)
2,469
37,744
3,122
3,102–3,372
km/day
130
140
135
The GSC is collecting seismic data in
U.S. waters at the request of the U.S.
and would not otherwise be operating in
U.S. waters. Dr. Jonathan Childs, USGS
liaison aboard the St. Laurent, will be
responsible for establishing the start and
end points of the lines within U.S.
waters and for compliance with
conditions of the IHA. The Categorical
Declaration from Natural Resources
Canada, United Nations Convention on
the Law of the Sea (UNCLOS) Program
(see p. 116 in Appendix C of the EA)
further states:
‘‘While in U.S. waters (i.e., the U.S.
EEZ), the GSC operators will comply
with any and all environmental
mitigation measures required by the
NMFS and/or USFWS. A NMFS
approved PSO and a U.S. liaison aboard
the St. Laurent will be responsible for
ensuring that all mitigation measures
required by NMFS and/or USFWS are
implemented while the St. Laurent
operates in U.S. waters.’’
‘‘While operating in U.S. waters, the
GSC operators of the seismic profiling
system categorically consent to comply
with all applicable U.S. laws, including
the MMPA and the ESA, as well as any
terms and conditions that may be
required under an IHA issued by NMFS
and any measures that may arise from
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ESA consultations with NMFS and/or
USFWS. Operation of the seismic
profiling system includes conditions
under which the system will be turned
on and operation continued or ceased in
the presence of marine mammals
(including polar bears), and the
diversion of scientific tracklines for
avoidance of observed wildlife. This
declaration should in no way be
constructed to influence or alter the safe
operation of the vessel which is at the
sole discretion of the CCG and its
Commanding Officer.’’
Comment 2: The Commission
recommends that NMFS approve the
requested IHA, provided NMFS work
with the applicant to re-estimate
exposures for ice-breaking activities
based upon the total area that may be
exposed to sound levels greater than or
equal to 120 dB re 1 μPa (rms).
Response: The Commission’s
concerns are that the USGS application
states that an area of water 4,109 km2
(1,586.5 mi2) will be exposed to sound
levels ≥120 dB re 1 μPa (rms) but that
the marine mammal ‘‘takes’’ are
estimated using a larger number of 5,137
km2 (1,983.4 mi2) to allow for turns,
repetition of certain tracklines because
of poor data quality or minor changes in
survey design (this larger number
represents an uncertainty estimate of
approximately 20 percent). A critical
clarification is that the 4,109 km2 and
5,137 km2 numbers are for estimating
the area of takes within U.S. waters
based on seismic operations, using a
radius of approximately 2,500 m (8,202
ft) (see page 69 of the EA) for the ≥160
dB re 1 μPa (rms) isopleths, and not on
the area ensonified by continuous noise
of icebreaking at ≥120 dB re 1 μPa (rms).
This approach was taken because the
area of take for the seismic source ≥160
dB re 1 μPa (rms), estimated at
approximately a 2,500 m (8,202 ft)
radius was greater than that estimated
for ≥120 dB re 1 μPa (rms) of continuous
sound from icebreaking, estimated at
1,750 m (5,741.5 ft) radius (see page 213
of the EA). The estimated area
ensonified for icebreaking outside of
U.S. waters is 11,802 km2 (4,556.8 mi2)
(see p. 213 of the EA).
A point of confusion in this
clarification is that the original request
from NMFS was to estimate takes from
icebreaking, rather than the total area
exposed to sound levels ≥120 dB re 1
μPa (rms). The addendum on
icebreaking (see Appendix J of the EA)
only estimated takes for the Healy
breaking ice outside of U.S. waters
because there would be no additional
takes for the sound of icebreaking
within U.S. waters beyond those
estimated for the seismic source.
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One can calculate the area of potential
icebreaking within U.S. waters by using
the estimated track length
(approximately 806 km [500.8 mi], page
69 of the EA) and the ≥120 dB μPa (rms)
radius, estimated at 1,750 m (5,741.5 ft)
(see page 213 of the EA), to get an
ensonified area of 2,821 km2 (1,089.2
mi2), which, with an additional
uncertainty estimate of 20 percent totals
3,385 km2 (1,307 mi2). This number is
still smaller than either the 4,109 km2 or
5,137 km2 numbers cited in the
comments from the Commission.
It is important to also clarify that (a)
the USGS estimated icebreaking
assuming that maximum noise of
icebreaking would occur along the total
length of tracklines. The preferred
strategy operating in the ice is to follow
leads whenever possible, which reduces
the total icebreaking effort. Canadian
and U.S. ice observers and analysts are
aboard both vessels to select paths
through the ice to minimize icebreaking;
(b) for some part of the cruise,
depending on ice conditions, the St.
Laurent will be leading Healy so that
high-quality multi-beam data can be
collected, further reducing the amount
of icebreaking the Healy will be doing
(and therefore reducing the area of
ensonfication for ≥120 dB re 1 μPa
[rms]). The estimates of the area of
ensonification in the EA and IHA do not
include a correction for this type of data
acquisition. Hence the area of
ensonification is likely to be
overestimated; (c) the tracklines are laid
out to enable flexibility in where the
ship may navigate through the ice,
maximizing the opportunities to follow
leads and reduce the requirement for
icebreaking and therefore minimize the
noise of icebreaking. Under
international law as reflected in Article
76 of UNCLOS, the ECS outer limit
points are to be no more than 111.1 km
(60 nmi) apart. The cruise tracks are
planned 92.6 km (50 nmi) apart or less
so that the vessels can deviate
approximately 18.5 km (10 nmi) either
side of the track to follow leads; and (d)
based on the latest ice imagery for
August 3, 2010, there will probably be
no need to break ice within U.S. waters.
As of August 3, 2010, http;//
arctic.atmos.uiuc.edu/cryosphere/
NEWIMAGES/
arctic.seaice.color.000.png shows the
ice extent in the area north of the Alaska
coast to be mostly open water. The PSOs
aboard the Healy will be monitoring
actual takes from icebreaking during the
cruise, which can be compared with
takes estimated and authorized in the
IHA.
Comment 3: The Commission
recommends that NMFS approve the
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60179
requested IHA, provided NMFS advise
the applicant to consult with the
USFWS regarding the need for a
separate incidental taking authorization
for walruses and polar bears.
Response: On May 7, 2010, USGS
requested that the USFWS review the
operations for the summer 2010 Arctic
Ocean geophysical experiment for
potential impacts on Pacific walruses
and polar bears. Given the USFWS’s
understanding of polar bear and walrus
distribution, the planned travel routes
and locations of the activity, the USFWS
believe that it is unlikely the proposed
studies will result in any major
disturbances or impacts to individual
polar bears or walruses. Considering the
relatively low likelihood of
encountering polar bears or walruses,
along with the limited impact and
anticipated responses of affected
animals that would likely ensue from an
encounter with either or both vessels,
the USFWS has determined that an
incidental take authorization is not
necessary for this project. See the
USFWS’s informal ESA Section 7
consultation letter regarding walruses
and polar bears in Appendix E of the EA
(p. 128 to 132).
Comment 4: The Commission
recommends that NMFS approve the
requested IHA, provided NMFS provide
additional justification for its
preliminary determination that the
planned monitoring program will be
sufficient to detect, with a high level of
confidence, all marine mammals within
or entering the identified exclusion
zones (EZs). At a minimum, such
justification should (1) identify those
species that it believes can be detected
with a high degree of confidence using
visual monitoring only, (2) describe
detection probability as a function of
distance from the vessel, (3) describe
changes in detection probability under
various sea state and weather conditions
and at night, and (4) explain how close
to the vessel marine mammals must be
for observer to achieve the anticipated
high nighttime detection rate.
Response: NMFS believes that the
planned monitoring program will be
sufficient to visually detect, with
reasonable certainty, most marine
mammals within or entering identified
EZs. This monitoring, along with the
required mitigation measures, will help
ensure the authorized taking effects the
least practicable adverse impact on the
affected species or stocks and will have
a negligible impact on the affected
species or stocks.
Until proven technological advances
are made, nighttime mitigation
measures during operations include
combinations of the use of PSOs and
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night vision devices (NVDs). Should the
airgun array be powered-down, it is
believed that the operation of a single
airgun continues to serve as a sound
source deterrent to marine mammals. In
the event of a complete shut-down of
the airgun array, for mitigation or
repairs, airgun operations are suspended
until nautical twilight-dawn (when
PSOs are able to clear the EZ). Airgun
operations do not begin until the entire
EZ radius is visible for at least 30
minutes. In all likelihood there will be
no nighttime start-ups for the time that
the seismic data are collected in U.S.
waters (mid-August), when 24 hour
daylight is still occurring.
Comment 5: The Commission
recommends that NMFS approve the
requested IHA, provided NMFS clarify
the meaning of the qualifiers ‘‘when
practical,’’ ‘‘if practical,’’ and ‘‘when
feasible’’ to indicate how often and
under what specific conditions the
applicant expects to use (1) two
Protected Species Observer (PSOs) to
monitor the EZ for marine mammals
during daytime operations and
nighttime start-ups of the airguns, (2)
crew members to assist PSOs in
detecting marine mammals and
implementing mitigation requirements,
and (3) PSOs during daytime periods to
compare sighting rates and animal
behavior during times when seismic
airguns are and are not operating.
Response: The St. Laurent and Healy
will carry trained, NMFS-qualified and
experienced PSOs for the seismic study
involving the use of airguns and
icebreaking for the upcoming proposed
project. PSOs are appointed by USGS
with NMFS concurrence. USGS will
utilize vessel-based PSOs to watch for
and monitor marine mammals near the
icebreaking and seismic source vessels
during all daytime airgun operations
and before and during start-ups of the
airguns day or night. PSOs will have
access to reticle binoculars and NVDs to
scan the area around each vessel. PSOs
will alternate between binoculars and
the naked eye to avoid eye fatigue.
During all monitoring periods, PSOs
will be on duty from observation
locations that allow for optimal
monitoring capabilities. During meal
times and restroom breaks it is
sometime difficult to have the full
complement of PSOs on effort, but at
least one PSO will be on watch during
those brief times. The complement of
PSOs rotates shifts, with duty shift
lasting generally one to four hours.
Regarding the Commission’s subcomment (1), the intention and
requirement is for two PSOs to stand
watch during all seismic operations in
U.S. waters, including cold start and
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ramp-ups. Only one PSO is on watch
during daylight non-seismic operations.
Two U.S. PSOs will join the St. Laurent
before seismic operations begin in U.S.
waters so that there will be five PSOs
aboard the St. Laurent for all seismic
data collected in U.S. waters. The
restriction on the U.S. PSOs not
standing watch for more than four hours
at a time and the as yet unknown
schedules of the Canadian watches
makes actual schedules at this time
unknown, hence the qualifiers ‘‘when
practical,’’ etc., are used to account for
this uncertainty. There may also be
short periods of time, for example
during mandatory fire and boat safety
drills, when the PSOs on watch must
leave their observing stations. It is the
responsibility of the U.S. liaison aboard
the St. Laurent working with the
Canadian counterparts to develop a
watch schedule consistent with the
requirements of the IHA, especially for
the ramp-ups, whether during the day or
night. In all likelihood there will be no
nighttime start-ups for the time that the
seismic data are collected in U.S. waters
(mid-August), when 24 hour daylight is
still occurring.
Canada will follow its own permitting
requirements for watches and start-ups
when operating outside of U.S. waters.
The two U.S. PSOs aboard the St.
Laurent during the time the St. Laurent
is in U.S. waters will return to the Healy
after the U.S. waters portion of the
survey is completed and stand watch on
the Healy to aid in sighting marine
mammals and alert the PSOs aboard the
St. Laurent of their sightings during the
two ships’ operations.
Regarding the Commission’s subcomment (2), the qualifiers to this
condition refer to the situations in
which (a) other members of the ship’s or
scientific crew on either vessel notice a
marine mammal near the vessel and
report it to the bridge or the PSOs; (b)
the bridge watch can assist in marine
mammal observations during the night
when the PSO is not required to be on
the bridge; or (c) the bridge watch
aboard the Healy (in the steering station
above the bridge, which is the highest
and best vantage point for making
observations) sees marine mammals. It
is impossible to predict the frequency
that these situations will occur, only
that many more eyes are available to
spot marine mammals than those of the
PSOs, and that these additional eyes
should be used whenever possible,
practical, or feasible. It is not the
intention in any of these situations for
the crew or the bridge to implement
mitigation requirements because that
authority is with the PSOs. However,
the bridge often acts as a central point
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of communication among science crew,
ship’s crew, and PSOs, and therefore
plays a vital role in ensuring that the
PSOs can implement appropriate
mitigation procedures at the appropriate
times.
Regarding the Commission’s subcomment (3), the U.S. PSOs aboard the
Healy (or when aboard the St. Laurent)
will be on watch collecting marine
mammal observation data whether the
airguns are operating or not. When the
Healy is operating independently of the
St. Laurent (e.g., steaming north from
Dutch Harbor or for operations at the
beginning of the survey when in open
water—and therefore independently
surveying), the data collected by the
PSOs is baseline data. For the seismic
survey within U.S. waters, the St.
Laurent will be steaming to the start of
the tracks from the east and will have
the U.S. PSOs aboard to record baseline
observations during the steaming time.
Both U.S. and Canadian observers will
be recording baseline information for at
least 30 min on site prior to initial startup and ramp-ups of the airgun
operations during the survey. If the St.
Laurent is operating independently in
either international or Canadian waters,
it is the responsibility of the Canadian
Chief Scientist, using the conditions set
forth in the Canadian permits to
determine whether the Canadian
observers will stand watch to collect
baseline information. When the ships
are operating together in international or
Canadian waters, the PSOs aboard the
Healy will be making observations
either in front of the St. Laurent (during
seismic operations) or behind the St.
Laurent (during multi-beam operations).
It is neither practical nor economical to
pre-survey all tracks for the presence of
marine mammals (and baseline
behavior) prior to conducting seismic
operations because of the huge area
covered by the joint expedition, so the
most likely baseline information to be
collected will be at breaks in lines for
repair or maintenance of the seismic
gear and at the start of the survey. Using
the experience of 2008 and 2009, halts
in seismic acquisition for equipment
maintenance generally occurred every
48 to 72 hours and lasted from 6 to 48
hours. Marine mammal observations
made aboard the Healy cruise will allow
the PSOs to collect baseline information
whenever the seismic equipment is not
operating.
Comment 6: The Commission
recommends that NMFS approve the
requested IHA, provided NMFS propose
to USGS that it revise its study design
to collect meaningful baseline data on
sighting rates for marine mammals.
Such information is essential for a
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realistic assessment of impacts from the
proposed activities and recovery from
those impacts.
Response: NMFS is unclear about the
Commission’s recommendation
regarding the revision of USGS’s ‘‘study
design.’’ Please clarify if you are
referring to USGS overall study design
or more specifically to the monitoring
plan required under the MMPA. The
purpose of the USGS’s project is for
marine geophysical research, not to
conduct a dedicated marine mammal
research survey. Extending the survey is
not practicable from an operational
standpoint for the applicant. Due to the
remote location of the survey and the
length of time needed to conduct the
requested science experiment, there
may be little time left for the vessel to
operate without the need for refueling
and servicing.
During the cruise, there will be
significant amounts of transit time preand post-survey during which PSOs will
be on watch (e.g., prior to and after the
seismic portions of the survey). The
collection of this observational data by
PSOs may provide meaningful baseline
data for marine mammals, but it is
unlikely that the information would
result in any statistically robust
conclusions for this particular seismic
survey. See NMFS responses to
comments above.
To augment detection and baseline
observations, the U.S. liaison aboard the
St. Laurent will request that prior to the
start of seismic activities in U.S. waters,
the GSC operators deploy a sonobuoy
that can be monitored through an audio
channel for the presence of whales for
at least the 30 min time period that the
vessel is on site before commencing
seismic operations. Detected
vocalizations can be used to augment
visual observations. The sonobuoy
audio information is only intended to be
used to identify the presence or absence
of animals because the relative direction
and distance to vocalizing animals
cannot be determined from these
sounds. The sonobuoy information is
not intended to be used for mitigation
purposes. As stated in the IHA, seismic
operations will not begin if any
bowhead whales are seen or heard. Use
of sonobuoys is contingent upon
concurrence by GSC operators, who are
generally supportive of collecting
additional data in support of marine
mammal observations.
In addition, USGS proposes that the
sonobuoy data from the refraction part
of the experiment will be made
available to an appropriate biologist or
acoustician for analysis for the presence
of marine mammals. The data is
recorded continuously for
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approximately eight hours, and the
sonobuoy records sounds not only from
the airguns, but ambient noise and any
other sounds long after the vessel has
left the area. Although no noise trains
that might be interpreted as marine
mammal sounds have been definitively
identified on the sonobuoys examined
during 2008 and 2009 joint expeditions
(Chian, pers. comm.), the sonobuoys are
a source of information available for
closer scrutiny.
Comment 7: The Commission
recommends that NMFS approve the
requested IHA, provided NMFS require
the applicant to collect information to
evaluate the assumption that 160 dB re
1 μPa (rms) is the appropriate threshold
at which harassment occurs for all
marine mammals in the survey area.
This assumption can and should be
tested using in-situ measurements of
sound propagation concurrent with
observations of the responses of marine
mammals exposed to such sounds. Such
tests should be conducted using speciesspecific data, and test results should be
used to inform decision makers
regarding the applicability of the 160 dB
re 1 μPa (rms) threshold for specific
species and to improve future mitigation
measures.
Response: Behavioral responses to
sound are context specific and can vary
by species and other factors. However,
there are not currently enough speciesspecific data showing how marine
mammals respond to sound to support
the development of separate harassment
thresholds for every species. Therefore,
NMFS uses the best available applicable
data, which includes studies of several
different species, to predict at what
levels marine mammals are likely to be
harassed and NMFS believes that the
160 dB re 1 μPa (rms) threshold remains
appropriate for the species in this
project area.
Regarding testing these behavioral
harassment assumption, NMFS
primarily relies on scientific research
advances, and applicable monitoring
results (where appropriate) to inform
them. Behavioral response field studies
that are able to definitively track what
an animal is doing for some period of
time (a baseline), expose it to a known
received sound level, and record its
behavior afterwards until it goes back to
baseline are expensive and challenging
to execute and while a few are currently
underway, relatively few have been
completed. Separately, in required
monitoring measures, PSOs are required
to make behavioral observations during
seismic activities, however, while they
can very effectively detect a marine
mammal, identify it, and record its
behavior at the surface for the moments
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that it is within view of the moving
vessel—this information is typically not
enough to support the development of a
harassment threshold. Alternatively,
there has been one longer-term (i.e.,
associated with a five year rulemaking)
monitoring study that has generated
numerous data of a robust and
measureable nature through the
deployment of an extensive hydrophone
array.
Regarding bowhead whales
specifically, some published articles
indicate that they may avoid seismic
vessels at levels below 160 dB (rms),
NMFS does not believe that these
responses rise to the level of a take.
Miller et al. (1999) indicated that some
bowhead whales may have started to be
deflected from their migratory path at 35
km (21.7 mi) from the seismic vessel,
during migration, however, as described
in MMS’ 2006 Final Programmatic
Environmental Assessment (PEA), this
response has not been seen at other
times of the year and during other
activities. To show the contextual
nature of this minor behavioral
modification, recent monitoring studies
of Canadian seismic operations
indicated that feeding, non-migratory
bowhead whales do not move away
from a noise source at an SPL of 160 dB.
NMFS therefore continues to estimate
‘‘takings’’ under the MMPA from
impulse noises, such as seismic, as
occurring at 160 dB (re 1 μPa [rms]).
Comment 8: The Commission
recommends that NMFS approve the
requested IHA, provided NMFS require
the applicant to make observations
during all ramp-up procedures to gather
the data needed to analyze and report
on their effectiveness as mitigation. As
it has noted in past correspondence, the
Commission would be pleased to
discuss with NMFS the collection and
analysis of such data and the design of
such experiments to promote a better
understanding of the utility and
shortcomings of ramp-up as a mitigation
measure.
Response: The IHA requires that PSOs
on the St. Laurent and Healy make
observations for 30 min prior to rampup, during all ramp-ups, and during all
daytime seismic operations and record
the following information when a
marine mammal is sighted:
(i) Species group size, age/size/sex
categories (if determinable), behavior
when first sighted and after initial
sighting, heading (if consistent), bearing
and distance from seismic vessel,
sighting cue, apparent reaction to the
airguns or vessel (e.g., none, avoidance,
approach, paralleling, etc., and
including responses to ramp-up), and
behavioral pace; and
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(ii) Time, location, heading, speed
activity of the vessel (including number
of airguns operating and whether in
state of ramp-up or power-down),
Beaufort wind force and sea state,
visibility, and sun glare.
One of the primary purposes of
monitoring is to result in ‘‘increased
knowledge of the species’’ and the
effectiveness of monitoring and
mitigation measures; marine mammal
reactions to ramp-up would be useful
information in this regard. NMFS has
asked USGS to gather all data that could
potentially provide information
regarding the effectiveness of ramp-ups
as a mitigation measure. However,
considering the low numbers of marine
mammal sightings and low number of
ramp-ups, it is unlikely that the
information will result in any
statistically robust conclusions for this
particular seismic survey. Over the long
term, these requirements may provide
information regarding the effectiveness
of ramp-up as a mitigation measure,
provided animals are detected during
ramp-up.
A study investigating the efficacy of
ramp-up has been jointly funded by the
Bureau of Ocean Energy Management,
Regulation, and Enforcement (BOEMRE)
and the Joint Industry Programme (JIP).
Post-cruise monitoring reports for
numerous seismic surveys are currently
available on the NMFS MMPA
Incidental Take Program Web site
should there be interest in further
analysis of this data by the public.
Comment 9: The NSB and its
residents as well as the AEWC are
concerned about potential health
impacts to the environment associated
with offshore development (i.e.,
industrial and commercial activities) on
the North Slope. Activities allowed by
the proposed authorization pose direct,
indirect, and cumulative impacts on
species (especially marine mammals)
that are critical to the subsistence
harvesting villages the AEWC represents
and the NSB people’s subsistence
harvest.
Response: NMFS is unclear about the
specific meaning of the term ‘‘health
impacts’’ as used in the public
comments. The USGS and NMFS are
making every effort to minimize the
direct, indirect, and cumulative impacts
through the federal NEPA, MMPA, and
ESA process, as well as consulting with
the Native communities. Cumulative
impact assessments are USGS and
NMFS responsibility under NEPA. The
revised EA has addressed concerns
about potential impacts using the best
available science. In evaluating the
severity of the impacts, it is important
to realize that the proposed seismic
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activity within the U.S. EEZ is more
than 100 km (54 nmi) offshore in a
region well away from the main
migration routes of the bowhead whale
and will occur at a time prior to the
bowhead whales beginning their fall
migration from the Canadian Beaufort.
Although a single individual bowhead
whale has been identified in this region
from tagging, there is little evidence to
suggest that the location or timing of the
survey overlaps with or interferes with
bowhead whaling activities. As noted in
the EA, ‘‘available information * * *
does not indicate that marine and
seismic surveys for oil and gas
exploration activities has had detectable
long-term adverse population-level
effects on the overall health, current
status, or recovery of marine mammal
species and populations in the Arctic
region. For example, data indicated that
the Bering-Chukchi-Beaufort (BCB)
bowhead whale population has
continued to increase over the
timeframe that oil and gas activities
have occurred. There is no long-term
displacement from habitat (although
studies have not specifically focused on
addressing this issue) * * * monitoring
studies indicate that most fall migrating
whales avoid an area with a radius of
about 20 to 30 km (12.4 to 18.6 mi)
around a seismic vessel operating in
nearshore waters (Miller et al., 2002).
USGS is not aware of data, however that
indicate that such avoidance is longlasting after cessation of the activity’’
(EA, p. 81 to 82). Seismic survey
activities in the Canadian and Russian
Arctic occur in different geographical
areas, therefore, they are not analyzed.
NMFS does not allow activities in the
Arctic, NMFS only authorizes the take
of marine mammals incidental to an
otherwise legal specified activity in a
specified geographic area.
Comment 10: The NSB is concerned
that NSB communities are being
overwhelmed by multiple planning
processes both because of the
constraints on time and expertise of
communities and individuals and
because of the seeming inability to
meaningfully influence the decisions
being made.
Response: It is unfortunate that the
NSB communities feel overwhelmed by
the multiple planning processes, time
constraints, and other issues. Because of
the statutory timelines associated with
the MMPA IHA process (which include
the 30-day public review period), NMFS
is also forced to work within
challenging time constraints. However,
NMFS has encouraged Arctic applicants
to apply earlier than required by the
regulations, which allows NMFS, NSB,
BOEMRE, and the affected communities
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time to review the applications prior to
meeting in Spring at the Open Water
Meeting to discuss the applications. If
the NSB has process recommendations
that could make things easier for the
communities while still allowing NMFS
to meet our regulatory requirements,
NMFS would be glad to discuss them.
Separately, NMFS makes every effort to
incorporate input from the NSB
communities, where appropriate given
our regulatory requirements.
USGS included a statement about
environmental justice in the EA, ‘‘the
proposed action complies with EO
12898, Federal Actions to Address
Environmental Justice in Minority and
Low-income Populations and EO 13045,
Protection of Children from
Environmental Health Risks and Safety
Risks. USGS solicited public comment
on their Draft EA and published a
Notice of Availability in the Federal
Register on June 11, 2010 (75 FR 33326).
NMFS published a Notice of Receipt of
the USGS application and proposed IHA
in the Federal Register on July 8, 2010
(75 FR 39336). The public comments
were considered by USGS in developing
the EA and by NMFS in developing the
IHA. ‘‘As part of its Plan of Cooperation,
USGS is hiring an Alaska native to be
a member of the science crew, serve as
an observer, and provide
communication with the subsistence
communities.’’
Comment 11: The NSB and AEWC
recognize the efforts made by the USGS
to meet with representatives of their
communities and to provide
information on the proposed seismic
survey work planned for this summer.
The AEWC appreciate the opportunity
to receive information directly from the
Federal agency planning the activities,
and those efforts have helped to provide
the AEWC with a better understanding
of the proposed seismic surveys. The
AEWC looks forward to further dialogue
in the future should the Federal
government continue with similar work
in the Arctic, AEWC wishes to
emphasize that, given the willingness of
the USGS to work with the AEWC. The
NSB and AEWC do no object to the
issuance of an IHA for these operations,
despite the serious process concerns
raised in their public comments.
Response: NMFS has issued an IHA to
USGS for conducting a marine seismic
survey in the Arctic Ocean from August
to September, 2010, which includes the
mitigation, monitoring, and reporting
requirements described below.
Comment 12: The NSB and AEWC
objects to the ongoing flawed public
process employed by the NMFS Office
of Protected Resources (OPR), in which
it purports to accept and consider
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public comment (from local
communities in regulating activities in
the Arctic) on requests for Incidental
Harassment Authorizations and in
regulating activities in the Arctic. The
AEWC strenuously objects to a public
comment process that fails to provide an
opportunity for meaningful input before
the activities are scheduled to occur.
Congress intended that the local
impacted communities have an
opportunity to provide substantive
feedback to the Federal government
before decisions are made and before
any harassment takes place. The AEWC
states that the people on the North
Slope feel like they have no opportunity
to influence government
decisionmaking and therefore do not
feel like NMFS’ decisions reflect the
interests or input of the local whaling
captains, who have invaluable
observations and direct experience,
developed over hundreds of
generations, to offer.
This particular case provides a stark
example of how and why OPR’s process
is flawed to the point of being irrelevant
for the local impacted communities on
the North Slope and must be wholly
reformulated. The AEWC states that
these issues have plagued OPR’s
program for years, and despite many
lessons learned in the offshore context
over the past several years, nothing at
OPR has changed for the better. The
AEWC welcomes the opportunity to
work with OPR leadership to improve
upon this important regulatory program
if NMFS and OPR are willing to make
substantive changes to ensure adequate
public participation and adequate
protection of their local communities
and the marine mammals upon which
they depend.
Response: In order to issue an
authorization pursuant to Section
101(a)(5)(D) of the MMPA, NMFS must
determine that the taking by harassment
of small numbers of marine mammals
species or stocks will have a negligible
impact on affected species or stocks,
and will not have an unmitigable
adverse impact on the availability of
affected species or stocks for taking for
subsistence uses. If NMFS is able to
make these findings, the Secretary is
required to issue an IHA. As required by
the MMPA and its implementing
regulations, NMFS published a Notice
of Receipt of the USGS application and
proposed IHA in the Federal Register
on July 8, 2010 (75 FR 39336). All
substantive public comments were
considered by NMFS in developing the
IHA and responses to those public
comments can be found here in this
notice. NMFS determined that it was
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able to make the required MMPA
findings.
For many years, NMFS has conducted
the Arctic Open Water Meeting, which
brings together the Federal agencies, the
oil and gas industry, and affected Alaska
Native organizations to discuss the
proposed activities and monitoring
plans. Local and traditional knowledge
is considered at these times, and it is
not too late for that knowledge to serve
a useful purpose. These communities
are also afforded an opportunity to
submit comments on the IHA
application and proposed IHA notice,
which are then considered by NMFS
before making a final determination on
whether or not to issue an IHA.
Comment 13: The AEWC states that in
implementing the MMPA, NMFS has
done everything in its power to gut
Congress’ expressed intent to provide
meaningful public participation. The
way in which NMFS sequences the IHA
applications and the public notices
renders the public comment process
ineffective and irrelevant for NMFS’s
decision-making process.
The NSB and AEWC state that in this
action the proposed seismic activities
were scheduled to begin at least two
days before the public comment period
closed. NMFS requested that comments
be received by August 9, 2010, and the
agency then supposedly has 45 days
within which to analyze the comments
and issue a final IHA. In the Federal
Register notice, however, NMFS
clarifies that USGS’s two ships intend to
rendezvous in the survey area on
August 7, 2010. The obvious problem is
that the ships have been deployed, the
crews have been informed of their
operational restrictions, and seismic
activities have likely commenced before
NMFS receives public comment or
issues the final IHA. As a result, the
AEWC cannot possibly provide
meaningful input into the operations or
how they should be regulated. While the
AEWC are being forced to write detailed
comments on a lengthy IHA application
and Federal Register notice, the ships
are already out in the water adding
noise to the marine environment and
transiting the Chukchi Sea. The AEWC
states that it is absolutely insulting for
the activities to commence before the
public comment deadline has even been
closed.
The AEWC states that it is readily
apparent from this sequencing that
NMFS is actually allowing the USGS to
operate without an IHA (or simply
looking the other way) during a
significant portion of the planned
activities. Based on past experiences, it
has taken NMFS several weeks to
review public comments and issue a
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final IHA. Here, USGS plans to operate
during August and September, and yet
the public comment period did not
close until August 9. It’s very likely in
this situation that USGS will therefore
complete a majority of its planned
operations before even receiving from
NMFS the actual IHA, which spells out
specific mitigation requirements such as
monitoring of EZs and shut-down and
ramp-up procedures. In its responses to
comments, the AEWC requests explicit
clarification from NMFS on whether
and to what extent NMFS knew of or
allowed USGS to conduct seismic
activities before the IHA was issued.
The AEWC also requests explicit
clarification on whether USGS or NMFS
was in violation of any provisions of the
MMPA as a result.
Response: NMFS received a revised
IHA application from USGS that was
deemed adequate and complete on June
1, 2010. NMFS published a Notice of
Receipt of the USGS application and
proposed IHA in the Federal Register
on July 8, 2010 (75 FR 39336), but due
to the close of the 30 day public
comment period falling on a weekend,
the closing date was calculated as
August 9, 2010 in the Federal Register.
USGS was notified of the delayed
closing date by NMFS. While it usually
takes several weeks to address public
comments, NMFS worked especially
diligently to review and consider the
comments in a timely manner such that
NMFS could make a final decision in a
time frame that would allow USGS and
GSC to conduct the proposed seismic
operations if NMFS did issue an IHA.
NMFS does not authorize USGS to
conduct seismic activities, NMFS
authorizes the take of marine mammals
incidental to an otherwise legal specific
activity in a specified geographic area.
While beginning seismic work in the
U.S. EEZ on approximately August 7,
2010, was the optimum plan for the
two-icebreaker experiment, experiments
this large always have contingency
plans for unexpected conditions (such
as weather, ice conditions, equipment
maintenance, ship maintenance, other
emergencies, etc.). In the case of this
experiment, the St. Laurent had
approximately 10 days of work planned
inside the Canadian EEZ after the twoicebreaker experiment ended. This
Canadian survey work was started to
account for the delay in obtaining the
IHA. Likewise, the Healy had
contingency multi-beam survey work
planned on the Beaufort margin that
could be conducted independently of
the St. Laurent in case open water
would allow the vessels to operate
independently. The Healy began this
work and continued doing this survey
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work until the St. Laurent entered the
ice on her way north. The Healy and St.
Laurent did not begin any activities that
NMFS believes would result in the
potential take of marine mammals until
after they received the IHA on August
11, 2010.
Below is the sequence of dates and
events of interactions between NMFS,
USGS, and the GSC regarding the IHA
and seismic survey:
• August 2, 2010—Healy departed
Dutch Harbor, Alaska.
• August 6, 2010—St. Laurent
underway from Kugluktuk, Nunavut,
Canada.
• August 8, 2010—Healy commenced
hydrographic survey of U.S./Canada
disputed zone.
• August 9, 2010—Healy finished
hydrographic survey of U.S./Canada
disputed zone.
• August 10, 2010—Healy and St.
Laurent rendezvous, transfer personnel,
and proceed in convoy toward U.S. EEZ.
• August 11, 2010—Healy proceeds
alone within U.S. EEZ for sampling
program. IHA received via email and
MSR received to conduct science
operations in U.S. EEZ.
• August 12, 2010—St. Laurent
begins seismic operations (line 6) in the
U.S. EEZ.
• August 13, 2010—Healy joins the
St. Laurent for seismic operations (line
7).
While USGS has yet to submit its
draft 90 day monitoring report, NMFS is
not aware of any incidences of noncompliance or violations of the MMPA.
Comment 14: The AEWC states that
the authorization itself must prescribe
certain requirements such as
‘‘permissible methods for taking by
harassment,’’ ‘‘means of effecting the
least practicable impact on such
species,’’ measures to ‘‘ensure no
unmitigable adverse impact on the
availability of the species or stock for
taking for subsistence use,’’
requirements pertaining to ‘‘monitoring
and reporting,’’ and for ‘‘independent
peer review’’ of such monitoring and
reporting if the taking may affect
subsistence use. Indeed, NMFS’
regulations further provide that ‘‘any
preliminary finding of ‘negligible
impact’ and ‘no unmitigable adverse
impact’ shall be proposed for public
comment along with the proposed IHA.’’
Without understanding exactly how the
IHA incorporates these requirements
through specific language, the public is
foreclosed from providing input on how
the activities will be regulated.
Response: The July 8, 2010, proposed
IHA notice (75 FR 39336) contained all
the relevant information needed by the
public to provide comments on the
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proposed authorization itself. The
notice contained the permissible
methods of taking by harassment, means
of effecting the least practicable impact
on such species or stocks (i.e.,
mitigation), information that ensures no
unmitigable adverse impact on the
availability of the species or stock for
taking for subsistence use, and
requirements pertaining to the
monitoring and reporting of such taking.
The notice provided detail on all of
these points and, in NMFS view,
allowed the public to comment on the
proposed authorization and inform
NMFS’ final decision. Additionally, the
notice contained NMFS’ preliminary
findings of small numbers, negligible
impact, and no unmitigable adverse
impact.
NMFS’ implementing regulations at
50 CFR 216.108(d) state that an
independent peer review of a
monitoring plan is required if the
activity may affect the availability of a
species or stock of marine mammals for
taking for subsistence purposes. The
independent peer review of monitoring
plans for ITA applications is not
required for activities that occur outside
of Arctic waters or in Arctic waters if it
is determined that the activity will not
affect the availability of a species or
stock of marine mammals for taking for
subsistence purposes. The USGS
provided NMFS with a draft IHA
application in early March, 2010, which
included information on the timing and
location of its proposed seismic lines.
The USGS application stated that the
proposed survey will begin inside the
U.S. EEZ and then move further and
further offshore and eventually outside
the U.S. EEZ for the majority of the
survey. The lines inside U.S. waters
were approximately 96.6 km (60 mi)
from Barrow and will be surveyed for
five days, planned for mid-August. If
equipment or weather malfunctions
cause some delays, the USGS had
indicated to NMFS that they will be
outside of the U.S. EEZ by August 25,
which has been the typical shut-down
date in the Beaufort Sea so that villages
could begin to prepare for the fall
bowhead hunt. This whaling shut-down
date especially applies to activities
occurring near Kaktovik and Cross
Island. This survey will be occurring
west of those two communities’ hunts.
Based on this information, NMFS
preliminarily determined that the
proposed USGS seismic survey would
not affect the availability of bowhead
whales for taking for subsistence
purposes. Belugas are not hunted at this
time of the year in this particular part
of the Arctic. Additionally, while seal
hunting can occur year round in the
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Beaufort Sea, it most commonly occurs
from October until June (outside of the
time frame of the USGS’s activity).
Moreover, most seal hunting does not
occur this far offshore.
Therefore, since NMFS preliminarily
determined (based on the information
contained in the draft IHA application)
that the USGS’s activity would not
affect the availability of a species or
stock of marine mammals for taking for
subsistence purposes, NMFS
determined that their activity did not
trigger the requirement for independent
peer review of the monitoring plan. The
trigger for needing an independent peer
review of the monitoring plan is slightly
different than the ‘‘no unmitigable
adverse impact’’ determination that
NMFS must make prior to the issuance
of an IHA. If the AEWC or other
interested parties wish to have the
opportunity to make comments on the
monitoring proposed by the USGS for
its seismic survey, comments may be
provided to NMFS for consideration
during the 30-day public comment
period for the proposed IHA announced
in the Federal Register notice.
Comment 15: The Conflict Avoidance
Agreement (CAA) contains protective
measures that should have been applied
to USGS’s operations to ensure effective
communication between the ships and
AEWC whaling captains and to ensure
that those ships adhere to travel routes
through the Chukchi that AEWC
whaling captains have designated. The
AEWC is particularly concerned
because the Federal Register notice and
the IHA application make clear that the
USGS intends to transit the Healy
through the Bering Strait, across the
Chukchi Sea, and into the survey area
in the Beaufort Sea during the first week
of August, 2010. The NSB and AEWC
states that vessel transit across the
Chukchi, a major issue of concern for
their whaling community and a focus of
the Open Water Season CAA, was to
begin even earlier. The NSB and AEWC
also reiterates that NMFS should be
imposing the mitigation measures
developed in the CAA to ensure that
regulated activities do not have an
unmitigable adverse impact on
subsistence activities. In this case, the
USGS plans to transit the Chukchi Sea
in early August and the CAA speaks
directly to this issue, with those
provisions having been developed by
whaling captains and offshore operators
over several seasons. Neither USGS nor
NMFS discusses in the IHA application
or the Federal Register notice the
potential impacts resulting from vessel
transit or the protective measures
developed by the AEWC, which have
been approved by the local whaling
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captains. The AEWC asks for
clarification from NMFS as to whether
it views the USGS’s vessel transit as an
activity that potentially results in take of
marine mammals or adverse impacts to
subsistence activities. The AEWC is
concerned that NMFS failed to consider
at all the potential impacts of vessel
traffic to and from the survey area. A
simple and straightforward manner to
address these issues would be to adopt
the provisions of the CAA or simply
require the USGS the CAA as a basis for
making the statutorily required findings
of no unmitigable adverse impacts to
subsistence activities. The AEWC states
that it is extremely unfortunate that the
AEWC are only being given an
opportunity to comment on these
activities as they are already occurring
or have already occurred.
Response: USGS, in the comments
matrix of the EA, responded to the
overall concern about complying with
the CAA as follows ‘‘the CAA is
intended primarily for oil and gas
activities in the nearshore (see scope
statement, p. 4 of CAA, industry
funding of communication centers p. 14
of CAA, etc.).’’ To the extent the
proposed activity of this EA is to
conduct work greater than 100 km (62.1
mi) offshore, primarily for scientific
research, the CAA is not directly
applicable.
However, USGS is following the spirit
of the CAA through their Plan of
Cooperation. Through discussions with
the NSB and AEWC about conducting
the seismic lines within the U.S. EEZ,
i.e., the lines closest to the locations of
the potential migration pathway of the
bowhead whale and subsistence hunting
activities, USGS has agreed to conduct
these tracks at the beginning of the
survey (early to mid August) when it
should pose no interference or potential
to interfere with the Nuiqsut, Kaktovik,
or Barrow whaling seasons.
Part of the Plan of Cooperation is for
the Healy to also carry as part of the
science party an Alaska Native
community observer to ensure that
communications with the subsistence
community are maintained. Both the
Healy and St. Laurent will have PSOs as
part of the proposed strategy for
monitoring and mitigation.
With regards to the concern about the
Healy in the Chukchi Sea, the Healy was
on transit through the Chukchi Sea to
begin work in the Beaufort Sea. The
CAA requests that transiting vessels
‘‘should remain as far offshore as
weather and ice conditions allow and at
all times at least 8 km (5 mi) during
transit.’’ During transit, the Healy
remained more than 48.3 km (30 mi)
offshore during its transit through the
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Chukchi Sea. USGS also has hired a
member of the Alaska Native
community as an observer and
communicator aboard the Healy.
Therefore, although USGS has not
specifically mentioned the CAA in the
EA (and the CAA, which focuses on
industry activities, is not directly
relevant to the proposed USGS activity),
USGS is following the spirit of the
agreement. Location of the Healy’s
transit track through the Chukchi Sea, as
monitored by the sailwx.info
organization can be found online at:
https://www.sailwx.info/shiptrack/
shipposition.phtml?call=NEPP.
The signing of a CAA is not a
requirement to obtain an IHA. The CAA
is a document that is negotiated
between and signed by the industry
participant, AEWC, and the Village
Whaling Captains’ Associations. NMFS
has no role in the development or
execution of this agreement. Although
the contents of a CAA may inform
NMFS’ no unmitigable adverse impact
determination for bowhead and beluga
whales and ice seals, the signing of it is
not a requirement. Despite the lack of a
signed CAA for USGS activities, NMFS
is confident that USGS’s survey and the
measures contained in the IHA will
ensure no unmitigable adverse impact to
subsistence users.
Comment 16: The NSB and AEWC
reiterates earlier comments they have
made with respect to previous IHA
applications and proposed IHAs for this
open water season, namely that OPR
lacks an adequate scientific and legal
basis for issuing the proposed IHAs. As
an example, OPR continues to operate
under flawed monitoring and mitigation
measures that fail to provide adequate
protections against takes for Level A
harassment and do not adhere to the
best available science. And, OPR
similarly fails entirely to consider the
impacts of this project in the context of
all other oil and gas activities planned
for the Arctic Ocean. As opposed to
restating those comments, the NSB and
AEWC incorporates them by reference
and asks that NMFS give serious
consideration to the concerns set forth
in those earlier documents.
Response: NMFS has addressed the
NSB’s and AEWC’s comments
submitted regarding earlier proposed
IHAs for this open water season, see
NMFS’ responses in the Notice of
Issuance of IHAs for Shell Offshore, Inc.
(75 FR 49710) and Statoil USA E&P (75
FR 49760), published in the Federal
Register. NMFS believes that USGS’
monitoring and mitigation measures are
adequate (see Mitigation and Monitoring
and Reporting sections below), and
NMFS has determined that USGS’
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60185
activities will not result in Level A
harassment (injury) or mortality of
marine mammals, and no injury or
mortality is authorized under the IHA.
A number of public comments about
the accuracy of data were raised in the
EA and are addressed in the comment
matrix (p. 228 to 232). USGS’s final EA
and Finding of No Significant Impact
can be found online at: https://
pubs.usgs.gov/of/2010/1117/. Included
in the comment matrix are a response to
questions about associations between
seismic activity and to Level A
harassment, strandings and mortality.
USGS agrees that more data are
required, but ‘‘nearly all cases have
shown clear evidence of harm or cause
of death by something other than
underwater sounds.’’ The EA also
expanded the section on cumulative
impacts to address similar concerns
raised in comments on the draft EA.
Comment 17: The AEWC reiterates
how this proposed project demonstrates
the flawed nature of NMFS’ mitigation
measures as they relate to EZs. As plain
logic and the best available science tell
us, EZs are only as effective as the
people who monitor those areas for
marine mammals. NMFS has stated that
the PSO will not be on duty during
nighttime operations and yet seismic
operations will be allowed to continue
24 hours per day (75 FR 39369). USGS
survey crews will encounter as much as
8.5 hours of darkness per day during the
survey operations. During those times,
NMFS states that bridge personnel will
keep watch for marine mammals
‘‘insofar as practical.’’ This requirement
is meaningless, as anyone who has
spent time on the water will tell you
that no bridge personnel can identify
marine mammals at night in Arctic
conditions. It is absolutely unacceptable
for NMFS to simply look the other way
while vessels shoot seismic in the Arctic
without any monitoring at all to prevent
take by Level A harassment. Given the
fact that the proposed operations will
emit sounds well in excess of 190 dB
(rms), and the fact that USGS will be
operating without any observers for
much of the time, AEWC fails to see
how NMFS could possibly rule out the
potential for take by Level A
harassment. This determination simply
has no basis in science or law.
Response: It will be continuous
daylight during most of the survey,
which will accommodate 24 hour/day
monitoring by PSOs during most of the
survey. The IHA, which authorizes
Level B harassment, is only valid for the
St. Laurent and Healy’s activities
associated with seismic survey
operations within the EEZ of the U.S.
and the Healy’s icebreaking operations
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in international waters. The GSC has
written a Categorical Declaration stating
that ‘‘while in U.S. waters, the GSC
operators will comply with any and all
environmental mitigation measures
required by NMFS.’’ The two icebreakers
work cooperatively in U.S. waters for
only a small portion (approximately 5
days) of the seismic survey. NMFS has
determined that USGS’ activities will
not result in injury or mortality of
marine mammals, and no injury or
mortality is authorized under the IHA.
Comment 18: Because the AEWC is
responsible for protecting their bowhead
subsistence hunt, that is the cornerstone
of their subsistence livelihood and way
of life, they take very seriously the
changes and impacts the AEWC are
seeing in their waters and the need for
vigilant Federal regulatory oversight of
potential impacts. The AEWC hope that
NMFS and NOAA will take seriously
the lessons being learned at the
Department of the Interior regarding the
costs of lax regulatory oversight, in the
wake of the Deep Water Horizon
disaster. Similarly, the AEWC hopes
that these agencies will take seriously
the legal risk their communities face in
the context of an increasingly irrational
process at the International Whaling
Commission.
Response: USGS and NMFS
conducted a thorough analysis of the
potential impacts of this proposed
activity (with a focus on sound from
geophysical surveys and icebreaking) on
marine mammals; a cumulative impact
analysis was also done under NEPA.
Multiple studies and research have been
cited that support NMFS’ MMPA and
NEPA determinations that the localized
and short-term disturbance from seismic
surveys, with strict mitigation and
monitoring measures implemented, is
likely to result in negligible impacts to
marine mammals and no significant
impact to the human environment,
respectively. NMFS does not have any
direct role in issuing permits for
offshore drilling other than evaluating
impacts of leasing and other activities
under the MMPA and ESA. NOAA has
been in communication with the
BOEMRE regarding activities on the
outer continental shelf.
Comment 19: The AEWC states that
they are forced to write comments to
NMFS expressing their concerns about
impacts to their marine mammal species
from operations that are supposedly
regulated by NMFS that are already
occurring out in the water. Rather than
consult with the directly affected
communities, as it has agreed to do,
NMFS ignores the AEWC, allowing
applicants to commence operations
before reviewing their public comments
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submitted as part of the general public
process, before responding to their
comments, or even before the IHA has
been issued. AEWC states that this is no
more than a simple exercise in paper
shuffling without any substantive and
meaningful opportunity for input from
the local community.
Response: NMFS does not authorize
operations in Arctic waters; NMFS
authorizes the take of marine mammals
incidental to an otherwise legal specific
activity in a specified geographic area.
NMFS disagrees with the AEWC’s
statement regarding ignoring the review
of their public comments submitted as
part of the general public process. The
AEWC submitted comments on the
USGS IHA application and proposed
IHA to NMFS OPR via email after the
close of business on August 11, 2010
and were reviewed by NMFS OPR on
August 12, 2010. The public comment
period for the USGS proposed IHA
closed on August 9, 2010, and the IHA
was issued to USGS on August 11, 2010,
after reviewing and responding to
substantive comments from the
Commission and NSB. See other NMFS
responses to comments in this notice
regarding opportunities for substantive
and meaningful input from the local
community.
Comment 20: AEWC states that NMFS
is in plain violation of the MMPA by
failing to provide to the public a
‘‘proposed IHA.’’ Instead of providing a
draft of the authorization itself, NMFS
publishes a Federal Register notice that
describes the application and the basis
for the agency’s proposed statutory
findings. Because the IHA is the specific
authorization that governs the harassing
activities, it is imperative that the
AEWC be allowed input into the actual
draft authorization and not simply be
given a description of the mitigation
measures and proposed findings. In a
functional governmental system, NMFS
would publish a draft authorization and
take public comment on that document
well in advance so that AEWC whaling
captains could provide meaningful
input. In the alternative and in the event
of a timing issue, NMFS would consult
directly with AEWC under the NMFS/
NOAA–AEWC Cooperative Agreement.
Because the ships have already been
deployed, it would be impossible for
NMFS to consult with us or review the
AEWC comments and, for instance,
require USGS to implement more
rigorous monitoring protocols. That is
now impossible or impractical because
the ships have already left port. This is
but one example of NMFS disregard of
its regulatory responsibilities and its
utter lack of concern for the local
impacts it is charged with preventing.
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Response: The July 8, 2010, proposed
IHA notice (75 FR 39336) contained all
the relevant information needed by the
public to provide comments on the
proposed authorization itself. The
notice contained the permissible
methods of taking by harassment, means
of effecting the least practicable impact
on such species or stocks (i.e.,
mitigation), information that ensures no
unmitigable adverse impact on the
availability of the species or stock for
taking for subsistence use, and
requirements pertaining to the
monitoring and reporting of such taking.
The notice provided detail on all of
these points and, in NMFS view,
allowed the public to comment on the
proposed authorization and inform
NMFS’ final decision.
Also, for many years, NMFS has
conducted the Arctic Open Water
Meeting, which brings together the
Federal agencies, the oil and gas
industry, and affected Alaska Native
organizations to discuss the proposed
activities and monitoring plans. Local
knowledge is considered at these times,
and it is not too late for that knowledge
to serve a useful purpose. These
communities are also afforded the
opportunity to submit comments on the
application and proposed IHA notice,
which are then considered by NMFS
before making a final determination on
whether or not to issue an IHA.
NOAA and the AEWC co-manage
bowhead whales pursuant to a
cooperative agreement. This agreement
has allowed the AEWC to play a
significant role in the management of a
valuable resource by affording Alaska
Natives the opportunity to protect
bowhead whales and the Eskimo culture
and to promote scientific investigation,
among other purposes. NMFS works
closely with Alaska Natives when
considering whether to permit the take
of marine mammals incidental to
operations in the Arctic. NMFS has met
repeatedly over the years with Alaska
Native representatives to discuss
concerns related to NMFS’ MMPA
program in the Arctic, and has also
taken into account recommended
monitoring and mitigation measures to
reduce the impact of operations on
marine mammals and to ensure the
availability of marine mammals for
taking for subsistence uses. NMFS has
participated in Alaska Native
community meetings in the past and
will continue to do so.
Comment 21: The AEWC states that
NMFS has a long track record of
publishing its response to AEWC public
comments many weeks and months
after the IHA has been issued and after
the activities have commenced (and in
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many times concluded). This issue
again convinces us that the AEWC
comments are not given serious
consideration by the agency before its
decision has been made. If the agency
cannot articulate a rationale response to
public comments, it should not grant
the requested authorization. Moreover,
if activities are going to commence in
AEWC waters, potentially interfering
with subsistence activities or the
migration of the AEWC’s marine
mammals, the government owes us a
reasoned response to their concerns
before allowing the activities to proceed.
Again, as the AEWC writes their
comments, they know that the boats are
already in the water, the activities will
begin in a matter of days, and NMFS
will not bother to respond to the
AEWC’s concerns until well after the
harmful activities have taken place. This
is little more than an exercise in paper
shuffling with the agency already
having made up its mind or simply
turning a blind eye to activities that will
occur without coverage from a valid
IHA.
The AEWC states that NMFS’ public
process is fundamentally broken and
must be reformulated. NMFS should not
allow USGS to commence operations
until the AEWC has had the statutorily
required opportunity to comment on the
draft authorization and NMFS has
published responses to those comments.
Time and again, NMFS has requested
input from the AEWC and other
stakeholders into how the agency can
better respond to the AEWC’s concerns.
At bare minimum, the AEWC asks that
NMFS reformulate its public
participation process to provide
meaningful opportunities for the local
community. As it stands now, the
agency has given every indication that
it does not give serious consideration to
the AEWC’s concerns.
Response: NMFS does not agree with
AEWC’s statement that NMFS’ failure to
release its response to comments until
after an IHA has been issued or
activities have commenced casts doubt
on the validity of NMFS’ public
involvement process, or the underlying
analysis of impacts to subsistence
activities and marine mammals. All
substantive public comments received
during the 30 day comment period on
proposed IHAs are seriously considered
before NMFS’ decides whether to issue
IHAs. The decision to issue an IHA to
USGS for its proposed marine surveys
in the Arctic Ocean is based in large
part on NMFS’ definitions of ‘‘negligible
impact’’ and ‘‘unmitigable adverse
impact,’’ the proposed mitigation and
monitoring measures, the scope of
activities proposed to be conducted,
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including time of year, location, and
presence of marine mammals in the
project area, extensive research and
studies on potential impacts of
anthropogenic sounds to marine
mammals, marine mammal behavior,
distribution, and movements in the
vicinity of USGS’s proposed project
area, USGS’s Plan of Cooperation, and
on public comments received during the
commenting period. The reason that
NMFS was not able to publish its
response to comments on proposed IHA
activities for USGS’s until the end of the
survey activities was largely due to
travel and workload issues. NMFS will
continue to ensure that all public
comments are considered in full and
strive to publish responses at the time
IHAs or LOAs are issued.
Description of Marine Mammals in the
Activity Area
Regarding marine mammals, a total of
nine cetacean species, including four
odontocete species (dolphins, porpoises,
and small- and large-toothed whales),
five mysticete species (baleen whales),
and five pinniped species (seals, sea
lions, and walrus) and the polar bear are
known to occur in the area affected by
the specified activities associated with
the proposed Arctic Ocean marine
seismic survey (see Table 3 of USGS’s
application). Cetaceans and pinnipeds,
which are the subject of this IHA
application, are protected by the MMPA
and managed by NMFS in accordance
with its requirements. In the U.S., the
walrus and polar bear are managed
under the jurisdiction of the USFWS
and are not considered further in this
analysis. Information on the occurrence,
distribution, population size, and
conservation status for each of the 14
marine mammal species that may occur
in the proposed project area is presented
in the Table 4 of USGS’s application as
well as here in the table below (Table 4).
Several marine mammal species that
may be affected by the proposed IHA are
listed as Endangered or Threatened
under Section 4 of the ESA, including
the bowhead, fin and humpback whale,
and polar bear. The bowhead whale is
common in the Arctic, but unlikely in
the survey area. Based on a small
number of sightings in the Chukchi Sea,
the fin whale is unlikely to be
encountered along the planned trackline
in the Arctic Ocean. Humpback whales
are uncommon in the Chukchi Sea and
normally do not occur in the Beaufort
Sea. Several humpback sightings were
recorded during vessel-based surveys in
the Chukchi Sea in 2007 (three
sightings) and 2008 (one sighting; Haley
et al., 2009). The only known
occurrence of humpback whale in the
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Beaufort Sea was a single sighting of a
cow and calf reported and photographed
in 2007 (Green et al., 2007). Based on
the low number of sightings in the
Chukchi and Beaufort seas, humpback
whales would be unlikely to occur in
the vicinity of the proposed geophysical
activities.
The marine mammal species under
NMFS jurisdiction most likely to occur
in the seismic survey area include two
cetacean species (beluga and bowhead
whales), and two pinniped species
(ringed and bearded seals). These
species however, will likely occur in
low numbers and most sightings will
likely occur in locations within 100 km
(62 mi) of shore where no seismic work
is planned. The marine mammal most
likely to be encountered throughout the
cruise is the ringed seal.
Five additional cetacean species—
narwhal, killer whale, harbor porpoise,
gray whale, and minke whale—could
occur in the project area. Gray whales
occur regularly in continental shelf
waters along the Chukchi Sea coast in
summer and to a lesser extent along the
Beaufort Sea coast. Recent evidence
from monitoring activities in the
Chukchi and Beaufort seas during
industry seismic surveys suggests that
harbor porpoise and minke whales,
which have been considered uncommon
or rare in the Chukchi and Beaufort
seas, may be increasing in numbers in
these areas (Funk et al., 2009). Small
numbers of killer whales have also been
recorded during these industry surveys,
along with a few sightings of fin and
humpback whales. The narwhal occurs
in Canadian waters and occasionally in
the Beaufort Sea, but is rare there and
not expected to be encountered. Each of
these species is uncommon or rare in
the Chukchi and Beaufort seas, and
relatively few if any encounters with
these species are expected during the
seismic program.
Additional pinniped species that
could be encountered during the
proposed seismic survey include
spotted and ribbon seals, and Pacific
walrus. Spotted seals are more abundant
in the Chukchi Sea and occur in small
numbers in the Beaufort Sea. The ribbon
seal is uncommon in the Chukchi Sea
and there are few sightings in the
Beaufort Sea. The Pacific walrus is
common in the Chukchi Sea, but
uncommon in the Beaufort Sea and not
likely to occur in the deep waters of the
proposed survey area. None of these
species would likely be encountered
during the proposed cruise other than
perhaps transit periods to and from the
survey area.
Table 4 below outlines the marine
mammal species, their habitat and
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abundance in the proposed project area,
their conservation status, and density.
Additional information regarding the
distribution of these species expected to
be found in the project area and how the
estimated densities were calculated may
be found in USGS’s IHA application and
was included in the notice of the
proposed IHA (75 FR 39336, July 8,
2010).
TABLE 4—THE HABITAT, REGIONAL ABUNDANCE, CONSERVATION STATUS, AND BEST AND MAXIMUM DENSITY ESTIMATES
OF MARINE MAMMALS THAT COULD OCCUR IN OR NEAR THE SEISMIC SURVEY AREA IN THE ARCTIC OCEAN. See
TABLE 4 AND 5 IN USGS’S APPLICATION FOR FURTHER DETAIL
Species
Odontocetes:
Beluga whale
(Delphinapterus
leucas).
Narwhal (Monodon
monocerus).
Abundance/regional
population size
Habitat
ESA a
Best b density
(#/km2) open
water, ice margin, polar pack
MMPA o
Max c density (#/
km2) open water,
ice margin, polar
pack
0.0354
0.0354
0.0035
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0709
0.0709
0.0071
0.0001
0.0002
0.0001
0.0001
0.0001
0.0001
0.0000
0.0000
0.0001
0.0001
0.0001
0.0001
Offshore, coastal, ice
edges.
3,710 d ........................
39,257 e ......................
NL
NC ..............................
D—Cook Inlet .............
Offshore, ice edge ......
Rare f ..........................
NL
N.A. ............................
Killer whale
(Orcinus orca).
Widely distributed .......
Rare ............................
NL
Harbor porpoise
(Phocoena
phocoena).
Mysticetes:
Bowhead whale
(Balaena
mysticetus).
Eastern Pacific
gray whale
(Eschrichtius
robustus).
Minke whale
(Balaenoptera
acutorostrata).
Fin whale
(Balaenoptera
physalus).
Humpback whale
(Megaptera
novaeangliae).
Pinnipeds:
Bearded seal
(Erignathus
barbatus).
Spotted seal
(Phoca largha).
Coastal, inland waters,
shallow offshore waters.
Common (Chukchi) ....
Uncommon (Beaufort)
NL
NC ..............................
D—AT1 Transient
Population, Southern Resident Population.
NC ..............................
Pack ice and coastal ..
10,545 g ......................
EN
D .................................
N.A.
N.A.
Coastal, lagoons ........
488 h ...........................
17,500 i .......................
NL
NC ..............................
D—Western North Pacific Population.
0.0000
0.0000
0.0000
0.0001
0.0001
0.0001
Shelf, coastal ..............
Small numbers ...........
NL
NC ..............................
Slope, mostly pelagic
Rare (Chukchi) ...........
E
D .................................
Shelf, coastal ..............
Rare ............................
EN
D .................................
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0001
0.0001
0.0001
0.0001
0.0001
0.0001
0.0001
0.0001
0.0001
Pack ice, open water
300,000—450,000 j .....
C
NC ..............................
Pack ice, open water,
coastal haul-outs.
59,214 k ......................
P–T
NC ..............................
Landfast and pack ice,
open water.
18,000 l .......................
208,000–252,000 m ....
C
NC ..............................
Pack ice, open water
90,000–100,000 n .......
NL
NC ..............................
0.0096
0.0128
0.0013
0.0001
0.0001
0.0000
0.1883
0.2510
0.0251
N.A.
0.0384
0.0512
0.0051
0.0004
0.0004
0.0000
0.7530
1.0040
0.1004
N.A.
Ice, coastal .................
N.A. ............................
NL
S—Pacific ...................
N.A.
N.A.
Ice, coastal .................
N.A. ............................
T
S—Chukchi/Bearing
Sea.
N.A.
N.A.
Ringed seal
(Phoca hispida).
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Ribbon seal
(Histriophoca
fasciata).
Pacific walrus
(Odobenus
rosmarus
divergens).
Carnivores: Polar bear
(Ursus maritimus
marinus)
N.A.—Data not available or species status was not assessed.
a U.S. Endangered Species Act: EN = Endangered, T = Threatened, C = Candidate, P = Proposed, NL = Not listed.
b Best estimate as listed in Table 5 and Add-3 of the application.
c Maximum estimate as listed in Table 5 and Add-3 of the application.
d Eastern Chukchi Sea stock based on 1989 to 1991 surveys with a correction factor (Angliss and Allen, 2009)
e Beaufort Sea stock based on surveys in 1992 (Angliss and Allen, 2009)
f DFO (2004) states the population in Baffin Bay and the Canadian Arctic archipelago is approximately 60,000; very few of these enter the
Beaufort Sea.
g Abundance of bowhead whales surveyed near Barrow, as of 2001 (George et al., 2004). Revised to 10,545 by Zeh and Punt (2005).
h Southern Chukchi Sea and northern Bering Sea (Clarks and Moore, 2002)
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i Eastern
North Pacific gray whale population (Rugh et al., 2008)
on earlier estimates, no current population estimate available (Angliss and Allen, 2009)
stock based on aerial surveys in 1992 (Angliss and Allen, 2009)
l Beaufort Sea minimum estimate with no correction factor based on aerial surveys in 1996 to 1999 (Frost et al., 2002 in Angliss and Allen,
2009)
m Eastern Chukchi Sea population (Bengston et al., 2005)
n Bering Sea population (Burns, 1981a in Angliss and Allen, 2009)
o U.S. Marine Mammal Protection Act: NC = Not Classified, D = Depleted, S = Strategic.
j Based
k Alaska
Within the latitudes of the proposed
survey when the Healy will be breaking
ice outside of U.S. waters, no cetaceans
were observed by PSOs along
approximately 21,322 km (13,248.9 mi)
of effort during projects in 2005, 2006,
2008, and 2009 (Haley and Ireland,
2006; Haley, 2006; Jackson and
DesRoches, 2008; Mosher et al., 2009).
The estimated maximum amount of
icebreaking outside of U.S. waters for
this project, i.e., 3,372 line km (2,095.3
mi), is considerably less than the
combined trackline for the
aforementioned projects. At least one
PSO will stand watch at all times while
the Healy is breaking ice for the St.
Laurent. USGS does not expect that
PSOs will observe any cetaceans during
the proposed survey. Seals were
reported by PSOs during the 2005, 2006,
2008, and 2009 effort within the
latitudes of the proposed survey.
TABLE 5—NUMBER OF PINNIPEDS REPORTED DURING 2005, 2006, 2008, AND 2009 PROJECTS WITHIN THE LATITUDES
WHERE THE Healy WILL BE BREAKING ICE OUTSIDE OF U.S. WATERS FOR THE PROPOSED ARCTIC OCEAN SURVEY
(HALEY AND IRELAND, 2006; HALEY, 2006, GSC UNPUBLISHED DATA, 2008; MOSHER ET AL., 2009)
Number of
sightings
Pinniped species
Number of
individuals
Ringed seal ..............................................................................................................................................................
Bearded seal ............................................................................................................................................................
Unidentified seal ......................................................................................................................................................
116
24
128
125
26
140
Totals ................................................................................................................................................................
268
291
Potential Effects on Marine Mammals
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Potential Effects of Airgun Sounds
The effects of sounds from airguns
might result in one or more of the
following: tolerance, masking of natural
sounds, behavioral disturbances,
temporary or permanent hearing
impairment, or non-auditory physical or
physiological effects (Richardson et al.,
1995; Gordon et al., 2004; Nowacek et
al., 2007; Southall et al., 2007).
Permanent hearing impairment, in the
unlikely event that it occurred, would
constitute injury, but temporary
threshold shift (TTS) is not an injury
(Southall et al., 2007). Although the
possibility cannot be entirely excluded,
it is unlikely that the project would
result in any cases of temporary or
especially permanent hearing
impairment, or any significant nonauditory physical or physiological
effects. Some behavioral disturbance is
expected, but this would be localized
and short-term.
The notice of the proposed IHA (75
FR 39336, July 8, 2010) included a
discussion of the effects of sound from
airguns on mysticetes, odontocetes, and
pinnipeds, including tolerance,
masking, behavioral disturbance,
hearing impairment, and other nonauditory physical effects. Additional
information on the behavioral reactions
(or lack thereof) by all types of marine
mammals to seismic vessels can be
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found in USGS’s application and
associated EA.
The notice of the proposed IHA also
included a discussion of the potential
effects of the multi-beam echosounders
(MBES), sub-bottom profilers (SBP),
acoustic Doppler current profilers
(ADCP), and icebreaking activities.
Because of the shape of the beams of
these sources (i.e., MBES, SBP, and
ADCP), NMFS believes it unlikely that
marine mammals will be exposed to
sound levels at or above those likely to
cause Level B harassment.
Estimated Take of Marine Mammals by
Incidental Harassment
The notice of the proposed IHA (75
FR 39336, July 8, 2010) included an indepth discussion of the methods used to
calculate the densities of the marine
mammals in the area of the seismic
survey and the take estimates.
Additional information was included in
USGS’s application. A summary is
included here.
All anticipated takes would be ‘‘takes
by Level B harassment,’’ involving
temporary changes in behavior. The
proposed monitoring and mitigation
measures are expected to minimize the
possibility of injurious takes or
mortality. However, as noted earlier,
there is no specific information
demonstrating that injurious ‘‘takes’’ or
mortality would occur even in the
absence of the planned monitoring and
mitigation measures. NMFS believes,
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therefore, that injurious take or
mortality to the affected species marine
mammals is extremely unlikely to occur
as a result of the specified activities
within the specified geographic area for
which USGS seeks the IHA. The
sections below describe methods to
estimate ‘‘take by harassment,’’ and
present estimates of the numbers of
marine mammals that could be affected
during the seismic study in the Arctic
Ocean. The estimates of ‘‘take by
harassment’’ are based on data obtained
during marine mammal surveys in and
near the Arctic Ocean by Stirling et al.
(1982), Kingsley (1986), Moore et al.
(2000b), Haley and Ireland (2006), Haley
(2006), GSC unpublished data (2008),
and Mosher et al. (2009), Bowhead
Whale Aerial Survey Program (BWASP),
and on estimates of the sizes of the areas
where effects could potentially occur. In
some cases these estimates were made
from data collected from regions and
habitats that differed from the proposed
project area.
Detectability bias, quantified in part
by ƒ(0), is associated with diminishing
sightability with increasing lateral
distance from the trackline. Availability
bias (g[0]) refers to the fact that there is
less than 100 percent probability of
sighting an animal that is present along
the survey trackline. Some sources of
densities used below included these
correction factors in their reported
densities. In other cases the best
densities used below included these
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correction factors in their reported
densities. In other cases the best
available correction factors were applied
to reported results when they had not
been included in the reported data
(Moore et al., 2000b). Adjustments to
reported population or density estimates
were made on a case by case basis to
take into account differences between
the source data and the general
information on the distribution and
abundance of the species in the
proposed project area.
Although several systematic surveys
of marine mammals have been
conducted in the southern Beaufort Sea,
few data (systematic or otherwise) are
available on the distribution and
numbers of marine mammals in the
northern Beaufort Sea or offshore water
of the Arctic Ocean. The main sources
of distributional and numerical data
used in deriving the estimates are
described in the next subsection. Both
‘‘maximum estimates’’ as well as ‘‘best
estimates’’ of marine mammal densities
(see Table 5 of the IHA application) and
the numbers of marine mammals
potentially exposed to underwater
sound (see Table 6 of the IHA
application) were calculated as
described below. The best (or average)
estimate is based on available
distribution and abundance data and
represents the most likely number of
animals that may be encountered during
the survey, assuming no avoidance of
the airguns or vessel. The maximum
estimate is either the highest estimate
from applicable distribution and
abundance data or the average estimate
increased by a multiplier intended to
produce a very conservative (over)
estimate of the number of animals that
may be present in the survey area. There
is some uncertainty about how
representative the available data are and
the assumptions used below to estimate
the potential ‘‘take by harassment.’’
However, the approach used here is
accepted by NMFS as the best available
at this time.
USGS has calculated exposures to
marine mammals within U.S. waters
only. After the St. Laurent (a Canadian
icebreaker) exits U.S. waters, their
activities no longer fall under the
jurisdiction of the U.S. or the MMPA.
The following estimates are based on
a consideration of the number of marine
mammals that might be disturbed
appreciably over the approximately 806
line km (501 mi) of seismic surveys
within U.S. waters across the Arctic
Ocean. An assumed total of 1,007.5 km
(626 mi) of trackline includes a 25
percent allowance over and above the
planned approximately 806 km to allow
for turns, lines that might have to be
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repeated because of poor data quality, or
for minor changes to the survey design.
The anticipated radii of influence of
the lower energy sound sources
including Chirp echosounder (on the St.
Laurent) and bathymetric echosounder
(on the Healy) are less than that for the
airgun configuration. It is assumed that
during simultaneous operation of the
airgun array and echosounder, any
marine mammals close enough to be
affected by the MBES, SBP, and ADCP
would already be affected by the
airguns. However, whether or not the
airguns are operating simultaneously
with the other sound sources, marine
mammals are expected to exhibit no
more than short-term and
inconsequential responses to the MBES,
SBP, and ADCP sounder given its
characteristics (e.g., narrow downwarddirected beam) and other considerations
described in the IHA application.
Similar responses are expected from
marine mammals exposed to the Healy’s
bathymetric profiler. Such reactions are
not considered to constitute ‘‘taking’’ as
defined by NMFS (NMFS, 2001).
Therefore, no additional allowance is
included for animals that might be
exposed to sound sources other than the
airguns and icebreaking.
Marine Mammal Density Estimates
Numbers of marine mammals that
might be present and potentially
disturbed are estimated based on
available data about marine mammal
distribution and densities in the Arctic
Ocean study area during the summer.
‘‘Take by harassment’’ is calculated by
multiplying expected densities of
marine mammals likely to occur in the
survey area by the area of water
potentially ensonified to sound levels
≥160 dB re 1 μPa (rms) for the airgun
operations and ≥120 dB re 1 μPa (rms)
for icebreaking activities. Estimates for
icebreaking are based on a consideration
of the number of marine mammals that
might be disturbed appreciably over the
approximately 3,102 to 3,372 line km
(1,927.5 to 2,095.3 mi) of icebreaking
that may occur during the proposed
project. This section provides
descriptions of the estimated densities
of marine mammals that may occur in
the proposed survey area. The area of
water that may be ensonified to the
indicated sound level is described
further below. There is no evidence that
avoidance at received sound levels ≥160
dB would have significant effects on
individual animals or that the subtle
changes in behavior or movements
would rise to the level of taking
according to guidance by NMFS (NMFS,
2001).
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Some surveys of marine mammals
have been conducted near the southern
end of the proposed project area, but
few data are available on the species
and abundance of marine mammals in
the northern Beaufort Sea and the Arctic
Ocean. No published densities of
marine mammals are available for the
region of the proposed survey
(including between 74° and 84° North
where the Healy will be breaking ice
outside U.S. waters), although vesselbased surveys through the general area
in 2005, 2006, 2008, and 2009
encountered few marine mammals. A
total of two polar bears, 36 seals, and a
single beluga whale sighting(s) were
recorded along approximately 2,299 km
(1,429 mi) of monitored trackline
between 71° North and 74° North (Haley
and Ireland, 2006; Haley, 2006; GSC
unpublished data, 2008; Mosher et al.,
2009). PSOs recorded 268 sightings of
291 individual seals along
approximately 21,322 km (13,248.9 mi)
of monitored trackline between 74° and
84° North (Haley and Ireland, 2006;
Haley, 2006; GSC unpublished data,
2008; Mosher et al., 2009). No cetaceans
were observed during the surveys
between 74° and 84° North. Given the
few sightings of marine mammals along
the 21,322 km (13,248.9 mi) vessel
trackline in previous years, USGS
estimate that the densities of marine
mammals encountered while breaking
ice will be 1/10 of the estimated
densities of marine mammals
encountered within the ice margin
habitat described in the original
application.
Given that the survey lines within
U.S. waters extend from latitudes 71° to
74° North, it is likely that seismic
operations will be conducted in both
open-water and sea-ice conditions.
Because densities of marine mammals
often differ between open-water and
pack-ice areas, the likely extent of the
pack-ice at the time of the survey was
estimated. Images of average monthly
sea ice concentration for August from
2005 through 2009, available from the
National Snow and Ice Data Center
(NSIDC), were used to identify 74°
North latitude as a reasonable ice-edge
boundary applicable to the proposed
study period and location. Based on
these satellite data, the majority of the
survey in U.S. waters will be conducted
in open water and unconsolidated pack
ice, in the southern latitudes of the
survey area. This region will include the
ice margin where the highest densities
of cetaceans and pinnipeds are likely to
be encountered. The proposed survey
lines within U.S. waters reach
approximately 74.10° North, extending
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within the estimated ice-edge boundary
for August, 2010 by approximately 19
km (10 nmi). This comprises less than
3 percent of the total trackline within
U.S. waters. USGS has divided the
survey effort between the two habitat
zones of open water and ice margin
based on the 2005 to 2009 NSIDC
satellite data described above and the
planed location of the tracklines. NSIDC
data from 2005 to 2009 suggests little ice
will be present south of 74° North,
although data from the 2009 cruise
(Mosher et al., 2009) shows that interannual variability could result in a
greater amount of ice being encountered
than expected. As a conservative
measure, USGS estimated that, within
U.S. waters, 80 percent of the survey
tracklines will occur in open water and
20 percent of the tracklines will occur
within the ice margin.
The NSIDC (2009) reported that more
Arctic sea ice cover in 2009 remained
after the summer than in the recordsetting low years of 2007 and 2008.
USGS expects that sea ice density and
extent in 2010 will be closer to the
density and extent of sea ice in 2009
rather than the record-setting low years
of 2007 and 2008. All animals observed
during the 2009 survey (Mosher et al.,
2009) were north of the proposed
seismic survey area, i.e., north of 74°
North.
Cetaceans—Average and maximum
densities for each cetacean species or
species group reported to occur in U.S.
waters of the Arctic Ocean, within the
study area, are presented in Table 5 of
the IHA application. Densities were
calculated based on the sightings and
effort data from available survey reports.
No cetaceans were observed during
surveys near the proposed study area in
August/September, 2005 (Haley and
Ireland, 2006), August, 2006 (Haley,
2006), August/September, 2008 (GSC
unpublished data, 2008) or August/
September, 2009 (Mosher et al., 2009).
Seasonal (summer and fall)
differences in cetacean densities along
the north coast of Alaska have been
documented by Moore et al. (2000b).
The proposed survey will be conducted
in U.S. waters from approximately
August 6 to 12, 2010, and is considered
to occur during the summer season.
The summer beluga density (see Table
5 of the IHA application) was based on
41 sightings along 9,022 km (5,606 mi)
of on-transect effort that occurred over
water greater than 2,000 m (6,561.7 ft)
during the summer in the Beaufort Sea
(Moore et al., 2000b; see Table 2 of the
IHA application). A mean group size of
2.8 derived from BWASP data of August
beluga sightings in the Beaufort Sea in
water depths greater than 2,000 m was
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used in the density calculation. A ƒ(0)
value of 2.326 from Innes et al. (1996)
and a g(0) value of 0.419 from Innes et
al. (1996) and Harwood et al. (1996)
were also used in the density
computation. The CV associated with
group size was used to select an
inflation factor of 2 to estimate the
maximum density that may occur in the
proposed study area within U.S. waters.
Most Moore et al. (2000b) sightings were
south of the proposed seismic survey.
However, Moore et al. (2000b) found
that beluga whales were associated with
both light (1 to 10 percent) and heavy
(70 to 100 percent) ice cover. Five of 23
beluga whales that Suydam et al. (2005)
tagged in Kaseglauk Lagoon (northeast
Chukchi Sea) traveled to 79 to 80° North
into the pack ice and within the region
of the proposed survey. These and other
tagged whales moved into areas as far as
1,100 km (594 nmi) offshore between
Barrow and the Mackenzie River delta,
spending time in water with 90 percent
ice coverage. Therefore, we applied the
observed density calculated from the
Moore et al. (2000b) sightings as the
average density for both ‘‘open water’’
and ‘‘ice margin’’ habitats. Because no
beluga whales were sighted during
surveys in the proposed survey area
(Harwood et al., 2005; Haley and
Ireland, 2006; Haley, 2006; GSC
unpublished data, 2008; and Mosher et
al., 2009) the densities in Table 5 of the
IHA application are probably higher
than densities likely to be encountered.
By the time the survey begins in early
August, most bowhead whales have
typically traveled east of the proposed
project area to summer in the eastern
Beaufort Sea and Amundsen Gulf.
Industry aerial surveys of the
continental shelf near Camden Bay in
2008 recorded eastward migrating
bowhead whales until July 12 (Lyons
and Christie, 2009). No bowhead
sightings were recorded again despite
continued flights until August 19, 2010.
A summer bowhead whale density was
derived from 9,022 km (5,606 mi) of
summer (July/August) aerial survey
effort reported by Moore et al. (2000b)
in the Alaska Beaufort Sea during which
six sightings of bowhead whales were
documented in water greater than 2,000
m (6,561.7 ft). A mean group size of
bowhead whale sightings in September,
in waters greater than 2,000 m deep,
was calculated to be 1.14 (CV = 0.4)
from BWASP data. A ƒ(0) value of 2.33
and g(0) value of 0.073, both from
Thomas et al. (2002) were used to
estimate a summer density for bowhead
whales of 0.0122 whales/km2. This
density falls within the range of
densities, i.e., 0.0099 to 0.0717 whales/
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km2, reported by Lyons and Christie
(2009) based on data from three July,
2008 surveys.
Treacy et al. (2006) reported that in
years of heavy ice conditions, bowhead
whales occur farther offshore than in
years of light to moderate ice. NSIDC
(2009) reported that September, 2009
had the third lowest sea ice extent since
the start of their satellite records in
1979. The extent of sea ice at the end
of the 2009 Arctic summer, however,
was greater than in 2007 or 2008. USGS
does not expect 2010 to be a heavy ice
year during which bowhead whales
might occur farther offshore in the area
of the proposed survey. During the
lowest ice-cover year on record (2007),
BWASP reported no bowhead whale
sightings in the greater than 2,000 m
depth waters far offshore. Because few
bowhead whales have been documented
in the deep offshore waters of the
proposed survey area, half of the
bowhead whale density estimate from
size and standard error reported in
Thomas et al. (2002) for ƒ(0) and g(0)
correction factors suggest that an
inflation factor of two is appropriate for
estimating the maximum density from
the average density. NSIDC did not
forecast that 2010 would be a heavy ice
year and USGS anticipates that
bowheads will remain relatively close to
shore, and in areas of light ice coverage.
Therefore, USGS has applied the same
density for bowheads to the open-water
and ice-margin categories. Bowhead
whales were not sighted during recent
surveys in the Arctic Ocean (Haley and
Ireland, 2006; Haley, 2006; GSC
unpublished data, 2008; Mosher et al.,
2009), suggesting that the bowhead
whale densities shown in Table 5 are
likely higher than actual densities in the
survey area.
For other cetacean species that may be
encountered in the Beaufort Sea,
densities are likely to be very low in the
summer when the survey is scheduled.
Fin and humpback whales are unlikely
to occur in the Beaufort Sea. No gray
whales were observed in the Beaufort
Sea by Moore et al. (2000b) during
summer aerial surveys in water greater
than 2,000 m. Gray whales were not
recorded in water greater than 2,000 m
by the BWASP during August in 29
years of survey operation. Harbor
porpoises are not expected to be present
in large numbers in the Beaufort Sea
during the fall although small numbers
may be encountered during the summer.
Neither gray whales nor harbor
porpoises are likely to occur in the faroffshore waters of the proposed survey
area (Table 5 of the IHA application).
Narwhals are not expected to be
encountered within the survey area
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although a few individuals could be
present if ice is nearby. Because these
species occur so infrequently in the
Beaufort Sea, little to no data are
available for the calculation of densities.
Minimal cetacean densities have
therefore been assigned to these three
species for calculation purposes and to
allow for chance encounters (see Table
5 of the IHA application). Those
densities include ‘‘0’’ for the average and
0.0001 individuals/km2 for the
maximum.
Pinnipeds—Extensive surveys of
ringed and bearded seals have been
conducted in the Beaufort Sea, but most
surveys were conducted over the
landfast ice during aerial surveys, and
few seal surveys have occurred in open
water or in the pack ice. Kingsley (1986)
conducted ringed seal surveys of the
offshore pack ice in the central and
eastern Beaufort Sea during the late
spring (late June). These surveys
provide the most relevant information
on densities of ringed seals in the ice
margin zone of the Beaufort Sea. The
density estimate in Kingsley (1986) was
used as the average density of ringed
seals that may be encountered in the
ice-margin area of the proposed survey
(see Table 5 of the IHA application). The
average density was multiplied by four
to estimate maximum density, as was
done for all seal species likely to occur
within the survey area. Ringed seals are
closely associated with sea ice therefore
the ice-margin densities were multiplied
by a factor of 0.75 to estimate a summer
open-water ringed-seal density for
locations with water depth greater than
2,000 m (6,561.7 ft).
Densities of bearded seals were
estimated by multiplying the ringed seal
densities by 0.051 based on the
proportion of bearded seals to ringed
seals reported in Stirling et al., (1982;
see Table 6–3 of IHA application).
Because bearded seals are associated
with the pack ice edge and shallow
water, their estimated summer icemargin density was also multiplied by
a factor of 0.75 for the open-water
density estimate. Minimal values were
used to estimate spotted seal densities
because they are uncommon offshore in
the Beaufort Sea and are not likely to be
encountered.
Numbers of marine mammals that
might be present and potentially
disturbed are estimated below based on
available data about marine mammal
distribution and densities in the three
different habitats during the summer as
described in Table 5 of the IHA
application.
The number of individuals of each
species potentially exposed to received
levels greater than or equal to 160 dB re
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1 μPa (rms) (for seismic airgun
operations) or 120 dB re 1 μPa (rms) (for
icebreaking) was estimated by
multiplying:
• The anticipated area to be
ensonified to the specified sound level
in both open water, the ice margin, and
polar pack by
• The expected species density.
Some of the animals estimated to be
exposed to sound levels greater than or
equal to 160 dB re 1 μPa (rms) or 120
dB re 1 μPa (rms), particularly migrating
bowhead whales, might show avoidance
reactions before actual exposure to this
sound level (see Appendix D of the IHA
application). Thus, these calculations
actually estimate the number of
individuals potentially exposed to
greater than or equal to 160 dB (rms) or
120 dB re 1 μPa (rms) that would occur
if there were no avoidance of the area
ensonified to that level.
Estimated Area Exposed to ≥160 dB
(rms)
The area of water potentially exposed
to received levels greater than or equal
to 160 dB by the proposed operations
was calculated by multiplying the
planned trackline distance within U.S.
waters by the cross-track distance of the
sound propagation. The airgun array of
two 500 in3 and one 150 in3 G-airguns
that will be used for the proposed 2010
survey within U.S. waters was measured
during a 2009 project in the Arctic
Ocean. The propagation experiment
took place at 74°50.4′ North; 156°34.31′
West, in 3,863 m (12,674 ft) of water.
The location was near the northern end
of the two proposed survey lines in U.S.
waters. USGS expects the sound
propagation by the airgun array in the
planned 2010 survey will be the same
as that measured in 2009, because of the
similar water depths and relative
locations of the test site and proposed
survey area. The greater than or equal to
160 dB (rms) sound level radius was
estimated to be approximately 2,500 m
(8,202.1 ft) based on modeling of the 0
to peak energy of the airgun array (Roth
and Schmidt, 2010). The 0 to peak
values were corrected to rms by
subtracting 10 dB.
Closely spaced survey lines and large
cross-track distances of the greater than
or equal to 160 dB radii can result in
repeated exposure of the same area of
water. Excessive amounts of repeated
exposure can lead to overestimation of
the number of animals potentially
exposed through double counting. The
trackline for the proposed USGS survey
in U.S. waters, however, covers a large
geographic area without adjacent
tracklines and the potential for multiple
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or repeated exposure is unlikely to be a
concern.
The USGS 2010 geophysical survey is
planned to occur approximately 108 km
(67.1 mi) offshore, along approximately
806 km (501 mi) of survey lines in U.S.
waters, during the first half of August
exposing a total of approximately 4,109
km2 (1,586.5 mi2) of water to sound
levels of greater than or equal to 160 dB
(rms). USGS included an additional 25
percent allowance over and above the
planned tracklines within U.S. waters to
allow for turns, lines that might have to
be repeated because of poor data
quality, or for minor changes to the
survey design. The resulting estimate of
5,136.5 km2 (1,983.2 mi2) was used to
estimate the numbers of marine
mammals exposed to underwater sound
levels greater than or equal to 160 dB
(rms).
Based on the operational plans and
marine mammal densities described in
Table 5 of the IHA application, the
estimates of marine mammals
potentially exposed to sounds greater
than or equal to 160 dB (rms) in the
proposed survey area within U.S. waters
are presented in Table 6 of the IHA
application. For the common species,
the requested numbers are calculated as
described above and based on the
average densities from the data reported
in the different studies mentioned
above. For less common species,
estimates were set to minimal values to
allow for chance encounters. Discussion
of the number of potential exposures is
summarized by species in the following
subsections.
Cetaceans—Based on density
estimates and area ensonified, one
endangered cetacean species (bowhead
whale) is expected by USGS to be
exposed to received levels greater than
or equal to 160 dB, unless bowheads
avoid the survey vessel before the
received levels reach 160 dB. Migrating
bowheads are likely to do so, though
many of the bowheads engaged in other
activities, particularly feeding and
socializing may not. The USGS
estimated the number of bowhead
whales potentially exposed to sound
levels ≥160 dB (rms) in the portion of
the survey area in U.S. waters to be
between 31 and 63 (see Table 6 of the
IHA application). NMFS subsequently
did an analysis and found that bowhead
whales are unlikely to be exposed to
sound levels ≥160 dB (rms). Although
take was calculated based on density
estimates in the proposed action area,
the proposed seismic survey will be
conducted during the fall migration for
bowhead whales, but at locations
starting at greater than 185.2 km (100
nmi) offshore, well north of the known
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bowhead migration corridor and well
beyond distances (20 to 30 km [12.4 to
18.6], Miller et al., 1999; Richardson et
al., 1999) known to potentially affect
this species. Other endangered cetacean
species that may be encountered in the
area are fin and humpback whales; both
are unlikely to be exposed given their
minimal density in the area.
The only other cetacean species likely
to occur in the proposed survey area is
the beluga whale. Average (best) and
maximum estimates of the number of
exposures of belugas to sound levels
greater than or equal to 160 dB (rms) are
182 and 364, respectively. Estimates for
other cetacean species are minimal (see
Table 6 of the IHA application).
Pinnipeds—The ringed seal is the
most widespread and abundant
pinniped in ice-covered arctic waters,
and there is a great deal of annual
variation in abundance and distribution
of these marine mammals. Ringed seals
account for the vast majority of marine
mammals expected to be encountered,
and hence exposed to airgun sounds
with received levels greater than or
equal to 160 dB (rms) during the
proposed marine seismic survey. The
average (best and maximum number of
exposures of ringed seals to sound
levels greater than or equal to 160 dB
(rms) were estimated to be 1,031 and
4,126, respectively.
Two additional pinniped species
(other than the Pacific walrus) are likely
to occur in the proposed project area.
The average and maximum numbers of
exposures of bearded seals to sound
levels greater than or equal to 160 dB
(rms) were estimated to be 53 and 210,
respectively. The ribbon seal is unlikely
to be encountered in the survey area,
but a chance encounter could occur.
Estimated Area Exposed to ≥120 dB
(rms)
The area potentially exposed to
received levels greater than or equal to
120 dB (rms) due to icebreaking
operations was estimated by
multiplying the anticipated trackline
distance breaking ice by the estimated
cross-track distance to received levels of
120 dB caused by icebreaking.
In 2008, acousticians from Scripps
Institution of Oceanography Marine
Physical Laboratory and University of
New Hampshire Center for Coastal and
Ocean Mapping conducted
measurements of SPLs of Healy
icebreaking under various conditions
(Roth and Schmidt, 2010). The results
indicated that the highest mean SPL
(185 dB [rms]) was measured at survey
speeds of 4 to 4.5 knots in conditions of
5⁄10 ice and greater. Mean SPL under
conditions where the ship was breaking
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heavy ice by backing and ramming was
actually lower (180 dB). In addition,
when backing and ramming, the vessel
is essentially stationary, so the
ensonified area is limited for a short
period (on the order of minutes to tens
of minutes) to the immediate vicinity of
the boat until the ship breaks free and
once again makes headway.
Although the report by Roth and
Schmidt has not yet been reviewed
externally nor peer-reviewed for
publication, the SPL results reported are
consistent with previous studies
(Thiele, 1981, 1988; LGL and
Greenridge, 1986; Richardson et al.,
1995).
The existing threshold for Level B
harassment for continuous sounds is a
received sound level of 120 dB SPL.
Using a spherical spreading model, a
source level of 185 dB decays to 120 dB
in about 1,750 m (5,741.5 ft). This
model is corroborated by Roth and
Schmidt (2010). Therefore, as the ship
travels through the ice, a swath 3,500 m
(11,483 ft) wide would be subjected to
sound levels greater than or equal to 120
dB (rms). This results in the potential
exposure of 11,802 km2 (4,557.8 mi2) to
sounds greater than or equal to 120 dB
(rms) from icebreaking.
Based on the operational plans and
marine mammal densities described
above, the estimates of marine mammals
exposed to sounds greater than or equal
to 120 dB (rms) during the maximum
estimation of icebreaking outside of U.S.
waters (3,372 km [2,095.3 mi]) are
presented in Table Add-4 of the IHA
application. For the common marine
mammal species, the requested numbers
are calculated as described above and
based on the average densities from the
data reported in the different studies
mentioned above. For less common
species, estimates were set to minimal
values to allow for chance encounters.
Based on models, bowhead whales
likely would respond to the sound of
the icebreakers at distances of 2 to 25
km (1.2 to 15.5 mi) from the icebreakers
(Miles et al., 1987). This study predicts
that roughly half of the bowhead whales
show avoidance responses to an
icebreaker underway in open water at a
range of 2 to 12 km (1.3 to 7.5 mi) when
the sound-to-noise ratio is 30 dB (rms).
The study also predicts that roughly half
of the bowhead whales would show
avoidance response to an icebreaker
pushing ice at a range of 4.6 to 6.2 km
(2.9 to 12.4 mi) when the sound-to-noise
ratio is 30 dB.
Richardson et al. (1995b) found that
bowheads migrating in the nearshore
lead during the spring migration often
tolerated exposure to playbacks of
recorded icebreaker sounds at received
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60193
levels up to 20 dB or more above the
natural ambient noise levels at
corresponding frequencies. The source
level of an actual icebreaker is much
higher than that of the projectors
(projecting the recorded sound) used in
this study (median difference 34 dB
over the frequency range 40 Hz to 6.3
kHz). Over the two-season period (1991
and 1994) when icebreaker playbacks
were attempted, an estimated 93
bowheads (80 groups) were seen near
the ice camp when the projectors were
transmitting icebreaker sounds into the
water, and approximately 158 bowheads
(116 groups) were seen near there
during quiet periods. Some bowheads
diverted from their course when
exposed to levels of projected icebreaker
sound greater than 20 dB above the
natural ambient noise level in the 1⁄3
octave band of the strongest icebreaker
noise. However, not all bowheads
diverted at that sound-to-noise ratio,
and a minority of whales apparently
diverted at a lower sound-to-noise ratio.
The study concluded that exposure to a
single playback of variable icebreaker
sounds can cause statistically, but
probably not biologically significant
effects on movements and behavior of
migrating whales in the lead system
during the spring migration east of Point
Barrow, Alaska. The study indicated the
predicted response distances for
bowheads around an actual icebreaker
would be highly variable; however, for
typical traveling bowheads, detectable
effects on movements and behavior are
predicted to extend commonly out to
radii of 10 to 30 km (6.2 to 18.6 mi).
Predicting the distance a whale would
respond to an icebreaker like the Healy
is difficult because of propagation
conditions and because ambient noise
varies with time and with location.
However, because the closest survey
activities and icebreaking are
approximately 116 km (72.1 mi) away
and are of limited duration (5 days), and
the next closest survey activities are 397
km (246.7 mi) away to the north and
west in the Arctic ocean, NMFS does
not anticipate that icebreaking activities
would have biologically significant
effects on the movements and behavior
of bowhead whales.
Table 6 (see below) outlines the
species, estimated stock population
(minimum and best), and estimated
percentage of the regional population or
stock exposed to seismic pulses and
icebreaking activities in the project area.
Additional information regarding the
status, abundance, and distribution of
the marine mammals in the action area
and how densities were calculated was
included in Table 4 (see above), the
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notice of the proposed IHA (75 FR
39337, July 8, 2010) and may be found
in USGS’s application.
TABLE 6—THE ESTIMATES OF THE POSSIBLE NUMBERS OF MARINE MAMMALS EXPOSED TO SOUND LEVELS GREATER
THAN OR EQUAL TO 120 DB (RMS) (FOR ICEBREAKING) OR 160 DB (RMS) (FOR SEISMIC AIRGUN OPERATIONS) DURING USGS’S PROPOSED SEISMIC SURVEY IN U.S. WATERS IN THE NORTHERN BEAUFORT SEA AND ARCTIC OCEAN,
IN AUGUST 2010. RECEIVED LEVELS ARE EXPRESSED IN DB RE 1 μPA (RMS) (AVERAGED OVER PULSE DURATION),
CONSISTENT WITH NMFS’ PRACTICE. NOT ALL MARINE MAMMALS WILL CHANGE THEIR BEHAVIOR WHEN EXPOSED
TO THESE SOUND LEVELS, BUT SOME MAY ALTER THEIR BEHAVIOR WHEN LEVELS ARE LOWER (SEE TEXT). SEE
TABLES 4 TO 5 AND ADD-3 AND ADD-4 IN USGS’S APPLICATION FOR FURTHER DETAIL.
# of individuals exposed
(best) 1
open water,
ice margin,
polar pack
Species
# of individuals exposed
(max) 2
open water,
ice margin,
polar pack
146
36
42
0
0
0
0
0
0
0
0
0
Odontocetes:
Beluga whale (Delphinapterus leucas) .....................................................................
Narwhal (Monodon monocerus) ...............................................................................
Killer whale (Orcinus orca) .......................................................................................
Harbor porpoise (Phocoena phocoena) ...................................................................
Mysticetes:
Bowhead whale (Balaena mysticetus) .....................................................................
Eastern Pacific gray whale (Eschrichtius robustus) .................................................
Minke whale (Balaenoptera acutorostrata) ..............................................................
Fin whale (Balaenoptera physalus) ..........................................................................
Humpback whale (Megaptera novaeangliae) ...........................................................
Pinnipeds:
Bearded seal (Erignathus barbatus) ........................................................................
Spotted seal (Phoca largha) .....................................................................................
Ringed seal (Phoca hispida) ....................................................................................
Ribbon seal (Histriophoca fasciata) .........................................................................
Pacific walrus (Odobenus rosmarus divergens) ......................................................
Carnivores:
Polar bear (Ursus maritimus marinus) .....................................................................
Total
(best)
Approx.
percent of
regional
population
(best) 2
291
73
84
1
1
1
0
0
1
0
0
1
224
....................
....................
0
....................
....................
0
....................
....................
0
....................
....................
0.57
....................
....................
0
....................
....................
0
....................
....................
0
....................
....................
N.A.
0
0
0
0
0
0
0
0
0
0
0
0
N.A.
0
0
1
0
0
1
0
0
1
0
0
0
N.A.
0
....................
....................
0
....................
....................
0
....................
....................
0
....................
....................
N.A.
0
....................
....................
0
....................
....................
0
....................
....................
0
....................
....................
39
13
15
0
0
0
774
258
296
N.A.
N.A.
158
53
60
2
0
0
3,094
1,031
1,185
N.A.
N.A.
67
....................
....................
0
....................
....................
1,328
....................
....................
N.A.
N.A.
0.02
....................
....................
0
....................
....................
7.38
....................
....................
N.A.
N.A.
N.A.
N.A.
N.A.
N.A.
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N.A.—Data not available or species status was not assessed.
1 Best estimate and maximum density estimates are from Table 5 and Table Add-3 of USGS’s application.
2 Regional population size estimates are from Table 4.
Conclusions—Bowhead whales are
considered by NMFS to be disturbed
after exposure to underwater sound
levels greater than or equal to 160 dB
(rms) for impulse sources and 120 dB
(rms) for continuous sources. The
relatively small airgun array proposed
for use in this survey limits the size of
the 160 dB (rms) EZ around the vessel
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and is not expected to result in any
bowhead whale exposures to
underwater sound levels sufficient to
reach the disturbance criterion as
defined by NMFS.
Odontocete reactions to seismic
energy pulses are usually assumed to be
limited to lesser distances from the
airgun(s) than are those of mysticetes,
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probably in part because odontocete
low-frequency hearing is assumed to be
less sensitive than that of mysticetes.
However, at least when in the Canadian
Beaufort Sea in summer, belugas appear
to be fairly responsive to seismic energy,
with few being sighted within 10 to 20
km (6.2 to 12.4 mi) of seismic vessels
during aerial surveys (Miller et al.,
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2005). Belugas will likely occur in small
numbers in the project area within U.S.
waters during the survey period. Most
belugas will likely avoid the vicinity of
the survey activities and few will likely
be affected.
Taking into account the mitigation
measures that are planned, effects on
cetaceans are generally expected to be
restricted to avoidance of a limited area
around the survey operation and shortterm changes in behavior, falling within
the MMPA definition of ‘‘Level B
harassment.’’ Furthermore, the estimated
numbers of animals potentially exposed
to sound levels sufficient to cause
appreciable disturbance are very low
percentages of the population sizes in
the Bering-Chukchi-Beaufort Seas.
Based on the ≥160 dB disturbance
criterion, the best estimates of the
numbers of cetacean exposures to
sounds ≥160 dB re 1 μPa (rms) represent
less than one percent of the populations
of each species in the Chukchi Sea and
adjacent waters. For species listed as
Endangered under the ESA, USGS
estimates suggest it is unlikely that fin
whales, or humpback whales will be
exposed to received levels ≥160 dB and/
or ≥120 dB, but that approximately 38
bowheads (0.36 percent of the regional
population) may be exposed at this
level. The latter is less than one percent
of the Bering-Chukchi-Beaufort
population of greater than 14,247
animals assuming 3.4 percent
population growth from the 2001
estimate of greater than 10,545 animals
(Zeh and Punt, 2005). NMFS
subsequently did an analysis, and found
that bowheads are unlikely to be
exposed to sound levels ≥160 dB (rms)
from airgun operations and/or ≥120 dB
(rms) from icebreaking activities. NMFS
does not anticipate bowhead whales to
be potentially affected by the proposed
survey activities due to its location far
offshore of the bowhead fall migration
pathway.
Some monodontids may be exposed
to sounds produced by the airgun arrays
during the proposed survey, and the
numbers potentially affected are small
relative to the population sizes (see
Table 6 of the IHA application). The
best estimate of the number of belugas
(224 animals) that might be exposed to
≥160 dB and/or ≥120 dB represents less
than one percent (0.57 percent) of their
regional population.
The many reported cases of apparent
tolerance by cetaceans of seismic
exploration, vessel traffic, and some
other human activities show that coexistence is possible. Monitoring and
mitigation measures such as controlled
vessel speed, dedicated PSOs, nonpursuit, shut-downs or power-downs
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when marine mammals are seen within
defined ranges will further reduce shortterm reactions and minimize any effects
on hearing sensitivity. In all cases, the
effects are expected to be short-term,
with no lasting biological consequence.
Several pinniped species may be
encountered in the study area, but the
ringed seal is by far the most abundant
marine mammal species in the survey
area. The best (average) estimates of the
numbers of individual seals exposed to
airgun sounds at received levels ≥160
dB re 1 μPa (rms) and/or ≥120 dB re 1
μPa (rms) for icebreaking during the
marine survey are as follows: Ringed
seals (1,328 animals; 7.4 percent of the
regional population), bearded seals (67
animals; 0.02 percent of the regional
population), and spotted seals (0
animals, 0 percent of the regional
population), representing less than a
few percent of the Bering-ChukchiBeaufort populations for each species. It
is probable that only a small percentage
of the pinnipeds exposed to sound level
≥160 dB (rms) or 120 dB (rms) would
actually be disturbed. The short-term
exposures of pinnipeds to airgun sounds
are not expected to result in any longterm negative consequences for the
individuals or their populations.
Potential Effects on Habitat
The proposed USGS seismic survey
will not result in any permanent impact
on habitats used by marine mammals,
including the food sources they use. The
proposed activities will be of short
duration in any particular area at any
given time; thus any effects would be
localized and short-term. The main
impact associated with the proposed
activity will be temporarily elevated
noise levels and the associated direct
effects on marine mammals, as
described above.
Icebreaking could alter ice conditions
in the immediate area around the
vessels. However, ice conditions at this
time of year are typically highly variable
and relatively unstable in most locations
the survey will take place. Although
there is the potential for the destruction
of ringed seal lairs or polar bear dens
due to icebreaking, these animals will
not be using lairs or dens at the time of
the planned survey.
One of the reasons for the adoption of
airguns as the standard energy source
for marine seismic surveys was that,
unlike explosives, they do not result in
any appreciable fish kill. However, the
existing body of information relating to
the impacts of seismic on marine fish
and invertebrate species, the primary
food sources of pinnipeds and belugas,
is very limited.
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In water, acute injury and death of
organisms exposed to seismic energy
depends primarily on two features of
the sound source: (1) The received peak
pressure, and (2) the time required for
the pressure to rise and decay (Hubbs
and Rechnitzer, 1952; Wardle et al.,
2001). Generally, the higher the received
pressure and less time required for the
pressure to rise and decay, the greater
the chance of acute pathological effects.
Considering the peak pressure and rise/
decay time characteristics of seismic
airgun arrays used today, the
pathological zone for fish and
invertebrates would be expected to be
within a few meters of the seismic
source (Buchanan et al., 2004). For the
proposed survey, any injurious effects
on fish would be limited to very short
distances from the sound source and
well away from the nearshore waters
where most subsistence fishing
activities occur.
The survey off of northern Alaska will
occur in an area designated as Essential
Fish Habitat (EFH) for Arctic cod
(Arctogadus glacialis) (NPFMC, 2009).
The approximately 806 km (435 nmi) of
seismic survey lines that will be
conducted in U.S. waters represents the
maximum possible extent of potential
EFH that would be ensonified during
the project; the border of the U.S. EEZ
defines the potential Arctic cod EFH
boundary for Arctic cod. Effects on
managed EFH species (Arctic cod) by
the seismic operations assessed here
would be temporary and minor. The
main effect would be short-term
disturbance that might lead to
temporary and localized relocation of
the EFH species or their food. The
actual physical and chemical properties
of the EFH will not be impacted. The
only other designated Essential Fish
Habitat (EFH) species that may occur in
the area of the project during the
seismic survey are salmon (adult), and
their occurrence in waters north of the
Alaska coast is limited. Adult fish near
seismic operations are likely to avoid
the immediate vicinity of the source,
thereby avoiding injury (see Appendix E
of the IHA application). No EFH species
will be present as very early life stages
when they would be unable to avoid
seismic exposure that could otherwise
result in minimal mortality.
Studies have been conducted on the
effects of seismic activities on fish
larvae and a few other invertebrate
animals. Generally, seismic was found
to only have potential harmful effects to
larvae and invertebrates that are in
direct proximity (a few meters) of an
active airgun array (see Appendix E and
F of the IHA application). The proposed
Arctic Sea seismic program for 2010 is
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predicted to have negligible to low
physical effects on the various life
stages of fish and invertebrates.
Therefore, physical effects of the
proposed program on fish and
invertebrates would not be significant.
The Healy is designed for continuous
passage at 5.6 km (3 knots) through ice
1.4 m (4.6 ft) thick. During this project
the Healy will typically encounter firstor second-year ice while avoiding thick
ice floes, particularly large intact multiyear ice, whenever possible. In addition,
the icebreaker will follow leads when
possible while following the survey
route. As the icebreaker passes through
the ice, the ship causes the ice to part
and travel alongside the hull. This ice
typically returns to fill the wake as the
ship passes. The effects are transitory,
i.e., hours at most, and localized, i.e.,
constrained to a relatively narrow swath
perhaps 10 m (32.8 ft) to each side of the
vessel.
The Healy’s maximum beam is 25 m
(82 ft). Applying the maximum
estimated amount of icebreaking, i.e.,
3,372 km (2,095.3 mi), to the corridor
opened by the ship, USGS anticipates
that a maximum of approximately 152
km2 (58.7 mi2) of ice may be disturbed.
This encompasses an insignificant
amount (less than 0.005 percent) of the
total Arctic ice extent in August and
September of 2008 and 2009 which
ranged from 3.24 million to 4.1 million
km2 (1,235,527 to 1,583,019 mi2).
Potential Effects on Marine Mammal
Habitat
A detailed discussion of the potential
effects of this action on marine mammal
habitat, including physiological and
behavioral effects on marine fish and
invertebrates was included in the
proposed IHA (75 FR 39336, July 8,
2010). Based on the discussion in the
proposed IHA notice and the nature of
the activities (limited duration), the
authorized operations are not expected
to have any habitat-related effects that
could cause significant or long-term
consequences for individual marine
mammals or their populations or stocks.
Similarly, any effects to food sources are
expected to be negligible.
The airgun operations will not result
in any permanent impact on habitats
used by marine mammals, or to the food
sources they use. The main impact issue
associated with the activities will be
temporarily elevated noise levels and
the associated direct effects on marine
mammals, as well as the potential
effects of icebreaking, as described
above. The potential effects of
icebreaking include locally altered ice
conditions which may temporarily alter
the haul-out pattern of seals in the
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immediate vicinity of the vessel. The
destruction of ringed seal lairs or polar
bear dens is not expected to be a
concern at this time of year.
Mitigation
In order to issue an Incidental Take
Authorization (ITA) for small numbers
of marine mammals 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 on the availability of
such species or stock for taking for
certain subsistence uses. For the
proposed seismic survey in the Arctic
Ocean, USGS will deploy an airgun
array of three G-airguns. The source will
be relatively small in size and source
level, relative to airgun arrays typically
used for industry seismic surveys.
Important mitigation factors built into
the design of the survey include the
following:
• In deep offshore waters (where the
survey will occur), sound from the
airguns is expected to attenuate
relatively rapidly as compared with
attenuation in shallower waters;
• The airguns comprising the array
will be clustered with only limited
horizontal separation (see Appendix B
of the IHA application), so the arrays
will be less directional than is typically
the case with larger airgun arrays. This
will result in less downward directivity
than is often present during seismic
surveys, and more horizontal
propagation of sound; and
• Airgun operations will be limited to
offshore waters, far from areas where
there is subsistence hunting or fishing,
and in waters where marine mammal
densities are generally low.
In addition to the mitigation measures
that are built into the general project
design, several specific mitigation
measures will be implemented to avoid
or minimize effects on marine mammals
encountered along the tracklines. These
include ramping-up the airguns at the
beginning of operations, and powerdowns or shut-downs when marine
mammals are detected within specified
distances from the source. The GSC has
written a Categorical Declaration (see
Appendix C of the IHA application)
stating that: ‘‘While in U.S. waters (i.e.,
the U.S. 200 mile EEZ), the GSC
operators will comply with any and all
environmental mitigation measures
required by the U.S. National Marine
Fisheries Service (NMFS) and/or the
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U.S. Fish and Wildlife Service
(USFWS).’’
Received sound fields were measured
for the airgun configuration, in relation
to distance and direction from the
airgun(s). The proposed radii around the
airgun(s) where received levels would
be 180 and 190 dB (rms) are shown in
Table 2 of the IHA application. The 180
and 190 dB (rms) levels are used to
initiate a power-down or, if necessary,
shut-down criteria applicable to
cetaceans and pinnipeds, respectively,
as specified by NMFS (2000).
Vessel-based PSOs will watch for
marine mammals near the airgun(s)
when they are in use. Mitigation and
monitoring measures proposed to be
implemented for the seismic survey
have been developed and refined in
cooperation with NMFS during previous
seismic studies in the Arctic and
described in associated EAs, IHA
applications, and IHAs. The mitigation
and monitoring measures described
herein represent a combination of the
procedures required by past IHAs for
Arctic projects.
Some cetacean species (such as
bowhead whales) may be feeding or
migrating in the Beaufort Sea during
August and September. However, most
of the proposed geophysical activities
will occur north of the main migration
corridor and the number of individual
animals expected to closely approach
the vicinity of the proposed activity will
be small in relation to regional
population sizes. With the monitoring,
ramp-up, power-down, and shut-down
provisions (see below), any effects on
individuals are expected to be limited to
behavioral disturbance. The following
subsections provide more detailed
information about the mitigation
measures that are an integral part of the
planned activity.
Exclusion Zones (EZ)
Mosher et al. (2009) collected
received sound level data for the airgun
configuration that will be used in the
proposed survey in similar water
depths, i.e., greater than 2,000 m
(6,561.7 ft). The empirical data were
plotted in relation to distance and
direction from the three airguns by Roth
and Schmidt (2010; see Figure B–3).
Based on model fit to the measured
received levels and source modeling
estimates from Gundalf, the 180 and 190
dB (rms) EZ are estimated to be 216 m
(708.7 ft) and 68 m (223.1 ft),
respectively. As a conservative measure
for the proposed EZ, the sound-level EZ
indicated by the empirical data have
been increased to 500 m (1,640.4 ft) for
the 180 dB isopleths and to 100 m (328
ft) for the 190 dB isopleths (see Table 2
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of the IHA application). The 180 and
190 dB levels are shut-down criteria
applicable to cetaceans and pinnipeds,
respectively, as specified by NMFS
(2000); these levels were used to
establish the EZs. If the PSO detects
marine mammal(s) within or about to
enter the appropriate EZ, the airguns
will be powered-down (or shut-down if
necessary) immediately (see below).
Detailed recommendations for new
science-based noise exposure criteria
were published in early 2008 (Southall
et al., 2007). USGS will be prepared to
revise its procedures for estimating
numbers of mammals ‘‘taken,’’ EZs, etc.,
as may be required by any new
guidelines that result. As yet, NMFS has
not specified a new procedure for
determining EZs. Such procedures, if
applicable would be implemented
through a modification to the IHA if
issued.
In addition to monitoring, mitigation
measures that will be adopted during
the Arctic Ocean survey include:
(1) Speed or course alteration,
provided that doing so will not
comprise operational safety
requirements;
(2) Power-down procedures;
(3) Shut-down procedures; and
(4) Ramp-up procedures.
No start-up of airgun operations
would be permitted unless the full 180
dB (rms) EZ is visible for at least 30 min
during day or night. Other proposed
provisions associated with operations at
night or in periods of poor visibility
include the following:
• During foggy conditions or darkness
(which may be encountered starting in
late August), the full 180 dB (rms) EZ
may not be visible. In that case, the
airguns could not start-up after a full
shut-down until the entire 180 dB (rms)
radius was visible.
• During any nighttime operations, if
the entire 180 dB (rms) EZ is visible
using vessel lights, then start-up of the
airgun array may occur following a 30
min period of observation without
sighting marine mammals in the EZ.
• If one or more airguns have been
operational before nightfall, they can
remain operational throughout the
night, even though the entire EZ may
not be visible.
Speed or Course Alteration—If a
marine mammal (in water) is detected
outside the EZ and, based on its
position and relative motion, is likely to
enter the EZ, the vessel’s speed and/or
direct course may, when practical and
safe, be changed in a manner that also
minimizes the effect on the planned
science objectives. The marine mammal
activities and movements relative to the
seismic vessel will be closely monitored
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to ensure that the marine mammal does
not approach within the EZ. If the
mammal appears likely to enter the EZ,
further mitigative actions will be taken,
i.e., either further course alterations or
power-down or shut-down of the
airgun(s).
Power-down Procedures—A powerdown involves reducing the number of
airguns in use such that the radius of
the 180 dB or 190 dB (rms) EZ are
decreased to the extent that marine
mammals are no longer in or about to
enter the EZ. A power-down of the
airgun array can also occur when the
vessel is moving from one seismic line
to another. During a power-down for
mitigation, one airgun (or some other
number of airguns less than the full
airgun array) will be operated. The
continued operation of one airgun is
intended to alert (1) marine mammals to
the presence of the seismic vessel in the
area, and (2) retain the option of
initiating a ramp-up to full operations
under poor visibility conditions. In
contrast, a shut-down occurs when all
airgun activity is suspended.
If a marine mammal is detected
outside the EZ but is likely to enter the
EZ, and if the vessel’s speed and/or
course cannot be changed to avoid
having the marine mammal enter the
EZ, the airguns (as an alternative to a
complete shut-down) will be powereddown to a single airgun before the
animal is within the EZ. Likewise, if a
mammal is already within the EZ when
first detected, the airguns will be
powered-down immediately if this is a
reasonable alternative to a complete
shut-down. During a power-down of the
airgun array, the number of operating
airguns will be reduced to a single 150
in3 G-airgun. The 180 dB (rms) EZ for
the power-down sound source has been
estimated to be 62 m (203 ft); the
proposed distance for use by PSOs is 75
m (246 ft). If a marine mammal is
detected within or near the smaller EZ
around that single 150 in3 airgun (see
Table 2 of USGS’s application and Table
2 above), all airguns will be shut-down
(see next subsection).
Following a power-down, operation of
the full airgun array will not resume
until the marine mammal is outside the
EZ for the full array. The animal will be
considered to have cleared the EZ if it:
(1) Is visually observed to have left
the EZ, or
(2) Has not been seen within the EZ
for 15 minutes in the case for species
with shorter dive durations (e.g., small
odontocetes and pinnipeds); or
(3) Has not been seen within the EZ
for 30 minutes in the case for species
with longer dive durations (e.g.,
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mysticetes and large odontocetes,
including killer whales).
During airgun operations following a
power-down (or shut-down) whose
duration has exceeded the limits
specified above and subsequent animal
departures, the airgun array will be
ramped-up gradually. Ramp-up
procedures are described below.
Shut-down Procedures—The
operating airguns(s) will be shut-down
if a marine mammal is detected within
or approaching the EZ for a single
airgun source (i.e., a power-down is not
practical or adequate to reduce exposure
to less than 190 or 180 dB (rms), as
appropriate). Shut-downs will be
implemented (1) if an animal
approaches or enters the EZ of the single
airgun after a power-down has been
initiated, or (2) if an animal is initially
seen within the EZ of a single airgun
when more than one airgun (typically
the full array) is operating. Airgun
activity will not resume until the marine
mammal has cleared the EZ, or until the
PSO is confident that the animal has left
the vicinity of the vessel (or the PSO not
observing the animal[s] within the EZ
for 15 or 30 min depending upon the
species). Criteria for judging that the
animal has cleared the EZ will be as
described in the preceding subsection.
Ramp-up procedures will be followed
during resumption of full seismic
operations after a shut-down of the
airgun array.
Ramp-up Procedures—A ramp-up
procedure will be followed when the
airgun array begins operating after a
specified period without airgun
operations or when a power-down (or
reduced airgun operations) has
exceeded that specified duration period.
The specified period depends on the
speed of the source vessel, the size of
the airgun array that is being used, and
the size of the EZ, but is often about 10
min. NMFS normally requires that, once
ramp-up commences, the rate of rampup be no more than 6 dB per 5 min
period. Ramp-up will begin with a
single airgun (the smallest airgun in the
array). Airguns will be added in a
sequence such that the source level of
the array will increase in steps not
exceeding 6 dB per 5 min period over
a total duration of approximately 10
minutes. During ramp-up, the PSOs will
monitor the EZ, and if marine mammals
are sighted, a power-down or shut-down
will be implemented as though the full
array were operational.
If the complete 180 dB (rms) EZ has
not been visible for at least 30 min prior
to the start of operations in either
daylight or nighttime, ramp-up will not
commence unless at least one airgun
(150 in3 or similar) has been operating
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during the interruption of seismic
survey operations. Given these
provisions, it is likely that the three Gairgun array will not be ramped-up from
a complete shut-down at night or in
thick fog, because the outer part of the
EZ for that array will not be visible
during those conditions. If the entire EZ
is visible using vessel lights, then startup of the airguns from a complete shutdown may occur at night. If one airgun
has operated during a power-down
period, ramp-up to full power will be
permissible at night or in poor visibility,
on the assumption that marine
mammals will be alerted to the
approaching seismic vessel by the
sounds from the single airgun and could
move away if they choose. Given the
responsiveness of bowhead and beluga
whales to airgun sounds, it can be
assumed that those species in particular
will move away during a ramp-up.
Ramp-up of the airguns will not be
initiated during the day or at night if a
marine mammal is sighted within or
near the applicable EZ during the
previous 15 or 30 min, as applicable.
Helicopter Flights—The use of a
helicopter to conduct ice
reconnaissance flights and vessel-tovessel personnel transfers is likely to
occur during survey activities in U.S.
waters. However, collection of spot
bathymetry data or on-ice landings, both
of which required low altitude flight
patterns, will not occur in U.S. waters.
Monitoring and Reporting
In order to issue an ITA for an
activity, Section 101(a)(5)(D) of the
MMPA states that NMFS must set forth
‘‘requirements pertaining to the
monitoring and reporting of such
taking.’’ The MMPA implementing
regulations at 50 CFR 216.104(a)(13)
require that requests for IHAs must
include the suggested means of
accomplishing the necessary monitoring
and reporting that will result in
increased knowledge of the species and
of the level of taking or impacts on
populations of marine mammals that are
expected to be present.
USGS will sponsor marine mammal
monitoring during the proposed project,
in order to implement the mitigation
measures that require real-time
monitoring, to satisfy the anticipated
monitoring requirements of the IHA,
and to meet any monitoring
requirements agreed to as part of the
Plan of Cooperation. USGS’s Monitoring
Plan is described below as well as in
their IHA application.
The monitoring work described here
has been planned as a self-contained
project independent of any other related
monitoring projects that may be
occurring simultaneously in the same
regions. USGS is prepared to discuss
coordination of its monitoring program
with any related work that might be
done by other groups insofar as this is
practical and desirable.
Vessel-based Visual Monitoring
Vessel-based Protected Species
Observers (PSOs) will monitor for
marine mammals near the seismic
source vessel during all daytime airgun
operations and during any nighttime
start-ups of the airguns. The survey area
within U.S. waters is located within
high latitudes (approximately 72° to 74°
North) and the project will take place
during the summer when little darkness
will be encountered (see Table 9 of the
IHA application). Some periods of
darkness will be encountered towards
the end of the survey when there will
be several hours between sunset and
sunrise.
The PSO’s observations will provide
the real-time data needed to implement
the key mitigation measures. Airgun
operations will be powered-down or (if
necessary) shut-down when marine
mammals are observed within, or about
to enter, a designated EZ where there is
a possibility of effects on hearing or
other physical effects. Vessel-based
PSOs will also watch for marine
mammals near the seismic vessel for at
least 30 min prior to the planned start
of airgun operations after an extended
shut-down of the airgun. When feasible,
observations will also be made during
daytime periods without seismic
operations (e.g., during transits).
TABLE 7—THE DAYLIGHT TIMES AND PERIODS WITHIN THE PROPOSED PROJECT AREA FROM BEGINNING (AUGUST 7,
2010) TO END (SEPTEMBER 3, 2010) OF THE PLANNED SURVEY ACTIVITIES WITHIN LATITUDES OF THE PLANNED
SURVEY WITHIN U.S. WATERS. TIME IS IN ALASKA DAYLIGHT TIME (AKDT)
72° North
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Date .................................................................................................................
Sunrise .............................................................................................................
Sunset ..............................................................................................................
Period of daylight (hours) ................................................................................
• During daylight, vessel-based PSOs
will watch for marine mammals near the
seismic vessel during all periods of
airgun activity and for a minimum of 30
min prior to the planned start of airgun
operations after an extended shut-down.
• Although there will be only a brief
period during the survey when darkness
will be encountered in U.S. waters,
USGS proposes to conduct nighttime as
well as daytime operations. PSOs
dedicated to protected species
observations are proposed not to be on
duty during ongoing seismic operations
at night, given the very limited
effectiveness of visual observation at
night. At night, bridge personnel will
watch for marine mammals (insofar as
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09:29
06:42
21:13
practical at night) and will call for the
airguns to be shut-down if marine
mammals are observed in or about to
enter the EZ.
PSOs will be stationed aboard both
the seismic source vessel (St. Laurent)
and Healy during the proposed survey.
The vessels will typically work together
in tandem while making way through
heavy ice with the Healy in the lead
breaking ice and collecting multi-beam
data. The St. Laurent will follow
collecting seismic reflection and
refraction data. In light ice conditions,
the vessels will separate to maximize
data collection. ‘‘Real-time’’
communication between the two vessels
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74° North
September 3
12:14
03:45
15:31
August 7
—
—
24:00
September 3
12:00
03:59
15:59
regarding marine mammal detections
will be available through VHF radio.
During operations in U.S. EEZ waters,
a complement of five PSOs will work on
the source vessel, the St. Laurent, and
two will be stationed on the Healy.
Three trained PSOs will board the St.
Laurent in Kagluktuk, Nunavut, Canada.
Three experienced PSOs and one Alaska
Native community observer will be
aboard the Healy at the outset of the
project. Before survey operations begin
in U.S. waters, two of the PSOs on the
Healy will transfer to the St. Laurent to
provide additional observers during
airgun operations. When not surveying
in U.S. waters, the distribution of PSOs
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will return to three on the St. Laurent
and four on the Healy.
PSOs on the St. Laurent will monitor
for marine mammals during all daylight
airgun operations. Airgun operations
will be shut-down when marine
mammals are observed within, or about
to enter, a designated EZ (see below)
where there may be a possibility of
significant effects on hearing or other
physical effects. PSOs on both the
source vessel and the Healy will also
watch for marine mammals within or
near the EZ for at least 30 min prior to
the planned start of airgun operations
after an extended shut-down of the
airgun array. When feasible,
observations will also be made during
periods without seismic operations (e.g.,
during transits). Environmental
conditions will be recorded every half
hour during PSO watch.
The PSOs aboard the Healy will also
watch for marine mammals during
daylight seismic activities conducted in
both U.S. and international waters. They
will maximize their time on watch but
will not watch continuously, as will
those on the St. Laurent, because they
will not have mitigation duties and
there will be only two PSOs aboard the
Healy. The Healy PSOs will report
sightings to the PSOs on the St. Laurent
to alert them of possible needs for
mitigation.
In U.S. waters, at least one observer,
and when practical two observers, will
monitor for marine mammals from the
St. Laurent during ongoing daytime
operations and nighttime start-ups
(when darkness is encountered). Use of
two simultaneous observers will
increase the proportion of the animals
present near the source vessel that are
detected. PSOs will normally be on duty
in shifts of no longer than four hours
duration although more than one hour
shift may be worked per day with a
maximum of 12 hours of daily watch
time. During seismic operations in
international waters, PSOs aboard the
St. Laurent will conduct eight hour
watches. This schedule accommodates
24 hour/day monitoring by three PSOs
which will be necessary during most of
the survey when daylight will be
continuous. Healy PSOs will limit
watches to four hours in U.S. waters.
The St. Laurent crew will be
instructed to assist in detecting marine
mammals and implementing required
mitigation (if practical). The crew will
be given instruction on mitigation
requirements and procedures for
implementation of mitigation prior to
the start of the seismic survey. Members
of the Healy crew will be trained to
monitor for marine mammals and asked
to contact the Healy observers for
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sightings that occur while the PSOs are
off-watch.
The St. Laurent and Healy are suitable
platforms for observations for marine
mammals. When stationed on the flying
bridge, eye level will be approximately
15.4 m (51 ft) above sea level on the St.
Laurent and approximately 24 m (78.7
ft) above sea level on the Healy. On both
vessels the PSO will have an
unobstructed view around the entire
vessel from the flying bridge. If
surveying from the bridge of the St.
Laurent or the Healy the PSO’s eye level
will be approximately 12.1 m (40 ft)
above sea level or 21.2 m (69 ft) above
sea level, respectively. The PSO(s) will
scan the area around the vessel
systematically with laser range finding
binoculars and with the unaided eye.
The survey will be conducted at high
latitudes and continuous daylight will
persist through much of the proposed
survey area through the month of
August. Day length will decrease to
approximately 18 hours in the northern
portion of the survey area by about early
September. Laser range-finding
binoculars (Leica LRF 1200 laser
rangefinder or equivalent) will be
available to assist with distance
estimation; this equipment is useful in
training observers to estimate distances
visually, but is generally not useful in
measuring distances to animals directly.
When marine mammals are detected
within or about to enter the designated
EZ, the airgun(s) will be powered-down
or shut-down immediately. The
distinction between power-downs and
shut-downs is described above and in
the IHA application. Channels of
communication between the PSOs and
the airgun technicians will be
established to assure prompt
implementation of shut-downs when
necessary as has been done in other
recent seismic survey operations in the
Arctic (e.g., Haley, 2006). During powerdowns and shut-downs, PSOs will
continue to maintain watch to
determine when the animal(s) are
outside the EZ. Airgun operations will
not resume until the animal is outside
the EZ. The animal will be considered
to have cleared the EZ if it is visually
observed to have left the EZ.
Alternatively, in U.S. waters the EZ will
be considered clear if the animal has not
been seen within the EZ for 15 min for
small odontocetes and pinnipeds or 30
min for mysticetes. Within international
waters the PSOs will apply a 30 min
period for all species.
PSO Data and Documentation
PSOs will record data to estimate the
numbers of marine mammals exposed to
various received sound levels and to
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document apparent disturbance
reactions or lack thereof. Data will be
used to estimate numbers of animals
potentially ‘taken’ by harassment (as
defined in the MMPA). They will also
provide information needed to order a
power-down or shut-down of the
seismic source when a marine mammal
is within or near the EZ.
When a sighting is made, the
following information about the sighting
will be recorded:
(1) Species, group size, and age/size/
sex categories (if determinable);
behavior when first sighted and after
initial sighting; heading (if consistent),
bearing, and distance from seismic
vessel; sighting cue; apparent reaction to
the seismic source or vessel (e.g., none,
avoidance, approach, paralleling, etc.);
and behavioral pace.
(2) Time, location, heading, speed,
activity of the vessel, sea state,
visibility, and sun glare.
The data listed under (2) above will
also be recorded at the start and end of
each observation watch, and during a
watch whenever there is a change in one
or more of the variables.
All observations, as well as
information regarding seismic source
power-downs and shut-downs, will be
recorded in a standardized format. Data
will be entered into a custom database
using a notebook computer. The
accuracy of data entry will be verified
by computerized data validity checks as
the data are entered and by subsequent
manual checking of the database. These
procedures will allow initial summaries
of data to be prepared during and
shortly after the field program, and will
facilitate transfer of the data to
statistical, graphical, and other
programs for further processing and
archiving.
Results for the vessel-based
observations will provide:
(1) The basis for real-time mitigation
(airgun power-down or shut-down).
(2) Information needed to estimate the
number of marine mammals potentially
taken by harassment, which must be
reported to NMFS per terms of MMPA
authorizations or regulations.
(3) Data on the occurrence,
distribution, and activities of marine
mammals in the area where the seismic
study is conducted.
(4) Information to compare the
distance and distribution of marine
mammals relative to the source vessel at
times with and without seismic activity.
(5) Data on the behavior and
movement patterns of marine mammals
seen at times with and without seismic
activity.
A report on USGS activities and on
the relevant monitoring and mitigation
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results will be submitted to NMFS
within 90 days after the end of the
cruise. The report will describe the
operations that were conducted and
sightings of marine mammals near the
operations. The report will be submitted
to NMFS, providing full documentation
of methods, results, and interpretation
pertaining to all acoustic
characterization work and vessel-based
monitoring. The 90-day report will
summarize the dates and locations of
seismic operations, and all marine
mammal sightings (dates, times,
locations, activities, associated seismic
survey activities). The number and
circumstances of ramp-ups, powerdowns, shut-downs, and other
mitigation measures will be reported.
Sample size permitting, the report will
also include estimates of the amount
and nature of potential ‘‘take’’ of marine
mammals.
All injured or dead marine mammals
(regardless of cause) will be reported to
NMFS as soon as practicable. The report
will include species or description of
animal, condition of animal, location,
time first found, observed behaviors (if
alive) and photo or video, if available.
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Encouraging and Coordinating Research
USGS will coordinate the planned
marine mammal monitoring program
associated with the seismic survey in
the Arctic Ocean with other parties that
may have an interest in this area and/
or be conducting marine mammal
studies in the same region during
operations. No other marine mammal
studies are expected to occur in the
main (northern) parts of the study area
at the proposed time. However, other
industry-funded seismic surveys may be
occurring in the northeast Chukchi and/
or western Beaufort Sea closer to shore,
and those projects are likely to involve
marine mammal monitoring. USGS has
coordinated, and will continue to
coordinate, with other applicable
Federal, State and Borough agencies,
and will comply with their
requirements.
Negligible Impact and Small Numbers
of Marine Mammals Analysis and
Determination
The Secretary, in accordance with
paragraph 101(a)(5)(D) of the MMPA,
shall authorize the take of small
numbers of marine mammals incidental
to specified activities other than
commercial fishing within a specific
geographic region if, among other
things, he determines that the
authorized incidental take will have a
‘‘negligible impact’’ on species or stocks
affected by the authorization. NMFS
implementing regulations codified at 50
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CFR 216.103 states that a ‘‘negligible
impact is an impact resulting from the
specified activity that cannot be
reasonably expected to, and is not
reasonably likely to, adversely affect the
species or stock through effects on
annual rates of recruitment or survival.’’
Based on the analysis contained
herein, of the likely effects of the
specified activity on marine mammals
and their habitat within the specific area
of study for the Arctic Ocean marine
geophysical survey, and taking into
consideration the implementation of the
mitigation and monitoring measures
NMFS, on behalf of the Secretary, found
that USGS’s proposed activities would
result in the incidental take of small
numbers of marine mammals, by Level
B harassment only, and that the total
taking from the proposed seismic survey
would have a negligible impact on the
affected species or stocks of marine
mammals. As a basis for its small
numbers determination, NMFS
evaluated the number of individuals
taken by Level B harassment relative to
the size of the stock or population.
While the number of marine
mammals potentially incidentally
harassed will depend on the
distribution and abundance of marine
mammals in the vicinity of the survey
activity, the number of potential Level
B incidental harassment takings (see
Table 6 above) is estimated to be small,
less than a few percent of any of the
estimated population sizes based on the
data disclosed in Tables 4 and 6 of this
notice, and has been mitigated to the
lowest level practicable through the
incorporation of the monitoring and
mitigation measures mentioned
previously in this document. Tables 4
and 6 in this notice disclose the habitat
regional abundance, conservation status,
density, and the number of individuals
exposed to sound levels greater than or
equal to 120 dB (rms) (for icebreaking)
or 160 dB (rms) (for seismic airgun
operations). Also, there are no known
important reproductive or feeding areas
in the proposed action area.
For reasons stated previously in this
document, the specified activities
associated with the proposed survey are
not likely to cause TTS, PTS or other
non-auditory injury, serious injury, or
death to affected marine mammals
because:
(1) The likelihood that, given
sufficient notice through relatively slow
ship speed, marine mammals are
expected to move away from a noise
source that is annoying prior to its
becoming potentially injurious;
(2) The fact that cetaceans and
pinnipeds would have to be closer than
500 m (1,640.4 ft) and 30 m (98.4 ft), in
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deep water when the full array is in use
at tow depth from the vessel to be
exposed to levels of sound (180 dB and
190 dB, respectively) believed to have
even a minimal chance of causing PTS;
(3) The fact that marine mammals
would have to be closer than 2,500 m
(8,202.1 ft) in deep water when the full
array is in use at tow depth from the
vessel to be exposed to levels of sound
(160 dB) believed to have even a
minimal chance of causing TTS; and
(4) The likelihood that marine
mammal detection ability by trained
observers is high at that short distance
from the vessel.
As a result, no take by injury, serious
injury, or death is anticipated or
authorized, and the potential for
temporary or permanent hearing
impairment is very low and will be
avoided through the incorporation of
the proposed monitoring and mitigation
measures.
In making a negligible impact
determination NMFS evaluated factors
such as: no anticipated injury, serious
injury or mortality; the number, nature,
intensity and duration of harassment
(all relatively limited); the low
probability that take will likely result in
effects to annual rates of recruitment of
survival; the context in which it occurs
(i.e., 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
mammal (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.
Impact on Availability of Affected
Species for Taking for Subsistence Uses
There is subsistence hunting for
marine mammals in the waters off of the
coast of Alaska, in the Arctic Ocean,
that implicates MMPA Section
101(a)(5)(D). Subsistence hunting and
fishing continue to be prominent in the
household economies and social welfare
of some Alaska residents, particularly
among those living in small, rural
villages (Wolfe and Walker, 1987;
Braund and Kruse, 2009). Subsistence
remains the basis for Alaska Native
culture and community. In rural Alaska,
subsistence activities are often central to
many aspects of human existence,
including patterns of family life, artistic
expression, and community religious
and celebratory activities.
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Subsistence Hunting
Marine mammals are legally hunted
in Alaskan waters by coastal Alaska
Natives; species hunted include
bowhead and beluga whales; ringed,
spotted, and bearded seals; walruses,
and polar bears. The importance of each
of the various species varies among the
communities based largely on
availability. Bowhead whales, belugas,
and walruses are the marine mammal
species primarily harvested during the
time of the proposed seismic survey.
Subsistence remains the basis for Alaska
Native culture and community, and
subsistence activities are often central to
many aspects of human existence,
including patterns of family life, artistic
expression, and community religious
and celebratory activities.
Bowhead whale hunting is a key
activity in the subsistence economies of
Barrow and other Native communities
along the Beaufort Sea coast. The whale
harvests have a great influence on social
relations by strengthening the sense of
Inupiat culture and heritage in addition
to reinforcing family and community
ties.
An overall quota system for the
hunting of bowhead whales was
established by the International Whaling
Commission in 1977. The quota is now
regulated through an agreement between
NMFS and the Alaska Eskimo Whaling
Commission (AEWC) which extends to
2012 (NMFS, 2008b). The AEWC
allocates the number of bowhead whales
that each whaling community may
harvest annually during five-year
periods (USDI/BLM, 2005; NMFS,
2008).
The community of Barrow hunts
bowhead whales in both the spring and
fall during the whales’ seasonal
migration along the coast (see Figure 2
of the IHA application). Often the bulk
of the Barrow bowhead harvest is taken
during the spring hunt. However, with
larger quotas in recent years, it is
common for a substantial fraction of the
annual Barrow quota to remain available
for the fall hunt (see Table 7 of the IHA
application). The communities of
Nuiqsut and Kaktovik participate only
in the fall bowhead harvest. The fall
migration of bowhead whales that
summer in the eastern Beaufort Sea
typically begins in late August or
September. Fall migration into Alaskan
waters is primarily during September
and October. However, in recent years a
small number of bowheads have been
seen or heard offshore from the Prudhoe
Bay region during the last week of
August (Treacy, 1993; LGL and
Greenridge, 1996; Greene, 1997; Greene
et al., 1999; Blackwell et al., 2004).
TABLE 8—NUMBER OF BOWHEAD WHALE LANDING BY YEAR AT BARROW, CROSS ISLAND (NUIQSUT), AND KAKTOVIK,
1993 TO 2008. BARROW NUMBERS INCLUDE THE TOTAL NUMBER OF WHALES LANDED FOR THE YEAR FOLLOWED BY
THE NUMBERS LANDED DURING THE FALL HUNT IN PARENTHESES. CROSS ISLAND (NUIQSUT) AND KAKTOVIK LANDINGS ARE IN AUTUMN
Year
1993
1994
1995
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
2007
2008
Point Hope
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
................................................................................................
Wainwright
2
5
1
3
4
3
2
3
4
0
4
3
7
0
3
2
Barrow
5
4
5
3
3
3
5
5
6
1
5
4
4
2
4
2
23 (7)
16 (1)
19 (11)
24 (19)
30 (21)
25 (16)
24 (6)
18 (13)
27 (7)
22 (17)
16 (6)
21 (14)
29 (13)
22 (19)
20 (7)
21 (12)
Cross Island
Kaktovik
3
0
4
2
3
4
3
4
3
4
4
3
1
4
3
4
erowe on DSK5CLS3C1PROD with NOTICES2
Sources: USDI/BLM and references therein; Burns et al., 1993; Koski et al., 2005; Suydam et al., 2004, 2005, 2006, 2007, 2008, and 2009.
The spring hunt at Barrow occurs
after leads open due to the deterioration
of pack ice; the spring hunt typically
occurs from early April until the first
week of June. The location of the fall
subsistence hunt depends on ice
conditions and (in some years)
industrial activities that influence the
bowheads as they move west (Brower,
1996). In the fall, subsistence hunters
use aluminum or fiberglass boats with
outboards. Hunters prefer to take
bowheads close to shore to avoid a long
tow during which the meat can spoil,
but Braund and Moorehead (1995)
report that crews may (rarely) pursue
whales as far as 80 km (49.7 mi). The
fall hunts begin in late August or early
September in Kaktovik and at Cross
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17:47 Sep 28, 2010
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Island. At Barrow the fall hunt usually
begins in mid-September, and mainly
occurs in the waters east and northeast
of Point Barrow in the Chukchi Sea
(Suydam et al., 2008). The whales have
usually left the Beaufort Sea by late
October (Treacey, 2002a, b).
The scheduling of this seismic survey
has been discussed with representatives
of those concerned with the subsistence
bowhead hunt, most notably the AEWC,
the Barrow Whaling Captains’
Association, and the North Slope
Borough (NSB) Department of Wildlife
Management. The timing of the
proposed seismic survey in early to
mid-August will affect neither the
spring nor the fall bowhead hunt. The
Healy is planning to change crew after
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the completion of the seismic survey
through Barrow via helicopter or boat.
That crew change is scheduled for
approximately September 4 to 5, 2010,
well before the fall bowhead whaling
which typically begins late September
or early October. All of the proposed
geophysical activities will occur
offshore between 71° and 84° North
latitude well north of Beaufort Sea
whaling activities.
Beluga whales are available to
subsistence hunters at Barrow in the
spring when pack-ice conditions
deteriorate and leads open up. Belugas
may remain in the area through June
and sometimes into July and August in
ice-free waters. Hunters usually wait
until after the spring bowhead whale
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Federal Register / Vol. 75, No. 188 / Wednesday, September 29, 2010 / Notices
hunt is finished before turning their
attention to hunting belugas. The
average annual harvest of beluga whales
taken by Barrow for 1962 to 1982 was
five (MMS, 1996). The Alaska Beluga
Whale Committee recorded that 23
beluga whales had been harvested by
Barrow hunters from 1987 to 2002,
ranging from zero in 1987, 1988 and
1995 to the high of eight in 1997 (Fuller
and George, 1997; Alaska Beluga Whale
Committee, 2002 in USDI/BLM, 2005).
The proposed seismic survey is unlikely
to overlap with the beluga harvest, and
the survey initiates well outside the area
where impacts to beluga hunting by
Barrow villagers could occur.
Ringed seals are hunted mainly from
October through June. Hunting for these
smaller mammals is concentrated
during winter because bowhead whales,
bearded seals, and caribou are available
through other seasons. In winter, leads
and cracks in the ice off points of land
and along barrier islands are used for
hunting ringed seals. The average
annual ringed seal harvest by the
community of Barrow from the 1960s
through much of the 1980s has been
estimated as 394 (see Table 8 of the IHA
application). More recently Bacon et al.
(2009) estimated that 586, 287, and 413
ringed seals were harvest by villagers at
Barrow in 2000, 2001, and 2003,
respectively. Although ringed seals are
available year-round, the seismic survey
will not occur during the primary
period when these seals are typically
harvested. Also, the seismic survey will
be largely in offshore waters where the
activities will not influence ringed seals
in the nearshore areas where they are
hunted.
The spotted seal subsistence hunt
peaks in July and August, as indicated
by data from 1987 to 1990, but involves
few animals. Spotted seals typically
migrate south by October to overwinter
in the Bering Sea, Admiralty Bay, less
than 60 km (37.3 mi) to the east of
Barrow, is a location where spotted
seals are harvested. Spotted seals are
also occasionally hunted in the area off
Point Barrow and along the barrier
islands of Elson Lagoon to the east
(USDI/BLM, 2005). The average annual
spotted seal harvest by the community
of Barrow from 1987 to 1990 was one
animal (Braund et al., 1993; see Table 7
of the IHA application). More recently
however, Bacon et al. (2009) estimated
that 32, 7, and 12 spotted seals were
harvested by villagers at Barrow in
2000, 2001, and 2003, respectively.
Spotted seals become less abundant at
Nuiqsut and Kaktovik and few if any
spotted seal are harvested at these
villages. The seismic survey will
commence at least 115 km (71.5 mi)
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offshore from the preferred nearshore
harvest area of these seals.
Bearded seals, although not favored
for their meat, are important to
subsistence activities in Barrow because
of their skins. Six to nine bearded seal
hides are used by whalers to cover each
of the skin-covered boats traditionally
used for spring whaling. Because of
their valuable hides and large size,
bearded seals are specifically sought.
Bearded seals are harvested during the
summer months in the Beaufort Sea
(USDI/BLM, 2005). The animals inhabit
the environment around the ice floes in
the drifting ice pack, so hunting usually
occurs from boats in the drift ice.
Braund et al. (1993) estimated that 174
bearded seals were harvested annually
at Barrow from 1987 to 1990 (see Table
8 of the IHA application). More recently
Bacon et al. (2009) estimated that 728,
327, and 776 bearded seals were
harvested by villagers at Barrow in
2000, 2001, and 2003, respectively.
Braund et al. (1993) mapped the
majority of bearded seal harvest sites
from 1987 to 1990 as being within
approximately 24 km (14.9 mi) of Point
Barrow, well inshore of the proposed
survey which is to start approximately
115 km (71.5 mi) offshore and terminate
greater than 200 km (124.3 mi) offshore.
The average annual take of bearded
seals by the Barrow community from
1987 to 1990 was 174 (see Table 8 of the
IHA application).
people of Barrow to identify and avoid
areas of potential conflict.
• The USGS initiated contact with
NSB scientists and the chair of the
AEWC in mid-December, 2010 via an
emailed description of the proposed
survey that included components
intended to minimize potential
subsistence conflict.
• Invitations were extended
December 31, 2009 to members of the
NSB, AEWC, and North Slope
Communities to attend a teleconference
arranged for January 11, 2010. The
teleconference served as a venue to
promote understanding of the project
and discuss shareholder concerns.
Participants in the teleconference
included Harry Brower, chair of the
AEWC, and NSB wildlife biologist Dr.
Robert Suydam.
• To further promote cooperation
between the project researchers and the
community, Dr. Deborah Hutchinson
with USGS presented the proposed
survey at a meeting of the AEWC in
Barrow on February 11, 2010. Survey
plans were explained to local hunters
and whaling captains, including NSB
Department of Wildlife Management
biologists, Craig George and Dr. Robert
Suydam. Dr. Hutchinson consulted with
stakeholders about their concerns and
discussed the aspects of the survey
designed to mitigate impacts.
• Dr. Deborah Hutchinson of the
USGS emailed a summary of the topics
discussed during the teleconference and
TABLE 9—AVERAGE ANNUAL TAKE OF the AEWC meeting in Barrow to
MARINE MAMMALS OTHER THAN representatives of the NSB, AEWC, and
BOWHEAD WHALES HARVEST BY THE North Slope communities. These
COMMUNITY OF BARROW (COMPILED included:
Æ Surveying within U.S. waters is
BY LGL ALASKA RESEARCH ASSOCIscheduled early (approximately August
ATES, 2004)
11 to 19) to avoid conflict with hunters.
Æ The EA and IHA application have
Beluga
Ringed Bearded Spotted
been distributed as early as possible to
whales
seals
seals
seals
NSB and AEWC.
Æ A community observer will be
** 5
* 394
* 174
*1
present aboard the Healy during the
* Average annual harvest for years 1987 to
project.
1990 (Braund et al., 1993).
Æ Mitigation of the one crew transfer
** Average annual harvest for years 1962 to
1982 (MMS, 1996).
near Barrow in early September will be
arranged—probably through Barrow
Plan of Cooperation
Volunteer Search and Rescue.
The USGS has communicated with
• Representatives of the USGS
community authorities and residents of
attended the Arctic Open-water Meeting
Barrow to foster understanding of the
in Anchorage, March 22 to 24, 2010.
proposed survey. There are elements of
Æ Dr. Deborah Hutchinson presented
the proposed survey, intrinsic to the
information regarding the proposed
project that significantly limit the
survey to the public during the Openpotential conflict with subsistence
water meeting.
users. Operations will be conducted
Æ Dr. Jonathan Childs and Dr.
during early August before bowhead
Deborah Hutchinson also met with
whale hunting typically occurs off
stakeholders and agency representatives
Barrow and approximately 108 km (67.1 while at the meeting.
mi) offshore, farther offshore than
Subsequent meetings with whaling
traditional subsistence hunting grounds. captains, other community
USGS continues to work with the
representatives, the AEWC, NSB, and
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any other parties to the plan will be
held if necessary to coordinate the
planned seismic survey operation with
subsistence hunting activity. The USGS
has informed the chairman of the Alaska
Eskimo Whaling Committee (AEWC),
Harry Brower, Jr., of its survey plan.
As noted above and in the IHA
application, in the unlikely event that
subsistence hunting or fishing is
occurring within 5 km (3 mi) of the
project vessel tracklines, or where
potential impacts could occur, the
airgun operations will be suspended
until the vessel is greater than 5 km
away and otherwise not interfering with
subsistence activities.
erowe on DSK5CLS3C1PROD with NOTICES2
Endangered Species Act (ESA)
On May 21, 2010, USGS initiated
informal consultation, under Section 7
of the ESA, with the NMFS, Office of
Protected Resources, Endangered
Species Division, on this seismic
survey. Based on the information
provided by USGS, NMFS concurred
with their determination that the
activities conducted during the
proposed seismic survey are not likely
to adversely affect endangered whales in
the study area. No designated critical
habitat occurs within the action area for
this experiment, therefore, no critical
habitat will be affected by the proposed
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Jkt 220001
bathymetric and seismic surveys and
other associated activities.
National Environmental Policy Act
(NEPA)
USGS provided NMFS an
Environmental Assessment (EA)
analyzing the direct, indirect and
cumulative environmental impacts of
the proposed specified activities on
marine mammals including those listed
as threatened or endangered under the
ESA. The EA, prepared by LGL
Environmental Research Associated
(LGL) on behalf of USGS, is titled
‘‘Environmental Assessment of a Marine
Geophysical Survey of Parts of the
Arctic Ocean, August—September 2010
(EA)’’. NMFS has adopted the USGS’s
EA and issued a Finding of No
Significant Impact (FONSI) for the
issuance of the IHA.
Determinations
NMFS has determined that the impact
of conducting the specific marine
seismic survey activities described in
this notice and the IHA request in the
specific geographic region within the
U.S. EEZ and within the Arctic Ocean
may result, at worst, in a temporary
modification in behavior (Level B
harassment) of small numbers of marine
mammals. No take by injury (Level A
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60203
harassment), serious injury, or mortality
is anticipated, and take by harassment
will be at the lowest level practicable
due to incorporation of the mitigation
and monitoring measures mentioned
previously in this document. Further,
this activity is expected to result in a
negligible impact on the affected species
or stocks of marine mammals. NMFS
has determined that this proposed
activity will not have an unmitigable
impact on the availability of the affected
species or stock of marine mammals for
subsistence uses. USGS will coordinate
with local communities on
implementation of the Plan of
Cooperation.
As a result of these determinations,
NMFS issued an IHA to USGS for
conducting a marine seismic survey in
the Arctic Ocean from August to
September 2010, including the
previously mentioned mitigation,
monitoring, and reporting requirements.
The duration of the IHA does not exceed
one year from the date of its issuance.
Dated: September 22, 2010.
James H. Lecky,
Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. 2010–24335 Filed 9–28–10; 8:45 am]
BILLING CODE 3510–22–P
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Agencies
[Federal Register Volume 75, Number 188 (Wednesday, September 29, 2010)]
[Notices]
[Pages 60174-60203]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-24335]
[[Page 60173]]
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Part II
Department of Commerce
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National Oceanic and Atmospheric Administration
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Incidental Takes of Marine Mammals During Specified Activities; Marine
Seismic Survey in the Arctic Ocean, August to September, 2010; Notice
Federal Register / Vol. 75 , No. 188 / Wednesday, September 29, 2010
/ Notices
[[Page 60174]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XW05
Incidental Takes of Marine Mammals During Specified Activities;
Marine Seismic Survey in the Arctic Ocean, August to September, 2010
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; issuance of an incidental take authorization.
-----------------------------------------------------------------------
SUMMARY: In accordance with the Marine Mammal Protection Act (MMPA)
regulations, notification is hereby given that NMFS issued an
Incidental Harassment Authorization (IHA) to the U.S. Geological Survey
(USGS) for the take of small numbers of marine mammals, by Level B
harassment, incidental to conducting a marine seismic survey in the
Arctic Ocean during August to September, 2010.
DATES: Effective August 11, 2010, through October 21, 2010.
ADDRESSES: A copy of the IHA and application are available by writing
to P. Michael Payne, Chief, Permits, Conservation, and Education
Division, Office of Protected Resources, National Marine Fisheries
Service, 1315 East-West Highway, Silver Spring, MD 20910 or by
telephoning the contact listed here.
A copy of the application containing a list of the references used
in this document may be obtained by writing to the address specified
above, telephoning the contact listed below (see FOR FURTHER
INFORMATION CONTACT), or visiting the internet at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm. Documents cited in this
notice may be viewed, by appointment, during regular business hours, at
the aforementioned address.
FOR FURTHER INFORMATION CONTACT: Howard Goldstein or Jolie Harrison,
Office of Protected Resources, NMFS, 301-713-2289.
SUPPLEMENTARY INFORMATION:
Background
Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.)
direct the Secretary of Commerce (Secretary) to allow, upon request,
the incidental, but not intentional, taking of small numbers of marine
mammals by United States (U.S.) citizens who engage in a specified
activity (other than commercial fishing) within a specified
geographical region if certain findings are made and either regulations
are issued or, if the taking is limited to harassment, a notice of a
proposed authorization is provided to the public for review.
An authorization for incidental taking of small numbers of 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, and if the permissible methods of taking
and requirements pertaining to the mitigation, monitoring and reporting
of such takings are set forth. NMFS has defined ``negligible impact''
in 50 CFR 216.103 as `` * * * an impact resulting from the specified
activity that cannot be reasonably expected to, and is not reasonably
likely to, adversely affect the species or stock through effects on
annual rates of recruitment or survival.''
Section 101(a)(5)(D) of the MMPA established an expedited process
by which citizens of the United States can apply for an authorization
not to exceed one year to incidentally take small numbers of marine
mammals by harassment. Except with respect to certain activities not
pertinent here, the MMPA defines ``harassment'' as:
Any act of pursuit, torment, or annoyance which (i) has the
potential to injure a marine mammal or marine mammal stock in the
wild [``Level A harassment'']; or (ii) has the potential to disturb
a marine mammal or marine mammal stock in the wild by causing
disruption of behavioral patterns, including, but not limited to,
migration, breathing, nursing, breeding, feeding, or sheltering
[``Level B harassment''].
16 U.S.C. 1362(18)
Section 101(a)(5)(D) establishes a 45-day time limit for NMFS'
review of an application followed by a 30-day public notice and comment
period for any proposed authorizations for the incidental harassment of
marine mammals. Within 45 days of the close of the comment period, NMFS
must either issue or deny the authorization.
Summary of Request
On March 9, 2010, NMFS received an IHA application and a draft
Environmental Assessment (EA) from USGS for the taking, by Level B
harassment only, of small numbers of several species of marine mammals
incidental to conducting a marine seismic survey in the Arctic Ocean
during August to September, 2010. NMFS received a revised IHA
application on June 1, 2010, and a final EA on August 6, 2010.
Description of the Specified Activity
USGS is conducting a marine geophysical (seismic reflection/
refraction) and bathymetric survey in the Arctic Ocean in August and
September, 2010 (see Tables 1 and 2, and Figure 3 of the IHA
application). The survey is being conducted from the Canadian Coast
Guard (CCG) vessel CCGS Louis S. St. Laurent (St. Laurent) which will
be accompanied by the U.S. Coast Guard Cutter (USCGC) Healy, both of
which are polar-class icebreakers. Descriptions of the vessels and
their specifications are presented in Appendix A of the IHA
application. The two vessels operate in tandem in the presence of ice
but may diverge and operate independently in open water. Some minor
deviation of the dates is possible, depending on logistics and weather
(i.e., the cruise may depart earlier or be extended due to poor
weather; there could be extra days of seismic operations if collected
data are of sub-standard quality).
One CCG helicopter is available for deployment from the St. Laurent
for ice reconnaissance and crew transfers between the vessels during
survey operations. Helicopter transfer of crew from the Healy is also
planned for approximately one day during a ship-to-shore crew change at
Barrow, Alaska at the end of the survey. The helicopter operations in
Barrow will be conducted under Department of Interior (DOI) contract.
Daily helicopter operations are anticipated pending weather conditions.
Spot bathymetry will also be conducted from the helicopter outside U.S.
waters.
Acoustic sources onboard the St. Laurent include an airgun array
comprised of three Sercel G-airguns and a Knudsen 320BR ``Chirp'' pulse
echosounder operating at 12 kHz. The St. Laurent also tows a 3 to 5 kHz
sub-bottom profiler while in open water and when not working with the
Healy. The airgun array consists of two 500 in\3\ and one 150 in\3\
airguns for an overall discharge of 1,150 in\3\. Table 2 of the IHA
application presents different sound pressure level (SPL) radii of the
airgun array. Acoustic sources being operated on the St. Laurent are
described in detail in Section VII and Appendix B in the IHA
application. The seismic array and a hydrophone streamer towed from the
St. Laurent operate under the provisions of a Canadian authorization
based on Canada's environmental assessment of the proposed survey while
in Canadian or international waters, and under the provisions of an IHA
issued to the USGS by NMFS in U.S. waters. NMFS cannot issue an IHA
directly to a non-U.S.
[[Page 60175]]
citizen, however, the Geological Survey of Canada (GSC) has written a
Categorical Declaration stating that ``while in U.S. waters (i.e., the
U.S. 200 mile Exclusive Economic Zone), the GSC will comply with any
and all environmental mitigation measures required by the U.S. NMFS
and/or the U.S. Fish and Wildlife Service.'' The St. Laurent follows
the lead of the Healy. The Healy breaks and clears ice approximately
1.6 to 3.2 km (1 to 2 miles [mi]) in advance of the St. Laurent. In
situations where the array (and hydrophone streamer) cannot be towed
safely due to ice cover, the St. Laurent may escort the Healy. The
Healy uses a multi-beam echosounder (Kongsberg EM122), a sub-bottom
profiler (Knudsen 3.5 kHz Chirp), and a ``piloting'' echosounder (ODEC
1500) continuously when underway and during the seismic profiling.
Acoustic Doppler current profilers (75 kHz and 150 kHz) may also be
used on the Healy. The Healy's acoustic systems are described in
further detail in Section VII and Appendix B of the IHA application.
In addition to the hydrophone streamer, marine sonobuoys are
deployed to acquire wide angle reflection and refraction data for
velocity determination to convert seismic reflection travel time to
depth. Sonobuoys are deployed off the stern of the St. Laurent
approximately every eight hours during seismic operations with as many
as three deployments per day. The sonobuoy's hydrophone activates at a
water depth of approximately 60 m (196.9 ft) and seismic signals are
communicated via radio to the St. Laurent. The sonobuoys are pre-set to
scuttle (i.e., deliberately sink) eight hours after activation.
The program within U.S. waters consists of approximately 806 km
(500.8 mi) of survey transect line, not including transits when the
airguns are not operating (see Figure 1 and Table 1 of the IHA
application). U.S. priorities include another 997 km (619.5 mi) of
survey lines north of the U.S. Exclusive Economic Zone (EEZ), for a
total of 1,804 km (1,121 mi) of tracklines of interest to the U.S.
Table 1 of the IHA application lists all U.S. priority tracklines;
Figure 1 of the IHA application includes all U.S. priority tracks and
the area of interest to Canada near the proposed U.S. tracklines. Water
depths within the U.S. study area range from approximately 1,900 to
4,000 m (6,233.5 to 13,123.4 ft) (see Figure 1 of the IHA application).
There may be additional seismic operations associated with airgun
testing, start-up, and repeat coverage of any areas where initial data
quality is sub-standard. The tracklines being surveyed in U.S. waters
include the southern 263.8 km (164 mi) of the line that runs North-
South in the western EEZ, the southern 264.5 km (164.4 mi) of the line
that runs North--South in the central EEZ, and 277.7 km (172.6 mi) of
trackline that connects the two (see Table 1 here and in Figure 1 of
the IHA application). The IHA application requested the authorization
of incidental takes of marine mammals for activities within U.S.
waters. The survey line nearest to shore in U.S. waters is
approximately 116 km (63 nmi) offshore at its closest point.
Table 1--U.S. Priority Tracklines for USGS and Geological Survey of Canada (GSC) 2010 Extended Continental Shelf
Survey in the Northern Beaufort Sea and Arctic Ocean
----------------------------------------------------------------------------------------------------------------
Time (Hour
Location End point 1 End point 2 Kilometer Nautical mile [hr]) @ 4 nmi/
(km) (nmi) hr
----------------------------------------------------------------------------------------------------------------
NS in central EEZ (south).... 71.22[deg] 72.27[deg] 118 64 16
North; North;
145.17[deg] 145.41[deg]
West. West.
NS in central EEZ (north).... 72.27[deg] 73.92[deg] 183 100 25
North; North;
145.41[deg] 145.30[deg]
West. West.
Central-western EEZ connector 73.92[deg] 71.84[deg] 317 171 43
North; North;
145.30[deg] 151.82[deg]
West. West.
NS in western EEZ............ 71.84[deg] 74.32[deg] 281 152 39
North; North;
151.82[deg] 150.30[deg]
West. West.
South Northwind Ridge........ 74.32[deg] 74.96[deg] 239 129 32
North; North;
150.30[deg] 158.01[deg]
West. West.
Northwind Ridge connector.... 74.96[deg] 76.30[deg] 161 87 22
North; North;
158.01[deg] 155.88[deg]
West. West.
Mid-Northwind Ridge.......... 76.30[deg] 75.41[deg] 274 148 37
North; North;
155.88[deg] 146.50[deg]
West. West.
Northwind Ridge connector.... 75.41[deg] 76.57[deg] 129 70 17
North; North;
146.50[deg] 146.82[deg]
West. West.
Mid-Northwind Ridge.......... 76.57[deg] 76.49[deg] 102 55 14
North; North;
146.82[deg] 150.73[deg]
West. West.
-----------------------------------------------
Totals................... ................ ............... 1,804 976 245
----------------------------------------------------------------------------------------------------------------
The two vessels operate cooperatively during the seismic survey.
The St. Laurent conducts seismic operations using an airgun array and
also operates a 12 kHz Chirp echosounder. The St. Laurent also operates
a 3 to 5 kHz sub-bottom profiler in open water when not working with
the Healy. The Healy normally escorts the St. Laurent in ice cover, and
continuously operates a bathymetric multi-beam echosounder, a 3.5 kHz
Chirp sub-bottom profiler, a piloting echosounder, and two acoustic
Doppler current profilers.
The St. Laurent accessed the survey area from Canada and
rendezvoused with the Healy on approximately August 10, 2010; the Healy
approached the survey area from the Bering Straits. The St. Laurent
deploys a relatively small airgun array comprised of three G-airguns
and a single hydrophone streamer approximately 300 m (984 ft) in
length. The airgun array consists of two 500 in \3\ and one 150 in \3\
airguns for an overall discharge of 1,150 in \3\. The St. Laurent
follows the lead of the Healy which operates approximately 1.9 to 3.8
km (1 to 2 nmi) ahead of the St. Laurent. In ice conditions where
seismic gear cannot be safely towed, the St. Laurent escorts the Healy
to optimize multi-beam bathymetry data collection. If extended open-
water conditions are encountered, Healy and St. Laurent may operate
independently. After completion of the survey the St. Laurent will
return to port in Canada, and the Healy will change crew at Barrow via
helicopter or surface conveyance before continuing on another project.
Vessel Specifications
The CCGS St. Laurent was built in 1969 by Canadian Vickers Ltd. in
Montreal, Quebec, and underwent an extensive modernization in Halifax,
Nova Scotia between 1988 to 1993. The St. Laurent is based at CCG Base
Dartmouth in Dartmouth, Nova Scotia. Current vessel activities involve
summer voyages to the Canadian Arctic for sealifts to various coastal
communities and scientific expeditions. A description of the St.
Laurent with vessel specifications is presented in Appendix A of the
IHA application and is available online at: https://www.ccg-
[[Page 60176]]
gcc.gc.ca/eng/Fleet/Vessels?id=1111&info=5&subinfo.
The Healy is designed to conduct a wide range of research
activities, providing more than 390.2 m \2\ (4,200 ft \2\) of
scientific laboratory space, numerous electronic sensor systems,
oceanographic winches, and accommodations for up to 50 scientists. The
Healy is designed to break 1.4 m (4.5 ft) of ice continuously at 5.6
km/hour (three knots) and can operate in temperatures as low as -45.6 C
(-50 degrees F). The Healy is a USCG icebreaker, capable of traveling
at 5.6 km/hour (three knots) through 1.4 m (4.5 ft) of ice. A ``Central
Power Plant,'' four Sultzer 12Z AU40S diesel generators, provides
electric power for propulsion and ship's services through a 60 Hz,
three-phase common bus distribution system. Propulsion power is
provided by two electric AC Synchronous, 11.2 MW drive motors, fed from
the common bus through a Cycloconverter system, that turn two fixed-
pitch, four-bladed propellers.
The science community provided invaluable input on lab lay-outs and
science capabilities during design and construction of the ship. The
Healy is also a capable platform for supporting other potential
missions in the polar regions, including logistics, search and rescue,
ship escort, environmental protection, and enforcement of laws and
treaties, and will also serve as the platform from which vessel-based
Protected Species Observers (PSOs) will watch for marine mammals before
and during airgun operations. Other details of the Healy can be found
in Appendix A of the IHA application.
NMFS believes that the realistic possibility of a ship-strike of a
marine mammal by the vessel during research operations and in-transit
during the proposed survey is discountable. The probability of a ship
strike resulting in an injury or mortality of an animal has been
associated with ship speed; however, it is highly unlikely that the
proposed seismic survey would increase the rate of injury, serious
injury, or mortality given the St. Laurent and Healy's slow survey
speed.
Acoustic Source Specifications--Seismic Airguns and Radii
The seismic source for the seismic survey is comprised of three
Sercel G-airguns with a total volume of 1,150 in \3\. The three-airgun
array is comprised of two 500 in \3\ and one 150 in \3\ G-airguns in a
triangular configuration (see Figure B-1 in the IHA application). The
single 150 in \3\ G-airgun is used if a power-down is necessary for
mitigation. The G-airgun array is towed behind the St. Laurent at a
depth of approximately 11 m (36.1 ft) (see Figure B-2 in the IHA
application) along predetermined lines in water depths ranging from
1,900 to 4,000 m (6,233.6 to 13,123.4 ft). One streamer approximately
232 m (761.2 ft) in length with a single hydrophone is towed behind the
airgun array at a depth of approximately 9 to 30 m (29.5 to 98.4 ft).
A square wave trigger signal is supplied to the firing system
hardware by a FEI-Zyfer GPStarplus Clock model 565, based on GPS time
(typically at approximately 14 to 20 sec intervals). Vessel speed is
approximately 10.2 km/hour (5.5 knots) resulting in a shot interval
ranging from approximately 39 to 56 m (128 to 183.7 ft). G-airgun
firing and synchronization are controlled by a RealTime Systems
LongShot fire controller, which sends a voltage to the airgun solenoid
to trigger firing with approximately 54.8 ms delay between trigger and
fire point.
Pressurized air for the pneumatic G-airguns is supplied by two
Hurricane compressors, model 6T-276-44SB/2500. These are air cooled,
containerized compressor systems. Each compressor is powered by a C13
Caterpillar engine which turns a rotary screw first stage compressor
and a three stage piston compressor capable of developing a total air
volume of 600 SCFM @ 2,500 pounds per square inch (PSI). The seismic
system is operated at 1,950 PSI and one compressor could easily supply
sufficient volume of air under appropriate pressure.
Seismic acquisition requires a watchkeeper in the seismic lab and
another in the compressor container. The seismic lab watchkeeper is
responsible for data acquisition/recording, watching over-the-side
equipment, airgun firing and log keeping. A remote screen permits
monitoring of compressor pressures and alerts, as well as communication
with the compressor watchkeeper. The compressor watchkeeper is required
to monitor the compressor for any emergency shut-down and provide
general maintenance that might be required during operations.
Sound level radii for the proposed three airgun array were measured
in 2009 during a seismic calibration (Mosher et al., 2009; Roth and
Schmidt, 2010). A transmission loss model was then constructed assuming
spherical (20LogR) spreading and using the source level estimate 235 dB
re 1 [mu]Pa (rms) 0-peak; 225 dB re 1 [mu]Pa (rms) from the
measurements. The use of 20LogR spreading fit the data well out to
approximately 1 km (0.6 mi) where variability in measured vales
increased (see Appendix B in the IHA application for more details and a
figure of the transmission loss model compared to the measurement
data). Additionally, the Gundalf modeling package was used to model the
airgun array and estimated a source level output of 236.7 dB 0-peak
(226.7 dB [rms]). Using this slightly stronger source level estimate
and a 20LogR spreading the 180 and 190 dB (rms) radii are estimated to
be 216 m (708.7 ft) and 68 m (223.1 ft), respectively. As a
conservative measure for the proposed safety radii, the sound level
radii indicated by the empirical data and source models have been
increased to 500 m (1,640.4 ft) for the 180 dB isopleths and to 100 m
(328 ft) of the 190 dB isopleths.
The rms received levels that are used as impact criteria for marine
mammals are not directly comparable to the peak or peak-to-peak values
normally used to characterize source levels of airguns. The measurement
units used above to describe the airgun source, peak or peak-to-peak
dB, are always higher than the rms dB referred to in much of the
biological literature. A measured received level of 160 dB (rms) in the
far field would typically correspond to a peak measurement of about 170
to 172 dB, at the same location (Greene, 1997; McCauley et al., 1998,
2000). The precise difference between rms and peak or peak-to-peak
values for a given pulse depends on the frequency content and duration
of the pulse, among other factors. However, the rms level is always
lower than the peak or peak-to-peak level for an airgun-type source.
[[Page 60177]]
Table 2--Distances to Which Sound Levels Greater Than or Equal to 190, 180, and 160 dB re 1 [mu]Pa (rms) Could
Be Received in Deep (Greater Than 1,000 m) Water During the Survey in the Arctic Ocean, August 7, to September
3, 2010
----------------------------------------------------------------------------------------------------------------
Tow depth Predicted received RMS distances (m)
Source and volume (m) ice/ Water depth --------------------------------------
open water 190 dB 180 dB 160 dB
----------------------------------------------------------------------------------------------------------------
Single Mitigation Airgun (150 in\3\) 11/6-7 Deep (>1,000 m)....... 30 75 750
Three G-airguns (1,150 in\3\)....... 11/6-7 Deep (>1,000 m)....... 100 500 2,500
----------------------------------------------------------------------------------------------------------------
Acoustic Source Specifications--Multibeam Echosounders (MBES), Sub-
Bottom Profilers (SBP) and Acoustic Doppler Current Profilers (ADCP)
Along with the airgun operations, additional acoustic systems that
are operated during the cruise include a 12 kHz Chirp echosounder and a
3-5 kHz SBP from the St. Laurent. The Healy operates a 12 kHz Kongsberg
MBES, a Knudsen 320BR profiler, a piloting echosounder, and two ADCPs.
These sources are operated throughout most of the cruise to map
bathymetry, as necessary, to meet the geophysical science objectives.
During seismic operations, these sources are deployed from the St.
Laurent and the Healy and generally operate simultaneously with the
airgun array deployed from the St. Laurent.
The Knudsen 320BR echosounder provides information on depth and
bottom profile. The Knudsen 320BR is a dual-frequency system with
operating frequencies of 3.5 and 12 kHz, however, the unit functions at
the higher frequency, 12 kHz, because the 3.5 kHz transducer is not
installed.
While the Knudsen 320BR operates at 12 kHz, its calculated maximum
source level (downward) is 215 dB re [mu]Pa at 1 m. The pulse duration
is typically 1.5 to 5 ms with a bandwidth of 3 kHz (FM sweep from 3 kHz
to 6 kHz). The repetition rate is range dependent, but the maximum is a
one percent duty cycle. Typical repetition rate is between \1/2\ s (in
shallow water) to 8 s in deep water. A single 12 kHz transducer (sub-
bottom) array, consisting of 16 elements in a 4x4 array will be used
for the Knudsen 320BR. The 12 kHz transducer (TC-12/34) emits a conical
beam with a width of 30[deg].
The 3-5 kHz chirp SBP is towed by and operated from the St. Laurent
in open water when the St. Laurent is not working in tandem with the
Healy. The SBP provides information about sedimentary features and
bottom topography. The chirp system has a maximum 7.2 kW transmit
capacity into the towed array. The energy from the towed unit is
directed downward by an array of eight transducers in a conical
beamwidth of 80 degrees. The interval between pulses is no less than
one pulse per second. SBPs of that frequency can produce sound levels
200 to 230 dB re 1 [mu]Pa at 1 m (Richardson et al., 1995).
The Kongsberg EM 122 MBES operates at 10.5 to 13 (usually 12) kHz
and is hull-mounted on the Healy. The transmitting beamwidth is 1[deg]
or 2[deg] fore-aft and 150[deg] athwartship. The maximum source level
is 242 dB re 1 [mu]Pam (rms). Each ``ping'' consists of eight (in water
greater than 1,000 m deep) or four (less than 1,000 m) successive fan-
shaped transmissions, each ensonifying a sector that extends 1[deg]
fore-aft. Continuous-wave (CW) pulses increase from two to 15 ms long
in water depths up to 2,600 m (8,530 ft), and FM chirp pulses up to 100
ms long are used in water greater than 2,600 m (8,530 ft). The
successive transmissions span an overall cross-track angular extent of
about 150[deg], with 2 ms gaps between pulses for successive sectors.
The Knudsen 320BR hydrographic SBP provides information on
sedimentary layering, down to between 20 and 70 m (65.6 to 229.7 ft),
depending on bottom type and slope. The Knudsen 320 BR is a dual-
frequency system with operating frequencies of 3.5 and 12 kHz; only the
low frequency is being used during this survey. At 3.5 kHz, the maximum
output power into the transducer array, as wired on the Healy (where
the array impedance is approximately 125 ohms), is approximately 6,000
watts (electrical), which results in a maximum source level of 221 dB
re 1 [micro]Pa at 1 m downward. Pulse lengths range from 1.5 to 24 ms
with a bandwidth of 3 kHz (FM sweep from 3 kHz to 6 kHz). The
repetition rate is range dependent, but the maximum is a one percent
duty cycle. Typical repetition rate is between \1/2\ s (in shallow
water) to 8 s in deep water. The 3.5 kHz transducer array on the Healy,
consisting of 16 (TR109) elements in a 4x4 array, is being used for the
Knudsen 320BR. At 3.5 kHz the SBP emits a downward conical beam with a
width of approximately 26[deg].
The piloting echosounder on the Healy is an Ocean Data Equipment
Corporation (ODEC) Bathy-1500 that provides information on water depth
below the vessel. The ODEC system has a maximum 2 kW transmit capacity
into the transducer and has two operating modes, single or interleaved
dual frequency, with available frequencies of 12, 24, 33, 40, 100, and
200 kHz.
The 150 kHz ADCP has a minimum ping rate of 0.65 ms. There are four
beam sectors and each beamwidth is 3[deg]. The pointing angle for each
beam is 30[deg] off from vertical with one each to port, starboard,
forward, and aft. The four beams do not overlap. The 150 kHz ADCP's
maximum depth range is 300 m (984.3 ft).
The Ocean Surveyor 75 is an ADCP operating at a frequency of 75
kHz, producing a ping every 1.4 s. The system is a four-beam phased
array with a beam angle of 30[deg]. Each beam has a width of 4[deg] and
there is no overlap. Maximum output power is 1 kW with a maximum depth
range of 700 m (2,296.6 ft).
Acoustic Source Specifications--Icebreaking
Icebreaking is considered by NMFS to be a continuous sound and NMFS
estimates that harassment occurs when marine mammals are exposed to
continuous sounds at a received sound level of 120 dB SPL or above.
Potential takes of marine mammals may ensue from icebreaking activity
in which the Healy is expected to engage outside of U.S. waters, i.e.,
north of approximately 74.1[deg] North. While breaking ice, the noise
from the ship, including impact with ice, engine noise, and propeller
cavitation, will exceed 120 dB (rms) continuously. If icebreaking does
occur in U.S. waters, USGS expects it will occur during seismic
operations. The exclusion zone (EZ) for the marine mammal Level B
harassment threshold during the proposed seismic activities is greater
than the calculated radius during icebreaking. Therefore, if the Healy
breaks ice during seismic operations within the U.S. waters, the
greater radius, i.e., that for seismic operations, supersedes that for
icebreaking, so no
[[Page 60178]]
additional takes have been estimated within U.S. waters.
Dates, Duration, and Specific Geographic Area
The seismic survey is being conducted for approximately 36 days
from approximately August 2 to September 6, 2010. The approximately 806
km (501 mi) of tracklines within U.S. waters will be surveyed first.
These survey lines are expected to be completed by approximately August
19, 2010. The seismic vessel St. Laurent departed from Kugluktuk,
Nunavut, Canada on August 6, 2010 and returned to the same port on
approximately September 15, 2010. The Healy departed from Dutch Harbor,
Alaska on August 2, 2010, to meet the St. Laurent on August 10, 2010.
After completion of this survey, the Healy is changing crew through
Barrow via helicopter or surface vessel on September 6, 2010 (see Table
3 of the IHA application). The entire survey area will be bounded
approximately by 145[deg] to 158[deg] West longitude and 71[deg] to
84[deg] North latitude in water depths ranging from approximately 1,900
to 4,000 m (6,234 to 13,123 ft) (see Figure 1 and Table 1 of the IHA
application). Ice conditions are expected to range from open water to
10/10 ice cover. See Table 3 of the IHA application for a synopsis of
the 2010 St. Laurent and Healy Extended Continental Shelf expeditions
in the Arctic Ocean, August 2 to September 15, 2010.
Icebreaking outside U.S. waters will occur between the latitudes of
approximately 74[deg] to 84[deg] North. Vessel operations and ice
conditions from similar survey activities and timing in 2008 and 2009
were used to estimate the amount of icebreaking (in trackline km) that
is likely to occur in 2010. USGS expects that the St. Laurent and the
Healy will be working in tandem through the ice for a maximum of 23 to
25 days while outside of U.S. waters. The average distance travelled in
2008 and 2009 when the Healy broke ice for the St. Laurent was 135 km/
day (83.9 mi/day). Based on the 23 to 25 day period of icebreaking,
USGS calculated that, at most approximately 3,102 to 3,372 km (1,927.5
to 2,095.3 mi) of vessel trackline may involve icebreaking. This
calculation is likely an overestimation because icebreakers often
follow leads when they are available and thus do not break ice at all
times.
Table 3--Projected 2010 Icebreaking Effort for USGS/GSC 2010 Extended Continental Shelf Survey in the Northern
Beaufort Sea and Arctic Ocean
----------------------------------------------------------------------------------------------------------------
Two-Ship Two-Ship
operations operations km/day
(days) (km)
----------------------------------------------------------------------------------------------------------------
2008............................................................ 19 2,469 130
2009............................................................ 27 37,744 140
Average 2008 to 2009............................................ 23 3,122 135
Projected 2010.................................................. 23-25 3,102-3,372 ..............
----------------------------------------------------------------------------------------------------------------
Comments and Responses
A Notice of Receipt of the USGS application and proposed IHA was
published in the Federal Register on July 8, 2010 (75 FR 39336). During
the comment period, NMFS received comments from the Marine Mammal
Commission (Commission), the North Slope Borough (NSB) Office of the
Mayor, and the Alaska Eskimo Whaling Commission (AEWC). The public
comments can be found online at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm. The following are their comments, and NMFS's responses.
Comment 1: The Commission recommends that NMFS approve the
requested IHA, provided NMFS ascertain who will be responsible for
operating the Canadian vessel and the airguns and other instruments
deployed from the St. Laurent and issue an IHA for these activities
only if a U.S. agency or U.S. citizen(s) will be conducting those
operations.
Response: USGS's EA has clarified the roles and responsibilities of
the Canadian vessel St. Laurent while operating within and outside U.S.
waters:
``The activity that the USGS is funding and undertaking in both the
U.S. waters (maritime zones) and the high seas is to collect multi-
beam, associated chirp sub-bottom data, and possibly sediment and rock
samples both within and outside the 370.4 km (200 nmi) limit, as well
as to break ice for the St. Laurent during operations in ice-covered
area. The St. Laurent is a vessel entitled to sovereign immunity under
international law, operated by the CCG with a seismic system owned and
operated by Natural Resources Canada, and therefore not under the
jurisdiction of U.S. laws or regulations outside the U.S. maritime
zones where the U.S. has exclusive rights and jurisdiction. The USGS is
acting as the responsible agency for MMPA, ESA, and NEPA for the St.
Laurent while the St. Laurent is collecting seismic data within the
U.S. EEZ. The operators of the seismic equipment on the St. Laurent
have written a Categorical Declaration that, for operations in U.S.
waters (i.e., within the U.S. EEZ), they will comply with any and all
environmental mitigation measures required by NMFS and/or the U.S. Fish
and Wildlife Service (USFWS) (see Appendix C of the EA). There are no
U.S. Federal funds that are supporting the costs of operating St.
Laurent, or its seismic gear'' (see p. 2 to 3 of the EA).
The GSC is collecting seismic data in U.S. waters at the request of
the U.S. and would not otherwise be operating in U.S. waters. Dr.
Jonathan Childs, USGS liaison aboard the St. Laurent, will be
responsible for establishing the start and end points of the lines
within U.S. waters and for compliance with conditions of the IHA. The
Categorical Declaration from Natural Resources Canada, United Nations
Convention on the Law of the Sea (UNCLOS) Program (see p. 116 in
Appendix C of the EA) further states:
``While in U.S. waters (i.e., the U.S. EEZ), the GSC operators will
comply with any and all environmental mitigation measures required by
the NMFS and/or USFWS. A NMFS approved PSO and a U.S. liaison aboard
the St. Laurent will be responsible for ensuring that all mitigation
measures required by NMFS and/or USFWS are implemented while the St.
Laurent operates in U.S. waters.''
``While operating in U.S. waters, the GSC operators of the seismic
profiling system categorically consent to comply with all applicable
U.S. laws, including the MMPA and the ESA, as well as any terms and
conditions that may be required under an IHA issued by NMFS and any
measures that may arise from
[[Page 60179]]
ESA consultations with NMFS and/or USFWS. Operation of the seismic
profiling system includes conditions under which the system will be
turned on and operation continued or ceased in the presence of marine
mammals (including polar bears), and the diversion of scientific
tracklines for avoidance of observed wildlife. This declaration should
in no way be constructed to influence or alter the safe operation of
the vessel which is at the sole discretion of the CCG and its
Commanding Officer.''
Comment 2: The Commission recommends that NMFS approve the
requested IHA, provided NMFS work with the applicant to re-estimate
exposures for ice-breaking activities based upon the total area that
may be exposed to sound levels greater than or equal to 120 dB re 1
[mu]Pa (rms).
Response: The Commission's concerns are that the USGS application
states that an area of water 4,109 km\2\ (1,586.5 mi\2\) will be
exposed to sound levels >=120 dB re 1 [mu]Pa (rms) but that the marine
mammal ``takes'' are estimated using a larger number of 5,137 km\2\
(1,983.4 mi\2\) to allow for turns, repetition of certain tracklines
because of poor data quality or minor changes in survey design (this
larger number represents an uncertainty estimate of approximately 20
percent). A critical clarification is that the 4,109 km\2\ and 5,137
km\2\ numbers are for estimating the area of takes within U.S. waters
based on seismic operations, using a radius of approximately 2,500 m
(8,202 ft) (see page 69 of the EA) for the >=160 dB re 1 [micro]Pa
(rms) isopleths, and not on the area ensonified by continuous noise of
icebreaking at >=120 dB re 1 [mu]Pa (rms). This approach was taken
because the area of take for the seismic source >=160 dB re 1 [mu]Pa
(rms), estimated at approximately a 2,500 m (8,202 ft) radius was
greater than that estimated for >=120 dB re 1 [mu]Pa (rms) of
continuous sound from icebreaking, estimated at 1,750 m (5,741.5 ft)
radius (see page 213 of the EA). The estimated area ensonified for
icebreaking outside of U.S. waters is 11,802 km\2\ (4,556.8 mi\2\) (see
p. 213 of the EA).
A point of confusion in this clarification is that the original
request from NMFS was to estimate takes from icebreaking, rather than
the total area exposed to sound levels >=120 dB re 1 [mu]Pa (rms). The
addendum on icebreaking (see Appendix J of the EA) only estimated takes
for the Healy breaking ice outside of U.S. waters because there would
be no additional takes for the sound of icebreaking within U.S. waters
beyond those estimated for the seismic source.
One can calculate the area of potential icebreaking within U.S.
waters by using the estimated track length (approximately 806 km [500.8
mi], page 69 of the EA) and the >=120 dB [mu]Pa (rms) radius, estimated
at 1,750 m (5,741.5 ft) (see page 213 of the EA), to get an ensonified
area of 2,821 km\2\ (1,089.2 mi\2\), which, with an additional
uncertainty estimate of 20 percent totals 3,385 km\2\ (1,307 mi\2\).
This number is still smaller than either the 4,109 km\2\ or 5,137 km\2\
numbers cited in the comments from the Commission.
It is important to also clarify that (a) the USGS estimated
icebreaking assuming that maximum noise of icebreaking would occur
along the total length of tracklines. The preferred strategy operating
in the ice is to follow leads whenever possible, which reduces the
total icebreaking effort. Canadian and U.S. ice observers and analysts
are aboard both vessels to select paths through the ice to minimize
icebreaking; (b) for some part of the cruise, depending on ice
conditions, the St. Laurent will be leading Healy so that high-quality
multi-beam data can be collected, further reducing the amount of
icebreaking the Healy will be doing (and therefore reducing the area of
ensonfication for >=120 dB re 1 [mu]Pa [rms]). The estimates of the
area of ensonification in the EA and IHA do not include a correction
for this type of data acquisition. Hence the area of ensonification is
likely to be overestimated; (c) the tracklines are laid out to enable
flexibility in where the ship may navigate through the ice, maximizing
the opportunities to follow leads and reduce the requirement for
icebreaking and therefore minimize the noise of icebreaking. Under
international law as reflected in Article 76 of UNCLOS, the ECS outer
limit points are to be no more than 111.1 km (60 nmi) apart. The cruise
tracks are planned 92.6 km (50 nmi) apart or less so that the vessels
can deviate approximately 18.5 km (10 nmi) either side of the track to
follow leads; and (d) based on the latest ice imagery for August 3,
2010, there will probably be no need to break ice within U.S. waters.
As of August 3, 2010, http;//arctic.atmos.uiuc.edu/cryosphere/NEWIMAGES/arctic.seaice.color.000.png shows the ice extent in the area
north of the Alaska coast to be mostly open water. The PSOs aboard the
Healy will be monitoring actual takes from icebreaking during the
cruise, which can be compared with takes estimated and authorized in
the IHA.
Comment 3: The Commission recommends that NMFS approve the
requested IHA, provided NMFS advise the applicant to consult with the
USFWS regarding the need for a separate incidental taking authorization
for walruses and polar bears.
Response: On May 7, 2010, USGS requested that the USFWS review the
operations for the summer 2010 Arctic Ocean geophysical experiment for
potential impacts on Pacific walruses and polar bears. Given the
USFWS's understanding of polar bear and walrus distribution, the
planned travel routes and locations of the activity, the USFWS believe
that it is unlikely the proposed studies will result in any major
disturbances or impacts to individual polar bears or walruses.
Considering the relatively low likelihood of encountering polar bears
or walruses, along with the limited impact and anticipated responses of
affected animals that would likely ensue from an encounter with either
or both vessels, the USFWS has determined that an incidental take
authorization is not necessary for this project. See the USFWS's
informal ESA Section 7 consultation letter regarding walruses and polar
bears in Appendix E of the EA (p. 128 to 132).
Comment 4: The Commission recommends that NMFS approve the
requested IHA, provided NMFS provide additional justification for its
preliminary determination that the planned monitoring program will be
sufficient to detect, with a high level of confidence, all marine
mammals within or entering the identified exclusion zones (EZs). At a
minimum, such justification should (1) identify those species that it
believes can be detected with a high degree of confidence using visual
monitoring only, (2) describe detection probability as a function of
distance from the vessel, (3) describe changes in detection probability
under various sea state and weather conditions and at night, and (4)
explain how close to the vessel marine mammals must be for observer to
achieve the anticipated high nighttime detection rate.
Response: NMFS believes that the planned monitoring program will be
sufficient to visually detect, with reasonable certainty, most marine
mammals within or entering identified EZs. This monitoring, along with
the required mitigation measures, will help ensure the authorized
taking effects the least practicable adverse impact on the affected
species or stocks and will have a negligible impact on the affected
species or stocks.
Until proven technological advances are made, nighttime mitigation
measures during operations include combinations of the use of PSOs and
[[Page 60180]]
night vision devices (NVDs). Should the airgun array be powered-down,
it is believed that the operation of a single airgun continues to serve
as a sound source deterrent to marine mammals. In the event of a
complete shut-down of the airgun array, for mitigation or repairs,
airgun operations are suspended until nautical twilight-dawn (when PSOs
are able to clear the EZ). Airgun operations do not begin until the
entire EZ radius is visible for at least 30 minutes. In all likelihood
there will be no nighttime start-ups for the time that the seismic data
are collected in U.S. waters (mid-August), when 24 hour daylight is
still occurring.
Comment 5: The Commission recommends that NMFS approve the
requested IHA, provided NMFS clarify the meaning of the qualifiers
``when practical,'' ``if practical,'' and ``when feasible'' to indicate
how often and under what specific conditions the applicant expects to
use (1) two Protected Species Observer (PSOs) to monitor the EZ for
marine mammals during daytime operations and nighttime start-ups of the
airguns, (2) crew members to assist PSOs in detecting marine mammals
and implementing mitigation requirements, and (3) PSOs during daytime
periods to compare sighting rates and animal behavior during times when
seismic airguns are and are not operating.
Response: The St. Laurent and Healy will carry trained, NMFS-
qualified and experienced PSOs for the seismic study involving the use
of airguns and icebreaking for the upcoming proposed project. PSOs are
appointed by USGS with NMFS concurrence. USGS will utilize vessel-based
PSOs to watch for and monitor marine mammals near the icebreaking and
seismic source vessels during all daytime airgun operations and before
and during start-ups of the airguns day or night. PSOs will have access
to reticle binoculars and NVDs to scan the area around each vessel.
PSOs will alternate between binoculars and the naked eye to avoid eye
fatigue. During all monitoring periods, PSOs will be on duty from
observation locations that allow for optimal monitoring capabilities.
During meal times and restroom breaks it is sometime difficult to have
the full complement of PSOs on effort, but at least one PSO will be on
watch during those brief times. The complement of PSOs rotates shifts,
with duty shift lasting generally one to four hours.
Regarding the Commission's sub-comment (1), the intention and
requirement is for two PSOs to stand watch during all seismic
operations in U.S. waters, including cold start and ramp-ups. Only one
PSO is on watch during daylight non-seismic operations. Two U.S. PSOs
will join the St. Laurent before seismic operations begin in U.S.
waters so that there will be five PSOs aboard the St. Laurent for all
seismic data collected in U.S. waters. The restriction on the U.S. PSOs
not standing watch for more than four hours at a time and the as yet
unknown schedules of the Canadian watches makes actual schedules at
this time unknown, hence the qualifiers ``when practical,'' etc., are
used to account for this uncertainty. There may also be short periods
of time, for example during mandatory fire and boat safety drills, when
the PSOs on watch must leave their observing stations. It is the
responsibility of the U.S. liaison aboard the St. Laurent working with
the Canadian counterparts to develop a watch schedule consistent with
the requirements of the IHA, especially for the ramp-ups, whether
during the day or night. In all likelihood there will be no nighttime
start-ups for the time that the seismic data are collected in U.S.
waters (mid-August), when 24 hour daylight is still occurring.
Canada will follow its own permitting requirements for watches and
start-ups when operating outside of U.S. waters. The two U.S. PSOs
aboard the St. Laurent during the time the St. Laurent is in U.S.
waters will return to the Healy after the U.S. waters portion of the
survey is completed and stand watch on the Healy to aid in sighting
marine mammals and alert the PSOs aboard the St. Laurent of their
sightings during the two ships' operations.
Regarding the Commission's sub-comment (2), the qualifiers to this
condition refer to the situations in which (a) other members of the
ship's or scientific crew on either vessel notice a marine mammal near
the vessel and report it to the bridge or the PSOs; (b) the bridge
watch can assist in marine mammal observations during the night when
the PSO is not required to be on the bridge; or (c) the bridge watch
aboard the Healy (in the steering station above the bridge, which is
the highest and best vantage point for making observations) sees marine
mammals. It is impossible to predict the frequency that these
situations will occur, only that many more eyes are available to spot
marine mammals than those of the PSOs, and that these additional eyes
should be used whenever possible, practical, or feasible. It is not the
intention in any of these situations for the crew or the bridge to
implement mitigation requirements because that authority is with the
PSOs. However, the bridge often acts as a central point of
communication among science crew, ship's crew, and PSOs, and therefore
plays a vital role in ensuring that the PSOs can implement appropriate
mitigation procedures at the appropriate times.
Regarding the Commission's sub-comment (3), the U.S. PSOs aboard
the Healy (or when aboard the St. Laurent) will be on watch collecting
marine mammal observation data whether the airguns are operating or
not. When the Healy is operating independently of the St. Laurent
(e.g., steaming north from Dutch Harbor or for operations at the
beginning of the survey when in open water--and therefore independently
surveying), the data collected by the PSOs is baseline data. For the
seismic survey within U.S. waters, the St. Laurent will be steaming to
the start of the tracks from the east and will have the U.S. PSOs
aboard to record baseline observations during the steaming time. Both
U.S. and Canadian observers will be recording baseline information for
at least 30 min on site prior to initial start-up and ramp-ups of the
airgun operations during the survey. If the St. Laurent is operating
independently in either international or Canadian waters, it is the
responsibility of the Canadian Chief Scientist, using the conditions
set forth in the Canadian permits to determine whether the Canadian
observers will stand watch to collect baseline information. When the
ships are operating together in international or Canadian waters, the
PSOs aboard the Healy will be making observations either in front of
the St. Laurent (during seismic operations) or behind the St. Laurent
(during multi-beam operations). It is neither practical nor economical
to pre-survey all tracks for the presence of marine mammals (and
baseline behavior) prior to conducting seismic operations because of
the huge area covered by the joint expedition, so the most likely
baseline information to be collected will be at breaks in lines for
repair or maintenance of the seismic gear and at the start of the
survey. Using the experience of 2008 and 2009, halts in seismic
acquisition for equipment maintenance generally occurred every 48 to 72
hours and lasted from 6 to 48 hours. Marine mammal observations made
aboard the Healy cruise will allow the PSOs to collect baseline
information whenever the seismic equipment is not operating.
Comment 6: The Commission recommends that NMFS approve the
requested IHA, provided NMFS propose to USGS that it revise its study
design to collect meaningful baseline data on sighting rates for marine
mammals. Such information is essential for a
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realistic assessment of impacts from the proposed activities and
recovery from those impacts.
Response: NMFS is unclear about the Commission's recommendation
regarding the revision of USGS's ``study design.'' Please clarify if
you are referring to USGS overall study design or more specifically to
the monitoring plan required under the MMPA. The purpose of the USGS's
project is for marine geophysical research, not to conduct a dedicated
marine mammal research survey. Extending the survey is not practicable
from an operational standpoint for the applicant. Due to the remote
location of the survey and the length of time needed to conduct the
requested science experiment, there may be little time left for the
vessel to operate without the need for refueling and servicing.
During the cruise, there will be significant amounts of transit
time pre- and post-survey during which PSOs will be on watch (e.g.,
prior to and after the seismic portions of the survey). The collection
of this observational data by PSOs may provide meaningful baseline data
for marine mammals, but it is unlikely that the information would
result in any statistically robust conclusions for this particular
seismic survey. See NMFS responses to comments above.
To augment detection and baseline observations, the U.S. liaison
aboard the St. Laurent will request that prior to the start of seismic
activities in U.S. waters, the GSC operators deploy a sonobuoy that can
be monitored through an audio channel for the presence of whales for at
least the 30 min time period that the vessel is on site before
commencing seismic operations. Detected vocalizations can be used to
augment visual observations. The sonobuoy audio information is only
intended to be used to identify the presence or absence of animals
because the relative direction and distance to vocalizing animals
cannot be determined from these sounds. The sonobuoy information is not
intended to be used for mitigation purposes. As stated in the IHA,
seismic operations will not begin if any bowhead whales are seen or
heard. Use of sonobuoys is contingent upon concurrence by GSC
operators, who are generally supportive of collecting additional data
in support of marine mammal observations.
In addition, USGS proposes that the sonobuoy data from the
refraction part of the experiment will be made available to an
appropriate biologist or acoustician for analysis for the presence of
marine mammals. The data is recorded continuously for approximately
eight hours, and the sonobuoy records sounds not only from the airguns,
but ambient noise and any other sounds long after the vessel has left
the area. Although no noise trains that might be interpreted as marine
mammal sounds have been definitively identified on the sonobuoys
examined during 2008 and 2009 joint expeditions (Chian, pers. comm.),
the sonobuoys are a source of information available for closer
scrutiny.
Comment 7: The Commission recommends that NMFS approve the
requested IHA, provided NMFS require the applicant to collect
information to evaluate the assumption that 160 dB re 1 [mu]Pa (rms) is
the appropriate threshold at which harassment occurs for all marine
mammals in the survey area. This assumption can and should be tested
using in-situ measurements of sound propagation concurrent with
observations of the responses of marine mammals exposed to such sounds.
Such tests should be conducted using species-specific data, and test
results should be used to inform decision makers regarding the
applicability of the 160 dB re 1 [mu]Pa (rms) threshold for specific
species and to improve future mitigation measures.
Response: Behavioral responses to sound are context specific and
can vary by species and other factors. However, there are not currently
enough species-specific data showing how marine mammals respond to
sound to support the development of separate harassment thresholds for
every species. Therefore, NMFS uses the best available applicable data,
which includes studies of several different species, to predict at what
levels marine mammals are likely to be harassed and NMFS believes that
the 160 dB re 1 [mu]Pa (rms) threshold remains appropriate for the
species in this project area.
Regarding testing these behavioral harassment assumption, NMFS
primarily relies on scientific research advances, and applicable
monitoring results (where appropriate) to inform them. Behavioral
response field studies that are able to definitively track what an
animal is doing for some period of time (a baseline), expose it to a
known received sound level, and record its behavior afterwards until it
goes back to baseline are expensive and challenging to execute and
while a few are currently underway, relatively few have been completed.
Separately, in required monitoring measures, PSOs are required to make
behavioral observations during seismic activities, however, while they
can very effectively detect a marine mammal, identify it, and record
its behavior at the surface for the moments that it is within view of
the moving vessel--this information is typically not enough to support
the development of a harassment threshold. Alternatively, there has
been one longer-term (i.e., associated with a five year rulemaking)
monitoring study that has generated numerous data of a robust and
measureable nature through the deployment of an extensive hydrophone
array.
Regarding bowhead whales specifically, some published articles
indicate that they may avoid seismic vessels at levels below 160 dB
(rms), NMFS does not believe that these responses rise to the level of
a take. Miller et al. (1999) indicated that some bowhead whales may
have started to be deflected from their migratory path at 35 km (21.7
mi) from the seismic vessel, during migration, however, as described in
MMS' 2006 Final Programmatic Environmental Assessment (PEA), this
response has not been seen at other times of the year and during other
activities. To show the contextual nature of this minor behavioral
modification, recent monitoring studies of Canadian seismic operations
indicated that feeding, non-migratory bowhead whales do not move away
from a noise source at an SPL of 160 dB. NMFS therefore continues to
estimate ``takings'' under the MMPA from impulse noises, such as
seismic, as occurring at 160 dB (re 1 [mu]Pa [rms]).
Comment 8: The Commission recommends that NMFS approve the
requested IHA, provided NMFS require the applicant to make observations
during all ramp-up procedures to gather the data needed to analyze and
report on their effectiveness as mitigation. As it has noted in past
correspondence, the Commission would be pleased to discuss with NMFS
the collection and analysis of such data and the design of such
experiments to promote a better understanding of the utility and
shortcomings of ramp-up as a mitigation measure.
Response: The IHA requires that PSOs on the St. Laurent and Healy
make observations for 30 min prior to ramp-up, during all ramp-ups, and
during all daytime seismic operations and record the following
information when a marine mammal is sighted:
(i) Species group size, age/size/sex categories (if determinable),
behavior when first sighted and after initial sighting, heading (if
consistent), bearing and distance from seismic vessel, sighting cue,
apparent reaction to the airguns or vessel (e.g., none, avoidance,
approach, paralleling, etc., and including responses to ramp-up), and
behavioral pace; and
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(ii) Time, location, heading, speed activity of the vessel
(including number of airguns operating and whether in state of ramp-up
or power-down), Beaufort wind force and sea state, visibility, and sun
glare.
One of the primary purposes of monitoring is to result in
``increased knowledge of the species'' and the effectiveness of
monitoring and mitigation measures; marine mammal reactions to ramp-up
would be useful information in this regard. NMFS has asked USGS to
gather all data that could potentially provide information regarding
the effectiveness of ramp-ups as a mitigation measure. However,
considering the low numbers of marine mammal sightings and low number
of ramp-ups, it is unlikely that the information will result in any
statistically robust conclusions for this particular seismic survey.
Over the long term, these requirements may provide information
regarding the effectiveness of ramp-up as a mitigation measure,
provided animals are detected during ramp-up.
A study investigating the efficacy of ramp-up has been jointly
funded by the Bureau of Ocean Energy Management, Regulation, and
Enforcement (BOEMRE) and the Joint Industry Programme (JIP). Post-
cruise monitoring reports for numerous seismic surveys are currently
available on the NMFS MMPA Incidental Take Program Web site should
there be interest in further analysis of this data by the public.
Comment 9: The NSB and its residents as well as the AEWC are
concerned about potential health impacts to the environment associated
with offshore development (i.e., industrial and commercial activities)
on the North Slope. Activities allowed by the proposed authorization
pose direct, indirect, and cumulative impacts on species (especially
marine mammals) that are critical to the subsistence harvesting
villages the AEWC represents and the NSB people's subsistence harvest.
Response: NMFS is unclear about the specific meaning of the term
``health impacts'' as used in the public comments. The USGS and NMFS
are making every effort to minimize the direct, indirect, and
cumulative impacts through the federal NEPA, MMPA, and ESA process, as
well as consulting with the Native communities. Cumulative impact
assessments are USGS and NMFS responsibility under NEPA. The revised EA
has addressed concerns about potential impacts using the best available
science. In evaluating the severity of the impacts, it is important to
realize that the proposed seismic activity within the U.S. EEZ is more
than 100 km (54 nmi) offshore in a region well away from the main
migration routes of the bowhead whale and will occur at a time prior to
the bowhead whales beginning their fall migration from the Canadian
Beaufort. Although a single individual bowhead whale has been
identified in this region from tagging, there is little evidence to
suggest that the location or timing of the survey overlaps with or
interferes with bowhead whaling activities. As noted in the EA,
``available information * * * does not indicate that marine and seismic
surveys for oil and gas exploration activities has had detectable long-
term adverse population-level effects on the overall health, current
status, or recovery of marine mammal species and populations in the
Arctic region. For example, data indicated that the Bering-Chukchi-
Beaufort (BCB) bowhead whale population has continued to increase over
the timeframe that oil and gas activities have occurred. There is no
long-term displacement from habitat (although studies have not
specifically focused on addressing this issue) * * * monitoring studies
indicate that most fall migrating whales avoid an area with a radius of
about 20 to 30 km (12.4 to 18.6 mi) around a seismic vessel operating
in nearshore waters (Miller et al., 2002). USGS