Small Takes of Marine Mammals Incidental to Specified Activities;
Oceanographic Surveys in the Mid-Atlantic Ocean
[Federal Register: November 10, 2003 (Volume 68, Number 217)]
[Notices]
[Page 63761-63768]
From the Federal Register Online via GPO Access [wais.access.gpo.gov]
[DOCID:fr10no03-22]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
[I.D. 080803C]
Small Takes of Marine Mammals Incidental to Specified Activities;
Oceanographic Surveys in the Mid-Atlantic Ocean
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice of issuance of an incidental harassment authorization.
-----------------------------------------------------------------------
SUMMARY: In accordance with provisions of the Marine Mammal Protection
Act (MMPA) as amended, notification is hereby given that an Incidental
Harassment Authorization (IHA) to take small numbers of marine mammals,
by harassment, incidental to conducting oceanographic surveys in the
Mid-Atlantic Ocean has been issued to Lamont-Doherty Earth Observatory
(LDEO).
DATES: Effective from October 23, 2003 through October 22, 2004.
ADDRESSES: The application, a list of references used in this document,
and/or the IHA are available by writing to P. Michael Payne, Chief,
Marine Mammal Conservation Division, Office of Protected Resources,
National Marine Fisheries Service, 1315 East-West Highway, Silver
Spring, MD 20910-3225, or by telephoning the contact listed here.
FOR FURTHER INFORMATION CONTACT: Sarah C. Hagedorn, Office of Protected
Resources, NMFS, (301) 713-2322, ext 117.
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 to allow, upon request, the
incidental, but not intentional, taking of marine mammals by U.S.
citizens who engage in a specified activity (other than commercial
fishing) 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.
Permission may be granted if NMFS finds that the taking will have a
negligible impact on the species or stock(s) and will not have an
unmitigable adverse impact on the availability of the species or
stock(s) for subsistence uses and that the permissible methods of
taking and requirements pertaining to the 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.''
Subsection 101(a)(5)(D) of the MMPA established an expedited
process by which citizens of the United States can apply for an
authorization to incidentally take small numbers of marine mammals by
harassment. Under Section 3(18)(A), 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; 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.
The term ``Level A harassment'' means harassment described in
subparagraph (A)(i). The term ``Level B harassment'' means harassment
described in subparagraph (A)(ii).
Subsection 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 on 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 issuance of the authorization.
Summary of Request
On July 21, 2003, NMFS received an application from LDEO for the
taking,
[[Page 63762]]
by harassment, of several species of marine mammals incidental to
conducting a seismic survey program. As presently scheduled, two
seismic surveys will be conducted in the Mid-Atlantic Ocean. The Trans-
Atlantic Geotransect (TAG) cruise will be centered at 26[deg]N and
45[deg]W in the Mid-Atlantic Ocean during late October 2003, for a
total of six days of seismic surveying. The Atlantic Deep Western
Boundary Current (ADWBC) cruise will occur between 39[deg]
and 42[deg]N
and between 45[deg]
and 52.5[deg]W, during July and August of 2004 for
a total of approximately 20 days of surveying. These operations will
take place in international waters.
The seismic survey work conducted during the TAG cruise is part of
a multi-disciplinary experiment, taking place in the TAG Active Mound
area over a period of nine months. The TAG active mound (26[deg]N on
the Mid-Atlantic Ridge), which is one of the largest hydrothermal
deposits found to date on the seafloor, is a large, focused mineral
deposit on a slow-spreading ridge. The purpose of the TAG cruise is to
delineate the nature, position, and size of any heat sources (low-
velocity zones) that might drive convection at the TAG active mound,
and more generally, to provide an understanding of crustal architecture
in the TAG region. More specifically, the TAG experiment will address
key issues at the TAG site: (1) the nature of the heat source driving
circulation, (2) the relationship between faulting on the eastern flank
and fluid flow at the mound, (3) the possible existence of a low-
velocity zone beneath the rise axis, and (4) the hydraulic connectivity
of the shallow TAG mound.
The ADWBC cruise will determine the configuration, age, and
paleoceanographic significance of the sedimentary sequences on J
Anomaly Ridge and Southeast Newfoundland Ridge, which may show evidence
for strong boundary currents dating to the early Paleocene. Proposed
tracklines for the seismic survey were chosen with four primary
objectives in mind: (1) to map the main reflection sequences across the
full extent of the ridges and onto the edges of adjacent abyssal
plains, (2) to obtain continuity in tracing sequences by profiling
around major interruptions (seamounts) and optimizing track crossings,
(3) to provide abundant crossing lines in areas where existing seismic
and bathymetric data suggest that there are outcrops of pre-Neogene
strata, and (4) to take advantage of good-quality seismic data, where
they exist (e.g., Conrad 2510 MCS), in order to make loop correlations
between tracks.
Description of the Activity
The TAG seismic survey will involve a single vessel which will
conduct the seismic work, the R/V Maurice Ewing, operated by LDEO under
a cooperative agreement with the U.S. National Science Foundation
(NSF), owner of the vessel. The Maurice Ewing will deploy an array of
20 airguns as an energy source, and will deploy and retrieve Ocean
Bottom Hydrophones (OBHs). A hydrophone streamer will not be towed
during the TAG cruise. The energy to the airgun array is compressed air
supplied by compressors on board the source vessel. As the airgun array
is towed along the survey lines, the OBHs and Ocean Bottom Seismometers
(OBSs) will receive the reflected signals and transfer the data to the
onboard processing system. All planned geophysical data acquisition
activities will be conducted by LDEO scientists with onboard assistance
by the scientists who proposed the study. The TAG program will consist
of 185 km (100 n.mi.) of survey lines. There will be a total of three
seismic lines, two along- and one across-axis of the TAG. Water depths
in the area will vary from 1500 to 4500 m (4921-14,764 ft).
The ADWBC cruise will involve the oceanographic research vessel R/V
Knorr, a U.S. Navy-owned ship operated by the Woods Hole Oceanographic
Institution (WHOI), and will use a portable LDEO seismic system to
conduct the seismic survey. The vessel will deploy 2 General Injector
(GI)-guns as an energy source plus a towed streamer containing
hydrophones to receive the returning acoustic signals. The hydrophone
array will consist of a 600-m (1969 ft) solid state streamer with a
200-m (656 ft) tow leader. The energy to the airgun array is compressed
air supplied by compressors on board the source vessel. As the 2 GI-
guns are towed along the survey line, the hydrophone array will receive
the returning signals and transfer the data to the onboard processing
system. All planned geophysical activities will be conducted by the
scientists who have proposed the study, while LDEO will provide the
portable high-resolution seismic system that will support the seismic
surveys for the proposed study. The ADWBC program will consist of 4334
km (2340 n.mi.) of seismic profiles that will be shot over a period of
20 days. The most detailed grids of seismic lines are proposed for the
southern end of J Anomaly Ridge and for moats around seamounts on the
crest of the Southeast Newfoundland Ridge - both are areas where there
appear to be extensive pre-Neogene outcrops. Water depths in the area
will vary from 4000 - 5000 m (13,124-16,405 ft).
The procedures to be used for the two seismic studies will be
similar to those used during previous seismic surveys by LDEO, e.g., in
the equatorial Pacific Ocean (Carbotte et al., 1998, 2000). The
proposed seismic surveys will use conventional seismic methodology with
a towed airgun array as the energy source, and either a towed
hydrophone streamer or OBH and OBS receivers placed on the bottom to
receive the reflected signals. For the TAG survey, eighteen OBHs will
be deployed (and recovered) by the Maurice Ewing - eight along each of
the long axis lines and two on the across axis line. After the seismic
lines are shot, the data will be downloaded and the OBSs will be
retrieved during an, as of yet, unscheduled cruise in the summer of
2004 (during which no seismic sound sources will be used). Along three
selected seismic lines, 13 OBS receivers will be placed in the proposed
study area by the R/V Alvin from 7-24 June 2003, before the arrival of
the Maurice Ewing. In addition, a multi-beam bathymetric sonar will be
operated from the source vessel continuously throughout both cruises,
and a lower-energy sub-bottom profiler will also be operated during
most of both surveys. During the ADWBC study, coring of numerous
sedimentary outcrops known to exist on the ridges will also take place.
During both cruises, there will be additional operations associated
with equipment testing, startup, line changes, and repeat coverage of
any areas where initial data quality is sub-standard.
The R/V Maurice Ewing will be used as the source vessel during the
TAG cruise, and the R/V Knorr will be used as the source vessel during
the ADWBC cruise. Both vessels will tow airgun arrays along
predetermined lines, and will also serve as platforms from which
vessel-based marine mammal observers will watch for marine mammals
before and during airgun operations.
During TAG-study airgun operations, the vessel will travel at 7.4-
9.3 km/hr (4-5 knots), and seismic pulses will be emitted at intervals
of 60-90 seconds (OBS lines during the TAG cruise). The 60-90 sec.
spacing along OBS lines is to minimize reverberation from previous shot
noise during OBS data acquisition, and the exact spacing will depend on
water depth. The airgun array to be used will consist of 20 2000-psi
Bolt airguns, towed at a depth of 7.5 m (24.5 ft). The 20-gun array
will include airguns ranging in chamber volume from 80 to 850 in\3\,
with a total volume of 8,575 in\3\.
[[Page 63763]]
These airguns will be spaced in an approximate rectangle with
dimensions of 35 m (115 ft) (across track) by 9 m (30 ft) (along
track).
The ADWBC seismic survey will be high-resolution, consisting of two
105 in3 GI airguns with a total volume of approximately 210 in3, spaced
7.8 m (26 ft) apart, and towed 37 m (121 ft) behind the vessel at a
depth of 2-3 m (7-10 ft). Towing airguns at this shallow depth is
accomplished by suspending the guns from floats, and the resulting
short-period free surface ``ghosting'' keeps the spectral content broad
with usable signals up to 300-350 Hz. These airguns produce an
unusually clean impulse with sufficient energy to penetrate many
hundreds of meters of sediment. Airgun firing, timing, and
synchronizing is handled by a LDEO-built controller, which is
integrated with a SUN workstation-based DGPS navigation, data logging,
and fire control system. The air is produced by a standalone Price Co.
2000 psi compressor, and the seismic signals are detected by a solid
state ITI hydrophone ``Stealtharray'', with 48 12.5-m (41 ft) long
channels, and a total length of 600 m (1969 ft).
The dominant frequency components for both airgun arrays is 0 - 188
Hz. The 2-airgun array will have a peak sound source output level of
237 dB re 1 microPa or 243 dB peak-to-peak (P-P). The 20-airgun array
will have a peak sound source output level of 255 dB re 1 microPa or
262 dB P-P. Because the actual source is a distributed sound source (2
or 20 airguns) rather than a single point source, the highest sound
levels measurable at any location in the water will be less than the
nominal source level. Also, because of the downward directional nature
of the sound from these airgun arrays, the effective source level for
sound propagating in near-horizontal directions will be substantially
lower.
Along with the airgun operations, several additional acoustical
data acquisition systems will be operated during most or all of the
cruises. The ocean floor will be mapped with an Atlas Hydrosweep DS-2
multi-beam 15.5-kHz bathymetric sonar, and/or a 3.5-kHz sub-bottom
profiler. These mid-frequency sound sources are commonly operated from
research vessels simultaneous with airgun arrays as well as in the
absence of airgun activity.
The Atlas Hydrosweep sonar will be used during cruises by the R/V
Maurice Ewing, is mounted in the hull of the vessel, and operates in
three modes depending on the water depth. The first is a shallow-water
mode when water depth is <400 m (1312.3 ft); source output is 210 dB re
1 microPa-m rms and a single 1-millisec (ms) pulse or ``ping'' per
second is transmitted, with a beamwidth of 2.67 degrees fore-aft and 90
degrees in athwartship. The beamwidth is measured to the 3 dB point, as
is usually quoted for sonars. The other two modes are deep-water modes:
The Omni mode is identical to the shallow-water mode except that the
source output is 220 dB rms (normally used only during start up). The
Rotational Directional Transmission (RDT) mode is normally used during
deep-water operation and has a 237 dB rms source output. In the RDT
mode, each ``ping'' consists of five successive transmissions, each
ensonifying a beam that extends 2.67 degrees fore-aft and approximately
30 degrees in the cross-track direction. The five successive
transmissions (segments) sweep from port to starboard with minor
overlap, spanning an overall cross-track angular extent of about 140
degrees, with tiny (<1 millisec) gaps between the pulses for successive
30-degree segments. The total duration of the ``ping'', including all 5
successive segments, varies with water depth but is 1 ms in water
depths <500 m (1640.4 ft) and 10 ms in the deepest water. For each
segment, ping duration is 1/5th of these values or 2/5th for a receiver
in the overlap area ensonified by two beam segments. The ``ping''
interval during RDT operations depends on water depth and varies from
once per second in <500 m (1640.5 ft) water depth to once per 15
seconds in the deepest water.
For the ADWBC cruise, the SeaBeam 2100/12 multibeam 12 kHz
bathymetric sonar system will be used, with a source output of 237 dB
re 1 microPa-m. Operation of this system is similar to that of the
Atlas Hydrosweep (described above). The SeaBeam 2100/12 system has a
swath width of about 3 times the water depth, so it will provide data
over swaths 10-15 km (5-8 n.mi.) wide during most of the survey.
The sub-bottom profiler is normally operated to provide information
about the sedimentary features and bottom topography that is
simultaneously being mapped by the Hydrosweep. The energy from the sub-
bottom profiler is directed downward by a 3.5-kHz transducer mounted in
the hull of the vessel. The output varies with water depth from 50
watts in shallow water to 800 watts in deep water. Pulse interval is 1
sec. but a common mode of operation is to broadcast five pulses at 1-
sec. intervals followed by a 5-sec. pause. The beamwidth is
approximately 30[deg]
and is directed downward. Maximum source output
is 204 dB re 1 microPa, 800 watts, while nominal source output is 200
dB re 1 microPa, 500 watts. Pulse duration will be 4, 2, or 1 ms, and
the bandwith of pulses will be 1.0 kHz, 0.5 kHz, or 0.25 kHz,
respectively.
For the ADWBC cruise, the multibeam bathymetry and sub-bottom
profiling will be used to define windows where erosion or non-
deposition has exposed deeper sequences suitable for piston coring.
Coring transects across these windows will provide biostratigraphic age
determinations that can be used to constrain the age of reflections
throughout the study area. There will be five days of piston coring
following completion of the ADWBC seismic survey.
Additional information on the airgun arrays, bathymetric sonars,
and sub-bottom profiler specifications is contained in the application,
which is available upon request (see ADDRESSES).
Comments and Responses
A notice of receipt of LDEO's application for seismic work in the
Mid-Atlantic Ocean and proposed IHA was published in the Federal
Register on September 17, 2003 (68 FR 54421). That notice described in
detail the proposed activity and the marine mammal species that may be
affected by it. That information is not repeated here. During the 30-
day public comment period, comments were received from the Marine
Mammal Commission (Commission).
Comment 1: The Commission believes that NMFS' preliminary
determinations are reasonable, provided NMFS is satisfied that the
proposed mitigation and monitoring activities are adequate to detect
marine mammals in the vicinity of the proposed operations and to ensure
that marine mammals are not being taken in unanticipated ways or
numbers. In this regard, NMFS' Federal Register notice and the
application state that ``[v]essel-based observers will monitor marine
mammals near the seismic source vessel during all daylight airgun
operations and during any nighttime startups of the airguns...'' The
probability of detecting marine mammals about to enter or already
inside the presumed safety limits is probably close to zero at night.
Observers will generally not be on duty, and bridge personnel will have
limited time to search for marine mammals. The current Federal Register
notice states that ``[a]n image-intensifier night-vision device (NVD)
will be available for use at night,'' but previous Federal Register
notices have stated that ``past experience has shown that NVDs are of
limited value for this purpose.'' There is no discussion of why
nighttime operations are considered necessary, why experienced marine
mammal
[[Page 63764]]
observers will not be on duty during nighttime hours, or how effective
the observation efforts are expected to be. The efficacy of visual
monitoring is not clear and may be inadequate during some of the times
that airguns would be in use. The Commission notes that NMFS has
previously estimated in a Federal Register notice dated March 19, 2001,
that visual observation efforts were expected to detect about 5 percent
of animals inside safety limits (66 FR 15380). Although the efficacy of
visual observations will be determined by many factors (e.g., species
in the area, daylight, sea surface conditions, observer position), it
is feasible that many, if not most, marine mammals go undetected based
on visual observations alone. If information is available regarding the
efficacy of visual monitoring from the vessel to be used, then that
information should be provided to justify NMFS' confidence that the
proposed monitoring program will be adequate. If no information is
available to assess efficacy, then NMFS should seek alternative means
of ensuring that adequate monitoring methods are used, or conduct
research to evaluate their adequacy. In addition, the Commission notes
that it is unclear whether vessel-based passive acoustic monitoring
will be conducted as an adjunct to visual monitoring during the daytime
and particularly at night to detect, locate, and identify marine
mammals and, if not, why not.
Response: Nighttime operations are necessary due to cost
considerations. The daily cost to the federal government to operate
vessels such as the Ewing and the Knorr is approximately $33,000 to
$35,000/day (Ljunngren, pers. comm. May 28, 2003), or approximately
$910,000 for a total of 26 days of research during both Mid-Atlantic
cruises. If the vessels were prohibited from operating during
nighttime, it is possible that each trip would require an additional
three to five days, or up to $105,000 to $175,000 more, depending on
average daylight at the time of work.
Taking into consideration the additional costs of prohibiting
nighttime operations and the likely impact of the activity (including
mitigation and monitoring), NMFS has determined that the mitigation
required by the IHA ensures that the activity will have the least
practicable impact on the affected species or stocks. In summary,
marine mammals will have sufficient notice of a vessel approaching with
operating seismic airguns (at least one hour in advance), thereby
giving them an opportunity to avoid the approaching array; if ramp-up
is required after an extended power-down, two marine mammal observers
will be required to monitor the safety radii using night vision devices
for 30 minutes before ramp-up begins and verify that no marine mammals
are in or approaching the safety radii; ramp-up may not begin unless
the entire safety radii are visible; and ramp-up may occur at night
only if one airgun with a sound pressure level of at least 180 dB has
been maintained during interruption of seismic activity. Therefore, it
is likely that the 20-gun array will not be ramped-up from a shut-down
at night. See Mitigation and Monitoring for more details.
It is also noted that at times, pinnipeds and even some small
cetaceans will approach a vessel during transmissions (the vessel
itself moving forward at about 3-5 knots) from the side of the vessel
or the stern, meaning that the animal is voluntarily approaching a
noise source that is increasing in strength as the animal gets closer.
Experience indicates that pinnipeds will come from great distances to
scrutinize seismic-reflection operations. Seals have been observed
swimming within airgun bubbles only 10 m (33 ft) away from active
arrays. Also, Canadian scientists, who were using a high-frequency
seismic system that produced sound frequencies closer to pinniped
hearing than those used by the Ewing, describe how seals frequently
approached close to the seismic source, presumably out of curiosity.
Therefore, NMFS has concluded that this mitigation requirement is
reasonable because the bridge-watch will be concentrating on marine
mammals approaching the vessel from the bow. Also, the night-vision
ability of the trained bridge-watch staff will be better than observers
elsewhere on the vessel where normal ship-board lighting is more
likely. Finally, an observer is still required to be on standby,
meaning he or she will be in the vicinity of the bridge and is not
precluded from conducting observations during night-time.
The methodology for visual observations was changed since the 5
percent estimate (noted by the Commission above), resulting in a
revised estimate of 9 percent efficacy (67 FR 46712, July 16, 2002).
That figure includes both daytime and nighttime periods of observation.
The rate increases to 18 percent based only on daytime monitoring.
However, NMFS shipboard marine mammal assessment surveys estimate a
higher rate of efficacy. It should be understood that these efficacy
ratings were based on most difficult marine mammals to sight, such as
harbor porpoise and Cuvier's beaked whales, and not those more easily
sighted.
Passive means of monitoring was found to be 25 percent effective.
However, shipboard passive acoustics do not allow scientists to
determine a marine mammal's distance from the vessel through
triangulation; the vessel operator could determine only that a marine
mammal is some unknown distance from the vessel. In order to
triangulate on the animal, a system similar to that used in the Gulf of
Mexico (GOM) Sperm Whale Seismic Study (SWSS) in May, 2003 would be
needed. The passive acoustical monitoring equipment that was used
onboard the Ewing during the GOM SWSS is not the property of LDEO or
the Ewing, and therefore is not available for the Mid-Atlantic cruises.
LDEO is presently evaluating the scientific results of the passive
sonar from the SWSS trip to determine whether it is practical to
incorporate it into future seismic research cruises. NMFS expects a
report on this analysis shortly.
Finally, NMFS notes that the monitoring methods employed on the
Ewing are standard methods used onboard vessels for conducting marine
mammal abundance surveys and under IHA's. NMFS would welcome the
Commission's participation in its annual workshop in Seattle, WA to
discuss similar monitoring methodology used in oil exploration and
production, including vessel seismic operations, in Arctic waters or in
another venue. NMFS is especially interested in exploring with the
Commission the potential for alternative, practical, monitoring
methodology for use in waters too far from shore-side facilities to
make aircraft surveillance practical. Recently, LDEO submitted its
required monitoring report for the IHAs issued for the Ewing's seismic
work in the Gulf of Mexico (68 FR 32460, May 30, 2003) and Hess Deep
(68 FR 41314, July 11, 2003). Copies of those documents are available
upon request (see ADDRESSES).
Comment 2: Several species of cetaceans for which LDEO is seeking
incidental take authority stay submerged on most dives for more than 30
minutes. The Commission questions whether conducting monitoring ``for
at least 30 minutes prior to the planned start of airgun operations''
during the day and at night is sufficient to detect those species.
Response: NMFS believes that a 30-minute pre-ramp-up monitoring
period is sufficient considering that the ramp-up period will increase
SPLs at a rate no greater than 6 dB per 5-minutes for a ramp-up
duration of approximately 25 min for the 20-gun array and a total
[[Page 63765]]
monitoring period of approximately 55 minutes. Also, while some whale
species may dive for up to 45 minutes, it is unlikely that the ship's
bridge watch would miss a large whale surfacing from its previous dive
if it is within a mile or two of the vessel.
Comment 3: The Federal Register notice for the proposed IHA and the
applicant's request notes that there are several species of beaked
whales in the proposed survey area, but the notice makes no reference
to or requirement for any additional caution with respect to beaked
whales or that post-survey monitoring be conducted to search for
animals that may have been taken other than by harassment.
Response: While NMFS shares the Commission's concern regarding the
possible relationship between low-frequency seismic survey
transmissions and the beaked whale strandings in the Gulf of
California, NMFS believes that additional factors probably also
influence whether beaked whales will be affected in ways other than the
expected reaction of vacating the immediate vicinity of the noise,
similar to the reactions of other marine mammal species. For example,
beaked whales in the Gulf of Mexico have been exposed to seismic noise
for several decades, yet mass stranding events do not appear in the
stranding record. Finally, post-survey monitoring is not being required
under this IHA because it is neither practical given the location (mid-
ocean) and vessel commitments, nor warranted given the unlikelihood
(based on the 2000 Bahamas stranding event) that beaked whales will
show distress at the ocean surface. However, NMFS welcomes
recommendations regarding additional practical mitigation measures to
protect beaked whales from anthropogenic sounds.
Mitigation
For the TAG seismic survey, LDEO will use a 20-gun array with a
total volume of 8575 in\3\. Individual airguns will range in size from
80 to 850 in3. For the ADWBC cruise, LDEO will use 2 GI-guns with a
total volume of 210 in\3\. The airguns comprising these arrays will be
spread out horizontally, so that the energy from the arrays will be
directed mostly downward.
The sound pressure fields were modeled by LDEO in relation to
distance and direction from the 2 GI-guns and the 20-gun array, as
shown in Figures 5 and 6 of the application (LDEO Mid-Atlantic, 2003).
The radii around the arrays where the received level would be 180-dB re
1 microPa (rms) (NMFS' threshold level for onset of Level A harassment
applicable to cetaceans) were estimated as 54 m (177 ft) and 900 m
(2953 ft), respectively, for the 2-GI and 20-gun array. The radii
around the 2 GI-guns and the 20-gun array where the received level
would be 190 dB re 1 microPa (rms), (NMFS' threshold level for onset of
Level A harassment applicable to pinnipeds), were estimated as 17 m (56
ft) and 275 m (902 ft), respectively. A calibration study was conducted
prior to these surveys to determine the actual radii corresponding to
each sound level. These actual radii will be used to define the safety
radii to be used for this study. Until then, or if those measurements
appear defective, LDEO will use a precautionary 1.5 times the modeled
180- (cetaceans) and 190- (pinnipeds) dB radii as the safety radii.
Vessel-based observers will monitor marine mammals in the vicinity
of the arrays. LDEO will power-down the airguns if marine mammals are
observed approaching or within the safety radii. LDEO will employ a
ramp-up procedure when commencing operations using the 20-gun array.
Ramp-up will begin with the smallest gun in the array (80 in\3\), and
guns will be added in a sequence such that the source level of the
array will increase at a rate no greater than 6 dB per 5-minute period
over a total duration of about 25 minutes. Ramp-up will not occur for
the 2-GI gun array because the total air discharge volume is small (210
in\3\). Please refer to LDEO's application for more detailed
information. The directional nature of the 20-airgun array to be used
in this project is an important mitigating factor, resulting in lower
sound levels at any given horizontal distance than would be expected at
that distance if the source were omnidirectional with the stated
nominal source level. Because the actual seismic source is a
distributed sound source (2 or 20 guns) rather than a single point
source, the highest sound levels measurable at any location in the
water will be less than the nominal source level.
Marine Mammal Monitoring
At least two vessel-based observers will be stationed aboard LDEO's
seismic survey vessel during seismic operations in the Mid-Atlantic
Ocean. One or two marine mammal observers aboard the seismic vessel
will search for and observe marine mammals whenever seismic operations
are in progress during daylight hours, and if feasible, during periods
without seismic activity. Vessel-based observers will monitor for
marine mammals near and in the safety radii for at least 30 minutes
prior to and during all daylight ramp-up and airgun operations, and
during any nighttime startups of the airguns. Airgun operations will be
suspended when marine mammals are observed within, or about to enter,
the designated safety radii. Observers will not be required to be on
duty during ongoing seismic operations at night; bridge personnel will
watch for marine mammals during this period and will call for the
airguns to be powered down if marine mammals are observed in or about
to enter the safety radii. At least one marine mammal observer will be
on ``standby'' at night, in case bridge personnel see a marine mammal.
An image-intensifier night-vision device (NVD) will be available for
use at night. If the airguns are started up at night, two marine mammal
observers will monitor for marine mammals near the source vessel for 30
minutes prior to start up using NVDs. The 30-minute observation period
is only required prior to commencing seismic operations following an
extended shut down period (see Ramp-up Procedures below). After 30
minutes of observation, the ramp-up procedure will be followed.
The observers will watch for marine mammals from the highest
practical vantage point on the vessel, which is either the flying
bridge or the bridge. On the R/V Maurice Ewing, the observer's eye
level will be approximately 11 m (36 ft) above sea level when stationed
on the bridge, allowing for good visibility within a 210[deg]
arc. If
observers are stationed on the flying bridge, the eye level will be
14.4 m (47.2 ft) above sea level. The proposed monitoring plan is
summarized later in this document.
Mitigation During Operations
The following mitigation measures, as well as marine mammal
monitoring, will be adopted during the proposed Mid-Atlantic seismic
surveys, provided that doing so will not compromise operational safety
requirements: (1) Speed or course alteration; (2) Power-down
procedures; (3) Shut-down procedures; and (4) Ramp-up procedures.
Course Alteration
If a marine mammal is detected outside the appropriate safety
radius and, based on its position and the relative bearing, is likely
to enter the safety radius, the vessel's speed and/or direct course
will be changed in a manner that also minimizes the effect to the
planned science objectives. The marine mammal activities and movements
relative to the seismic vessel will be closely monitored to ensure that
the marine mammal does not approach or enter the safety radius. If the
mammal appears likely to enter the safety radius,
[[Page 63766]]
further mitigative actions will be taken, i.e., either further course
alterations or shutdown of the airguns.
Power-down and Shut-down Procedures
Received sound levels have been modeled for the 2-GI and 20-gun
arrays. Based on the modeling, estimates of the 190- and 180-dB re 1
microPa (rms) distances (safety radii) for these arrays have been
provided previously in this document.
Airgun operations will be powered- or shut-down immediately when
cetaceans or pinnipeds are seen within or about to enter the
appropriate 180-dB (rms) or 190-dB (rms) radius, respectively. These
180- and 190-dB criteria are consistent with guidelines listed for
cetaceans and pinnipeds by NMFS (2000) and other guidance by NMFS. If a
marine mammal is detected outside the safety radius but is likely to
enter the safety radius, and if the vessel's course and/or speed cannot
be changed to avoid having the marine mammal enter the safety radius,
the airguns will be powered-down before the mammal is within the safety
radius. If a mammal is already within the safety radius when first
detected, the airguns will be powered-down immediately. If a marine
mammal is seen within the appropriate safety radius of the array while
the guns are powered-down, airgun operations will be shut-down. For the
power-down procedure for the 20-gun array, one 80 in3 airgun will be
operated during the interruption of seismic survey. When the 2 GI-guns
are in use, a shut-down rather than a power-down will likely be
necessary. Airgun activity (after both power-down and shut-down
procedures) will not resume until the marine mammal has cleared the
safety radius. The animal has cleared the safety radius if it is
visually observed to have left the safety radius, or if it has not been
seen within the zone for 15 min (small odontocetes and pinnipeds) or 30
min (mysticetes and large odontocetes, including sperm, pygmy sperm,
dwarf sperm, beaked, and bottlenose whales).
Ramp-up Procedure
A ``ramp-up'' procedure will be followed when the airgun arrays
begin operating after a specified duration without airgun operations.
Under normal operational conditions (vessel speed 4 knots, or 7.4 km/
hr), a ramp-up would be required after a power-down or shut-down period
lasting about 8 minutes or longer if the Ewing was towing the 20-gun
array. At 4 knots, the source vessel would travel 900 m (2953 ft)
during an 8-minute period. If the towing speed is reduced to 3 knots or
less, as sometimes required when maneuvering in shallow water, a ramp-
up would be required after a ``no shooting'' period lasting 10 minutes
or longer. At towing speeds not exceeding 3 knots, the source vessel
would travel no more than 900 m (3117 ft) in 10 minutes. Based on the
same calculation, a ramp-up procedure would be required after a 6
minute period if the speed of the source vessel was 5 knots. During the
ramp-up procedures, the safety radii for the full gun array will be
maintained.
Ramp-up will not occur if the safety radius has not been visible
for at least 30 min prior to the start of operations in either daylight
or nighttime. If the safety radius has not been visible for that 30
minute period (e.g., during darkness or fog), ramp-up will not commence
unless one airgun with a sound pressure level (SPL) of at least 180 dB
has been maintained during the interruption of seismic activity.
Therefore, it is likely that the 20-gun array will not be ramped up
from a shut-down at night or in thick fog, since the safety radii for
this array will not be visible during those conditions.
Monitoring and Reporting
LDEO will conduct marine mammal monitoring of its Mid-Atlantic
seismic programs in order to verify that the taking of marine mammals,
by harassment, incidental to conducting the seismic survey will have a
negligible impact on marine mammal stocks and to ensure that these
harassment takings are at the lowest level practicable.
Vessel-based Visual Monitoring
The observer(s) will systematically scan the area around the vessel
with reticle binoculars (e.g., 7 X 50 Fujinon) and with the naked eye
during the daytime. At night, NVDs will be available (ITT F500 Series
Generation 3 binocular image intensifier or equivalent). Laser
rangefinding binoculars (Leica LRF 1200 laser rangefinder or
equivalent) will be available to assist with distance estimation.
At least two observers will be based aboard the vessel, and at
least one will be an experienced marine mammal observer. Observers will
be appointed by LDEO with NMFS concurrence. Observers will be on duty
in shifts of duration no longer than 4 hours. Use of two simultaneous
observers will increase the proportion of the marine mammals present
near the source vessel that are detected. LDEO bridge personnel will
also assist in detecting marine mammals and implementing mitigation
requirements whenever possible (they will be given instruction on how
to do so), especially during ongoing operations at night, when
designated observers will not be on duty. If ramp-up procedures must be
performed at night, two observers will be on duty 30 minutes prior to
the start of airgun operations and during the subsequent ramp-up
procedures. Ramp-up is not required for the 2 GI gun array, but
observers must watch for 30 minutes prior to operation of the 2 GI-guns
and the safety radii must be visible.
Reporting
When a mammal sighting is made, the following information about the
sighting will be recorded: (1) 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 seismic vessel
(e.g., none, avoidance, approach, paralleling, etc.), and behavioral
pace; and (2) time, location, heading, speed, activity of the vessel
(shooting or not), sea state, visibility, cloud cover, and sun glare.
The data listed under (2) 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 mammal observations and airgun power- and shut-downs will be
recorded in a standardized format. Data will be entered into a custom
database using a laptop computer when observers are off-duty. The
accuracy of the data entry will be verified by computerized validity
data 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 or other
programs for further processing and archiving.
A report will be submitted to NMFS within 90 days after the end of
each cruise in the Mid-Atlantic Ocean. The end of the TAG cruise is
predicted to occur on or about November 7, 2003. The end of the ADWBC
cruise is predicted to occur during August 2004. The report will
describe the operations that were conducted and the marine mammals that
were detected. The report will be submitted to NMFS, providing full
documentation of methods, results, and interpretation pertaining to all
monitoring tasks. The 90-day report will summarize the dates and
locations of seismic operations, marine mammal sightings (dates, times,
locations, activities, associated seismic survey
[[Page 63767]]
activities), and estimates of the amount and nature of potential take
of marine mammals by harassment or in other ways. The draft report will
be considered the final report unless comments and suggestions are
provided by NMFS within 60 days of its receipt of the draft report.
Estimates of Take by Harassment for the Mid-Atlantic Cruises
As described previously (see 68 FR 17909, April 14, 2003) and in
the LDEO application, animals subjected to sound levels [gteqt]160 dB
may alter their behavior or distribution, and therefore might be
considered to be taken by Level B harassment.
The estimates of takes by harassment are based on the number of
marine mammals that may be exposed to seismic sounds [gteqt]160 dB re 1
microPa (rms) by operations with the 20-airgun array and the 2 GI-guns,
during the TAG and ADWBC cruises, respectively. Based on marine mammal
density sightings and effort data collected during a survey of offshore
waters northeast of the Azores by Lens (1991), LDEO used their
estimates of marine mammal density to compute the best (and maximum)
estimates of the number of marine mammals that may be exposed to
received levels [gteqt]160-dB re 1 microPa (rms) (NMFS' current
criterion for onset of Level B harassment). The best estimates of
densities were then multiplied by the linear extent of the proposed
survey effort and by twice the 160-dB radius around the applicable
airgun array. The proposed survey effort is 185 km (100 n.mi.) for the
TAG cruise, and 4329 km (2340 n.mi.) for the ADWBC cruise. The 160-dB
radius for the TAG cruise (20-gun array) is 9000 m (29,529 ft), whereas
that for the ADWBC cruise (2 GI-guns) is 510 m (1673 ft). For large
cetaceans, LDEO used 0.5x the densities seen during the Lens (1991)
survey to calculate the numbers that might be exposed to seismic
sounds, but even this reduced number is likely a high estimate, because
the proposed survey areas are likely less productive, so feeding
aggregations similar to those seen by Lens (1991) are not likely to be
seen. In particular, the two areas where the proposed surveys will be
conducted are farther offshore and likely in less productive waters
than the area surveys northeast of the Azores (Lens 1991). Thus,
densities are likely to be much lower in the two survey areas than in
the Lens (1991) survey area.
Based on this method, tables 3 and 4 of LDEO's application give the
best estimates, as well as maximum estimates, of densities for each
species or species group of cetacean in the two seismic survey areas
during the TAG and ADWBC cruises, respectively, that might be exposed
to received levels [gteqt]160 dB re 1 microPa (rms), and thus
potentially taken by Level B harassment, during seismic surveys in the
proposed study areas of the Mid-Atlantic Ocean. During the TAG cruise,
38 of the marine mammals exposed to sounds [gteqt]160 dB re 1 microPa
(rms) would be endangered species, primarily fin (18) and sperm whales
(15). During the ADWBC cruise, 49 of the marine mammals exposed to
sounds [gteqt]160 dB re 1 microPa (rms) would be endangered species,
primarily fin (24) and sperm whales (20). During both research cruises,
Delphinidae would account for 92 percent of the overall estimate for
potential taking by harassment during each of the two seismic surveys
(i.e., 709 of 772 (TAG) and 943 of 1028 (ADWBC)). While there is no
agreement regarding any alternative to the 160-dB ``take'' criterion
for dolphins exposed to airgun pulses, if only those dolphins exposed
to [gteqt]170 dB re 1 microPa (rms) were considered taken by Level B
harassment, then the best estimate for common dolphins (the most
abundant dolphin in the area) would be 91 rather than 316 during the
TAG cruise, and 144 rather than 419 during the ADWBC cruise. These are
based on the predicted 170-dB radius around the 20- and 2-airgun arrays
(2600 and 175 m (8530 and 574 ft), respectively), and are considered to
be more realistic estimates of the number of each species of delphinid
that may be harassed, given their apparently higher tolerance of low
frequency sound. Therefore, the total number of animals likely to be
harassed is considerably lower than the estimated 772 (TAG cruise)
animals or 1028 (ADWBC cruise) animals.
Conclusions
Effects on Cetaceans
Strong avoidance reactions by several species of mysticetes to
seismic vessels have been observed at ranges up to 6 to 8 km (3.2 to
4.3 nm) and occasionally as far as 20-30 km (10.8-16.2 nm) from the
source vessel. Some bowhead whales in Arctic waters avoided waters
within 30 km (16.2 nm) of the seismic operation. However, reactions at
such long distances appear to be atypical of other species of
mysticetes, and even for bowheads may only apply during migration.
Odontocete reactions to seismic pulses, or at least those of
dolphins, are expected to extend to lesser distances than are those of
mysticetes. Odontocete low-frequency hearing is less sensitive than
that of mysticetes, and dolphins are often seen from seismic vessels.
There are documented instances of dolphins approaching active seismic
vessels. However, dolphins as well as some other types of odontocetes
sometimes show avoidance and/or other changes in behavior when near
operating seismic vessels.
Taking account of the mitigation measures that are planned, effects
on cetaceans are generally expected to be limited to avoidance of the
area around the seismic operation and short-term changes in behavior,
falling within the MMPA definition of ``Level B harassment.'' Reactions
by mysticetes are expected to involve small numbers of individual
cetaceans because few mysticetes occur in the area where seismic
surveys are proposed. For Bryde's whales, LDEO's best estimate is that
1 animal during each of the cruises, which translates to 3 percent of
the North Atlantic population for this species in the area of the TAG
survey, and 1.5 percent of the North Atlantic population for this
species in the area of the ADWBC survey, has the potential to be
exposed to sound levels [gteqt]160 dB re 1 microPa (rms) and
potentially affected. LDEO's best estimate is that 18 (TAG) and 24
(ADWBC) fin whales, both of which are <0.1 percent of the estimated
North Atlantic fin whale population (IWC 2003), will be exposed to
sound levels [gteqt]160 dB re 1 microPa (rms) and potentially affected.
Similarly, only 15 (TAG) and 20 (ADWBC) sperm whales, or approximately
0.1 and 0.2 percent of the estimated North Atlantic sperm whale
population, would receive seismic sounds [gteqt]160 dB. Therefore,
based on the relatively low numbers of marine mammals that will be
exposed at levels £160 dB and the expected impacts at these
levels, NMFS has determined that this action will have a negligible
impact on the affected species or stocks.
Larger numbers of odontocetes may be affected by the seismic
activities, but the populations sizes of most of the species are large
and the numbers potentially affected are small relative to the
population sizes. The best estimate of the total number of odontocetes
that might be exposed to [gteqt]160 dB re 1 microPa (rms) in the
proposed survey areas in the Mid-Atlantic Ocean is 746 for the TAG
cruise, and 991 for the ADWBC cruise. Of these, 709 (TAG cruise) and
943 (ADWBC cruise) are Delphinidae, and of these about 204 (TAG cruise)
and 322 (ADWBC cruise) might be exposed to [gteqt]170 dB. Approximately
316 and 419 common dolphins (the most abundant delphinid in the
proposed survey areas) are expected to be exposed to seismic sounds
[gteqt]160 dB in the TAG and
[[Page 63768]]
ADWBC seismic survey areas, respectively. These figures represent
considerably less than 0.2 and 0.3 percent of the North Atlantic
population of common dolphins, respectively. Of these, 91 and 144,
respectively, might be exposed to [gteqt]170 dB. These figures are much
less than 0.1 percent of the North Atlantic population and the 170-dB
values (91 and 144) are believed to be a more accurate estimate of the
number potentially affected. Smaller numbers of other species of
dolphins will be exposed to seismic sounds [gteqt]160 dB during the
surveys, and the numbers for each species represent considerably less
than 0.1 to 0.7 percent of each population. The numbers that might be
exposed to [gteqt]170 dB are even smaller and represent considerably
less than 0.1 to 0.2 percent of each population; these latter
percentages are believed to be a more accurate estimate of the numbers
potentially affected. Based on the relatively low numbers of marine
mammals that will be exposed at levels [gteqt]160 dB and the expected
impacts at these levels, NMFS has determined that this action will have
a negligible impact on the affected species or stocks.
Altogether, the mitigation measures explained in this document (See
Mitigation) will reduce short-term reactions to disturbance, and
minimize any effects on hearing sensitivity.
Effects on Pinnipeds
Very few if any pinnipeds are expected to be encountered during the
proposed seismic surveys in the Mid-Atlantic Ocean. Most have a coastal
distribution or are distributed along the pack-ice edge. Therefore, it
is unlikely that pinnipeds will be encountered in either study area.
However, if pinnipeds are encountered, they are more likely to be seen
during the ADWBC cruise in the northern Mid-Atlantic than during the
TAG cruise. A few gray seals, which are normally found in coastal areas
might be seen during the ADWBC cruise. In addition, a few vagrant
harbor seals, harp seals, or hooded seals might be encountered. None of
the pinniped species is endangered or depleted.
Because no seismic surveys will take place in coastal and nearshore
areas, the best estimate of the numbers of each of the more common (but
still unlikely) species that might be taken by Level B harassment is no
more than 2 and is most likely 0. For the other less-common species the
best estimate is zero. If pinnipeds are encountered, the proposed
seismic activities would have, at most, a short-term effect on their
behavior and no long-term impacts on individual seals or their
populations. Responses of pinnipeds to acoustic disturbance are
variable, but usually quite limited. Effects are expected to be limited
to short-term and localized behavioral changes falling within the MMPA
definition of Level B harassment. Therefore, based on these effects and
the relatively low numbers of pinniped species that may be exposed,
NMFS has determined that this action will have a negligible impact on
the affected species or stocks.
Determinations
Based on the information contained in the LDEO application, the NSF
EA, the September 17, 2003, proposed authorization notice (68 FR 54421)
and this document, NMFS has determined that conducting two marine
seismic surveys, one each by the Ewing and the Knorr, in the Mid-
Atlantic Ocean by LDEO would result in the harassment of small numbers
of marine mammals; would have no more than a negligible impact on the
affected marine mammal species or stocks; and would not have an
unmitigable adverse impact on the availability of stocks for
subsistence uses. This activity will result, at worst, in a temporary
modification in behavior by affected species of marine mammals. While
behavioral modifications may be made by these species as a result of
seismic survey activities, this behavioral change is expected to result
n no more than a negligible impact on the affected species. Also, while
the number of actual incidental harassment takes will depend on the
distribution and abundance of marine mammals in the vicinity of the
survey activity, the number of potential harassment takings is
estimated to be small. In addition, no take by injury and/or death is
anticipated, and the potential for temporary or permanent hearing
impairment is low and will be avoided through the incorporation of the
mitigation measures mentioned in this document and required under the
IHA. For these reasons therefore, NMFS has determined that the
requirements of section 101(a)(5)(D) of the MMPA have been met and the
authorization can be issued.
Endangered Species Act (ESA)
NMFS has concluded consultation under section 7 of the ESA on NMFS'
issuance of an IHA to take small numbers of marine mammals, by
harassment, incidental to conducting two oceanographic seismic surveys
in the Mid-Atlantic Ocean by LDEO. The consultation concluded with a
biological opinion that this action is not likely to jeopardize the
continued existence of marine species listed as threatened or
endangered under the ESA. No critical habitat has been designated for
these species in the equatorial Pacific Ocean; therefore, none will be
affected. A copy of the Biological Opinion is available upon request
(see ADDRESSES).
National Environmental Policy Act (NEPA)
On July 30, 2003, the NSF made a determination, based on
information contained within its Environmental Assessment (EA), that
implementation of the subject action is not a major Federal action
having significant effects on the environment within the meaning of
Executive Order 12114. NSF determined therefore, that an environmental
impact statement would not be prepared. On September 17, 2003 (68 FR
54421), NMFS noted that the NSF had prepared an EA for the Mid-Atlantic
surveys and made it available upon request. In accordance with NOAA
Administrative Order 216-6 (Environmental Review Procedures for
Implementing the National Environmental Policy Act, May 20, 1999), NMFS
has reviewed the information contained in NSF's EA and determined that
the NSF EA accurately and completely describes the proposed action
alternative, reasonable additional alternatives, and the potential
impacts on marine mammals, endangered species, and other marine life
that could be impacted by the preferred alternative and the other
alternatives. As a result, NMFS has determined that it is not necessary
to issue either a new EA, supplemental EA or an environmental impact
statement for the issuance of an IHA to LDEO for this activity.
Therefore, based on this review and analysis, NMFS is adopting the NSF
EA under 40 CFR 1506.3. A copy of the NSF EA for this activity is
available upon request (see ADDRESSES).
Authorization
NMFS has issued an IHA to take small numbers of marine mammals, by
harassment, incidental to conducting two marine seismic surveys, one by
the Ewing and one by the Knorr, in the Mid-Atlantic Ocean to LDEO for a
1-year period, provided the mitigation, monitoring, and reporting
requirements described in this document and the IHA are undertaken.
Dated:October 23, 2003.
Phil Williams,
Acting Director, Office of Protected Resources, National Marine
Fisheries Service.
[FR Doc. 03-28129 Filed 11-7-03; 8:45 am]
BILLING CODE 3510-22-S
![[logo] US EPA](http://www.epa.gov/epafiles/images/logo_epaseal.gif){kind=logo}