Incidental Takes of Marine Mammals During Specified Activities; Marine Geophysical Survey in Southeast Asia, March-July 2009, 41260-41322 [E9-19459]
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Federal Register / Vol. 74, No. 156 / Friday, August 14, 2009 / Notices
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XL89
Incidental Takes of Marine Mammals
During Specified Activities; Marine
Geophysical Survey in Southeast Asia,
March–July 2009
AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; issuance and
modification of an incidental take
authorization.
SUMMARY: In accordance with the
Marine Mammal Protection Act
(MMPA) regulations, notification is
hereby given that NMFS issued and
modified an Incidental Harassment
Authorization (IHA) to Lamont-Doherty
Earth Observatory (L–DEO), a part of
Columbia University, for the take small
numbers of marine mammals, by
harassment, incidental to conducting a
marine seismic survey in Southeast (SE)
Asia during March–July 2009.
DATES: Effective March 31, 2009,
through August 20, 2009.
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
20910–3235 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 online 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 Ken Hollingshead,
Office of Protected Resources, NMFS,
301–713–2289.
SUPPLEMENTARY INFORMATION:
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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 to allow,
upon request, the incidental, but not
intentional, taking of marine mammals
by United States (U.S.) citizens who
engage in a specified activity (other than
commercial fishing) within a specified
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geographical region if certain findings
are made and either regulations are
issued or, if the taking is limited to
harassment, a notice of a proposed
authorization is provided to the public
for review.
Authorization for incidental taking
shall be granted if NMFS finds that the
taking will have a negligible impact on
the species or stock(s), will not have an
unmitigable adverse impact on the
availability of the species or stock(s) for
subsistence uses (where relevant), and if
the permissible methods of taking and
requirements pertaining to the
mitigation, monitoring and reporting of
such takings are set forth. NMFS has
defined ‘‘negligible impact’’ in 50 CFR
216.103 as ‘‘ * * * an impact resulting
from the specified activity that cannot
be reasonably expected to, and is not
reasonably likely to, adversely affect the
species or stock through effects on
annual rates of recruitment or survival.’’
Section 101(a)(5)(D) of the MMPA
established an expedited process by
which citizens of the U.S. can apply for
an authorization 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 on any
proposed authorizations for the
incidental harassment of small numbers
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 October 27, 2008, NMFS received
an application from L–DEO for the
taking, by Level B harassment only, of
small numbers of marine mammals
incidental to conducting, under
cooperative agreement with the National
Science Foundation (NSF), a marine
seismic survey in SE Asia. The funding
for the Taiwan Integrated Geodynamics
Research (TAIGER) survey is provided
by the NSF. The proposed survey will
encompass the area 17°30′–26°30′ N,
113°30′–126° E within the Exclusive
Economic Zones (EEZ) of Taiwan,
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Japan, and the Philippines, and on the
high seas, and is scheduled to occur
from March 31 to July 20, 2009. Some
minor deviation from these dates is
possible, depending on logistics and
weather.
Taiwan is one of only a few sites of
arc-continent collision worldwide; and
one of the primary tectonic
environments for large scale mountain
building. The primary purpose of the
TAIGER project is to investigate the
processes of mountain building, a
fundamental set of processes which
plays a major role in shaping the face of
the Earth. The vicinity of Taiwan is
particularly well-suited for this type of
study, because the collision can be
observed at different stages of its
evolution, from incipient, to mature,
and finally to post-collision.
As a result of its location in an
ongoing tectonic collision zone, Taiwan
experiences a great number of
earthquakes, most are small, but many
are large and destructive. This project
will provide a great deal of information
about the nature of the earthquakes
around Taiwan and will lead to a better
assessment of the earthquake hazards in
the area. The information obtained from
this study will help the people and the
earthquake hazards in the area. The
information obtained from this study
will help the people and government of
Taiwan to better prepare for future
seismic events and may thus mitigate
some of the loss of life and economic
disruptions that will inevitably occur.
The action is planned to take place in
the territorial seas and EEZ’s of foreign
nations, and will be continuous with the
activity that takes place on the high
seas. NMFS does not authorize the
incidental take of marine mammals in
the territorial seas of foreign nations, as
the MMPA does not apply in those
waters. However, NMFS still needs to
calculate the level of incidental take in
territorial seas as part of the analysis
supporting issuance of an IHA in order
to determine the biological accuracy of
the small numbers and negligible
impact determination.
Description of the Specified Activity
The planned survey will involve one
source vessel, the R/V Marcus G.
Langseth (Langseth), which will occur
in SE Asia. The Langseth will deploy an
array of 36 airguns (6,600 in3) as an
energy source at a tow depth of 6–9 m
(20–30 ft). The receiving system will
consist of a hydrophone streamer and
approximately 100 ocean bottom
seismometers (OBSs). The Langseth will
deploy an 8 km (5 mi) long streamer for
most transects requiring a streamer;
however, a shorter streamer (500 m to 2
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Federal Register / Vol. 74, No. 156 / Friday, August 14, 2009 / Notices
km or 1,640 ft to 1.2 mi) will be used
during surveys in Taiwan (Formosa)
Strait. As the airgun array is towed
along the survey lines, the hydrophone
streamer will receive the returning
acoustic signals and transfer the data to
the on-board processing system. The
OBSs record the returning acoustic
signals internally for later analysis. The
OBSs to be used for the TAIGER
program will be deployed and retrieved
numerous times by a combination of 4
or 5 Taiwanese support vessels, as well
as the Langseth. The Langseth will also
retrieve 20 OBSs that were deployed in
the study area during previous years to
record earthquake activity.
Approximately 100 OBSs will be
deployed during the survey. OBSs will
likely be deployed and retrieved by the
Langseth as well as a combination of 4
to 5 Taiwanese vessels. The Taiwanese
vessels to be used include two 30 m
(98.4 ft) vessels (the R/V Ocean
Researcher 2 and the R/V Ocean
Researcher 3) and two vessels greater
than 60 m (196.8 ft) in length (R/V
Fisheries Research I and the Navy ship
Taquan). The R/V Ocean Research I
may also be used if the Langseth is not
used to deploy OBSs. The OBS
deployment spacing will vary
depending on the number of
instruments available and shiptime. The
nominal spacing is 15 km (9.3 mi), but
this will vary from as little as 5 km (3.1
mi) to perhaps as much as 25 km (15.5
mi). The OBSs will be deployed and
recovered several (2 to 4) times. 60 of
the 100 OBSs may be deployed from the
Langseth. All OBSs will be retrieved at
the end of the study.
Up to 3 different types of OBSs may
be used during the 2009 program. The
Woods Hole Oceanographic Institution
(WHOI) ‘‘D2’’ OBS has a height of
approximately 1 m (3.3 ft) and a
maximum diameter of 50 cm. The
anchor is made of hot-rolled steel and
weighs 23 kg (50.7 lbs). The anchor
dimensions are 2.5 x 30.5 x 38.1 cm.
The LC4x4 OBS from the Scripps
Institution of Oceanography (SIO) has a
volume of approximately 1 m3 (3.3 ft2),
with an anchor that consists of a large
piece of steel grating (approximately 1
m2 or 3.3 ft2). Taiwanese OBSs will also
be used; their anchor is in the shape of
an ‘x’ with dimensions of 51–76 cm2
(1.7–2.5 ft2). Once the OBS is ready to
be retrieved an acoustic release
transponder interrogates the OBS at a
frequency of 9–11 kHz, and a response
is received at a frequency of 9–13 kHz.
The burn wire release assembly is then
activated, and the instrument is released
from the anchor to float to the surface.
The seismic survey as described in
the Federal Register notice (73 FR
78294, December 22, 2008) for the
proposed IHA was 15,902 km (9,881 mi)
in length. After public comment, L–DEO
revised the tracklines so that the seismic
survey consists of approximately 14,515
km (9,019 mi) of transect lines within
the South and East China Seas as well
as the Philippine Sea, with the majority
of the survey effort occurring in the
South China Sea. The total length of the
revised tracklines is approximately 9
percent less than the total length of the
original tracklines. The survey will take
place in water depths ranging from
approximately 25 to 6,585 m (82–21,598
ft), but most of the survey effort
(approximately 84.4 percent) will take
place in water greater than 1,000 m
(3,280 ft), 11.4 percent will take place in
intermediate depth waters (100–1,000 m
or 328–3,280 ft), and 4.2 percent will
occur in shallow depth water (less than
100 m or 328 ft).
All planned geophysical data
acquisition activities will be conducted
by L–DEO with onboard assistance by
the scientists who have proposed the
study. The scientific team consists of Dr.
Francis Wu (State University of New
York at Binghamton) and Dr. Kirk
McIntosh (University of Texas at Austin,
Institute of Geophysics). The vessel will
be self-contained, and the crew will live
aboard the vessel for the entire cruise.
In addition to the operations of the
airgun array, a 12 kHz Simrad EM 120
multibeam echosounder (MBES) and a
3.5 kHz sub-bottom profiler (SBP) will
be operated from the Langseth
continuously throughout the TAIGER
cruise.
Dates, Duration, and Region of Activity
The survey will encompass the area
from approximately 17°30′–26°30′ N,
113°30′–126° E within the EEZs of
Taiwan, Japan, and the Philippines. The
vessel will approach mainland Taiwan
within 5.2 km (3.2 mi) and mainland
China within 116 km (72 mi). The vessel
will approach within 3.7 km (2.3 mi)
and 105 km (65 mi) of islands off the
coast of Taiwan and China, respectively.
The closest approach to the Ryuku
Islands and Okinawa Islands will be
51.5 km (32 mi) and approximately 400
km (249 mi), respectively. Although the
survey will occur at least 32 km (29.9
mi) from Luzon, Philippines, survey
lines will take place approximately 28.6
km (17.8 mi) and 8.8 km (5.5 mi) from
the Babuyan and Batan islands,
respectively. Water depths in the survey
area range from approximately 25 to
6,280 m (164–20,603 ft). There are not
seismic lines in less than 50 m (164 ft)
water depth. The closest seismic line to
land is approximately 3.7 km (2.3 mi)
from an island off the east coast of
Taiwan. The TAIGER program consists
of 4 legs, each starting and ending in
Kao-hsiung, Taiwan. The first leg is
expected to occur from approximately
March 31 to April 28, 2009 and will
include the survey lines in the South
China Sea. The second leg is scheduled
for May 3 to June 3, 2009 and will
include survey lines around Taiwan.
The third leg (approximately June 7–14,
2009) will involve OBS recovery by the
Langseth only; no seismic acquisition
will occur during this leg. The fourth
leg, consisting of the survey lines in the
Luzon Strait and Philippine Sea, is
scheduled to occur from June 18 to July
20, 2009. The program will consist of
approximately 103 days of seismic
acquisition. The exact dates of the
activities depend on logistics and
weather conditions.
Safety Radii
L–DEO estimated the safety radii
around their operations using a model
and by adjusting the model results
based on empirical data gathered in the
Gulf of Mexico in 2003. Additional
information regarding safety radii in
general, how the safety radii were
calculated, and how the empirical
measurements were used to correct the
modeled numbers may be found in
NMFS’ proposed IHA notice (73 FR
78294, December 22, 2008) and L–DEO’s
application. Using the modeled
distances and various correction factors,
Table 1 outlines the distances at which
three rms sound levels (190 dB, 180 dB,
and 160 dB) are expected to be received
from the various airgun configurations
in shallow, intermediate, and deep
water depths.
Predicted RMS Distances (m)
Source and volume
Tow depth (m)
Water depth
190 dB
Single Bolt airgun 40 in3 ...................
4 strings 36 airguns 6600 in3 ...........
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*6–9
........................
........................
6–7
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Deep .................................................
Intermediate .....................................
Shallow .............................................
Deep .................................................
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180 dB
12
18
150
220
14AUN2
160 dB
40
60
296
710
385
578
1,050
4,670
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Federal Register / Vol. 74, No. 156 / Friday, August 14, 2009 / Notices
Predicted RMS Distances (m)
Source and volume
Tow depth (m)
Water depth
190 dB
........................
........................
8–9
........................
........................
Intermediate .....................................
Shallow .............................................
Deep .................................................
Intermediate .....................................
Shallow .............................................
330
1,600
300
450
2,182
180 dB
1,065
2,761
950
1,425
3,694
160 dB
5,189
6,227
6,000
6,667
8,000
Table 1. Predicted distances to which sound levels ≥190, 180, and 160 dB re 1 μPa might be received in shallow (<100 m; 328 ft), intermediate (100–1,000 m; 328–3,280 ft), and deep (>1,000 m; 3,280 ft) water from the 36 airgun array, as well as a single airgun, used during the
Central American SubFac and STEEP Gulf of Alaska survey, and planned during the TAIGER SE Asia survey. *The tow depth has minimal effect on the maximum near-field output and the shape of the frequency spectrum for the single 40 in3 airgun; thus, the predicted safety radii are
essentially the same at each tow depth. The most precautionary distances (i.e., for the deepest tow depth, 9m) are shown.
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Because the predictions in Table 1 are
based in part on empirical correction
factors derived from acoustic calibration
of airgun configurations different from
those to be used on the Langseth (cf.
Tolstoy et al., 2004a,b), L–DEO
conducted an acoustic calibration study
of the Langseth’s 36 airgun
(approximately 6,600 in3) array in late
2007/early 2008 in the Gulf of Mexico
(LGL Ltd., 2006). Distances where sound
levels (e.g., 190, 180, and 160 dB re 1
μPa rms) were received in deep,
intermediate, and shallow water will be
determined for various airgun
configurations. Acoustic data analysis is
ongoing and a scientific paper on the
Langseth calibration study is currently
in review for future publication
(Tolstoy, pers. comm.). After analysis,
the empirical data from the 2007/2008
calibration study will be used to refine
the exclusion zones (EZ) proposed
above for use during the TAIGER cruise,
if the data are appropriate and available
for use at the time of the survey.
A more detailed description of the
authorized action, including vessel and
acoustic source specifications, was
included in the proposed IHA notice (73
FR 78294, December 22, 2008).
Comments and Responses
A notice of receipt of the L–DEO
application and proposed IHA was
published in the Federal Register on
December 22, 2008 (73 FR 78294). A
notice extending the public comment
period by 15 days, to February 5, 2009,
due to several Federal holidays, was
published in the Federal Register on
January 16, 2009 (74 FR 2995). During
the comment period, NMFS received
comments from the Marine Mammal
Commission (Commission). NMFS also
received comments from the Center for
Regulatory Effectiveness (CRE), Natural
Resources Defense Council (NRDC) (on
behalf of International Fund for Animal
Welfare, Whale and Dolphin
Conservation Society, Cetacean Society
International [CSI], Animals Asia
Foundation [AAF], New York Whale
and Dolphin Action League, Ocean
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Futures Society, and Jean-Michel
Cousteau), Wild at Heart Legal Defense
Association (WaH) (on behalf of
Changhua County Environmental
Protection Union, Clymene Enterprises,
Green Party Taiwan, Taiwan Friends of
the Global Greens, Leviathan Sciences,
Environment and Animal Society of
Taiwan, Wild Bird Society of Yunlin,
Matsu’s Fish Conservation Union, Blue
Dolphin Alliance, Hong Kong Dolphin
Conservation Society [HKDCS], Dr.
Ellen Hines, Taiwan Sustainable Union,
Jo Marie V. Acebes, APEX
Environmental, Coral Triangle Oceanic
Cetacean Program and IUCN Species
Survival Commission—Cetacean
Specialist Group, Kimberly Reihl,
Changhua Coast Conservation Action,
Ocean Park Corporation, Dr. Bradley
White, Ketos Ecology, CSI, Dr. Wang
Ding, Study Centre for Marine
Conservation, AAF, International
Laboratory for Dolphin Behaviour
Research, Mary Speer, and American
Cetacean Society), CSI, Linking
Individuals for Nature Conservation
(LINC), Humane Society International
(HSI), Dr. John Wang, Eastern Taiwan
Strait Sousa Technical Advisory
Working Group (ETSSTAWG), AAF,
HKDCS, Dr. Robert Brownell, Dr. LienSiang Chou, Dr. Linda Weilgart, Dr. Kirk
McIntosh and Dr. Francis Wu (Dr.
McIntosh and Dr. Wu), Dr. Lemnuel
Aragones, Dr. Joseph Minor and Dr.
Christine Wilson and James Minor and
Susan Wilson (Minor and Wilson), and
a private citizen. The public comments
can be found online at: https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm.
The following are their comments,
and NMFS’ responses.
Extension Requests
Comment 1: Numerous parties
expressed concern regarding L–DEO’s
IHA application under the MMPA to
incidentally harass marine mammals
during a proposed marine geophysical
survey in SE Asia from March–July,
2009, as published in the Federal
Register (73 FR 78294, December 22,
2008). Many interested persons and
organizations requested an extension of
the 30-day public comment period to
allow for the adequate review of lengthy
documents associated with the
proposed IHA and prepare responses.
Response: NMFS considered these
requests during the 30-day public
comment period and published a notice
in the Federal Register (74 FR 2995,
January 16, 2009) extending the public
comment period for the proposed IHA
from January 21 to February 5, 2009.
The 15-day extension is due to the
unique circumstances of the timing of
the publication of the Federal Register
notice (74 FR 2995, January 16, 2009)
relative to several Federal holidays. The
Federal Register notice (74 FR 2995,
January 16, 2009) published three days
before the Christmas holiday, which fell
on Thursday, December 25, 2008. The
following day, Friday, December 26,
2008 was declared a Federal holiday for
executive branch departments and
agencies. New Year’s Day, a Federal
holiday, was the following Thursday,
January 1, 2009. The 15-day extension
was given in recognition of the fact that
the timing of these three holidays led
many workers to be away for much of
the two-week period and some nongovernment organizations closed their
offices during that period. NMFS is also
aware that the proposed action was for
a new geographical area rather than a
renewal of a prior action, where the
associated documents are lengthy and
would likely not be familiar to many
interested parties. NMFS believes that a
30-day comment period with a 15-day
extension (for a total of 45 days) is more
than an adequate time period for the
public to address concerns and submit
comments.
General Comments
Comment 2: The CRE objects to the
statement in the proposed IHA (73 FR
78303, December 22, 2008) on page
78303, column one, paragraph three,
that states: ‘‘However, controlled
exposure experiments in the Gulf of
Mexico indicate that foraging behavior
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was altered upon exposure to airgun
sound (Jochens et al., 2006).’’ CRE states
that this statement is misleading, and
does not accurately reflect the
underlying data, and it is not based on
the most recent assessment of those
data. NMFS’ statement cites a 2006
Sperm Whale Seismic Study (SWSS) in
the Gulf of Mexico Report which
discusses data on foraging behavior and
avoidance movements of seven tagged
sperm whales in the Gulf of Mexico
during exposure to airguns. The CRE
requests that NMFS cite the final 2008
Synthesis Report on SWSS which
cautions that the ‘‘* * * sample size of
seven animals that conducted foraging
dives during exposure was too small to
provide definitive results * * * the
power of the test to detect small changes
in foraging success was low, and no
conclusions on the biological
significance of these effects for an
individual animal or for the populations
can be made from the data sets
available.’’
Response: As CRE points out in their
letter, L–DEO acknowledges in their
application (see Section VI, page 37)
that seismic energy alters sperm whale
foraging behavior. NMFS acknowledges
the commentor’s interpretation of 2006
SSWS. However, after reviewing the
2008 Synthesis Report, NMFS believes
that the following statement: ‘‘* * *
sample size of 7 animals conducted
foraging dives during exposure was too
small to provide definitive results * * *
the power of the test to detect small
changes in foraging success was low and
no conclusions on the biological
significance of these effects for an
individual animal or for the population
can be made from the data sets
available,’’ refers to having the
statistical power to detect small changes
in foraging success. Conversely, page
264 of the 2008 Synthesis Report states
the following: ‘‘* * * Our data seem to
indicate that airgun exposure—even at
low exposure levels observed in this
experiment—can result in large
reductions in foraging rate for some
individual sperm whales.’’ Therefore,
the proposed IHA notice statement that
data indicated alterations in foraging
behavior, is supported by one of the
conclusions discussed in the 2008
Synthesis Report. NSF and L–DEO
presented this study as one of several
pieces of information that relate to this
topic. Though the commenter has
presented an alternate interpretation of
the data related to foraging behavior,
NMFS finds that the EA provides
sufficient analysis of the available data
and the information is not such that
NMFS’ findings.
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Comment 3: The Commission is
concerned that most of the issues raised
in its letter have been raised before and,
to their knowledge, little is being done
to resolve them. The Commission
believes that the action agency and
contractor should bear primary
responsibility for carrying out the
studies needed to reduce the existing
uncertainty and that the authorizing and
oversight agencies have a degree of
responsibility as well.
Response: NMFS has responded to the
best of its ability regarding all of the
Commission’s concerns on various
issues during the public comment
process.
Comment 4: The Commission is
concerned that the opportunity for
scientists, conservationists, and other
interested parties from other countries
to comment on research activities to be
conducted by U.S. organizations in
foreign waters. Scientists,
conservationists, and others are
generally unfamiliar with the
procedures for permit review and
authorization in the U.S. but may have
a good understanding of the natural
history and vulnerability of potentially
affected species. The Commission
believes that they should be provided
with opportunities to contribute to the
evaluation of the potential effects of
seismic studies in the context of all
other factors that may be affecting these
species. If U.S. scientists and
institutions are to engage in research
activities in the waters of other
countries, it stands to reason that our
system of review should include
sufficient opportunities for foreign
parties to comment on potential effects.
This might be accomplished in any
number of ways, such as extending the
comment period to give them additional
time to comment and promoting
interaction between the research
organization and concerned parties from
other countries. The Commission
believes such participation is
appropriate and, in the long run, will
facilitate international cooperation on
conservation issues, more informed
comments, and more risk-averse
research methods and mitigation
procedures.
Response: NMFS agrees with the
Commission’s comments. NMFS
extended the 30 day public comment for
the proposed IHA by an additional 15
days to accommodate requests from the
public. See Extension Request above.
Comment 5: Dr. McIntosh and Dr. Wu
have provided some comments about
the nature and significance of our
project and also try to allay some of the
expressed concerns. As an introductory
statement, the research Dr. McIntosh
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and Dr. Wu plan targets fundamental
Earth processes that remain
inadequately understood; this includes
topics such as the growth and
composition of continents and the
fundamental processes of building
mountains. Dr. McIntosh and Dr. Wu
choose to do this research in the Taiwan
region because it is the best location, of
only a few places globally, where we
can study the collision of an oceanic
island chain with a continent.
Response: NMFS acknowledges Dr.
McIntosh and Dr. Wu’s comments.
Comment 6: Dr. McIntosh and Dr. Wu
state that as for marine mammal safety,
the community of marine mammal
biologists can be assured that their
project is not a reckless intrusion into
the marine habitat of endangered
species. In fact, detailed studies have
been conducted regarding the possible
impacts of this project on marine
mammal populations.
Response: NMFS acknowledges Dr.
McIntosh and Dr. Wu’s comments.
NMFS expects the principal scientists to
abide by the requirements described in
the IHA issued to L–DEO. After issuance
of the proposed IHA, L–DEO negotiated
with the project’s principal scientists to
modify the cruise plan and adopt more
precautionary mitigation measures for
purposes of marine mammal safety in
the study area.
Comment 7: Dr. McIntosh and Dr. Wu
state that they expect to produce the
most comprehensive subsurface images
of the rapidly rising Taiwan mountains
with their data. These images, along
with seismicity recorded by L–DEO’s
arrays, will form a greatly enhanced
basis for evaluating earthquake and
tsunami potentials of Taiwan and can
thus be used to improve the safety and
security of the human population at risk
to these phenomena.
Response: NMFS acknowledges Dr.
McIntosh and Dr. Wu’s comments.
Comment 8: CSI states that the IHA
application and EA are similar in many
respects to previous L–DEO EA’s. The
response, however, is not. The response
to this authorization request will prove
to be unique, a potential watershed in
the manner all future seismic surveys
should be critiqued by the scientific
community. To be helpful, CSI has
attached some relevant expert reviews
to their comments, even if they are
duplicated by others, to ensure that
NMFS has the opportunity to include
them in the deliberative process. The
expert level of opinion and proof
stimulated by the IHA application and
EA challenges previous assumption and,
CSI hopes, will stimulate adequate,
directed research to enable appropriate
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mitigations to satisfy various laws,
including the MMPA.
Response: NMFS received numerous
comments from interested parties on L–
DEO’s proposed IHA for a marine
geophysical survey in SE Asia, March to
July 2009. NMFS acknowledges CSI’s
and other interested parties’ comments
on the proposed IHA and EA during the
public comment period. After the
issuance of the proposed IHA, L–DEO
modified the cruise plan and adopted
more precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the monitoring
and mitigation measures described in
the IHA will have a negligible impact on
the affected species or stocks of marine
mammals in the study area.
L–DEO and NSF have formally
consulted with NMFS’ Permits,
Conservation, and Education Division
under the MMPA regarding the IHA and
NMFS’ Endangered Species Division
regarding a Biological Opinion under
Section 7 of the ESA for the marine
geophysical survey in SE Asia. NMFS
believes L–DEO and NSF have satisfied
their responsibilities under the laws of
the MMPA and ESA.
Comment 9: CSI states that the MMPA
only authorizes the lethal taking of
marine mammals under extraordinary
circumstances that do not apply to the
scientific research proposed by this
project. In the opinion of experts, as
expressed in the attachments,
mortalities are likely. How can NMFS
believe that all these experts are wrong,
or that associated mortalities would not
violate the MMPA? CSI urges NMFS to
apply these experts comments to the EA
and IHA application deficiencies and to
require that the L–DEO proposal address
them in the only legal format available
to them, an application for a LOA under
MMPA Section 101(a)(5)(A–C).
Because the L–DEO’s geophysical
research will have an incidental impact
on marine mammals that experts predict
will include mortalities and even
extirpation it must apply for a letter of
authorization under MMPA section
101(a)(5)(A–C).
Response: While an authorization for
taking marine mammals by mortality
cannot be authorized under Section
101(a)(5)(D) of the MMPA, those
paragraphs do authorize taking by Level
A harassment. Level A harassment
means any act of pursuit, torment, or
annoyance which has the potential to
injure a marine mammal or a marine
mammal stock in the wild. While it is
true that an injury can be so severe that
it later may result in mortality, the
MMPA does not preclude issuance of an
authorization under Section 101(a)(5)(D)
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of the MMPA for activities that have the
potential to cause injury. However, as
NMFS shows in this document morality
and serious injury are not anticipated to
occur during this seismic survey cruise
due to implementation of mitigation
measures (e.g., ramp-up, power-down,
shut-down, temporal and spatial
avoidance, procedures for species of
particular concern, passive acoustic and
visual monitoring, and quiet acoustic
periods). Nor is take by injury, serious
injury, or mortality authorized.
Therefore, issuance of an IHA is
appropriate. Monitoring and mitigation
measures are discussed later in this
document.
Comment 10: CSI states it is a relief
to find so many experts willing to
contribute their knowledge and
experience to this process. They do a far
better job than CSI or any NGO could of
addressing the specific flaws found in
this L–DEO IHA request. While some of
these same flaws in previous L–DEO
requests have been addressed, they may
have been more easily dismissed by
NMFS because very few were from
world authorities and scientific experts.
This time the experts have participated
directly, and cannot be dismissed.
Response: NMFS acknowledges CSI’s
comments and considers all relevant
public comments before making a
determination on the issuance of the
IHA. After issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures in
the study area. NMFS believes that L–
DEO’s revised survey as well as the
implementation of the required
monitoring and mitigation described in
the IHA will have a negligible impact on
the affected species or stocks of marine
mammals in the study area.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures in
the study area. NMFS believes that L–
DEO’s revised survey as well as the
implementation of the monitoring and
mitigation measures described in the
IHA will have a negligible impact on the
affected species or stocks of marine
mammals in the study area.
Comment 11: CSI states that the intent
of LGL’s comment is to manipulate
NMFS into a fast and uncritical
decision. By law, the schedules, as well
as the scientific and economic values of
this project, remain irrelevant to the
scope of NMFS’ deliberations on the
fitness of the proposal.
Response: 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
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comment period on any proposed
authorizations for the incidental
harassment of small numbers of marine
mammals. Within 45 days of the close
of the comment period, NMFS must
either issue or deny issuance of the
authorization. NMFS received an IHA
application from L–DEO on October 27,
2008. NMFS published a notice for the
proposed IHA in the Federal Register
on December 22, 2008 (73 FR 78294). A
notice on the 15-day extension of the
comment period for the proposed IHA
was published on January 16, 2009.
NMFS issued an IHA to L–DEO on
March 31, 2009 and amended the IHA
on May 1, 2009.
After issuance of the proposed IHA,
L–DEO modified the cruise plan and
adopted more precautionary monitoring
and mitigation measures in the study
area. NMFS believes that L–DEO’s
revised survey as well as the
implementation of the required
monitoring and mitigation described in
the IHA will have a negligible impact on
the affected species or stocks of marine
mammals in the study area. See L–
DEO’s Supplemental EA.
Comment 12: CSI states that it is well
aware that the L–DEO, NSF, and other
project supporters represent powerful
influences that NMFS must respect.
However, CSI trusts that these rational
influences also recognize the
overwhelming need to define and
mitigate anthropogenic affects on the
marine environment, with their rapidly
accelerating influences on the planet
and eventually human societies. Is it
necessary to do significant, irrevocable
damage to marine life in order to
understand geophysical processes?
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures in the study area.
NMFS believes that L–DEO’s revised
survey as well as the implementation of
the required monitoring and mitigation
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area.
On March 31, 2009, NMFS prepared
a Finding of No Significant Impact for
L–DEO’s marine geophysical survey in
SE Asia. NMFS determined that the
issuance of an IHA for the take, by
harassment, of small numbers of marine
mammals incidental to L–DEO’s March–
July, 2009, seismic survey in SE Asia
will not significantly impact the quality
of the human environment.
Comment 13: CSI states that in lieu of
such loft concerns economic efficiency
is an excellent rationale for increased
support of appropriate science to
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determine adequate mitigations.
Without better science this and future
proposals will face further challenges
that will cause delays in the L–DEO
schedule that are likely to have
economic consequence. The time and
financial loss is neither the fault of the
process or the responsibility of NMFS.
Why not do the job responsibly?
Response: NMFS acknowledges CSI’s
comments. An authorization for
incidental taking of marine mammals
shall be granted if NMFS finds that the
taking will have a negligible impact on
the species or stock(s), will have an
unmitigable adverse impact on the
availability of the species or stock(s) for
subsistence uses (where relevant), and if
the permissible methods of taking and
requirements pertaining to the
mitigation, monitoring, and reporting of
such takings are set forth.
After issuance of the proposed IHA,
L–DEO modified the cruise plan and
adopted more precautionary monitoring
and mitigation measures in the study
area. NMFS believes that L–DEO’s
revised survey as well as the
implementation of the required
monitoring and mitigation described in
the IHA will have a negligible impact on
the affected species or stocks of marine
mammals in the study area. NMFS and
the applicant (L–DEO) have fulfilled
their responsibilities under the MMPA
and ESA for the issuance of the subject
IHA.
Comment 14: CSI states that the
fundamental point of CSI’s comment
and many others, is that this L–DEO
project does not qualify for an IHA,
according to the criteria at
www.nmfs.noaa.gov/pr/permits/
incidental.htm. The fact that previous
L–DEO projects received IHAs does not
provide a precedent under which this
proposal also should receive an IHA,
because no matter how NMFS
rationalized those past IHAs this
proposal is different, different in scale,
scope, and expertise represented by the
formal comments and less public
complaints it has generated from
scientific world authorities and regional
and species experts. If these people had
been consulted by LGL, the inadequate
EA and request would never have been
submitted for an IHA. The original
intent of the IHA process was to
expedite some requests, not all requests.
Not this request.
Response: NMFS disagrees with CSI’s
comments. L–DEO’s marine geophysical
survey in SE Asia, March to July 2009,
qualifies for an IHA according to the
criteria on the NMFS Office of Protected
Resources Incidental Take
Authorizations Web site. Portions of L–
DEO’s project occurs on the high seas,
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which is applicable to the MMPA and
ESA. Section 101(a)(5)(D) of the MMPA
established an expedited process by
which citizens of the U.S. can apply for
an authorization to incidentally take
small numbers of marine mammals by
harassment.
After issuance of the proposed IHA,
L–DEO modified the cruise plan and
adopted more precautionary monitoring
and mitigation measures in the study
area. NMFS believes that L–DEO’s
revised survey as well as the
implementation of the required
monitoring and mitigation described in
the IHA will have a negligible impact on
the affected species or stocks of marine
mammals in the study area.
Comment 15: CSI states that there is
little knowledge available for most of
the species that inhabit the waters of SE
Asia. Even the most basic knowledge
about the presence/absence of species is
incomplete. Only a small proportion of
the large expanse of sea in the region
(and mostly coastal waters) has been
surveyed systematically for marine
mammals. Few estimates of abundance
or distribution exists for SE Asian
marine mammals an in most cases, this
information is for a limited region, often
bounded by political rather than
biological borders. What little is known
clearly shows the region to be an area
with a high diversity of marine mammal
(and other marine) species.
Response: NMFS agrees that the SE
Asia region is likely to have a high
diversity of marine mammal species and
that impacts on marine mammals
should be assessed on the population or
stock unit level whenever possible. L–
DEO’s IHA application provides
information on stock abundance in SE
Asia (when available), larger water
bodies (such as the North Pacific
Ocean), and the Eastern Tropical Pacific
Ocean (if data was unavailable). NMFS
believes that these data are the best
scientific information available for
estimating impacts on marine mammal
species and stocks. However, Congress
recognized that information on marine
mammal stock abundance may not
always be satisfactory. When
information is lacking to define a
particular population or stock of marine
mammals then impacts are to be
assessed with respect to the species as
a whole (54 FR 40338, September 29,
1989). See relevant discussions
throughout this document and L–DEO’s
Supplemental EA.
Comment 16: CSI states that the study
area is a region where marine mammals
are facing a myriad of serious threats
that have made the continued existence
of several marine mammal populations
and possibly some species uncertain
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(note: some of the same threats and
activities have resulted in the recent
‘functional extinction’ of the baiji
(Turvey et al. 2007), which is endemic
to the Yangtze River of China).
Response: L–DEO’s EA acknowledges
that there are numerous threats to
cetaceans in SE Asia including vessel
traffic, habitat loss, oil and gas industry,
pollution, fisheries, and hunting.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures.
NMFS believes that L–DEO’s revised
survey as well as the implementation of
the required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area. See L–DEO’s EA and
Supplemental EA.
Comment 17: CSI states that all small
cetaceans in Taiwanese waters are
threatened by fishermen using handharpoons, bycatch in fishing gear, and
noise. Those that inhabit coastal waters
of western Taiwan also face habitat
degradation, pollution, and possibly
prey reduction.
Response: NMFS does not regulate
activities (including fishing) in
Taiwanese waters. L–DEO’s EA
discusses direct and indirect effects on
marine mammals. The numerous threats
to cetaceans in SE Asia include vessel
traffic, habitat loss, oil and gas industry,
pollution, fisheries, and hunting.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures.
NMFS believes that L–DEO’s revised
survey as well as the implementation of
the required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area.
Comment 18: CSI states that some
marine mammals have been reduced to
numbers so low that even minimal
‘takes’ will have a large impact on the
remaining population.
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area.
Comment 19: CSI states that a number
of marine mammals are discussed in
their comments to NMFS based on what
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is known about their biology,
conservation status and threats in the
region. This does not imply other
marine mammals that are not
specifically discussed in detail are
‘‘safer’’ from the seismic surveys, in
most cases, too little information is
available to understand the impacts,
which may be as great as or greater than
the marine mammals discussed in detail
in their comments to NMFS.
Response: NSF’s and L–DEO’s IHA
application, EA, and Supplemental EA
sufficiently discusses the marine
mammals species and the possible
impacts from seismic surveys in the SE
Asia region. After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that the implementation of the required
monitoring and mitigation measures
will result in a negligible impact on
affected species and stocks of marine
mammals in the study area.
Comment 20: ETSSTAWG states that
it should be noted that many seismic
surveys are conducted in the Taiwan
region every year without requesting
IHAs. The actions of private oil and gas
companies within the EEZ’s of other
countries is beyond the jurisdiction of
the MMPA, thus they need no such U.S.
authorizations. However, this means
that L–DEO could become a scapegoat
for all survey operation in the region,
purely because they have to apply for
authorization, as they will clearly be
operating partly on the high seas (and
thus fall under MMPA jurisdiction) and
as they have government funding. This
is acknowledged, but until such time as
NMFS enforcement confirms the
locations and tracks of every survey
undertaken globally this situation is
unlikely to change.
Response: NMFS is aware of seismic
surveys and other activities undertaken
worldwide that occur (that may result in
incidental takes of marine mammals)
without requesting IHAs or LOAs.
NMFS may grant IHAs upon request by
U.S. citizens who engage in a specified
activity (other than commercial fishing)
within a specified geographical region.
L–DEO and NSF are considered U.S.
citizens under the MMPA. The MMPA
applies to U.S. citizens in U.S. waters,
and the high seas, but does not apply or
authorize the incidental take of marine
mammals in the territorial seas of
foreign nations. The MMPA does not
apply to non-U.S. citizens, unless they
are conducting a specified activity
(other than commercial fishing) that
may result in incidental takes of marine
mammals in U.S. waters. NMFS can
refer reports of possible violations of the
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MMPA and this subject IHA issued to
L–DEO to NOAA Enforcement for
investigation.
The IHA is valid only for the
Langseth’s activities associated with
seismic survey operations that are
specified in L–DEO’s EA, Supplemental
EA, and IHA application. L–DEO is
required to comply with the IHA and
the terms and conditions of the
Incidental Take Statement
corresponding to NMFS’ Biological
Opinion. L–DEO and NSF will be
required to reinitiate consultation with
NMFS if the identified action is
subsequently modified in a manner that
causes an effect that was not considered
during the analysis for making the
necessary determinations for the
issuance of the IHA. L–DEO is required
to submit a draft report on all activities
and monitoring results to the Office of
Protected Resources, NMFS, within 90
days of the completion of the Langseth’s
cruise in SE Asia. The report must
contain and summarize information
stated in the IHA issued to L–DEO.
Comment 21: WaH is aware that this
L–DEO survey proposal is one of a very
small number of requests for
authorization for geophysical surveys
while other user groups, including the
oil and gas industry, are not carrying out
such EAs or are not subjected to public
scrutiny in this way. Rather than
allowing the focus to be limited to
geological surveys such as L–DEO’s,
WaH recommends that measures be
taken to ensure that all future marine
seismic surveys (whether of an
academic or commercial nature) are
made subject to the same level of
scrutiny and transparency, such as by
requiring EAs or EISs to be submitted
for professional and public review and
with all relevant documents (including
post-survey reports and relevant local
permits, authorizations and licenses)
being made publicly available.
Response: All applications submitted
to NMFS are subject to public comment
periods. During the public comment
period, their NEPA documents and
incidental take authorization
applications are available on the NMFS
Web site (https://www.nmfs.noaa.gov/pr/
permits/incidental.htm) and are
reviewed by the Commission. NMFS
does not force an agency or other
organization to apply for and consult on
an incidental take authorization under
the MMPA.
General Opposition
Comment 22: A private citizen
questioned why this research was being
conducted in SE Asia. The commenter
also believes the U.S. should not be
doing work in the region.
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Response: Dr. McIntosh and Dr. Wu,
the principal investigators on the
seismic survey, state the primary
purpose of the TAIGER project is to
investigate the fundamental processes of
mountain building, which plays a major
role in shaping the face of the Earth.
Oceanic island chains, or arcs, along
convergent tectonic plate boundaries
result from a process known as
subduction where one of Earth’s
tectonic plates slides beneath another as
they move toward each other. As the
lower plate slides beneath the upper
plate, its trajectory usually steepens
with depth and eventually reaches
depths of several hundred (to greater
than 700) km. The arc is made up of a
chain of volcanoes on the upper plate,
and is typically situated above the point
where the lower plate is at about 100 km
(62 mi) depth. As this process of
subduction and volcanism continues
through time (millions of years) the
crust of the upper plate becomes
thicker, and develops properties more
like continental crust, which is much
thicker and less dense than ocean crust
and allows for land surface above sea
level. The results of many studies
indicates that much of the crust that
forms Earth’s continents was
accumulated through time by island
arcs colliding with continents leaving
remnants of the arcs attached to the
edge of the continents. Despite this
general interpretation, the actual
processes of how this happens,
including growth of collisional
mountain belts and deformation of arc
and continental crust, is poorly
understood and poorly documented.
Ancient collision zones have been
studied, but they have typically
undergone many stages of deformation
and erosion, leaving them difficult to
interpret. Currently active arc-continent
collision zones include Taiwan, Papua
New Guinea, and Timor. Of these active
collisions, Taiwan is currently the most
active. Taiwan is also the most favorable
of these to examine the full spectrum of
processes as a plate boundary changes
from oceanic subduction to arccontinent collision. This transition is a
major target of the TAIGER project
requiring that L–DEO obtain a series of
crustal-scale seismic transects from
south of Taiwan, where subduction is
active, to northern Taiwan, where the
collision has reached mature steady
state.
One of the by-products of the
collision in Taiwan is the generation of
frequent small earthquakes and less
frequent, large, destructive earthquakes.
By using the relatively small signals
from the Langseth source array
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(compared to those generated by nature)
scientists can topographically image the
mountains and thereby localize the
major breaks or faults underneath the
mountains and assess their seismic
potential. In addition to linear arrays of
seismographs, the Langseth signals will
also be recorded, as an integrated
TAIGER acquisition program, on over
200 land seismographs across the island
and 20 OBSs, all of which have been
recording earthquakes. Scientists expect
to produce the most comprehensive
subsurface images of the rapidly rising
Taiwan mountains with L–DEO’s data.
These images, along with seismicity
recorded by L–DEO’s arrays, will form
a greatly enhanced basis for evaluating
earthquake and tsunami potentials of
Taiwan and can thus be used to improve
the safety and security of the human
population at risk to these phenomena.
A previous U.S.-Taiwan project (the
1995 TAICRUST project) demonstrated
the feasibility of the approach to be used
in the TAIGER project, but this project
did not include significant seismic data
acquisition in the Taiwan Strait.
Subsequent analysis showed that
seismic profiles across the Taiwan,
recorded by seismographs in the strait
and on land in Taiwan, are necessary to
determine the crustal structure of the
Taiwan collisional mountain belt. Thus,
the principal scientist’s plans in the
Taiwan Strait are one of the key
elements required for the success of the
TAIGER project.
Comment 23: LINC objects to the IHA
application and states that other local
NGOs have not had time to respond due
to the lack of sufficient notice. LINC is
concerned that NMFS is eager to
approve the L–DEO application and
authorize destructive activities in the SE
Asia region without verifying that L–
DEO has complied with relevant local
conservation laws and regulations. LINC
strongly urges the NMFS to reject the
application of L–DEO until it can be
proven that they have (1) complied with
local laws and regulations, and (2) have
completed a comprehensive
consultation with local governments,
scientists, researchers, and NGOs based
in this region. LINC states that the
approval of the current L–DEO
application, as is, would demonstrate a
clear lack of concern for the
conservation laws, threats, and
environmental protection efforts in this
region.
Response: NMFS believes local NGOs
have had sufficient time to respond to
the proposed IHA published in the
Federal Register. A 30-day comment
period with a 15-day extension (for a
total of 45 days) is more than an
adequate time period for the public to
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address concerns and submit comments.
The NMFS has received numerous
comments from persons and
organizations located nationally and
worldwide. Generally, under the
MMPA, NMFS may authorize the
harassment of small numbers of marine
mammals incidental to an otherwise
lawful activity, provided NMFS finds
that the taking will have a negligible
impact on the species or stock(s), will
not have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (where
relevant), and if the permissible
methods of taking and requirements
pertaining to the mitigation, monitoring
and reporting of such takings are set
forth to achieve the least practicable
adverse impact. L–DEO and NSF have
consulted with the various governments
in the action area. To date, L–DEO and
NSF have received foreign clearance
notices from the governments of the
Philippines, Taiwan, and Japan. See
International Legal Compliance below.
Comment 24: Given the large volume
of evidence for the association between
anthropogenic noise and disturbance in
cetaceans and other marine mammal, a
precautionary approach is surely
required (as recommended by Gordon et
al., 2004). AAF urges NMFS to consider
the application from L–DEO with
information provided, and the findings
and recommendations of the
independent reviews of the Eastern
Taiwan Strait Sousa Technical Advisory
Working Group (ETSSTAWG) and
others, in mind.
Response: NMFS has developed
conservative monitoring, mitigation,
and reporting requirements in order to
reduce the potential effects of
anthropogenic noise on marine
mammals. L–DEO and NSF have
considered the numerous public
comments and revised the seismic
survey described in its IHA application.
L–DEO’s Supplemental EA is in
response to the comments received by
NMFS through the public comment
period associated with the IHA process.
L–DEO considered the
recommendations from several
independent reviewers including
ETSSTAWG. NSF received no direct
public comments on the draft EA during
(or after) the open comment period
November 14, 2008 through December
15, 2008. Included in L–DEO’s
Supplemental EA are a number of
changes to the survey design that were
made by L–DEO to address specific
comments, some received by a number
of individuals and agencies, and to
enhance measures already included in
the original documents to mitigate
effects of the proposed survey on marine
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mammals. NMFS has made its necessary
determinations based on L–DEO’s
revised seismic survey and
Supplemental EA.
Comment 25: Several commenters
requested that NMFS deny issuing the
IHA to L–DEO. They questioned: (1) The
adequacy of L–DEO’s scientific research
and lack of consultation with local
experts; (2) the survey’s potential to
expose ETS humpback dolphins to
received levels of 180 dB re 1 μPa (rms)
which they believed could cause
permanent physiological damage, thus
constituting at a minimum Level A
harassment; (3) the number of ETS
humpback dolphins that L–DEO
proposed to harass, stating that the
requested take of ETS humpback
dolphins to be harassed was likely to
exceed a sustainable level of take for the
population; (4) the adequacy of the
monitoring and mitigation measures for
endangered or cryptic species that may
be vulnerable to noise impacts (e.g., ETS
humpback dolphin and finless
porpoise); (5) the timing of the surveys
and their impacts on migration routes;
(6) biased and non-precautionary
assumptions; and (7) the cumulative
effects analyses in the EA.
Response: NMFS disagrees with the
commenters’ argument that NMFS
should have denied L–DEO’s
application for an IHA.
(1) NMFS is charged with issuing
IHAs for otherwise lawfully activity. L–
DEO’s research is otherwise lawful.
NMFS opened the proposed IHA to
public comment. L–DEO plans to
conduct the seismic survey along the
Taiwan arc-continental collision in the
China and Philippine Seas. Taiwan is
one of only a few sites of arc-continent
collision worldwide—one of the
primary tectonic environments for largescale mountain building. The primary
purpose for the TAIGER project is to
investigate the processes of mountain
building, a fundamental set of processes
which plays a major role in shaping the
face of the Earth. The vicinity of Taiwan
is particularly well-suited for this type
of study, because the collision can be
observed at different stages of its
evolution, from incipient, to mature,
and finally to post-collision. As a result
of its location in an ongoing tectonic
collision zone, Taiwan experiences a
great number of earthquakes; most are
small, but many are large and
destructive. This project will provide a
great deal of information about the
nature of the earthquakes around
Taiwan and will lead to a better
assessment of earthquake hazards in the
area. The information obtained from this
study will help the people and
government of Taiwan to better prepare
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for future seismic events and may thus
mitigate some of the loss of life and
economic disruptions that will
inevitably occur.
(2) NMFS disagrees with the
commenter’s characterization of the
potential risk to the ETS sub-population
of Indo-Pacific humpback dolphins.
After the issuance of the proposed IHA,
L–DEO negotiated with the project’s
principal scientists to modify the cruise
plan and adopt more precautionary
mitigation measures. L–DEO will limit
seismic survey lines to take place at
least 20 km from the west coast of
Taiwan, except for in the passage
between the Penghu Islands and the
Waishanding Jhou sandbar, where the
survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
1 μPa (rms). Thus, the precautionary
buffer recommended by ETSSTAWG in
their comments to NMFS will be
maintained, ‘‘at least 13 km and perhaps
a more precautionary 15 km of the ETS
Sousa population—meaning up to
around 20 km from shore.’’ L–DEO will
also shut-down the airgun array if an
ETS Indo-Pacific humpback dolphin is
visually sighted regardless of the
distance of the animal(s) to the sound
source. The array will not resume firing
until 15 minutes after the last
documented whale visual sighting.
(3) NMFS disagrees with the
commenter’s assertion that the
requested take of ETS Indo-Pacific
humpback dolphins by harassment is
likely to exceed a sustainable level of
take for the population. L–DEO’s
seismic survey was modified after the
issuance of the proposed IHA to include
more precautionary mitigation
measures. The incorporation of
precautionary measures reduced the
estimated number of ETS Indo-Pacific
humpback dolphins expected to be
harassed to zero, which is clearly a
sustainable level of take for the subpopulation.
(4) and (5) NMFS believes that the
mitigation and monitoring measures in
the IHA are adequate to protect species
of concern that may be vulnerable to
noise impacts. After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary mitigation measures,
especially for species that are of
particular concern and have cryptic
behaviors that may be vulnerable to
noise impacts as well as to address
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concerns on the timing of the surveys
and their impacts on migration routes.
See Monitoring, Mitigation, Species of
Particular Concern, and Temporal and
Spatial Avoidance sections below and
L–DEO’s Supplemental EA for more
information. NMFS has included
requirements to these effects in the IHA
issued to L–DEO.
(6) After issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
mitigation measures to address concerns
of potential impacts of the seismic
survey on affected species and stocks of
marine mammals in the study area.
NMFS believes that L–DEO’s IHA
application, EA, and Supplemental EA
are not biased as they adequately
consider alternatives, and provides
analysis on the affected environment
and environmental consequences of the
study area.
(7) The EA adequately addresses the
cumulative impacts of a relatively shortterm seismic airgun survey in relation to
long-term noise and events, such as
vessel traffic, habitat loss, oil and gas
industry, pollution, fishing, hunting,
and other human activities. These other
activities are long-term activities which
are unaffected by NMFS’ action here.
Nor does this action, when considered
in light of the other activities, become
significant.
For more information, see further
relevant discussions in this notice, L–
DEO’s IHA application, EA, and
Supplemental EA.
Comment 26: HSI states that while
they appreciate L–DEO’s efforts to
comply with the MMPA and the NEPA,
HSI is concerned that this request for an
incidental harassment authorization is
premature and that in fact a letter of
authorization for incidental take may be
required. HSUS/HSI strongly urges the
NMFS to deny this request as submitted
and at a minimum to require L–DEO to
resubmit its request with an updated
review of the region’s marine mammals,
a more complete review of relevant
literature, modified survey track lines
and schedules, and additional
mitigation measures.
Response: NMFS does not agree that
a Letter of Authorization for incidental
take is necessary in this case. Due to the
incorporation of monitoring and
mitigation measures, including L–DEO’s
revision of tracklines after the issuance
of the proposed IHA and in response to
public comments, NMFS does not
anticipated a potential for injury,
serious injury, or mortality to any
marine mammals under the jurisdiction
of the MMPA. Based on numerous
concerns regarding the proposed IHA,
L–DEO has revised its seismic survey
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and adopted more precautionary
mitigation measures. L–DEO has
prepared a Supplemental EA in
response to the comments received. NSF
received no direct public comments on
the draft EA during (or after) the open
comment period of November 14, 2008
through December 15, 2008. Included
are a number of changes to the survey
design that were made by L–DEO to
address specific comments, some
received by a number of individuals and
agencies, and to enhance precautionary
measures already included in the
original documents to mitigate potential
effects of the survey on marine
mammals.
Comment 27: ETTSTAWG states the
L–DEO project, as presently described
in the U.S. Federal Register, poses an
unacceptable risk to the ‘critically
endangered’ population of ETS IndoPacific humpback dolphins.
Response: NMFS disagrees with
ETSSTAWG’s characterization of the
risk to the sub-population of ETS IndoPacific humpback dolphins. After
issuance of the proposed IHA, L–DEO
modified the cruise plan and adopted
more precautionary mitigation
measures, especially considering the
‘critically endangered’ ETS subpopulation of Indo-Pacific humpback
dolphins. See ‘‘Species of Particular
Concern’’ section below and other
discussions presented in this document.
Comment 28: Dr. Linda Weilgart urges
NMFS to reject this application for an
IHA and states that L–DEO’s powerful
array of airguns, and argues that the
permit application does not seriously
consider the possibility of irreversible
harm to marine mammals and the
marine environment.
Response: NMFS disagrees with Dr.
Weilgart’s comments. After issuance of
the proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary mitigation measures.
NMFS believes L–DEO’s planned
seismic survey, as revised, will have a
negligible impact on the affected species
and stocks of marine mammals in the
study area.
Comment 29: The strong bias in the
Federal Register notice is disturbing.
The notice should be an objective
discussion that leaves open whether the
agency should issue the authorization or
not. As published, however, the notice’s
language leads inevitably to a decision
to issue the authorization, despite the
applicant’s failure to argue
convincingly, as required by law, that
the surveys will not result in serious
injury or death or even, in this case,
Level A harassment. In fact, there is an
insufficient scientific basis for
concluding that no serious injury, death,
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or Level A harassment of any marine
mammal species will occur.
Accordingly, the NMFS must deny this
request as submitted and at a minimum
request the applicant to submit a revised
application with a more realistic and
conservative analysis of potential
impacts. If a compelling argument to
support the conclusion that only
harassment (Level B or Level A) will
occur is not forthcoming, then the
NMFS must deny the request outright
and require the applicant to seek a letter
of authorization for incidental take
under Section 101(a)(5)(A–C) of the
MMPA.
Response: NMFS disagrees with the
commenter’s characterization of the
Notice of Proposed Issuance.
Furthermore, as NMFS shows in this
document mortality and serious injury
are not expected to occur during this
seismic survey cruise due to
implementation of monitoring and
mitigation measures (e.g., ramp-up,
power-down, shut-down, passive
acoustic and visual monitoring, and
quiet acoustic periods) as well as L–
DEO’s revision of tracklines in the
cruise plan. Nor is incidental take by
injury, serious injury, or mortality
authorized. Therefore, issuance of an
IHA is appropriate. The revised survey
and monitoring and mitigation measures
are discussed further in this document.
Comment 30: Minor and Wilson, as
scientists, are greatly saddened to see
government funding being used to cause
the ‘‘Level B harassment’’ of 71,669
cetaceans. Minor and Wilson also doubt
that the data that might be gained from
the proposed ‘‘taking’’ is worth the harm
that it will do. Minor and Wilson are
concerned about what the proposed
undertaking will do to the reputation of
U.S. science. Recently, one species of
cetacean was declared extinct in this
region, and several more endangered
species are in the proposed study area.
To have a U.S. flagged ship, owned by
the NSF, cruising around in the critical
habitat of multiple endangered species
conducting seismic testing is clearly
poor public relations. If another of these
species goes extinct soon, the NSF will
find itself trying to ‘‘sell’’ the notion that
its contribution to the extinction was
insignificant. The NMFS could make a
positive contribution to the long term
reputation of U.S. science if it could
show some backbone and talk the NSF
out of this idiocy.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the monitoring
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and mitigation measures described in
the IHA will have a negligible impact on
the affected species or stocks of marine
mammals in the study area. See relevant
discussions in this document as well as
L–DEO’s Supplemental EA.
Thresholds
Thresholds—Acoustic Thresholds for
Behavior
Comment 31: The proposed IHA
notice also draws conclusions that are
heavily biased in favor of a finding of
‘‘no impact.’’ For example, the notice
states that ‘‘many cetaceans * * * are
likely to show some avoidance of the
area with high received levels of airgun
sound * * * [and] the avoidance
responses of the animals themselves
will reduce or (most likely) avoid any
possibility of hearing impairment’’
(emphasis added, p. 78303). Setting
aside the lack of scientific
substantiation for the degree of certainty
displayed by this claim, there is no
presentation or discussion of the
opposing (and equally likely) possibility
that many cetaceans might not show
avoidance of an area ensonified by
airguns because it is important habitat.
Response: NMFS refers the
commenter to L–DEO’s EA (Chapter 4
and Appendix B) which summarized
avoidance response levels to seismic
pulses for a number of cetaceans. L–
DEO provided ample evidence of
avoidance behavior in marine mammals
in response to seismic surveys from
several peer-reviewed studies including
data on gray, bowhead, and humpback
whales (Richardson et al., 1995);
Gordon et al. (2004); humpback whale
(McCauley et al., 1998 and 2000a);
bowhead whales (Miller et al., 1999;
Richardson et al., 1999); and eastern
Pacific gray whales (Malme et al., 1986,
1988).
Conversely, the EA discussed the
possibility that cetaceans might not
exhibit avoidance behavior or may not
be as sensitive to seismic sources. L–
DEO presents data from peer-reviewed
focusing on humpback whales (Malme
et al., 1985); bowhead whales (Miller et
al., 2005; Harris et al., 2007); and fin
and sei whales (Stone, 2003; Stone and
Tasker, 2006). For marine mammals that
do not avoid the vessel and sound
source, L–DEO will implement
mitigation measures such as powerdowns and shut-downs for animals that
enter the respective safety zones to
prevent Temporary Threshold Shift
(TTS)/Permanent Threshold Shift (PTS)
for those respective species.
With the respect to the ETS
population of humpback dolphins,
NMFS has instituted precautionary
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mitigation measures to protect these
species within their habitat in
Taiwanese waters. L–DEO will limit
seismic survey lines to take place at
least 20 km from the west coast of
Taiwan, except for in the passage
between the Penghu Islands and the
Waishanding Jhou sandbar, where the
survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
μPa (rms).
Comment 32: The proposed IHA
notice states that ‘‘if a sound source
displaces marine mammals from an
important feeding or breeding area for a
prolonged period, impacts on animals or
on the stock or species could potentially
be significant’’ (p. 78301). It does not,
however, consider the reverse; that the
failure of a sound source to displace
animals from important feeding or
breeding habitat may indicate that the
area is so important that the animals are
willing/forced to tolerate a level of noise
exposure that is in fact harmful (see,
e.g., the discussion of this concept in
Richardson et al. 1995). The failure to
consider the possibility of an animal not
reacting because leaving a prime feeding
spot is more costly than moving
laterally along a migration pathway is
an example of the bias permeating the
entire analysis and has contributed to an
unacceptably incomplete level of
evaluation and discussion regarding
impacts and mitigation.
Response: NMFS refers the
commenter to page 78302 of the
proposed IHA notice, Chapter 4 and
Appendix B of the EA for L–DEO’s
presentation of cetaceans not exhibiting
avoidance behavior when exposed to
seismic pulses. L–DEO has
acknowledged the public’s concern for
coastal dwelling species in Taiwan, has
modified their cruise plan, and has
adopted more precautionary monitoring
and mitigation measures, especially for
species of particular concern. See
responses to comments regarding
mitigation measures such as the
implementation of power-downs and
shut-downs for animals discussed
within this document as well as within
L–DEO’s Supplemental EA.
Comment 33: The EA noted that
‘‘captive bottlenose dolphins and beluga
whales exhibited changes in behavior
when exposed to strong pulsed sounds
similar in duration to those typically
used in seismic surveys (Finneran et al.
2000, 2002). However, the animals
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tolerated high received levels of sound
before exhibiting aversive behaviors.’’ It
should be noted, however, that the
animals in the abovementioned Navy
studies were reported by Nowacek et al.
(2007) to be generally ‘‘tested in a
context where they were being rewarded
for tolerating high levels of noise’’ and
were ‘‘usually ‘punished’ in some way
* * * for failing to return to the
experimental station for additional
exposures.’’ This was not a problem for
their main results as the focus of the
work was on to TTS, but the setup does
invalidate any conclusions based on the
behavioral responses reported in the
same studies. For further discussion of
the need for precaution in the use of
captive studies to set exposure criteria
for wild animals, see Parsons et al.
(2008) and Wright et al. (in press).
Response: NMFS acknowledges the
commenter’s interpretation of captive
studies and have taken them into
consideration. Thresholds for behavioral
response are not based upon captive
studies. The 160 dB re 1 μPa threshold
was derived from data for mother-calf
pairs of migrating gray whales (Malme
et al., 1983, 1984) and bowhead whales
(Richardson et al., 1985, 1986)
responding when exposed to seismic
airguns (impulsive sound source).
Comment 34: The idea that behavioral
tolerance is a proxy for no impact has
no scientific merit. In fact, some fairly
sizable impacts have been reported in
various species despite a lack of
behavioral response. A recent panel of
experts also noted that an apparently
unresponsive animal may still be
undergoing a chronic and/or severe
acute stress response, with associated
physiological and psychological
consequences. These can result from
exposure directly, or through masking
and other phenomenon indirectly. Thus,
taking is entirely possible without
observable behavioral disturbance
reactions and this needs to be accounted
for.
Response: Section 101(a)(5)(D) of the
MMPA allows citizens of the United
States to take by harassment, small
numbers of marine mammals incidental
to a specified activity (other than
commercial fishing) within a specified
geographical region if NMFS is able to
make certain findings. NMFS must issue
an incidental harassment authorization
if 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.
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The mitigation measures set forth in
the IHA ensure that there will be
negligible impacts on the marine
mammals. Cetaceans are expected, at
most, to show an avoidance response to
the seismic pulses. Mitigation measures
such as visual marine mammal
monitoring, and shut-downs when
marine mammals are detected within
the defined ranges should further
reduce short-term reactions to
disturbance, and minimize any effects
on hearing sensitivity. Due to these
mitigation measures, and other reasons
discussed in the Conclusions section of
this document, NMFS believes the
impacts will be negligible.
Comment 35: Mortality (by human
causes) of even a single individual per
year from this population may not be
sustainable, and unless effective
mitigation measures are taken
immediately to reduce the threats to this
population, it is unlikely that the
population will continue to exist (Wang
et al., 2004, 2007b). Any single threat
has the potential to be the final cause of
extinction for this small population of
dolphins.
Response: Please note that in response
to public comments received on the
application and EA, L–DEO has
modified the survey design (see L–
DEO’s Supplemental EA) and adopted
more precautionary mitigation measures
to protect the critically endangered ETS
population, as well as ease potential
pressure on other coastal species.
Comment 36: One commenter was
concerned about the masking of the
noises made by threats, hindering
detection of the threats and increasing
the impact of the existing threats (e.g.,
water rushing past a gillnet, commercial
shipping) and the chances of mortality.
Response: NMFS expects the masking
effects of pulsed sounds on natural
sounds or other anthropogenic sounds
to be limited. Because of the
intermittent nature and low duty cycle
of seismic pulses, animals can emit and
receive sounds in the relatively quiet
intervals between pulses. Further,
masking effects of seismic pulses are
expected to be negligible in the case of
the smaller odontocetes, given the
intermittent nature of seismic pulses
plus the fact that sounds important to
these species are predominantly found
at much higher frequencies than are the
dominant components of airgun sounds.
Marine mammal communications will
not be masked appreciably by the
multibeam echosounder signals given
the low duty cycle of the echosounder
and the brief period when an individual
mammal is likely to be within its beam.
The majority of energy should be
concentrated in the beam (Kremser et
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al., 2005). Furthermore, in the case of
baleen whales, the MBES signals (12
kHz) do not overlap with the
predominant frequencies in the calls,
which would avoid any significant
masking. Masking effects on marine
mammals are discussed further in
Appendix B(4) of L–DEO’s EA.
Comment 37: Another commenter was
concerned about the impacts on
cetaceans due to displacement into
other waters. He noted that for
populations with low numbers,
restricted distributions, displacement
may increase energy expenditures by
the species already compromised
energetically (such as mothers with
calves) and increase exposure to other
threats (e.g., changes in migration routes
may result in animals using waters with
higher densities of fishing nets or lines
and thus increase their risk of mortality
due to entanglement).
Response: The incidental harassment
authorization includes mitigation and
monitoring measures to reduce potential
effects on populations with low
numbers and restricted distributions. L–
DEO and TAIGER’s principal
investigators have modified the cruise
plan and survey design to protect
displacing populations with low
numbers and restricted distributions.
First, L–DEO will shut down the airgun
array immediately if there is a sighting
at any distance of the Indo-Pacific
humpbacked dolphin or finless
porpoise. Second, L–DEO has re-routed
the cruise’s tracklines offshore Taiwan’s
west coast by approximately 20 km
(10.8 nautical mi) to protect the
critically endangered Sousa population
and the finless porpoise (except for in
the passage between the Penghu Islands
and the Waishanding Jhou (Wau-santing Chou) sandbar, where the survey
will pass through the 17.1 km (9.2
nautical mi) mid-line distance between
the two possibly sensitive areas).
Finally, L–DEO is restricted to
conducting seismic surveys in water
depths greater than 200 m (656 ft) in the
South China Sea, and as far east as
possible from the mainland China side
of the Taiwan Strait, to reduce potential
for effects on eastern Pacific gray
whales, Indo-Pacific humpback
dolphins, and finless porpoises.
Comment 38: Given the serious
conservation status of the ETS subpopulation and the small population
size of the JRE provisional population,
there must be a higher level of
precaution to avoid negative impacts of
additional threats on these dolphins.
Because even low level noise may
increase risks to these dolphins by
altering dolphin behavior, increasing
ambient noise levels that can ‘mask’
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biologically important sounds as well as
‘mask’ sounds that allow the detection
of other threats (e.g., the sound of water
flowing past gillnets, approaching boats,
etc.) should be avoided.
Response: Please see NMFS’
responses to comments under the
Species of Particular Concern section.
Thresholds—Acoustic Thresholds for
TTS and PTS
Comment 39: The notice states that
‘‘There is no specific evidence that
exposure to pulses of airgun sound can
cause PTS in any marine mammal, even
with large arrays of airguns’’ (p. 78304).
Such a statement is misleading on many
levels. For one, marine mammal science
has yet to develop ways to measure or
identify PTS (permanent threshold shift
or permanent hearing loss) in the field.
For another, it is known that exposure
to loud impulsive sounds such as are
produced by airguns can deafen
terrestrial species, including people. To
state that no specific evidence exists of
PTS in marine mammals exposed to
airguns when science cannot yet
identify such evidence is both specious
and disingenuous.
Response: First, mitigation and
monitoring requirements under the IHA
are expected to prevent TTS, thus
preventing PTS. NMFS acknowledges
the limitations of current data on the
measurement or identification of PTS in
marine mammals, let along free-ranging
animals.
Recent scientific research on marine
mammals and noise, include: estimating
hearing capabilities using various
behavioral and anatomical techniques;
measuring sub-injurious impacts on
hearing (temporary threshold shift, or
TTS); and estimating lethal and
injurious effects of acoustic exposure.
Richardson et al. (1995) noted, based on
terrestrial mammal data, that the
magnitude of TTS in marine mammals
was expected to depend on the level
and duration of noise exposure, among
other considerations. Southall et al.,
(2005) showed that long-term (four to
seven years) noise exposure on three
experimental pinniped species
(northern elephant seal (Mirounga
angustirostris), harbor seal (Phoca
vitulina), and California sea lion
(Zalophus californianus) had caused no
change on their underwater hearing
thresholds at frequencies of 0.2 to 6.4
kHz.
Finally, NMFS believes that the 180dB re: 1 μPascal (rms) criteria is a
reasonable and precautionary
interpretation of the current data at this
time. The precautionary nature of these
criteria is discussed in Appendix B(6) of
L–DEO’s application and in previous
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Federal Register notices (e.g., 67 FR
46711, July 16, 2002). The current safety
zones of 180 dB re: 1 μPa (rms) for
cetaceans is conservative and will
protect marine mammals from injury
(Level A harassment).
Comment 40: Recent research
examining the propagation of airgun
noise has shown that, contrary to
predictions, received levels can
decrease between 5 km and 9 km, but
then increase at distances between 9 km
and 13 km (Madsen et al. 2006). The
researchers stated that received levels
‘‘can be just as high * * * at 12 km as
at a range of 2 km from the array’’
(Madsen et al. 2006, p. 2374), ‘‘beyond
where visual observers on the source
vessel can monitor effectively’’ (Madsen
et al. 2006, p. 2376). Arguably, this
suggests that if the goal is to avoid
subjecting animals to Level A
harassment or worse, seismic surveys
should be conducted at a minimum
greater than 12 km from the offshore
boundary of a coastal species’ home
range.
Response: With regards to the
Langseth’s survey offshore of Taiwan’s
west coast, L–DEO has re-routed the
survey by approximately 20 km (10.8
nautical mi) to reduce potential effects
for marine mammals. For the passage
between the Penghu Islands and the
Waishanding Jhou (Wau-san-ting Chou)
sandbar, the survey will pass through
the 17.1 km (9.2 nautical mi) mid-line
distance between the two possibly
sensitive areas. Please see the
Mitigation—Tracklines section for
additional information.
Comment 41: HSI notes that the
Federal Register notice states (p.
78306): NMFS believes that to avoid the
potential for permanent physiological
damage (Level A harassment), cetaceans
and pinnipeds should not be exposed to
pulsed underwater noise at received
levels exceeding, respectively, 180 and
190 dB re 1 μPa (rms). The
precautionary nature of these criteria is
discussed in Appendix B (6) of L–DEO’s
application, including the fact that the
minimum sound level necessary to
cause permanent hearing impairment is
higher, by a variable and generally
unknown amount, than the level that
induces barely-detectable TTS and the
level associated with the onset of TTS
is often considered to be a level below
which there is no danger of permanent
damage [emphasis added]. The language
(see emphasis) functionally defining
Level A harassment is not found in the
MMPA or in its implementing
regulations. We advise the NMFS
against inserting ‘‘unofficial’’ definitions
of harassment into notices, regardless of
the context (here, it could be argued
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only hearing impairment was in
question, but these words could be
taken out of context). This wording
could be seen to encompass a broad
range of ‘‘damage’’—from a wound that
heals into a scar (clearly minor) to a
crippling injury that leads to death (so
clearly not Level A harassment but
rather serious injury). It also could be
seen to exclude reversible injuries that
should be categorized as Level A, not
Level B harassment (such as, for
example, broken bones that, until
healed, could result in lost mating
opportunities). We strongly recommend
that this language be expunged from any
subsequent rule on this application and
not used again in any future notices.
Response: NMFS concurs with HSI
and offers the following amendment to
the language contained in the proposed
rule: ‘‘NMFS believes that to avoid the
potential for Level A harassment from
exposure to pulsed underwater noise,
cetaceans and pinnipeds should not be
exposed to received levels exceeding,
respectively, 180 and 190 dB re 1 μPa
(rms). The precautionary nature of these
criteria is discussed in Appendix B(6) of
L–DEO’s application, including the fact
that the minimum sound level necessary
to cause permanent hearing impairment
is higher, by a variable and generally
unknown amount, than the level that
induces barely detectable TTS and the
level associated with the onset of TTS
is often considered to be a level below
which there is no danger of permanent
damage [emphasis added].’’
However, while not redefining the
statutory definition, it is necessary for
NMFS to include functional definitions
of effects that fall into the category of
Level A (or B) harassment in order to
meet our statutory responsibility to
quantify take. For example, for acoustic
effects, because the tissues of the ear
appear to be the most susceptible to the
physiological effects of sound, and
because threshold shifts tend to occur at
lower exposures than other more serious
auditory effects, NMFS has determined
that PTS is the best indicator for the
smallest degree of injury that can be
measured. Therefore, the acoustic
exposure associated with onset PTS is
used to define the lower limit of the
Level A harassment for acoustic effects.
Comment 42: L–DEO should use the
more precautionary 15 dB difference
being employed in converting the SELbased safety zones to SPL-based safety
zones. (From the EA: ‘‘At the distances
where rms levels are 160–190 dB re 1
μ Pa, the difference between the SEL and
SPL values for the same pulse measured
at the same location usually average
approximately 10–15 dB, depending on
the propagation characteristics of the
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location (Greene, 1997; McCauley et al.,
1998, 2000a; Appendix B). In this EA,
we assume that rms pressure levels of
received seismic pulses will be 10 dB
higher than the SEL values predicted by
L–DEO’s model. Thus, we assume that
170 dB SEL ∼ 180 dB re 1 μPa rms.’’).
Thus 180 dB rms SPL would be reached
with a SEL of 165 dB.
Response: L–DEO’s results indicate
(for shallow water, at least) the
difference between rms and SEL varies
between 8 and 13 dB. This result is
more or less in line with that found by
Madsen et al. (2006). The difference is
higher at offsets, where the more
impulsive direct arrival dominates the
sound field, and lower at larger offsets,
where the signal is more reverbatory.
The range at which the decrease occurs
depends a lot on water depth, but it’s
obvious that to use a 15 dB correction
elsewhere would nearly double the
numbers as far as offsets. The length of
the signal is an important factor as well
since there are greater differences
between SEL and SPL, which means the
signal is shorter, since it stretches as it
travels further.
Comment 43: The EA notes that
Southall et al. (2007) stated that TTS is
not injury. However I believe that they
have overstated their conclusions. It is
true that Southall et al. (2007) state:
‘‘[impacts resulting in] * * * TTS rather
than a permanent change in hearing
sensitivity * * * are within the nominal
bounds of physiological variability and
tolerance and do not represent physical
injury (Ward, 1997).’’ However, they
also note that ‘‘at present, however,
there are insufficient data to allow
formulation of quantitative criteria for
non-auditory injuries’’ and later
acknowledge that, while they believe
that ‘‘strong behavioral responses to
single pulses * * * are expected to
dissipate rapidly enough as to have
limited long-term consequence’’ there
are occasions where such responses may
‘‘secondarily result in injury or death
(e.g., stampeding)’’ (Southall et al.,
2007).
Response: In its 2002 Final Rule for
SURTASS LFA sonar, NMFS stated that
temporary threshold shift (TTS) is not
an injury. The required power-down
and shut-down zones, if properly
implemented, will avoid exposing
marine mammals to levels associated
with injury and minimize the number of
marine mammals exposed to levels
associated with TTS (See Mitigation
section).
With regards to non-auditory injuries,
the conclusion that the potential effects
on the stocks of marine mammals from
non-auditory injuries would be minimal
is discussed in the L–DEO’s EA. NMFS
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believes that L–DEO’s seismic survey
has met all of these requirements and
has been operating since 2003 without
any known physical injuries to marine
animals.
Comment 44: ‘‘Southall et al. (2007)
also add the following caveat with
regards to their report: Finally, we
emphasize that exposure criteria for
single individuals and relatively shortterm (not chronic) exposure events, as
discussed here, are insufficient to
describe the cumulative and ecosystemlevel effects likely to result from
repeated and/or sustained human input
of sound into the marine environment
and from potential interactions with
other stressors. Also, the injury criteria
proposed here do not predict what may
have been indirect injury from acoustic
exposure in several cases where
cetaceans of mass stranded following
exposure to mid-frequency military
sonar. Thus, since they did not attempt
to consider all possible methods of
injury in their deliberations and thus
their final figures, they should not be
directly applied to management
decisions that must, by law, consider
the full suite of potential impacts. Direct
application of their criteria would thus
not be precautionary enough to meet the
required legal standards.’’
Response: NMFS currently uses the
existing thresholds for Level A
harassment (sound pressure level of 180
dB re 1 μ Pa [rms]) (dB SPL), and Level
B harassment (160 dB SPL for impulse
noise and 120 dB SPL for continuous
sound). The science in the field of
marine mammals and underwater sound
is evolving relatively rapidly. NMFS is
in the process of revisiting our acoustic
criteria with the goal of developing a
framework (Acoustic Guidelines) that
allows for the regular and scientificallyvalid incorporation of new data into our
acoustic criteria. We acknowledge that
this model has limitations; however, the
limitations are primarily based on the
lack of applicable quantitative data. We
believe that the best available science
has been used in the development of the
criteria used in this IHA. We appreciate
the input from the public and intend to
consider it further as we move forward
and develop the Acoustic Guidelines.
Comment 45: It should be noted that
repeated TTS can lead eventually to
PTS, which would not be classed as
injury under these criteria. Other
potentially injurious impacts have also
been shown to occur below levels that
would cause TTS in humans. For
example, impaired reading
comprehension and recognition memory
in children is linked to aircraft noise at
exposure levels considerably less than
75 dB (Stansfeld et al., 2005), which,
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according to the U.S. National Institute
on Deafness and Other Communication
Disorders (NIDCD, 2007), are unlikely to
cause hearing loss (temporary or
otherwise) even after long exposure
(NIDCD, 2007).
Response: Mitigation and monitoring
requirements under the IHA should
prevent TTS. While there have been
debates among scientists regarding
whether a permanent shift in hearing
threshold (PTS) can occur with repeated
exposures of TTS, at least one study
showed that long-term (four to seven
years) noise exposure on three
experimental pinniped species had
caused no change on their underwater
hearing thresholds at frequencies of 0.2–
6.4 kHz (Southall et al., 2005).
TTS may be considered to be an
adaptive process (analogous to the dark
adaptation in visual systems) wherein
sensory cells change their response
patterns to sound. Tissues are not
irreparably damaged with the onset of
TTS, the effects are temporary
(particularly for onset-TTS), and NMFS
does not believe that this effect qualifies
as an injury.
Comment 46: It is strange that an
entire special issue devoted to noiserelated stress responses in marine
mammals resulting from a multidisciplinary panel of experts does not
get a single mention in this section,
even though a discussion of likely
impacts is offered in Wright et al.
(2007a, b) and the other papers within
(all of which are cited therein). The
papers are cited in Southall et al. (2007),
which the authors have obviously read.
I will not repeat the conclusions here,
but suggest they are included within the
EA (or more likely an EIS) before this
survey begins.
Response: NSF/L–DEO presented the
Southall et al. (2007) study as one of
several pieces of information that relate
to this topic. However, NMFS does not
solely rely upon NSF’s EA to arrive at
its determinations. NMFS is aware of
Wright et al. (2007a, b) paper as well as
others published in the International
Journal of Comparative Psychology.
However, NMFS finds that the
information is not such that it will affect
NMFS’ findings.
Comment 47: There is a high
likelihood that many individuals will be
exposed to sound levels that qualify as
Level A harassment. Any additional
threats (especially those where many
uncertainties exist about their impacts
and that have the potential to cause
serious harm or even death) to cetaceans
on the brink of extinction are not
‘‘negligible’’ for the affected species or
stocks.
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Response: The mitigation and
monitoring requirements under the IHA
are expected to prevent TTS (Level B
harassment), thus preventing PTS (Level
A harassment). NMFS believes that it is
very unlikely that Level A harassment
will result and, therefore, NMFS has not
authorized Level A harassment in this
IHA.
The IHA includes mitigation and
monitoring measures to reduce the
potential for injury or mortality, as well
as instituting immediate shutdown
protocols for the North Pacific right
whale, Western Pacific gray whale,
Indo-Pacific humpbacked dolphin, or
finless porpoise.
The mitigation measures (e.g., rampup, passive acoustic and visual
monitoring, and quiet acoustic periods)
set forth in the IHA ensure that there
will be negligible impacts on the marine
mammals by reducing short-term
reactions to disturbance and minimizing
any effects on hearing sensitivity. Due to
these measures, and other reasons
discussed in the Conclusions of this
document, NMFS believes the impacts
will be negligible.
Comment 48: Until the effects of
seismic surveys on these shallow water
dolphins and the combined and
cumulative impacts of all threats can be
better understood, a ‘‘safe’’ exposure
level cannot be determined.
Response: The temporary nature of
the activity and the implementation of
the new shut-down criteria and
mitigation measures as described in the
Species of Particular Concern and the
Mitigation sections, leads NMFS to
believe the activity will have a
negligible impact on shallow water
populations of the Indo-Pacific
humpback dolphin and finless porpoise.
Comment 49: Variability and
uncertainty in TTS threshold values.
Furthermore the TTS threshold is based
on limited information from only a few
species of cetaceans. Most of the species
of concern (e.g., baleen whales, beaked
whales, humpback dolphin, finless
porpoise, etc.) have not been examined
and there appears to be great variability
amongst individual cetaceans tested so
interspecific extrapolations need to be
considered cautiously (for a review, see
Weilgart, 2007).
Response: NMFS acknowledges that
the test-animals may not fully represent
the range of hearing responses across
multiple taxa. However, NMFS has used
the best science available to develop
these thresholds which have been in
effect for almost a decade. The current
safety zone of 180 dB rms for cetaceans
is conservative and will protect marine
mammals from injury (Level A
harassment).
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Comment 50: The difficulty in
predicting sound levels underwater
must be taken into account. Madsen et
al. (2006) reported that seismic sounds
did not always attenuate predictably
and sound levels can be the same at 2
km as well as at 12km. The same
unpredictability was found for sounds
from acoustic harassment and deterrent
devices, where increasing distance from
the sound source did not always result
in a reduction of exposure levels
(Shapiro et al., 2009). Even within a
fraction of a meter, sound level
differences may be several orders of
magnitude (Wahlberg, 2006 as cited in
Shapiro et al., 2009). These studies are
inconsistent with classic ideas of sound
propagation and attenuation (see
Richardson et al., 1995) and are very
concerning because the very dynamic
nature of the waters of western Taiwan
and the concrete walls lining the
shoreline may result in the sounds the
airguns to reach unexpectedly
dangerous exposure levels within the
distribution of the ETS population.
Response: Please see NMFS’ response
to Comment # in this section.
Comment 51: The survey will bring
the Langseth to waters within 1 km from
the shores of Taiwan and right through
the middle of almost the entire linear
coastal distribution of the eastern
Taiwan Strait population. At this
distance from shore, the Langseth will
inevitably subject the entire population
to noise levels greater than 180 dB. Even
staying at least 2 km from the coastline
does absolutely nothing to reduce the
noise exposure for these critically
endangered (IUCN Red List) dolphins.
And based on the values in Table 1 of
the Federal Register notice, even at 8–
10 km from shore, all dolphins will still
be exposed to at least 160 dB with an
unknown number that may be exposed
to > 180 dB.
Response: Please see the Species of
Particular Concern section.
Comment 52: Given the threat of noise
on the health of the ETS dolphins, the
ETSSTAWG recommended a buffer for
noise threats out to at least 5 km from
shore (note: for an area with an
expansive littoral zone such as western
Taiwan, ‘‘shore’’ can vary greatly with
tides; for clarity, ‘‘shore’’ is defined here
to include the littoral zone at the lowest
tide of the year). Calculations of how far
out the Langseth should be to prevent
exposure of ETS dolphins to received
levels greater than 160 dB should be
based on at least the recommended 5 km
buffer boundary (i.e., the waters from
shore, as defined above, to 5 km
offshore should not be exposed to levels
>160dB). Based on the values presented
in Table 1 (of the Federal Register) the
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41273
source should not be closer than 13 km
from shore. However, given the
population’s critical status and the
underestimated predicted distances for
each exposure threshold level
(especially for shallow water; see
above), greater precaution is needed
(i.e., the airguns should be even further
from shore).
Response: Please see the Mitigation
section in this notice.
Comment 53: For whales that are
using the shallow waters (e.g., Taiwan
Strait), the predicted distance for
exposure levels to be greater than 160
dB was 6,227 to 8,000 m and for 180 dB
the distances were 2,761 to 3,694 m. At
these distances, detection of whales by
observers can be difficult to impossible
depending on sighting conditions.
Therefore, some whales may be exposed
to greater than 180 dB without being
detected by observers.
Response: A key factor in estimating
the number of undetected mammals that
might occur within the 180 dB radius is
the fact that many marine mammals
move away from an approaching
seismic vessel (e.g., Richardson et al.,
1995; Stone, 2003). The conventional
estimates of the proportions present but
missed by visual observations, as
described in 73 FR 78294, December 22,
2008, will overestimate (sometimes by
very large factors) the numbers of
mammals that might be exposed to high
levels of sound near the ship. This is an
important consideration in assessing
possible exposures to high-level sound,
especially for the more responsive
species, notably some if not all baleen
whales, beaked whales, and harbor
porpoises. There is also some degree of
avoidance by a variety of other
odontocetes (Stone, 2003). In order to
derive unbiased estimates of numbers
that might be exposed to greater than
180 dB, density-based estimates that
include allowance for g(0) and f(0)
would need further adjustment to allow
for an ‘‘avoidance probability’’ factor.
Such factors are not generally available.
They would depend on species and
circumstances, and for some species
would, if applied, result in a large
decrease the estimates of the numbers
that would be exposed to high-level
sound.
Detectability is a measure of the
probability of detecting a marine
mammal that is present on a vessel’s
trackline (i.e., g(0)). L–DEO uses the
most applicable detectability values as
provided in Koski et al. (1998)
whenever estimates of marine mammal
detectability have not already been
calculated. They have compiled
previously reported detectability
information for various species and
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used data on surfacing/dive cycles to
estimate detectability values for species
or species groups of marine mammals
for which there are no published
detectability values. Thus the estimates
of incidental take in L–DEO’s IHA
application and the associated NSF EA
are either the same (if detectability had
already been taken into account) or
higher than would be obtained by direct
application of previously reported
density data.
NMFS acknowledges these
limitations. However, acoustic detection
has been demonstrated to augment
visual detection of marine mammal in
population estimates in a number of
studies (e.g., Moore et al., 1999; Swartz
et al., 2002). The use of PAM will
improve the detection of marine
mammals by indicating to the MMVOs
when a vocalizing animal is potentially
near and prompting a shut-down when
necessary.
Comment 54: Statements such as
‘‘However, there has been no specific
documentation of TTS let alone
permanent hearing damage, i.e., PTS, in
free-ranging marine mammals exposed
to sequences of airgun pulses during
realistic field conditions’’ are stupid.
Response: NMFS acknowledges the
commenter’s opinion. However, at the
time of publication, the statement that
‘‘there has been no specific
documentation of TTS let alone
permanent hearing damage, i.e.,
permanent threshold shift (PTS), in freeranging marine mammals exposed to
sequences of airgun pulses during
realistic field conditions,’’ was correct.
Lucke et al., (2009) recent auditory
study on documenting threshold shift in
harbor porpoises was published after L–
DEO submitted their application.
Monitoring
Comment 55: ETSSTAWG states that
a minimum of two MMOs should be
used at all times, with one of those
having considerable prior experience as
a MMO (preferably within the area of
Taiwan).
Response: Three MMOs are typically
on watch at a time, two MMVOs on the
observation tower conducting visual
observations and the third monitoring
the PAM equipment. On the observation
tower, two MMOs are on watch during
all daylight hours except during meal
times. At least one MMO and one
MMVO will be on watch during meal
times. The MMOs onboard the Langseth
are experienced and qualified, and
additional regional experts have been
brought onboard for this survey.
Comment 56: The Commission
recommends that, before issuing the
requested authorization, the NMFS
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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 safety zones.
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
observer, (3) describe changes in
detection probability at night, and (4)
explain how close to the vessel marine
mammals must be for observers to
achieve the anticipated high nighttime
detection rate.
Response: NMFS believes that the
planned monitoring program will be
sufficient to detect (using visual
detection and passive acoustic
monitoring [PAM]), with reasonable
certainty, most marine mammals within
or entering identified safety zones. This
monitoring, along with the required
mitigation measures (see below), will
result in the least practicable adverse
impact on the affected species or stocks
and will result in a negligible impact on
the affected species or stocks.
The Langseth is utilizing a team of
trained marine mammal observers
(MMOs) to both visually monitor from
the high observation tower of the
Langseth and to conduct PAM.
However, there are limitations on
marine mammal detection, and rampups are required as mitigation measures
due to these limitations. This
monitoring, along with the required
mitigation measures (see below), will
result in the least practicable adverse
impact on the affected species and/or
stocks and will result in a negligible
impact on the affected species and/or
stocks.
When stationed on the observation
platform of the Langseth, the eye level
will be approximately 17.8 m (58.4 ft)
above sea level, so the visible distance
(in good weather) to the horizon is 16.5
km (10.3 mi; the largest safety radii is
approximately 3.7 km, 2.3 mi). Big eyes
are most effective at scanning the
horizon (for blows), while 7x50 reticle
binoculars are more effective closer in
(MMOs also use a naked eye scan).
Night vision devices (NVDs) will be
used in low light situations.
Additionally, MMOs will have a good
view in all directions around the entire
vessel. Also, nearly 93 percent of the
survey lines are in intermediate or deep
water depths, where the safety radii are
all less than 1.4 km (0.87 mi).
Theoretical distance of this PAM
system is tens of kilometers. The PAM
is operated both during the day and at
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night. Though it depends on the lights
on the ship, the sea state, and thermal
factors, MMOs estimated that visual
detection is effective out to between 150
and 250 m (492 and 820 ft) using NVDs
and about 30 m (98.4 ft) with the naked
eye. However, the PAM operates equally
as effectively at night as during the day,
especially for sperm whales and
dolphins.
The PAM has reliable detection rates
out to 3 km (1.9 mi) and more limited
ability out to 10s of km. The largest 180dB safety radii (3.7 km, 2.3 mi), which
is the radii within which the Langseth
is required to shut down if a marine
mammal enters, are found when the 36
airgun array is operating in shallow
water at a 9 m (29.5 ft) tow depth. Only
approximately seven percent of the total
15,902 km survey lines of the planned
seismic survey (excluding contingency)
will take place in water less than 100 m
deep (shallow water). The species most
likely to be encountered in the waters
off of SE Asia are pantropical spotted,
Fraser’s, and spinner dolphins, which
have relatively larger group sizes (10s to
100s to 1,000s of animals for these
various dolphin species), are not cryptic
at the surface, and have relatively short
dive times (approximately 6 min for
some dolphin species), all which
generally make them easier to visually
detect. Other species that are likely to be
encountered during the seismic survey
include Bryde’s whales and humpback
whales, which have relatively long dive
times; however they are not cryptic at
the surface, have large blows and
distinct physical features, all which
generally make them easier to visually
detect. Furthermore, the vocalizations of
most of these species are easily detected
by the PAM. During the Ewing cruise in
the GOM in 2003, MMOs detected
marine mammals at a distance of
approximately 10 km (6.2 mi) from the
vessel and identified them to species
level at approximately 2.7 km (1.7 mi)
from the vessel, though the bridge of
that vessel was only 11 m (36 ft) above
the water (vs. the Langseth which is
more than 17 m (55.8 ft) above sea
level). All of the 180-dB safety radii for
other water depths and tow depths and
for the single 40 in3 airgun to be used
during ramp-ups and power-downs (see
below) are less than 2 km (1.2 mi).
The likelihood of visual detection at
night is significantly lower than during
the day, though the PAM remains just
as effective at night as during the day.
However, the Langseth will not be
starting up the airguns unless the safety
zone is visible for the entire 30 min
prior (i.e., not at night), and therefore in
all cases at night, the airguns will
already be operating, which NMFS
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believes will cause many cetaceans to
avoid the vessel, which therefore will
reduce the number likely to come
within the safety radii. Additionally all
of the safety radii in intermediate and
deep water depths are smaller than 3 km
(1.9 mi) and fall easily with the reliable
detection capabilities of PAM.
Comment 57: The Commission
recommends that, before issuing the
requested authorization, the NMFS
clarify the qualifiers ‘‘when practical’’
and ‘‘when feasible’’ with respect to (1)
using two MMOs to monitor the
exclusion zone for marine mammals
during daytime operations and
nighttime start-ups of the airguns, and
(2) using MMOs during daytime periods
to compare sighting rates and animal
behavior when the seismic airguns are
operating and when they are not.
Dr. John Wang states that the
inadequacy of MMVO coverage in this
respect would be wholly inadequate
even for small-scale marine mammal
surveys where the consequence of
failing to detect animals are much less
serious.
Response: The Langseth carries five
trained, NMFS-qualified and
experienced MMOs for every seismic
study involving use of an airgun system
comparable to that planned for the
TAIGER project. MMOs are appointed
by L–DEO with NMFS concurrence. L–
DEO plans to employ a regional expert
as one of the MMOs, and negotiations
were currently underway with experts
from National Taiwan University,
Academia Sinica, and National Taiwan
Ocean University during the preparation
of this notice. L–DEO will have a sixth
MMO and regional expert during the
second leg of the cruise as well. L–DEO
will utilize two (except during meal
times), NMFS-qualified, vessel-based
MMVOs to watch for and monitor
marine mammals near the seismic
source vessel during all daytime airgun
operations and before and during startups of airguns day or night. MMVOs
will have access to reticle binoculars
(7×50 Fujinon), big-eye binoculars
(25x150), and night vision devices to
scan the area around the vessel. MMOs
will alternate between binoculars and
the naked eye to avoid eye fatigue.
During all daytime periods, two
MMVOs will be on effort from the
observation town to monitor greater
than 90 percent of the time. During
mealtimes it is sometimes difficult to
have two MMOs on effort, but at least
one MMVO will be on watch during
those brief scheduled times. Three
MMOs are typically on watch at a time,
and typically observe for one to three
hours. Two MMVOs will also be on
watch during all nighttime start-ups of
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the seismic airguns. A third MMO will
be monitoring the PAM equipment 24
hours a day to detect vocalizing marine
mammals present in the action area.
Comment 58: Dr. John Wang states
that in shallow waters (Taiwan Strait),
the predicted distance for exposure
levels of 180dB and 190dB was
estimated by L–DEO to be 2,761 to
3,694m and 1,600 to 2,182 m,
respectively. At these distances (which
are underestimated) and under ideal
sighting conditions, detection of finless
porpoises by observers is of limited
ineffectiveness at the closest range and
very ineffective at the greater distances.
Sighting effectiveness will drop
dramatically even for highly
experienced observers in slight seas.
Under conditions where white caps are
present, sightings of finless porpoises
are rarely made and researchers
generally stop observations. At several
kilometers distance in shallow water,
PAM would not be able to detect finless
porpoises adequately because finless
porpoises are not always actively
vocalizing and the very high frequency
sounds emitted by porpoises (Akamatsu
et al., 1998) attenuate quickly so the
PAM’s detection range will be limited.
Therefore, finless porpoises can and
will likely be exposed to >>180dB
without being detected especially if
sighting conditions are not ideal. For
finless porpoises, L–DEO’s airguns have
the potential to inflict serious
permanent injuries or even cause death,
directly or indirectly.
Response: There is a scientific
methodology to estimate the probability
of detection marine mammal on the
surface, as explained in detail in
Buckland et al. (1993). This includes
several components, including the
probability that the mammal will be at
the surface and potentially sightable
while within visible range of the
observers, the probability that an animal
at the surface will in fact be detected,
and the relationship between sighting
probability and lateral distance from the
trackline.
A certain portion of the population is
presumed to be submerged at any given
time and is therefore unavailable for
detection. However, if the ship speed is
slow, many of these animals would
surface at some point while within
visual range of MMVO’s aboard the
approaching vessel. The speed of the
Langseth, and other seismic vessels
while operating airguns, will generally
be four to five knots of vessels
conducting marine mammal line
transect surveys.
All L–DEO estimates of potential
numbers of animals take account of all
these factors to the extent that available
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data allow. Detectability is a measure of
the probability of detecting a marine
mammal that is present on a vessel’s
trackline. L–DEO uses the most
applicable detectability values as
provided in Koski et al. (1998)
whenever estimates of marine mammal
detectability have not already been
calculated. They compiled previously
reported detectability information on
various species and used data on
surfacing/dive cycles to estimate
detectability values for species or
species groups of marine mammals for
which there is no published
detectability values. Thus the estimates
of incidental take in L–DEO’s IHA
application and Supplemental EA are
either the same (if detectability had
already been taken into account) or
higher than would be obtained by direct
application of previously reported
density data.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures.
NMFS believes that L–DEO’s revised
survey as well as the implementation of
the required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area. See Effects Analysis,
Species of Particular Concern, and L–
DEO’s Supplemental EA.
Monitoring—PAM
Comment 59: ETSSTAWG asks about
the frequency range of the PAM system,
and if it is suitable for detecting signals
produced by all the marine mammals
within the area.
Response: L–DEO’s PAM system is
suitable for detecting frequencies up to
96 kHz (192 sampling rate). The virtual
bandwidth of the new digital array and
sound analysis workstation is 96 kHz
(the real bandwidth is around 90 kHz),
which is at least double when compared
to some of the best PAM systems
normally available and four times that
of most of the basic systems. L–DEO has
the potential for expanding the PAM
system to a bandwidth of 160 kHz, but
a new hydrophone array will need to be
designed to add the required special
additional sensors. The array is capable
of detecting porpoises, but not harbor
porpoises (Phocena phocena), which
have clicks at 140 kHz.
The low frequency sensor end of the
PAM system can detect mysticetes,
however there is a problem with low
frequency noise and vibration induced
in the array by movements in towing the
acoustic array system, in particular if a
short cable and a depressor are used. To
allow detection of low frequency waves,
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it is necessary to have a long cable
towed with a good vibration damping
system and the array should be deep
and far from the ship. In the past, Right
Wave’s PAM system has been able to
detect frequencies as low as 10 Hz for
fin whales (on the NATO Alliance), but
due to towing conditions on the
Langseth the current configuration can
detect a minimum low frequency of 100
Hz.
The digital array is suitable for
detecting beaked whales, as it can
monitor and record at 48 kHz to get
their clicks. The PAM’s sound analysis
and display system has been proven
effective for detecting Cuvier’s beaked
whale clicks (Sirena 2008 cruise in the
Alboran Sea). It is important to note
here that in order to detect very diverse
sound categories, it is necessary to set
up a very powerful computer that is able
to signal process to produce and display
different real-time views, each view
well-tailored on that particular signals’
characteristics.
The PAM system has been improved
and now has a shot blanking system. A
new piece of hardware compresses the
shots without blanking them. It works
on the PAM operator’s headphone
output and doesn’t affect the recording
system. This allows the PAM operator to
hear faint signals along with the
(volume compressed) ‘‘shots’’ so that
they are always aware of what is
occurring underwater.
Comment 60: ETSSTAWG states the
MMO operating the PAM system (which
should be in addition to the other two
at all times) should have considerable
experience working with the acoustic
signals of many of the marine mammal
taxa that are likely to be encountered in
the survey.
Response: The MMO operating the
PAM system will be on watch in
addition to the two MMVOs watching
from the observation tower. Right
Waves, an Italian bioacoustics company,
is providing L–DEO with state-of-the-art
underwater acoustic equipment and
skilled operators. Right Waves started
their studies on underwater acoustics
more than 15 years ago at the
Interdisciplinary Center for Bioacoustics
and Environmental Research (CIBRA)
Institute, which is part of the University
of Pavia in Italy. They have organized
and conducted several research cruises
in order to develop their software,
hardware, and data collection protocols.
The PAM operators have applied
acoustic monitoring and mitigation
worldwide for both civil and military
institutions. Right Waves is currently
working with organizations such as
WHOI and NATO to provide their
expertise in underwater acoustics. They
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are also involved in writing mitigation
policies for the Italian Navy, NATO, and
other European organizations. Part of
their activities is described and can
be found on the CIBRA Web site at
https://www.unipv.it/cibra. The Right
Waves Web site will be available online
soon. NMFS considers the operators of
L–DEO’s PAM system to be qualified
and experienced.
Comment 61: The Commission
recommends that, before issuing the
requested authorization, the NMFS
consult with the applicant to clarify and
describe the potential conditions that
would render the use of PAM
impracticable for complementing the
visual monitoring program.
Response: Before the issuance of the
requested authorization, NMFS
consulted with L–DEO to clarify and
describe the potential conditions that
would render the use of PAM
impracticable for complementing the
visual monitoring program. L–DEO’s
lead bioacoustician has stated that there
are difficulties with towing the PAM
array because the space off the stern of
the Langseth is mostly filled by the
airgun array and streamers. L–DEO tried
to tow the PAM from the paravane
boom, paravane tow cable, and with
floats. Using these methods was not
acceptable because the quality of
acoustics was considered poor due to
tow depth and it also posed a higher
risk of totally losing the array. During L–
DEO’s recent seismic survey near Tonga,
PAM operators have found a more
successful solution to towing the PAM
array by using a depressor (intended to
sink fishing gear) that can withstand
rough weather and sea conditions. The
depressor sinks the PAM array’s lead-in
cable so that it does not get too close to
the airgun array cables. This technique,
while it works, can still be improved for
a series of reasons. Potential problems
that the current PAM set up could
experience on the Langseth include
operations in very shallow waters (20 m
or less) and operations in areas with
large amounts of fishing gear (longlines,
driftnets, etc.) that could lead to
entanglement. L–DEO has been
provided two new PAM hydrophone
arrays that are state-of-the-art, one is a
unique digital PAM array.
Comment 62: Dr. John Wang states
that L–DEO should address the
effectiveness of PAM for detecting very
high frequency vocalizations of small
cetaceans in shallow waters several
kilometers away (due to rapid
attenuation of high frequency sounds).
Response: Currently, the detection of
high-frequency marine mammals signals
in shallow water using PAM has
limitations in terms of physics, and
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perhaps even more limitations in terms
of the deployment of hydrophone
arrays. The size of the cetacean is not
likely to be a factor.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures,
including temporal and spatial
avoidance of species of particular
concern, which includes some small
cetacean species (e.g., Indo-Pacific
humpback dolphins and finless
porpoises). See NMFS’ responses to
comments above and L–DEO’s
Supplemental EA.
Comment 63: Dr. John Wang states
that L–DEO should address the
ineffectiveness of PAM at determining
the location and direction of travel of
cetaceans.
Response: One of the major reasons
PAM is not a self standing mitigation
tool is the limitations of determining
range and bearing. For a seismic vessel
on a fixed tract, the signal processing to
determine a range has not yet arrived.
Bearing is useful, but range is the
critical measure for purposes of
implementing mitigation measures for
the safety radii. In a research vessel
situation, free to change course, and
with highly trained visual and acoustic
teams, PAM can be quite effective to
track and stay with vocal marine
mammals. The potential to improve
PAM technology certainly exists. See
NMFS’ responses to comments above.
Comment 64: CSI states that in
shallow water, PAM is unlikely to be
effective in detecting finless porpoises.
Finless porpoises are not always
vocalizing and the high frequency
sounds produced by finless porpoises
attenuate quickly.
Response: L–DEO’s PAM system is
capable of detecting the high frequency
vocalizations of finless porpoises. See
responses to comments regarding finless
porpoises in Species of Particular
Concern section below. See L–DEO’s
Supplemental EA for information. After
issuance of the proposed IHA, L–DEO
modified the cruise plan and adopted
additional monitoring and mitigation
measures to reduce potential impacts on
finless porpoises. NMFS has not
authorized any takes of finless porpoises
in the IHA issued to L–DEO.
Comment 65: Dr. John Wang states
that in shallow water, PAM would be
almost completely ineffective at
detecting (never mind locating or
tracking) cetaceans especially at the
predicted rms distances for the different
exposure levels. Furthermore, PAM is
only capable of detecting cetaceans
when they are vocalizing. Some species
have been known to reduce
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vocalizations during seismic surveys
while other species do not vocalize
much at or near the surface (e.g., beaked
whales).
Response: MFS believes that visual
observers and PAM are effective tools
for monitoring marine mammals in the
affected area during the seismic survey.
PAM is required for monitoring on the
Langseth (when practicable), but not for
the implementation of mitigation
measures. PAM is used by MMOs and
the lead bioacoustician aboard the
Langseth for the detection of vocalizing
marine mammals. Any confirmed
marine mammal vocalization detections
using PAM are communicated to the
MMVOs on watch on the observation
tower to help alert the MMVOs to the
presence of vocalizing marine mammals
in the survey area (not necessarily the
safety radii). The use of PAM is
therefore used in aid of visual observers,
who monitor the applicable safety radii
for presence of marine mammals. The
detection of marine mammals in the
vicinity of the array in turn triggers
mitigation requirements specified in the
IHA issued to L–DEO.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures.
NMFS believes that the L–DEO’s revised
survey as well as the implementation of
the required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area.
Monitoring—Visual
Comment 66: ETSSTAWG states L–
DEO’s ability to monitor the exclusion
zone (‘‘EZ’’) proposed by NMFS cannot
be properly evaluated because the EZ
has not yet been established and awaits
further data from L–DEO’s 2007/2008
calibration study. See 73 FR 78297,
December 22, 2008.
Response: Acoustic data analysis for
L–DEO’s 2007/2008 calibration study is
ongoing. Results from the 2007/2008
calibration study in the Gulf of Mexico
are in review and a scientific paper on
the Langseth’s airgun sound source will
be published on a future date (Tolstoy,
pers. comm.). After the analysis is
complete and published, the empirical
data from the 2007/2008 calibration
study will be used to refine the EZ’s for
future proposed cruises as appropriate.
NMFS considers the results from the
2004 calibration study to be the best
scientific data available for L–DEO’s
purposes of monitoring the EZ’s
described in Table 1 (above).
Comment 67: Dr. John Wang states
that although large pink/white animals
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(i.e., Indo-Pacific humpback dolphins)
are highly visible within 1 km in calm
conditions, younger grey and spotted
animals can be easily missed. However,
beyond 1 km, high atmospheric
humidity and smog that is often present
along the west coast of Taiwan can
reduce visibility of these animals by a
considerable but unquantified amount
(personal observation) even with optical
aids. Furthermore, because these
dolphins are often swimming along the
shoreline next to the surf, even pink/
white dolphins can be easily missed by
offshore observers looking inshore
towards the surf. Jefferson (2000)
showed that humpback dolphin
sightings dropped off considerably
beyond a perpendicular distance of
about 400 to 500 m and none were
observed beyond about 1,500 m. Within
the predicted (but underestimated)
distances for exposure to >180 dB, many
dolphins can go undetected by MMVOs.
Response: NMFS agrees that some
species of marine mammals can be
difficult to visually detect in certain
environmental conditions. In order to
reduce potential impacts on the ETS
sub-population of Indo-Pacific
humpback dolphins, L–DEO will limit
seismic survey lines to take place at
least 20 km from the west coast of
Taiwan, except for in the passage
between the Penghu Islands and the
Waishanding Jhou (Wau-san-ting Chou)
sandbar, where the survey will pass
through the approximately 17.1 km midline distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins to
SPLs >=160 dB re 1 μPa (rms).
Comment 68: Dr. John Wang states
that L–DEO should address the
ineffectiveness of MMVOs at detecting
cetaceans, especially small cetaceans,
under non-ideal sighting conditions
(low light, rough seas, rain) and the
ineffectiveness of MMVOs at detecting
cetaceans, especially small cetaceans, at
distances beyond about 1 km but well
within the waters ensonified by levels
>180 dB in shallow waters (potentially
farther than 3.7km).
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO will be
avoiding areas where some species of
small cetaceans that are difficult to
visually detect (e.g., Indo-Pacific
humpback dolphins and finless
porpoises) are likely to occur. A sixth
MMO and regional expert will be
onboard the Langseth for the duration of
the survey in order to improve visual
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detection capabilities. L–DEO will also
be using a PAM system in order to
detect any vocalizing marine mammals.
See L–DEO’s Supplemental EA.
Comment 69: Dr. John Wang states
that L–DEO should address the
ineffectiveness of MMVOs at detecting
finless porpoise at distances beyond 1
km under any conditions, but well
within the waters ensonified by levels
>180dB (possibly >190 dB) in shallow
waters (potentially farther than 3.7km).
Response: The monitoring methods
for detection of marine mammals on the
Langseth are relatively standard
methods used onboard vessels for
conducting marine mammal abundance
surveys and under IHA’s. The PAM
system onboard the vessel is capable of
detecting the vocalizations of finless
porpoises. A description of the
monitoring methods can be found below
(see Monitoring and Mitigation). In
response to concerns about marine
mammal species of particular concern,
L–DEO will be avoiding the potential
habitat of finless porpoises. L–DEO will
shut-down the airgun array immediately
if there is a sighting at any distance of
finless porpoises in order to prevent
exposure of animals to received levels
greater than or equal to 160 dB and
especially 180 dB. No incidental take of
finless porpoises are anticipated or
authorized in the IHA issued to L–DEO.
Comment 70: Dr. John Wang states
that L–DEO should address the
ineffectiveness of MMVOs with little
experience with local marine mammal
species and conditions (species
identification can be problematic even
for experienced researchers in this
region due to the large number of
species). MMVOs that are highly
experienced with the fauna and
conditions of the region need to be
involved.
Response: The Langseth normally
carries five qualified and experienced
MMOs for every seismic study involving
use of an airgun system comparable to
the array used for this project. L–DEO
will also employ a sixth MMO and
regional expert for the duration of the
survey. MMOs are appointed by L–DEO
with NMFS concurrence.
Comment 71: Dr. John Wang states
that L–DEO should address MMVO
fatigue and lack of vigilance during
search (on-duty search times of up to
four hours is far too long; should be
reduced to rotations of between 30 and
60 minutes at most).
Response: MMO’s typically observe
for one to three hours. Because there are
usually two MMVO’s on visual watch at
a time, they alternate between visually
observing with reticle binoculars (7x50
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Fujinon), Big-eye binoculars (25x150),
and the naked eye to avoid eye fatigue.
Comment 72: Dr. John Wang states
that L–DEO should address the
ineffectiveness of night vision
equipment for small cetaceans,
especially at distances beyond about 1
km but well within the waters
ensonified by levels >180dB in shallow
waters (potentially farther than 3.7km).
Response: Though it depends on the
lights on the ship, the sea state, and
thermal factors, MMVOs estimated that
visual detection is effective out to
between 150 and 250 m using NVDs and
about 30 m with the naked eye.
However, the PAM operates equally as
effectively at night as during the day,
especially for sperm whales and
dolphins (dolphins and porpoises are
the only species likely to be detected in
the ‘‘shallow’’ depths, where the safety
zones are the largest).
Marine geophysical surveys may
continue into night and low-light hours
is such segment(s) of the survey is
initiated when the entire relevant safety
zones are visible and can be effectively
monitored. No initiation of airgun array
operations is permitted from a shutdown position at night or during lowlight hours (such as in dense fog or
heavy rain) when the entire relevant
safety zone cannot be effectively
monitored by the MMVOs on duty.
NMFS has included a requirement to
this effect in the IHA issued to L–DEO.
Comment 73: Dr. John Wang states
that L–DEO should address the
ineffectiveness of MMVOs at detecting
beaked whales, especially when they are
very quiet near the surface (detection is
known to be very low even for
experienced observers in good
conditions).
Response: NMFS agrees that beaked
whales are difficult to detect at the
surface. Three MMOs are typically on
watch at a time, two on the observation
tower conducting visual observations
and the third monitoring the PAM
equipment. The MMVOs will alternate
between surveying with reticle
binoculars (7x50 Fujinon), Big-eye
binoculars (25x150), and the naked eye
to avoid eye fatigue. The PAM system is
capable of detecting beaked whale clicks
as well.
Statements have been made in the
past that little information is available
on beaked whales because they avoid
survey vessels. One can presume
therefore, that MMOs onboard a vessel
conducting seismic operations are
unlikely to see beaked whales not only
because they are cryptic, but also
because beaked whales are likely to
avoid an approaching sound source and
leave the area.
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When operating the sound source(s),
L–DEO will minimize approaches to
slopes, submarine canyons, seamounts,
and other underwater geologic features,
if possible, because of sensitivity of
beaked whales and possible beaked
whale habitat. If concentrations or
groups of beaked whales are observed
(by visual or passive acoustic detection)
at a site such as on the continental
slope, submarine canyon, seamount, or
other underwater geologic feature just
prior to or during the airgun operations,
those operations will be powered/shutdown and/or moved to another location
along the site, if possible, based on
recommendations by the on-duty MMO
aboard the Langseth. NMFS has
included requirements to this effect in
the IHA issued to L–DEO.
Comment 74: Dr. John Wang states
that L–DEO should address the
ineffectiveness of MMVOs at detecting,
tracking and following animals entering
and exiting the area being ensonified by
sounds greater than the thresholds
stated (in shallow waters >180dB can be
farther than 3.7km).
Response: There are significant
limitations to PAM as PAM technology
is presently immature, yet constantly
improving. PAM is a useful
enhancement tool to visual observer
efforts and every effort is made to use
it when practicable. NMFS believes that
visual observers and PAM are effective
tools for monitoring marine mammals in
the affected area during the seismic
survey. PAM is required for monitoring
on the Langseth (when practicable), but
not for the implementation of mitigation
measures. PAM is used by MMOs and
the lead bioacoustician aboard the
Langseth for the detection of vocalizing
marine mammals. Any confirmed
marine mammal vocalization detections
using PAM are communicated to the
MMVOs on watch on the observation
tower to help alert the MMVOs to the
presence of vocalizing marine mammals
in the survey area (not necessarily the
safety radii). The use of PAM is
therefore used in aid of visual observers,
who monitor the applicable safety radii
for presence of marine mammals. The
detection of marine mammals in the
vicinity of the array in turn triggers
mitigation requirements specified in the
IHA issued to L–DEO.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures.
NMFS believes that L–DEO’s revised
survey as well as the implementation of
the monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
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or stocks of marine mammals in the
study area.
Comment 75: Dr. John Wang states
that it is unclear how it can be visually
observed that an animal has left the EZ
if the EZ is more distant than 1 km and
during poor sighting conditions. Not
detecting an animal within the EZ
boundary may be determined
erroneously as the animal having left
the area rather than observers failing to
see the animal. Such situations are
likely to occur very frequently when
sightings conditions are not ideal and
the EZ’s distance from source extends
beyond 1km. Obviously, this can have
serious consequences.
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO will alter
speed or course during seismic
operations if a marine mammal, based
on its position and relative motion,
appears likely to enter the relevant
safety zone. If speed or course alteration
is not safe or practicably, or if after
alteration the marine mammal still
appears likely to enter the safety zone,
further mitigation measures, such as a
power-down or shut-down, will be
taken. Following a power-down, if the
marine mammal approaches the smaller
designated safety radius, the airguns
must then be completely shut-down.
Airgun activity will not resume until the
MMVO has visually observed the
marine mammal(s) exiting the safety
radius and is not likely to return, or has
not been seen within the radius for 15
min (species with shorter dive
durations—smaller odontocetes) or 30
min (species with longer dive
durations—mysticetes and large
odontocetes, including sperm, pygmy
sperm, dwarf sperm, killer, and beaked
whales). Following a power-down or
shut-down and subsequent animal
departure, airgun operations may
resume following ramp-up procedures
described in the IHA. NMFS has
included requirements to these effects
in the IHA issued to L–DEO. NMFS
believes that L–DEO’s revised survey as
well as the implementation of the
required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area.
Comment 76: Dr. John Wang states
that secondary support vessels should
be used to search for cetaceans with
MMVOs to cover a sufficient amount of
water to reduce the number of marine
mammals being exposed to >160 dB.
Response: Prior to issuing this IHA,
NMFS thoroughly investigated all
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measures that might reduce the
incidental taking of marine mammals to
the lowest level practicable. Monitoring
and mitigation measures are discussed
later in this document. Mitigation
measures, such as aerial overflights or
support vessels to look for marine
mammals prior to an animal entering a
safety zone, may be given consideration
if the safety zone cannot be adequately
monitored from the source vessel.
Consideration also must be given to
aircraft/vessel availability, access to
nearby airfields, distance from an
airfield to the survey area, and the
aircraft’s flight duration. These are
serious safety issues regarding aircraft
flights over water that must be
considered prior to requiring aerial
overflights. Additional consideration
must be give to the potential for aircraft
to also result in Level B harassment
since a plane or helicopter would need
to fly at low altitudes to be effective.
Even if aircraft or a second vessel are
not necessary or feasible to monitor a
safety zone, they might be appropriate
to monitor shorelines (presumably for
strandings related to the activity). For
this survey, the most appropriate
monitoring is for the MMOs onboard the
Langseth to observe visually and using
the PAM system.
Comment 77: CSI states that based on
the table of predicted rms distances for
different received levels, MMVOs may
be completely ineffective for detecting
small cetaceans in shallow coastal
waters because the distance from source
will be great even for 190 dB received
level (1,600 to 2,182 m); for 180 dB, the
distances can be 2,761 to 3,694 m from
source and for 160 dB, the distances are
6,227 to 8,000 m. Again, these distances
must be considered underestimates
because the coastal waters of western
Taiwan in which some cetaceans
inhabit are much shallower than 100 m
(e.g., the critically endangered ETS subpopulation of Indo-Pacific humpback
dolphin are in waters from 1.5 to 15 m
deep; finless porpoises and Indo-Pacific
bottlenose dolphins are often commonly
observed in waters shallower than about
50 m). Finless porpoises are difficult to
detect even if they are within several
hundred meters and sighting is during
excellent conditions and by experienced
observers (note: excellent weather
conditions for sighting cetaceans in the
waters around most of Taiwan,
especially western Taiwan, are very
limited). Nighttime visual detection of
these coastal species is impossible at the
distances shown above even with nightvision equipment. MMVOs have limited
effectiveness in detecting many deepdiving species such as beaked whales
and Kogia sp. These are all difficult
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species to observe and study by
experienced researchers. Barlow (1999)
reported that very few beaked whales
are detected even in prime sighting
conditions by cetacean researchers,
Barlow and Gisiner (2006) estimated
that less than 2% of the beaked whales
are likely to be observed by typical
mitigation monitoring (this estimation
did not account for observer experience,
which will greatly affect detection).
With such a low detection rate, other
mitigation measures dependent upon
detection and tracking will be
compromised. None of the mitigation
measures takes into account sighting
conditions. This is important as several
of the mitigation measures are
dependent upon observers sighting
marine mammals.
Response: NMFS agrees that some
deep-diving species (such as beaked
whales and Kogia sp.), which may be
found in the study area, are cryptic at
the surface and difficult to observe. The
Langseth carried five qualified and
experienced MMOs for every seismic
study involving use of an airgun system
comparable to that used for this project.
MMOs are appointed by L–DEO with
NMFS concurrence. L–DEO is also
employing a regional expert as a sixth
MMO.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures.
NMFS believes that the L–DEO’s revised
survey as well as the implementation of
the required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area. See Species of Particular
Concern and L–DEO’s Supplemental
EA.
Comment 78: CSI states that L–DEO
claims that ‘‘marine mammal detection
by MMVOs is high at short distances
from the source.’’ With the possible
exception of 180 dB at 950 m for deep
water, the distances mentioned above
(especially for operations in shallow
waters) are not short for sighting
cetaceans (small or large). Detection of
most species drops off beyond 1 km
from a ship. Even 25x150 (Big-eye)
binoculars may have limited use in a
region with high humidity and smog in
coastal regions (e.g., western Taiwan),
which can reduce the clarity of high
power optical aids. The detection of
finless porpoises at distances beyond 1
km is poor. At 3,694 m, detection for
small cetaceans is limited and maybe
questionable (especially for finless
porpoises) when sighting conditions are
sub-optimal. In no way can the
detection of small cetaceans in shallow
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water at distances of several kilometers
be considered high. For beaked whales,
only a small proportion of the animals
are detected by experienced observers in
good sighting conditions (Barlow, 1999).
As such, beaked whale detection cannot
be considered to be high either. Because
detection of both shallow water small
cetaceans and beaked whales were
wrongly concluded to be high, take by
injury or death cannot be dismissed and
the potential for temporary or
permanent hearing impairment is not
low and (as discussed above) cannot be
avoided by implementing the
inadequate mitigation measures
proposed.
Response: The Langseth travels at a
much slower operation speed (four to
five kts) than vessels conducting
cetacean surveys (typically 10 kts).
Statements have been made in the past
that little information is available on
beaked whales because they avoid
survey vessels. One can presume
therefore, that MMVO’s onboard a
vessel conducting seismic operations
are unlikely to see beaked whales not
only because they are cryptic, but also
because the animals would see or hear
the slowly approaching vessel and leave
the area. NMFS presumes that beaked
whales will similarly avoid sources of
anthropogenic noise, provided they are
afforded sufficient notice of the activity
through a gradual increase in noise
levels rather than receiving a sudden,
loud sound that might inflict a panic
reaction or perhaps serious injury.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures.
NMFS believes that the L–DEO’s revised
survey as well as the implementation of
the required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area. See Species of Particular
Concern and L–DEO’s Supplemental
EA.
Comment 79: Seismic surveys should
not be conducted in poor cetacean
sighting conditions (low light, SS>4,
rain, heavy fog or haze) until a proven
(acceptable to most marine mammal
scientists) method for detecting
cetaceans is developed for such
conditions. Low light and night time
seismic surveys should not be permitted
at this time.
Dr. John Wang states that detection of
marine mammals as part of a mitigation
measure has to be at least as effective,
but preferably better, at detecting
cetaceans as cetacean survey projects
because the consequences are more
serious if cetaceans are not detected.
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Response: MMO’s effectively conduct
systematic surveys for detecting
cetaceans during the seismic cruise
onboard the Langseth. In addition to
visual observations using reticle
binoculars, big-eye binoculars, night
vision devices, and the naked eye, PAM
is used day and night (as practical),
which can detect vocalizing marine
mammals present in the area. Many
dedicated cetacean survey projects use
the same or similar equipment as the
MMO’s onboard the Langseth. The
Langseth’s crew will also assist in
detecting marine mammal, when
practicable.
During ramp-ups of the airgun array,
if for any reason the entire radius cannot
be seen for the entire 30 min (i.e., rough
seas, fog, darkness), or if marine
mammals are near, approaching, or in
the safety radius, the airguns may not be
started up. Marine seismic surveys may
continue into night and low-light hours
if such segment(s) of the survey is
initiated when the entire relevant safety
zones are visible and can be effectively
monitored. No initiation of airgun array
operations is permitted from a shutdown position at night or during lowlight hours (such as dense fog or heavy
rain) when the entire relevant safety
zone cannot be effectively monitored by
the MMVOs on duty.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures.
NMFS believes that the L–DEO’s revised
survey as well as the implementation of
the required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area.
Comment 80: The Commission
recommends that, before issuing the
requested authorization, the NMFS
extend the monitoring period to at least
one hour before initiation of seismic
activities and at least one hour before
the resumption of airgun activities after
a power-down because of a marine
mammal sighting within the safety zone.
Response: As the Commission points
out, several species of deep-diving
cetaceans are capable of remaining
underwater for more than 30 minutes,
however, for the following reasons
NMFS believes that 30 minutes is an
adequate length for the monitoring
period prior to the start-up of airguns:
(1) Because the Langseth is required to
ramp-up the time of monitoring prior to
start-up of any but the smallest array is
effectively longer than 30 minutes
(ramp-up will begin with the smallest
gun in the array and airguns will be
added in sequence such that the source
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level of the array will increase in steps
not exceeding approximately 6 dB per 5
min period over a total duration of 20–
30 min), (2) in many cases MMOs are
making observations during times when
seismic is not being operated and will
actually be observing prior to the 30 min
observation period anyway, (3) the
majority of the species that may be
exposed do not stay underwater more
than 30 minutes, and (4) all else being
equal and if deep diving individuals
happened to be in the area in the short
time immediately prior to the pre-startup monitoring, if an animal’s maximum
underwater time is 45 min, there is only
a one in three chance that the last
random surfacing would be prior to the
beginning of the required 30 min
monitoring period.
Also, seismic vessels are moving
continuously (because of the long,
towed array) and NMFS believes that
unless the animal submerges and
follows at the speed of the vessel (highly
unlikely, especially when considering
that a significant part of their
movements is vertical [deep-diving]),
the vessel will be far beyond the length
of the safety radii within 30 min, and
therefore it will be safe to start the
airguns again.
Mitigation
Comment 81: Dr. John Wang states
that the effectiveness of the mitigation
measures proposed by L–DEO for
reducing threats range between having
questionable effectiveness and being
entirely inadequate.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area.
Comment 82: NRDC is concerned that
L–DEO’s EA and NMFS’ proposed IHA
do not meet the rigorous standards of
environmental review required by the
NEPA and the MMPA. For example, L–
DEO’s EA does not properly analyze
impacts or adopt adequate mitigation
measures. Although the EA notes the
lack of scientific information regarding
species distribution and acoustic
impacts of seismic activities, it
nonetheless and without basis
concludes that the proposed surveys
will have only ‘‘minor’’ effects on
marine mammal species. NMFS’
proposed IHA also notes the lack of
density data yet nevertheless concludes,
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again without basis, that the proposed
seismic surveys will have only
negligible impacts on marine mammals.
And, like L–DEO, NMFS does not
propose meaningful mitigation
measures.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. NMFS and NSF have
satisfied all requirements of NEPA and
the MMPA.
Comment 83: WaH states that while it
may be true that some of the planned
monitoring and mitigation measures
‘‘would reduce the possibility of
injurious effects,’’ the proposed
monitoring and mitigation measures are
inadequate and cannot be argued to
prevent the possibility of injurious
effects to cetaceans, which are highly
likely to occur. The claim in the EA that
‘‘no long-term or significant effects are
expected on individual marine
mammals * * * the populations to
which they belong, or their habitats’’ is
ill-founded and should be reconsidered
in light of the above concerns.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the required
monitoring and mitigation measures
described in the IHA issued to L–DEO
will have a negligible impact on the
affected species or stocks of marine
mammals in the study area. See L–
DEO’s Supplemental EA.
Comment 84: WaH states that there is
a lack of understanding of the
distribution and status of the species
and populations mentioned in their
comments highlights the need for
greater precaution and investigation
prior to carrying out seismic surveys in
this region. However several proposed
monitoring and mitigation measures do
not reflect the need for precaution, for
example: (1) The proposed number of
MMOs is insufficient (a minimum of
only one observer working during
daytime operations, except for 30
minutes before and after ramp-up when
this will be increased to two observers);
(2) nighttime seismic survey could be
(but are not) prohibited, meaning
impaired effectiveness of MMVOs and
greater reliance on PAM, which
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provides no certainty of detection of
animals that are not vocalizing.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. The Langseth
carries five qualified and experience
MMOs for every seismic study involving
the use of an airgun system comparable
to that planned for this project. L–DEO
is employing a regional expert as a sixth
MMO. Three MMOs are typically on
watch at a time, two on the observation
tower conducting visual watch and the
third MMO monitoring the PAM
equipment. On the tower, two MMVOs
are on watch during all daylight hours
except during meal times. The scientists
conducting the survey have considered
the recommendation for no nighttime
seismic operations, and have decided
that it is not feasible, as limiting the
surveys to daytime only would either
result in the loss of half of the data or
would necessitate doubling the duration
of the project. Doubling the duration of
the surveys is not possible because the
Langseth has other research
commitments after this cruise, and
because of weather conditions
associated with the typhoon season.
However, the seismic source will not be
started if the observers cannot view the
entire safety radius for any reason
(darkness, for, or rough seas). In
addition, PAM is being used day and
night as practical, which can detect
vocalizing marine mammals present in
the study area. NMFS believes that L–
DEO’s revised survey as well as the
implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area.
Comment 85: Minor and Wilson are
greatly saddened to see the high
proportion of cetaceans that are
endangered in the proposed study area.
Some of the species have population
levels that are so low that the loss of a
single individual could significantly
increase the chances of extinction.
Minor and Wilson do not feel that
chasing these animals around with a
boat that produces seismic ‘‘bangs’’ that
are still 170 dB at a distance of 7,808 m
from the boat will be anything other
than harmful to these endangered
animals.
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the monitoring
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and mitigation measures described in
the IHA will have a negligible impact on
affected species or stocks of marine
mammals in the study area.
The principal investigator’s intended
work in the Taiwan Strait is designed so
that seismic energy from the Langseth
can be recorded by OBSs in the Taiwan
Strait and by land instruments. By using
both seismic reflections from various
rock layers and refracted seismic energy
they can determine the thickness of the
crust and get an idea of the type of rocks
in the crust. If they record data on a long
profile they can compare the crustal
structure, and, in the case of Taiwan,
identify what the structure is before and
after deformation caused by the
collision with the Luzon volcanic arc. In
Taiwan, the affects of collision increase
from south to north and also from west
to east.
Comment 86: Dr. Linda Weilgart
states that the treatment of possible
impact is very superficial, and does not
take into account that ecological and
population-level consequences may
result. Especially where many depleted
species in the area are faced with a
myriad of threats and stressors already,
the addition of noise may prove to be
the final straw. In nature, cumulative
stressors often interact synergistically,
particularly if there are several stressors.
Noise impacts should not be reduced to
merely hearing impairment, though that
is certainly possible and serious. Even
TTS can compromise an animal’s
survival, in that its feeding, predator
avoidance, and social behavior are
impacted. Other behavioral responses
such as permanent avoidance of an area
that is associated with a frightening,
loud noise are also possible.
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures in the study area.
NMFS believes that L–DEO’s revised
survey as well as the implementation of
the required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area.
Comment 87: HSI states that the
Federal Register notice for the proposed
IHA and IHA application have failed to
consider some key papers in the recent
acoustics literature, at least one of
which is a significant and telling
omission. Madsen et al. (2006) is not
cited by L–DEO in its application and
although it is cited in the EA, the
discussion there about its implications
for marine mammals with high
frequency hearing and the propagation
of seismic airgun sounds is shallow.
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41281
This is unacceptable. Clearly seismic
airguns have the capacity to propagate
well beyond the exclusion zones
proposed by L–DEO and to affect marine
mammals with higher frequency
hearing, yet the mitigation measures
discussed do not address this at all.
Response: A number of comments
pointed out shortcomings in the EA and
proposed IHA that do not alter the
overall conclusions (e.g., particular
publications that were not cited); NSF
and NMFS are grateful for those
comments and have taken note of them
for future reference.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures.
NMFS believes L–DEO’s revised survey
as well as the implementation of the
required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area.
Comment 88: CSI states that the
current EA is deficient, but its critique
will provide stakeholders with
resources to define what truly adequate
mitigations are possible, while meeting
the project’s goals. Not only that, but by
example, the world’s increasingly
active, but unregulated seismic industry
will benefit from learning what
mitigations are most effective.
Response: NMFS disagrees with CSI’s
comment. NMFS reviewed the EA and
determined that it contains an adequate
description of the proposed action and
reasonable alternatives, the affected
environment, the effects of the action,
and appropriate monitoring and
mitigation measures.
After issuance of the proposed IHA,
L–DEO modified the cruise plan and
adopted more precautionary monitoring
and mitigation measures. NMFS
believes that L–DEO’s revised survey as
well as the implementation of the
required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area.
Comment 89: CSI states that previous
L–DEO authorizations have proceeded
on the assumption that there was no
proof of significant impact, without
supporting adequate, directed research
to validate that claim. The attached
expert reviews declare several
significant research questions that need
to be answered to judge the potential
impacts from this proposal. Will L–
DEO, the NSF, and other supporters
work with the experts to enable
adequately mitigated seismic research?
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Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. NMFS prepared a Finding of
No Significant Impact and determined
that the issuance of an IHA for the take,
by harassment, of small numbers of
marine mammals incidental to L–DEO’s
March to July, 2009, seismic survey in
SE Asia will not significantly impact the
quality of the human environment, as
described in the EA.
Comment 90: Dr. McIntosh and Dr.
Wu state that a mitigation plan has been
developed that will insure the safety of
marine mammals that may be present in
the survey areas. With this mitigation
plan and lack of documented historical
impacts, they deem that injury to
marine mammals is exceedingly
unlikely and disturbance, if any, would
be minimal, local, and short-term. In
contrast, the impact of this research on
our understanding of fundamental Earth
processes is likely to be significant.
Response: NMFS acknowledges the
principal investigators’ comments and
expects L–DEO to comply with all the
requirements stipulated in the IHA.
After issuance of the proposed IHA, L–
DEO negotiated with the project’s
principal scientists (Dr. McIntosh and
Dr. Wu) and modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures.
NMFS believes that L–DEO’s revised
survey as well as the implementation of
the required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area.
Comment 91: Dr. McIntosh and Dr.
Wu state the Langseth is operated in
strict compliance with requirements
mandated by NMFS. The underlying
guidelines are based on requirements of
the ESA and the MMPA. The Langseth
will have on board five marine mammal
observers for visual and acoustic
monitoring during all seismic
operations. These operations will be
ramped-down or shut down if marine
mammals or sea turtles enter into the
NMFS-approved safety zone. This
mitigation plan is similar to those used
during previous Langseth projects and
previous seismic projects on the Ewing,
the Langseth’s predecessor. Based on
past post-cruise reports, this plan has
successfully avoided takes of marine
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mammals during numerous seismic
projects.
Response: NMFS acknowledges the
principal investigators’ comments and
expects L–DEO to comply with all the
requirements stipulated in the IHA.
Comment 92: Dr. McIntosh and Dr.
Wu state, as noted above, their seismic
operations will be in strict compliance
with the mitigation practices developed
by the NMFS, and we will avoid the
sensitive near-coastal habitat. This type
of seismic project has been undertaken
many times in the past, with marine
biological observers present, and has not
resulted in any observed impacts.
Unlike many sources of marine noise,
which emit continuous sound, seismic
work involves a short pulse of acoustic
energy followed by a significant period
of quiet.
Response: NMFS acknowledges the
information and comments provided by
the principal investigators of L–DEO’s
TAIGER seismic survey. NMFS fully
expects L–DEO to comply with all the
requirements stipulated in the IHA.
Comment 93: Dr. McIntosh and Dr.
Wu state that the seismic program will
pass through any one area at a speed of
about 8 km/hr, so any impact will be
very limited in time, generally much
less than one hour. Furthermore, the
planned transects are very widely
spaced, so most parts of the Taiwan
Strait will be completely unaffected by
the project.
Response: NMFS acknowledges the
information and comments provided by
the principal investigators of L–DEO’s
TAIGER survey. This information was
used by NMFS in making its necessary
negligible impact determinations.
Comment 94: ETSSTAWG states that
the proposed mitigation practices are
inadequate to prevent injury to
cetaceans.
Response: NMFS disagrees with
ETSSTAWG’s comment. After issuance
of the proposed IHA, L–DEO modified
its cruise plan and adopted more
precautionary monitoring and
mitigation measures. The combination
of all the mitigation and monitoring
measures, along with the avoidance
responses of many marine mammals,
ensure that takings, incidental to this
activity, will result in no more than a
negligible impact on affected species
and stocks of marine mammals and will
result in the least practicable impact on
these affected species or stocks in the
study area. See L–DEO’s Supplemental
EA.
Comment 95: ETSSTAWG
recommends that two cetacean
observers, not just one, should be on
watch at the same time. The duration of
watch times should be reduced from 4
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to 2 hours to prevent compromised
efficiency as a result of fatigue. Also,
observers should be familiar with the
cetaceans expected in the area, the
nature of the local environment (i.e., a
locally trained person), operation of the
PAM system, and the observation
methods required.
Response: The Langseth carries five
qualified and experienced MMOs for
every seismic study involving use of an
airgun system comparable to that
planned for this project. MMOs are
appointed by L–DEO with NMFS
concurrence. L–DEO has employed a
regional expert as one of the MMOs for
the duration of the survey. Three MMOs
are typically on watch at a time, two on
the observation tower conducting visual
observations and the third monitoring
the PAM equipment. On the tower, two
observers are on watch during all
daylight hours except during meal
times. MMOs typically observe for one
to three hours. Because there are usually
two MMOs on the visual watch at a
time, they alternate between observing
with reticle binoculars (7x50 Fujinon),
big-eye binoculars (25x150), and the
naked eye to avoid eye fatigue.
Comment 96: Dr. Robert Brownell and
Dr. Lien-Siang Chou from National
Taiwan University’s Institute of Ecology
and Evolutionary Biology state that the
permit application is only requesting
permission for the incidental
harassment of marine mammals (Level
B) while conducting the proposed
marine geophysical survey in SE Asia.
The survey area includes the west coast
of Taiwan, which is a hot spot for small
cetacean mass stranding events (MSEs)
or near mass stranding events (NMSEs).
Since 1990, at least 16 MSEs or NMSEs
involving six species of small cetaceans
(pygmy killer whales, rough toothed
dolphins, striped dolphins, pantropical
spotted dolphins, melon-headed whales,
and ginkgo-toothed beaked whales) have
occurred during all months of the year
except May, August, October, and
December. Taiwan has the highest
number of pygmy killer whales MSE
compared to any other location in the
world (Brownell et al., 2009). It is
possible that at least some of these
MSEs may be related to anthropogenic
noise. While ‘‘NMFS has preliminarily
determined that the impact of
conducting the seismic survey in SE
Asia may result, at worst, in temporary
modification in behavior (Level B
harassment) of small numbers of marine
mammals,’’ there is no conclusive
evidence that the proposed seismic
survey will not cause some small
cetaceans to strand. Therefore, some
mitigation and monitoring plans need to
be developed in case any strandings or
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NMSEs occur. In addition to the above
noted MSEs for Taiwan, one unusual
cetacean mortality event occurred in
Taiwan between July 19 and August 13,
2005 that involved 23 small cetaceans of
seven species. Most of the strandings
(74 percent) were beaked and dwarf
sperm whales (Yang et al., 2008).
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. No injury (Level A
harassment), serious injury, or mortality
is anticipated or authorized. NMFS
believes that the implementation of the
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
and stocks of marine mammals in the
study area.
Comment 97: Minor and Wilson state
that the EA and IHA documents also fail
to deal with the reality of the strandings
that have been associated with previous
airgun operations (including one
stranding associated with a previous
survey conducted by the proponent, L–
DEO). Minor and Wilson think that
these strandings clearly constitute
something greater than ‘‘Level B
harassment.’’
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that the implementation of the
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. No injury (Level A
harassment), serious injury, and
mortality is anticipated or authorized.
See NMFS’ responses to relevant
discussions in this document.
Comment 98: The Commission
recommends that, before issuing the
requested authorization, the NMFS
require that observations be made
during all ramp-up procedures to gather
the data needed to analyze and provide
a report on their effectiveness as a
mitigation measure. CSI states that there
are uncertainties about the effectiveness
of ramp-up procedures and no data was
presented to show that this was indeed
useful in reducing impacts.
Response: The IHA requires that
MMOs on the Langseth make
observations for 30 minutes 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
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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
(ii) Time, location, heading, speed,
activity of the vessel (including number
of airguns operating and whether in
state of ramp-up or power-down), sea
state, visibility, cloud cover, and sun
glare.
NMFS has asked NSF and L–DEO to
gather all data that could potentially
provide information regarding
effectiveness of ramp-ups as a
mitigation measure. However,
considering the low numbers of marine
mammal sightings and low numbers 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.
Comment 99: Dr. John Wang states
that L–DEO did not provide any
supporting evidence that ramp-up
procedures are effective in reducing
impacts on cetaceans. Given that it
appears to be an important proposed
mitigation measure, effectiveness of
such a procedure should be convincing.
Response: As discussed in detail
elsewhere in this document, NMFS
believes that ramp-up of the seismic
airgun array in combination with the
slow vessel speed, use of trained and
qualified MMOs, PAM, shut-down and
power-down procedures, and the
behavioral response of marine mammals
to avoid areas of high anthropogenic
noise all provide protection to marine
mammals from injury (Level A
harassment), serious injury, or
mortality. NMFS believes that L–DEO’s
revised survey as well as the
implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks in the study area.
Comment 100: CSI states that a shutdown of 30 minutes was proposed. This
is clearly not sufficient as several
species of concern can stay submerged
for more than an hour and remain
undetected.
Response: NMFS disagrees with CSI’s
comment. A shut-down of 30 minutes is
a sufficient amount of time. For species
with longer dive durations (e.g.,
mysticetes and large odontocetes,
including sperm, pygmy sperm, dwarf
sperm, killer, and beaked whales), a
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significant portion of their travel is
spent diving vertically, while the
Langseth will be traveling horizontally
at an operational speed of 7.4 to 9.3 km/
hour during seismic acquisition. The
Langseth is also equipped with a PAM
system to detect vocalizing marine
mammals.
Comment 101: Dr. John Wang states
that the resumption of airgun operations
after not observing a small odontocete
and ‘‘large’’ (following FR) odontocetes
(i.e., sperm, dwarf and pygmy sperm
whales and beaked whales) for 15 and
30 minutes is baseless. These periods
are far too short for species that can stay
submerged for greater than 60 minutes.
For many species in the region,
submergence maximum time is not
known. To be precautionary, this shutdown and search time needs to be at
least 60 minutes for small cetaceans
with no information on submergence
time and at least 90 minutes for the
‘‘large’’ odontocetes (listed above) to
ensure animals have at least one chance
of surfacing before power-up.
Response: Several species of deepdiving cetaceans are capable of
remaining underwater for more than 30
minutes. However, NMFS believes that
30 minutes is an adequate length for the
monitoring period prior to the start-up
of airguns (1) because of ramp-up
operations, (2) MMOs are usually
visually observing and using the PAM
system during non-seismic operations,
(3) the majority of the marine mammal
species in the study area that may be
exposed do not stay underwater for
more than 30 minutes, and (4) if deep
diving animals happened to be in the
operation area in the short time
immediately prior to the pre-start-up
monitoring, if an animal’s maximum
underwater time is 45 min, there is only
a one in three chance that the last
random surfacing would be prior to the
beginning of the required 30 min
monitoring period.
Seismic vessels are moving
continuously (because of the long towed
array) and NMFS believes that unless
the animals submerge and follow at the
speed of the vessel (highly unlikely,
especially when considering that a
significant part of their movements is
vertical), the vessel will be far beyond
the length of the safety radii within 30
min, and therefore it will be safe to start
the airguns again.
The time periods determined for the
resumption of airgun operations is
based on the dive duration of certain
marine mammal species, not necessarily
the animal’s physical size. Small
odontocete and pinniped species are
likely to have shorter dive durations
than mysticetes and large odontocetes
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(including sperm, pygmy sperm, dwarf
sperm, killer, and beaked whales),
which may have longer dive durations.
See NMFS’ responses in Monitoring.
Comment 102: Dr. John Wang states
that the effectiveness of any shut-downs
would depend on: the ability to detect
cetaceans, communication of the
detection, amount of time for a decision
to shut down, and how quickly a shutdown can be executed. No time frame as
to how long such a procedure would
take after a cetacean is detected was
given. Clearly, timing is important for
determining the effectiveness of this
mitigation measure.
Response: The timing of the
implementation of a shut-down or other
mitigation measure is dependent on the
judgment, recommendation, and
communication of the on-duty MMOs
aboard the Langseth to the airgun
personnel. If a marine mammal is
detected near, approaching, or in the
safety radius, then the on-duty MMO
communicates the appropriate
mitigation measure via radio and/or
phone to the science lab and airgun
technicians for immediate action.
MMVO’s alternate between observing
with reticle binoculars, big-eye
binoculars, and the naked eye for visual
detection and to avoid eye fatigue. PAM
is used day and night as practical,
which can detect vocalizing marine
mammals present in the study area.
Comment 103: Dr. John Wang states
that seismic surveys should not be
conducted within at least 10 km from
areas where a steep shelf wall exists
(e.g., east coast of Taiwan) until the
effects of reflection and constructive
interference on sound levels are better
understood.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. The seismic survey
line paralleling the east coast of Taiwan
will be moved offshore at least 20 km
to decrease potential impacts on species
that occur in coastal waters and over the
continental slope. NMFS believes that
L–DEO’s revised survey as well as the
implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. See L–DEO’s Supplemental
EA.
Comment 104: HSUS/HSI is
concerned about other aspects of the
proposed mitigation measures,
including the use of only one MMVO
(two will be used only ‘‘when
practical’’— p. 78314); visual detection
as the primary mitigation measure,
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when several vulnerable species are
extremely difficult to see even under the
best of circumstances (e.g., beaked
whales); the use of any mitigation
measure(s) at night (there has yet to be
designed any suite of nighttime
mitigation measures that is even
remotely as effective as daytime
mitigation measures when it comes to
detecting and avoiding marine
mammals); the heavy reliance on rampup of the airgun arrays (even though
there is little if any independent field
testing of the assumption that ramp-up
causes animals to move away from a
sound source); and the failure to
consider alternate schedules to avoid
the overlap of the surveys with the
calving season for several cetacean
species in the region.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. See relevant discussions
regarding nighttime, ramp-up, temporal
and spatial avoidance, and species of
particular concern in NMFS’ responses
to comments here in this document.
Comment 105: ETSSTAWG states that
the EA states that ‘‘the current
procedures are based on best practices
noted by Pierson et al. (1998) and Weir
and Dolman (2007)’’. However, this is
clearly not the case since Weir and
Dolman (2007) call for, among other
things the avoidance of sensitive areas—
e.g., the western Taiwan coastline;
suspension of airgun use at night; and
additional restrictions in adverse
weather conditions. For example, the
EA states that ‘‘when at all possible,
seismic surveying will only take place at
least 8–10 km from the Taiwanese coast,
particularly the central western coast
(∼from Taixi to Tongshiao), to minimize
the potential of exposing these
threatened dolphins to SPLs >160 dB’’.
The use of the term ‘‘when at all
possible’’ is not reassuring.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. See NMFS’ responses to
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relevant discussions regarding temporal
and spatial avoidance, species of
particular concern, nighttime
operations, and others in this document.
Comment 106: ETTSTAWG states that
the predicted protection ranges (i.e.,
safety zones) should be confirmed in the
field at each point in the survey that the
bottom geography changes substantially.
The results should be reported to NMFS
immediately and safety zone sizes
should be adjusted accordingly.
Response: NMFS believes that a
sound source verification field test is
not necessary for this project. L–DEO
conducted an acoustic calibration study
of the Langseth’s airgun array in late
2007/early 2008 in the Gulf of Mexico
(LGL Ltd., 2006). Distances where sound
levels were received in deep,
intermediate, and shallow waters will
be determined for various airgun
configurations. Acoustic analysis is
ongoing and a scientific paper on the
Langseth calibration study is currently
in review for future publication
(Tolstoy, pers. comm.). After analysis,
the empirical data from the 2007/2008
study will be used in future NEPA
documents and IHA applications. NMFS
believes the distances predicted in
Table 1 (above) are the best science
available.
Comment 107: ETTSTAWG states that
the mitigation procedures offered
(especially the use of visual detection at
night) are known to be insufficient and
ineffective. To make the most of the
limited effectiveness, and thus offer the
greatest protection, I recommend that L–
DEO’s surveys in the Taiwan Strait (and
throughout the operation) shut down at
night.
Response: A number of public
comments concerned the inability to
detect marine mammals from the
Langseth at night and recommended no
nighttime operations. The scientists
conducting the survey have considered
this recommendation, and have decided
that it is not feasible, as limiting the
surveys to daytime only would either
result in the loss of half of the data or
would necessitate doubling the duration
of the project. Doubling the duration of
the surveys is not possible because the
Langseth has other research
commitments after the TAIGER cruise,
and because of weather conditions
associated with the typhoon season. It
would also incur other potential
environmental effects. However, the
seismic source will not be started if the
MMVOs cannot view the entire safety
radius for any reason (darkness, fog, or
rough seas). In addition, PAM will be
used day and night as practical, which
can detect vocalizing marine mammals
present in the area.
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If a seismic survey vessel is limited to
daylight seismic operations, efficiency
would be much reduced. For seismic
operators in general, a daylight-only
requirement would be expected to result
in one or more of the following
outcomes: cancellation of potentially
valuable seismic surveys, reduction in
the total number of seismic cruises
annually due to longer cruise durations,
a need for additional vessels to conduct
the seismic operations, or work
conducted by non-U.S. operators or
non-U.S. vessels when in waters not
subject to U.S. law.
MMVOs using NVDs will be on watch
during periods prior to and during a
ramp-up at night. At other times during
the night MMOs will be available, but
it is not necessary or very effective for
them to be on watch constantly. The use
of PAM will improve the detection of
marine mammals by indicating to the
MMVOs when an animal is potentially
near and prompting a power-down or
shut-down when necessary. Marine
mammals are unlikely to be injured,
seriously injured or killed by the noise
from approaching seismic arrays nor is
it authorized. Thus, limiting seismic
shooting to only daylight hours is
unnecessary and unlikely to result in
less Level B harassment to marine
mammals than would conducting 24
hour survey operations.
Because of the need to keep a vessel
at-speed in order to successfully tow the
hydrophone streamers, the vessel would
need to be underway throughout the
night whether or not the airguns are
fired at night. Additional down-time
could be anticipated each day as the
vessel maneuvers all night to come back
to the shut-down location 30 minutes
after daylight. This is unlikely to be
successful very often and will likely
result in additional time needed for
surveys to be completed.
L–DEO completed two tests of the
effectiveness of using NVDs (Smultea
and Holst, 2003; Holst, 2004). Results of
those tests indicated that the NVDs are
effective at least to 150 to 200 m (492
to 656 ft) away from certain conditions.
That type of NVD is not effective at the
much larger 180 dB radii applicable
when a large array of airguns is in use.
However, it is the smaller zone where
the received levels are well above 180
dB where detection of any marine
mammals that are present would be of
particular importance. The 205 dB zone,
within which TTS might occur, is likely
to approximately 100 m (328 ft) in
radius. That is sufficiently within the
range of the NVDs to allow some chance
of detecting marine mammals visually
within the area of potential TTS during
ramp-up. Furthermore, a substantial
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proportion of the marine mammals that
might be within that distance is
expected to move away either during
ramp-up or, if the airguns were already
operating, as the vessel approaches.
Taking into consideration the
additional costs of prohibiting nighttime
operations and the likely low impact of
the activity (given the required
monitoring and mitigation measures),
NMFS has determined that the IHA’s
requirements will ensure that the
activity will have the least practicable
impact on the affected species or stocks
for the following reasons. Marine
mammals will have sufficient notice of
a vessel approaching with operating
seismic airguns, thereby giving them an
opportunity to avoid the approaching
array.
Comment 108: ETSSTAWG
recommends that L–DEO must better
incorporate changes in bottom
topography during the survey into the
designation of ‘safety zones’, and adapt
the cruise accordingly.
Response: NMFS is unsure of what
ETSSTAWG is stating in its
recommendation. After issuance of the
proposed IHA, L–DEO has modified its
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO has rerouted survey tracklines and will
implement temporal and spatial
restrictions to avoid certain areas that
they may be considered significant or
core habitat for certain species of
particular concern (see L–DEO’s
Supplemental EA). Also, the predicted
safety radii for the various sound
isopleths from the Langseth’s airgun
array are related to water depth (see
Table 1 above). Water depths have been
categorized as deep (greater than 1,000
m), intermediate (100 to 1,000 m), and
shallow (less than 100 m).
Comment 109: ETSSTAWG
recommends that the survey effort
should be suspended at night as nighttime observations are of insufficient
acuity to detect cetaceans and that the
survey effort should be suspended when
adverse weather conditions prevail that
would preclude effective spotting (e.g.
in fog, rain, heavy seas > Beaufort 3).
Response: NMFS and L–DEO have
considered these recommendations, and
have decided it is not feasible to include
such restrictions, as limiting the surveys
to daytime only would either result in
the loss of half of the data or would
necessitate doubling the duration of the
project. Doubling the duration of the
surveys is not possible because the
Langseth has other research
commitments after the TAIGER cruise,
and because of weather conditions
associated with the typhoon season. It
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would also incur other potential
environmental effects. However, the
seismic source will not be started if the
MMVOs cannot view the entire safety
radius for any reason (darkness, fog, or
rough seas). In addition, PAM will be
used day and night as practical, which
can detect vocalizing marine mammals
present in the area (see L–DEO’s
Supplemental EA).
Comment 110: HSI states that L–DEO
has ignored the mitigation measure to
avoid species temporally and must offer
a strong rationale for doing so in any
application resubmission. The rationale
that resources have already been
committed to conducting these surveys
during this time period is of course not
only unacceptable as a justification; it is
also illegal under the NEPA.
Response: NMFS disagrees with HSI’s
comment. After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. The time for the
cruise is the most suitable time
logistically for the Langseth and the
participating scientists. Given the
limited weather window for the
operations and the fact that marine
mammals are widespread in the survey
area throughout the year, altering the
timing of the proposed project likely
would result in no net benefits. Issuing
the IHA for another period could result
in significant delays and disruptions to
the cruise as well as subsequent
geophysical studies that are planned by
L–DEO for 2009 and beyond. NMFS has
fully complied with its obligations
under NEPA. See Temporal and Spatial
Avoidance section below in this
document. See L–DEO’s Supplemental
EA for more information.
Comment 111: CSI is concerned with
the timing of the proposed seismic
surveys, especially regarding dates,
locations, and species.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures, which addressed
concerns regarding certain locations and
species of marine mammals. The time
for the cruise is the most suitable time
logistically for the Langseth and the
participating scientists. Given the
limited weather window for the
operations and the fact that marine
mammals are widespread in the survey
area throughout the year, altering the
timing of the proposed project likely
would result in no net benefits. NMFS
believes that L–DEO’s revised survey as
well as the implementation of the
required monitoring and mitigation
measures described in the IHA will have
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a negligible impact on the affected
species or stocks of marine mammals in
the study area. See Temporal and
Spatial Avoidance, Species of Particular
Concern, and L–DEO’s Supplemental
EA.
Comment 112: HSI states that it is
unclear why the surveys must take place
during the proposed time period (March
21 to July 14, 2009). The applicant
acknowledges that the best available
science shows the ‘‘highest number of
marine mammal sightings and species
occur during April and June’’ (p. 78298)
in the region—the overlap with the
survey dates is obvious. This also
happens to be the calving season for
many species in the region. The NMFS
should require at a minimum that L–
DEO provide clear and substantive
justification for the proposed survey
schedule. The most effective mitigation
measure known is to avoid species
spatially and/or temporally.
Response: The seismic survey will
provide data integral to advancing
scientific understanding of the process
of large-scale mountain building. The
study is designed to characterize the
birth and evolution of a mountain belt,
which in turn can provide information
on locations and source properties of
regional earthquakes. The information is
vital to understanding plate tectonic
processes and their effects on
earthquake occurrence and distribution.
The time for the cruise is the most
suitable time logistically for the
Langseth and the participating
scientists. Given the limited weather
window for the operations and the fact
that marine mammals are widespread in
the survey area throughout the year,
altering the timing of the proposed
project likely would result in no net
benefits. Issuing the IHA for another
period could result in significant delays
and disruptions to the cruise as well as
subsequent geophysical studies that are
planned by L–DEO for 2009 and
beyond.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures, of
which include temporal and spatial
avoidance of species of particular
concern (see Temporal and Spatial
Avoidance and Species of Particular
Concern below). NMFS has included
requirements to these effects in the IHA
issued to L–DEO. See L–DEO’s
Supplemental EA.
Comment 113: Dr. John Wang states
that the period of the proposed survey
also overlaps greatly with the presence
of the most vulnerable members of
marine mammal population (females
with young calves) some of which may
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be found in aggregations or following
certain migration routes during this
time.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures, which addressed
concerns regarding certain locations and
species of marine mammals. The time
for the cruise is the most suitable time
logistically for the Langseth and the
participating scientists. Given the
limited weather window for the
operations and the fact that marine
mammals are widespread in the survey
area throughout the year, altering the
timing of the proposed project likely
would result in no net benefits. Issuing
the IHA for another period could result
in significant delays and disruptions to
the cruise as well as subsequent
geophysical studies that are planned by
L–DEO for 2009 and beyond. NMFS
believes that L–DEO’s revised survey as
well as the implementation of the
required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area. See Temporal and
Spatial Avoidance, Species of Particular
Concern, and L–DEO’s Supplemental
EA.
Comment 114: NRDC states that
NMFS’ proposed IHA does not impose
meaningful mitigation measures. For
instance, it imposes only voluntary
spatial and temporal restrictions,
introducing caveats such as avoiding
humpback winter concentration areas
‘‘if practicable’’ and limiting seismic
operations to 8–10 km from the
Taiwanese coast ‘‘when possible’’ to
reduce harm to ETS Indo-Pacific
humpback dolphins, effectively leaving
decisions on habitat avoidance to the
project proponent. 73 FR 78315; see also
NRDC v. Gutierrez, 2008 WL 360852
(N.D. Cal., Feb. 6, 2008) (noting that it
is improper for NMFS, as the agency
tasked with implementing the MMPA,
to shift its burden). Nor, given the
distribution of species and the
propagation of airgun pulses, would the
proposed 2 km coastal avoidance do
much to mitigate the harm to the ETS
Indo-Pacific humpback dolphin
population, whose entire distribution
falls within the proposed survey areas.
See comment letter submitted by Dr.
John Wang. Such measures neither meet
the agency’s statutory burden nor satisfy
the strong interest in marine mammal
protection that is embodied in the
MMPA.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
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precautionary monitoring and
mitigation measures. L–DEO will limit
seismic survey lines to take place at
least 20 km from the west coast of
Taiwan, except for in the passage
between the Penghu Islands and the
Waishanding Jhou sandbar, where the
survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
1 μPa (rms). NMFS believes that L–
DEO’s revised survey as well as the
implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. See Temporal and Spatial
Avoidance, Species of Particular
Concern, and L–DEO’s Supplemental
IHA.
Comment 115: CSI states that calving
for most cetacean species in this region
is likely in the spring to early summer
as evidenced by sightings of many
females with young calves during
cetacean surveys that have been
conducted in Taiwan and the
examination of hundreds of carcasses.
The proposed survey schedule overlaps
greatly with the calving seasons of many
species or will occur as females are
accompanied by and nursing young
calves. This proposed period for the
seismic surveys is probably the worst
choice of seasons if minimizing the
impacts of this activity on marine
mammals in this region is a sincere goal.
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area.
In the EA and Supplemental EA, L–
DEO and NSF addressed potential
impacts of the proposed seismic survey
on marine mammals, as well as other
species of concern near the survey area,
including sea turtles, fish, and
invertebrates. The EA evaluates three
alternatives: (1) The proposed seismic
survey and the issuance of an associated
IHA; (2) a corresponding seismic survey
at an alternative time, along with
issuance of an associated IHA; and (3)
a no action alternative, with no IHA and
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no seismic survey. The EA assessed
impacts to marine mammals, including
consideration of impacts to prey species
and to marine mammal habitats. A
number of monitoring and mitigation
measures were proposed as part of the
action evaluated in the EA. In
consideration of public comments
received the Supplemental EA
particularly considered adjustments to
the preferred alternative and additional
mitigation measures. Taking into
account the mitigation measures that are
planned, the potential effects on marine
mammals from the preferred alternative
are generally expected to be limited to
avoidance of the area around the
seismic operation and short-term
behavioral changes, falling within the
MMPA definition of Level B
harassment. No injury (Level A
harassment), serious injury, or mortality
is anticipated or authorized. Numbers of
individuals of all species taken are
expected to be small (relative to species
abundance).
Comment 116: NRDC states that the
additional review of the region’s marine
mammal population should be
undertaken before authorizing
incidental takes. Furthermore,
meaningful spatial and temporal
restrictions on seismic activities must be
adopted, as described in further detail at
Appendix A.
Response: After issuance of the
proposed IHA, L–DEO reviewed
information on the region’s marine
mammal populations, modified the
cruise plan, and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. See Temporal and Spatial
Avoidance below and L–DEO’s
Supplemental EA.
Comment 117: The Commission
recommends that, before issuing the
requested authorization, the NMFS
require the applicant to take all
measures necessary to ensure that the
proposed activities are not conducted
near the Ryukyu Islands and Babuyan
Islands during peak occurrence of the
humpback whales in those areas (i.e.,
February through April).
Response: To mitigate against the
potential effects of the seismic survey
on humpback whales, particularly
mother and calves on the breeding
grounds or during the beginning of
migration to summer feeding grounds,
the surveys that approach the Babuyan
Islands have been rescheduled as late as
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possible to Leg 4 (June 18 to July 20,
2009) (see L–DEO’s Supplemental EA).
The humpback whales that winter and
calve in the Ryuku Islands are near
Okinawa (Nishiwaki, 1959; Rice, 1989;
Darling and Mori, 1993), which is
approximately 400 km (249 mi) north of
the most northerly survey lines. The
Langseth’s closest approach to the
Ryuku Islands is 51.5 km (32 mi), and
26.6 km (16.5 mi) and 8.8 km (5.5 mi)
to the Babuyan and Batan Islands,
respectively.
L–DEO will avoid the areas
(Ogasawara and Ryuku Islands in
southern Japan and the Batan and
Babuyan Islands in Luzon Strait in the
northern Philippines) at the time of
peak occurrence (February to April),
where concentrations of humpback
whales are known to winter, calve, and
nurse. Seismic survey lines will be
scheduled for as late as possible (June
to July) to avoid potential effects of the
surveys on humpback whales,
particularly mothers and calves on
breeding grounds or during the
beginning of migration to summer
feeding grounds. If concentrations or
groups of humpback whales are
observed (by visual or passive acoustic
detection) prior to or during the airgun
operations, those operations will be
powered/shut-down and/or moved to
another location, if possible, based on
recommendations by the on-duty MMO
aboard the Langseth. Also, if humpback
whale mother/calf pairs are visually
sighted, the airgun array will be shutdown regardless of the distance of the
animal(s) to the sound source. The array
will not resume firing until 30 min after
the last documented whale visual
sighting.
NMFS concurs with the Commissions
recommendation and has included a
requirement to this effect in the IHA.
Comment 118: WaH states that the
potential impacts on western North
Pacific humpback whales in the waters
of the Babuyan Islands (believed to be
calving and nursing grounds for a small
population of humpback whales) and
Taiwan (e.g., along the east coast and in
the Taiwan Strait) and the fact that
surveys will occur during the northward
migration of mothers and calves is
worrying. Mothers and calves may be
more sensitive to acoustic disturbance
and are probably more susceptible to the
impacts of stress responses to
disturbance of any kind.
CSI states that the timing of the L–
DEO surveys overlaps greatly in space
and time with the whales wintering in
the Babuyan Islands and coincides
spatially and temporally with the
northward migration of mothers and
neonatal and other young calves from
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the calving/nursing grounds in the
Babuyan waters.
NRDC urges NMFS to restrict L–
DEO’s access to the Ryuku Islands:
exclusion to 200 m depth from
December through May and year-round
coastal exclusion to 20 km (this is
important breeding ground for North
Pacific humpback whale, particularly
December through May).
Response: Many concerns were raised
in public comments about the proposed
survey lines scheduled for Leg 2 (April
20 to June 7, 2009) approaching
humpback whale breeding areas in the
Babuyan and Ryuku Islands. In fact, the
humpback whales that winter and calve
in the Ryuku Islands are near Okinawa
(Nishiwaki, 1959; Rice, 1989; Darling
and Mori, 1993), some 400 km north of
the most northerly survey. However, a
small population of humpbacks does
winter and calve in the Babuyan Islands
in Luzon Strait (Acebes and Lesaca,
2003; Acebes et al., 2007). The whales
may arrive in the area as early as
November and leave in May or even
June, with peak occurrence during
February through March or April
(Acebes et al., 2007).
To mitigate against the potential
effects of the surveys on humpbacks,
particularly mothers and calves on the
breeding grounds or during the
beginning of migration to summer
feeding grounds, the surveys that
approach the Babuyan Islands have
been rescheduled as late as possible, to
Leg 4 (June 18 to July 20, 2009). The
Langseth’s closest approach to the
Ryuku and Okinawa Islands are
approximately 51.5 and 400 km,
respectively.
L–DEO will avoid the areas
(Ogasawara and Ryuku Islands in
southern Japan and the Batan and
Babuyan Islands in Luzon Strait in the
northern Philippines) at the time of
peak occurrence (February to April),
where concentrations of humpback
whales are known to winter, calve, and
nurse. Seismic survey lines will be
scheduled for as late as possible (June
to July) to avoid potential effects of the
surveys on humpback whales,
particularly mothers and calves on
breeding grounds or during the
beginning of migration to summer
feeding grounds. If concentrations or
groups of humpback whales are
observed (by visual or passive acoustic
detection) prior to or during the airgun
operations, those operations will be
powered-down, shut-down, and/or
moved to another location, if possible,
based on recommendations by the onduty MMO aboard the Langseth. If
humpback whale mother/calf pair is
visually sighted, the airgun array will be
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shut-down regardless of the distance of
the animal(s) to the sound source. The
array will not resume firing until 30 min
after the last documented whale visual
sighting. NMFS has included
requirements to these effects in the IHA
issued to L–DEO.
Comment 119: CSI has concerns
regarding particular mitigation
measures. The mitigation measures
proposed by L–DEO would be
ineffective or have limited effectiveness
at best. The claim is that surveys will be
delayed as late as possible to avoid
humpback whales, but the timing of the
surveys overlap the presence of
humpback whales greatly and during a
time when newborn calves will be
accompanying mothers. The surveys
will also occur during or near the
calving season for most species in the
region; this is when females and calves
are the most vulnerable. Given the
entire period of the proposed survey
overlaps with humpback whale
concentrations in the Babuyan island
sand during the migration period, there
is no attempt to avoid this area, and
surveying the lines near the Ryuku and
Babuyan islands as late as possible
within the scheduled period of the
surveys does nothing but delay the
impact on the animals to a slightly later
period because the whales will still be
in the area. As such, this measure does
not mitigate anything.
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures, which addressed
concerns regarding certain locations and
species of marine mammals. The time
for the cruise is the most suitable time
logistically for the Langseth and the
participating scientists. Given the
limited weather window for the
operations and the fact that marine
mammals are widespread in the survey
area throughout the year, altering the
timing of the proposed project likely
would result in no net benefits. Issuing
the IHA for another period could result
in significant delays and disruptions to
the cruise as well as subsequent
geophysical studies that are planned by
L–DEO for 2009 and beyond. NMFS
believes that L–DEO’s revised survey as
well as the implementation of the
required monitoring and mitigation
measures described in the IHA will have
a negligible impact on the affected
species or stocks of marine mammals in
the study area. See NMFS responses
above, Species of Particular Concern,
and L–DEO’s Supplemental EA.
Comment 120: CSI states that the
schedule for surveying the Luzon Strait
and the Philippine Sea overlaps
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completely with the period when
humpback whales are still in the area
(and includes the latter portion of the
peak period (April) for humpback whale
concentrations in the Babuyan Islands).
Therefore it is unclear how the timing
of the surveys reduces the impacts on
humpback whales as claimed by L–
DEO. A large proportion of this
population of humpback whales will
also be migrating through the Philippine
Sea to northern waters at the same time
as the proposed surveys. Although the
exact migratory routes of most
humpback whales are unknown, it is
clear that at least some will follow a
path that is parallel and fairly close to
the shores of eastern Taiwan. One of the
proposed survey tracklines of the
Langseth also follows this course. Many
females undertaking the migration at
this time will also be accompanied by
neonatal calves and these are the most
sensitive individuals of the population
(McCauley et al., 2000).
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. Additionally, L–
DEO will avoid the areas (Ogasawara
and Ryuku Islands in southern Japan
and the Batan and Babuyan Islands in
Luzon Strait in the northern
Philippines) at the time of peak
occurrence (February to April), where
concentrations of humpback whales are
known to winter, calve, and nurse.
Seismic survey lines will be scheduled
for as late as possible (June to July) to
avoid potential effects of the surveys on
humpback whales, particularly mothers
and calves on breeding grounds or
during the beginning of migration to
summer feeding grounds.
If concentrations or groups of
humpback whales are observed (by
visual or passive acoustic detection)
prior to or during the airgun operations,
those operations will be powered-down,
shut-down, and/or moved to another
location, if possible, based on
recommendations by the on-duty MMO
aboard the Langseth. See Species of
Particular Concern and L–DEO’s
Supplemental EA.
Comment 121: NRDC urges NMFS to
restrict L–DEO’s access to the Ryukyu
Islands: exclusion to 200 m depth from
December through May and year-round
coastal exclusion to 20 km (this is
important breeding ground for North
Pacific humpback whale, particularly
December through May, as well as yearround habitat for Indo-Pacific bottlenose
dolphin).
NRDC also states that mitigation
measures should restrict access to the
islands between northern Luzon and
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Taiwan including Babuyan, Batanes,
Calayan Islands: exclusion to 200 m
depth from December through May, as
well as year-round coastal exclusion to
20 km (these are humpback whale
breeding grounds, particularly
December through May, and reflect high
cetacean diversity year-round).
Response: L–DEO will avoid the areas
(Ogasawara and Ryuku Islands in
southern Japan and the Batan and
Babuyan Islands in Luzon Strait in the
northern Philippines) at the time of
peak occurrence (February to April),
where concentrations of humpback
whales are known to winter, calve, and
nurse. Seismic survey lines will be
scheduled for as late as possible (June
to July) to avoid potential effects of the
surveys on humpback whales,
particularly mothers and calves on
breeding grounds or during the
beginning of migration to summer
feeding grounds. If Indo-Pacific
bottlenose dolphins are visually sighted,
the airgun array will be shut-down
regardless of the distance of the
animal(s) to the sound source. The array
will not resume firing until 15 min after
the last documented dolphin sighting.
NMFS has included requirements to this
effect in the IHA issued to L–DEO. See
Species of Particular Concern and L–
DEO’s Supplemental EA.
Comment 122: CSI states that the
routes and months when Western
Pacific gray whales may undertake their
migration from suspected wintering
grounds in the South China Sea are
unknown. However, it is likely that the
period for the migration is in the spring.
Scheduling the seismic surveys in the
South China Sea to be conducted in
March and April will likely coincide
with at least some migrating gray
whales. L–DEO did not address this
possibility and have not proposed any
mitigation measures to avoid this likely
overlap of seismic surveys and
migrating gray whales.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO will avoid
shallow water areas near the mainland
China coast and western part of the
Taiwan Strait during the Western
Pacific gray whale wintering period and
migration (December to April). L–DEO
will avoid shallow, coastal waters of the
South China Sea, and limit seismic
survey lines to water depths greater than
200 m in the South China Sea, and as
far east as possible from the mainland
China side of the Taiwan Strait to
reduce potential for effects on Western
Pacific gray whales. If a Western Pacific
gray whale is visually sighted, L–DEO
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will also shut-down the airgun array
regardless of the distance of the
animal(s) to the sound source. The array
will not resume firing until 30 min after
the last documented whale visual
sighting. NMFS believes that L–DEO’s
revised survey as well as the
implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. See L–DEO’s Supplemental
EA.
Comment 123: NRDC states that
mitigation measures should restrict
access to the Strait of Taiwan from
October through May (due to gray whale
migration, as well as high cetacean
density including endangered
population of Indo-Pacific humpback
dolphins).
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO will avoid
shallow water areas near the mainland
China coast and western part of the
Taiwan Strait during Western Pacific
gray whale wintering period and
migration (December to April). L–DEO
will limit seismic survey lines to water
depths greater than 200 m in the South
China Sea, and as far east as possible
from the mainland China side of the
Taiwan Strait, to reduce potential for
effects on Western Pacific gray whales,
Indo-Pacific humpback dolphins, and
finless porpoises. NMFS believes that
L–DEO’s revised survey as well as the
implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. See Species of Particular
Concern, Temporal and Spatial
Avoidance, and L–DEO’s Supplemental
EA.
Comment 124: NRDC urges NMFS to
restrict L–DEO’s access to all South
China Sea from December through May
(due to gray whale migration).
Response: L–DEO will avoid shallow
water area near the mainland China
coast and western part of the Taiwan
Strait during the Western Pacific gray
whale wintering period and migration
(December to April). L–DEO will also
avoid shallow, coastal waters of the
South China Sea. L–DEO will limit
seismic survey lines to water depths
greater than 200 m in the South China
Sea, and as far east as possible from the
mainland China side of the Taiwan
Strait, to reduce potential for effects on
Western Pacific gray whales. NMFS has
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included requirements to this effect in
the IHA issued to L–DEO.
Comment 125: CSI states that the
critically endangered ETS subpopulation of Indo-Pacific humpback
dolphins will be subjected to greater
than 180 dB received levels even if
mitigation measures are taken (i.e., to
remain offshore of 2 km from shore).
Even if the mitigation measures
proposed by L–DEO are fully
implemented, there will likely be ‘‘Level
A harassment’’ to the ETS population
that could have serious and likely
irreversible impacts on this population.
Based on the tabled predicted RMS
distances for different received levels
and accepting the recommendations of
the ETSSTAWG for this population that
for noise issues an additional (i.e.,
additional to the 3 km from shore
distribution that is known presently for
the ETS sub-population) 2 km buffer
should be considered, the Langseth
should not be within 13 km of western
coast of Taiwan to avoid exposing
dolphins to >160 dB levels. However,
the model underestimates the actual
levels at different distances. Further
compounding the underestimation of
levels is the fact that shallow water
category is less than 100 m but the ETS
population lives in waters less than 25
m. Much better predicted RMS
distances for different received levels
are needed for very shallow waters.
Being 2 km from shore puts the
Langseth in the middle of the
distribution of the ETS population and
does absolutely nothing to reduce the
exposure level to any dolphin. The only
reduction of noise is possibly with the
statement that surveying will only take
place 8 to10 km from shore but the
condition of when possible is not
acceptable because this can be a
subjective determination by someone
not concerned about the impacts on
critically endangered populations of
cetaceans. Furthermore, as discussed
above, 8 to 10 km from shore still may
not be sufficient to reduce exposure of
the animals to greater than 160 dB and
the distribution for the ETS population
is further south than Taixi (Wang et al.,
2007b). Chou (2006) also believes that
some of the waters south of Taixi are an
important breeding/nursing area for the
ETS population. These mitigation
measures are not effective and still pose
unacceptable risks to the dolphins of
being exposed to greater than 180 dB.
The proposed seismic surveys will
exposure almost the entire ETS
population of humpback dolphins to
levels greater than 180 dB. As such, all
or almost all ETS dolphins will be
exposed to greater than 160 dB levels
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even if the Langseth remains 8 to 10 km
from shore.
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO will limit
seismic survey lines to take place at
least 20 km from the west coast of
Taiwan, except for in the passage
between the Penghu Islands and the
Waishanding Jhou sandbar, where the
survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
1 μPa (rms). See Species of Particular
Concern and L–DEO’s Supplemental
EA.
Comment 126: The Commission
recommends that, before issuing the
requested authorization, the NMFS
describe the reasons why and the
conditions under which the application
would need to conduct surveys closer
than 8 to 10 km off the coast of Taiwan
where threatened Indo-Pacific
humpback dolphins are more likely to
be exposed to sound pressure levels
greater than 160 dB re 1 μPa (rms). The
Commission also notes that it makes
more sense to use a single distance,
rather than a range, to prevent the
survey from approaching the Taiwan
coast too closely.
Response: The critically endangered
ETS sub-population of the Indo-Pacific
humpback dolphin is considered a
foreign species and is not listed under
the ESA. Foreign species are those that
occur entirely outside of U.S. territory.
NMFS does not, and is not obligated to,
designate critical habitat or develop
recovery plans for foreign species. NSF
and L–DEO’s action is planned to take
place in the territorial seas and EEZ’s of
foreign nations, and will be continuous
with the activity that takes place on the
high seas. NMFS does not authorize the
incidental take of marine mammals in
the territorial seas of foreign nations, as
the MMPA does not apply in those
waters. However, NMFS still needs to
calculate the level of incidental take in
territorial seas as part of the proposed
issuance of an IHA in regards to NMFS’
analysis of small numbers and
negligible impact determination.
After the issuance of the proposed
IHA, L–DEO modified the cruise plan
and adopted more precautionary
monitoring and mitigation measures,
especially for the ETS sub-population of
Indo-Pacific humpback dolphins. Off
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Taiwan’s west coast, the cruise tracks
have been re-routed offshore by
approximately 20 km (12.4 mi) to
protect the critically endangered ETS
subpopulation of Indo-Pacific dolphins
and finless porpoises, as well as ease
potential pressure on other coastal
species. Thus, L–DEO now plans to
maintain the precautionary buffer
recommended by ETSSTAWG in their
comments to NMFS, ‘‘at least 13 km (8.1
mi) and perhaps a more precautionary
15 km (9.3 mi) of the ETS Sousa
population—meaning up to 20 km from
shore.’’
L–DEO will limit seismic survey lines
to take place at least 20 km from the
west coast of Taiwan, except for in the
passage between the Penghu Islands and
the Waishanding Jhou sandbar, where
the survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
μPa (rms). NMFS concurs with the
recommendations made by interested
parties and has included a requirement
to this effect in the IHA issued to L–
DEO.
Comment 127: CSI states that if the
Langseth approaches to within 10 km
from shore, dolphins using waters east
of the Chinmen Islands may be exposed
to levels greater than 160 dB and some
may be exposed to 180 dB or more
depending on where the dolphins are
found in their distribution and how
close the Langseth is to the 25–30 m
isobath.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. The Chinmen
Islands are located in the western
portion of the Taiwan Strait,
approximately 15 km from the coast of
mainland China. L–DEO will avoid
shallow water areas near the mainland
China coast and western part of the
Taiwan Strait during December to April.
L–DEO will also limit seismic survey
lines to water depths greater than 200 m
in the South China Sea, and as far east
as possible from the mainland China
side of the Taiwan Strait, to reduce
potential for effects on Western Pacific
gray whales, Indo-Pacific humpback
dolphins, and finless porpoises. L–DEO
has been denied access to the waters of
China as well. See L–DEO’s
Supplemental EA.
Comment 128: HSI states that
although the Federal Register notice
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and the application note that the rms
received level distances are potentially
very large for shallow water, there is no
effort to address the shortcomings of the
proposed mitigation measures under
those circumstances. As an example, the
most vulnerable cetacean population to
be affected by these surveys (i.e., ETS
Sousa) could be routinely exposed to
sound pressure levels of 180 dB re 1 μPa
(rms) or greater (the level beyond which
Level A harassment might occur), given
the track lines proposed. Individual
Sousa could be at risk of Level A
harassment (or worse) at a distance as
far from the Langseth as 4 km (see Table
1, p. 78297). This is well beyond visual
(and probably acoustic) detection range,
yet there is little effort in the application
(or the Federal Register notice) to
address this shortcoming. The proposal
to come no nearer to the west coast of
Taiwan than 2 km (and to remain
‘‘when possible’’—p. 78315—at least 8
to 10 km offshore) is not sufficient.
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO will limit
seismic survey lines to take place at
least 20 km from the west coast of
Taiwan, except for in the passage
between the Penghu Islands and the
Waishanding Jhou sandbar, where the
survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
1 μPa (rms).
Comment 129: NRDC states that
mitigation measures should include a
year-round coastal exclusion in the
waters surrounding Taiwan to 20 km
(because of Indo-Pacific humpback
dolphin and finless porpoise habitat).
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO will limit
seismic survey lines to take place at
least 20 km from the west coast of
Taiwan, except for in the passage
between the Penghu Islands and the
Waishanding Jhou sandbar, where the
survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
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SPLs greater than or equal to 160 dB re
1 μPa (rms). The seismic survey line
paralleling the east coast of Taiwan will
be moved offshore at least 20 km to
decrease potential impacts on species
that occur in coastal waters and over the
continental slope. If an Indo-Pacific
humpback dolphin or finless porpoise is
visually sighted, the airgun array will be
shut-down regardless of the distance of
the animal(s) to the sound source. The
array will not resume firing until 15 min
after the last documented dolphin/
porpoise sighting. NMFS has included
requirements to these effects in the IHA
issued to L–DEO. See L–DEO’s
Supplemental EA.
Comment 130: ETSSTAWG states that
the lack of separate consideration of the
genetically distinct ETS population of
Sousa is, of course, a concern. One of
the most effective ways to protect
cetaceans and their habitat from the
impacts of noise (and the cumulative
and synergistic impacts in combination
with other stressors) is through spatiotemporal restrictions, including marine
protected areas (Weilgart, 2006).
Response: NMFS, NSF, and L–DEO
have considered the genetically distinct
ETS sub-population on Indo-Pacific
humpback dolphins in L–DEO’s
Supplemental EA and issuance of the
IHA to L–DEO. Several temporal and
spatial restrictions for several cetacean
species have been incorporated in the
revision of the proposed survey and
have been incorporated in NMFS’ IHA
issued to L–DEO. See Temporal and
Spatial Avoidance section of this
document and L–DEO’s Supplemental
EA.
Comment 131: WaH states that
abundance and other data in SE Asia for
sperm whales, which are known to
‘startle’ in response to seismic surveys
and to face numerous threats in the SE
Asia region (including acoustic), are
unknown, justifying precautionary
measures.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO is expected
to implement any and all monitoring
and mitigation measures described in
the IHA that are applicable to sperm
whale visual and acoustic detections. If
concentrations or groups of sperm
whales are observed (by visual or
passive acoustic detection) prior to or
during the airgun operations, those
operations will be powered/shut-down
and/or moved to another location, if
possible, based on recommendations by
the on-duty MMO aboard the Langseth.
NMFS has included a requirement to
this effect in the IHA issued to L–DEO,
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as well as additional monitoring and
mitigation measures for marine
mammals.
Comment 132: Dr. John Wang states
that recognizing the sensitivity of
beaked whales, L–DEO proposed that as
a ‘special mitigation procedure’ for
beaked whales, ‘‘approach to slopes and
submarine canyons, if possible, during
the proposed survey.’’ It is unclear what
is meant by ‘if possible’. With this
condition it is not convincing that the
procedure will actually be
implemented.
Response: When operating the sound
source(s), L–DEO will minimize
approaches to slopes, submarine
canyons, seamounts, and other
underwater geologic features, whenever
possible, because of sensitivity of
beaked whales and to avoid possible
beaked whale habitat. If concentrations
or groups of beaked whales are observed
(by visual or passive acoustic detection)
at a site such as on the continental
slope, submarine canyon, seamount, or
other underwater geologic feature just
prior to or during the airgun operations
will be powered-down, shut-down, and/
or moved to another location, if
possible, based on recommendations by
the on-duty MMO aboard the Langseth.
NMFS has included requirements to this
effect in the IHA issued to L–DEO.
After issuance of the proposed IHA,
L–DEO modified the cruise plan and
adopted more precautionary monitoring
and mitigation measures. NMFS
believes that the revised survey as well
as the implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area.
Comment 133: NRDC states that
NMFS’ proposed mitigation measures
focus primarily on visual monitoring.
However, research has cast doubt on the
ability of shipboard observers to detect
whales or for vessels to avoid collisions
through visual monitoring, particularly
as the size of the vessel increases or
visibility decreases (Clyne and Leaper,
1999). Notably, detection rates for
marine mammals generally approach
only 5 percent. It has been estimated
that in anything stronger than a light
breeze, only one in fifty beaked whales
surfacing in the direct track line of a
ship would be sighted; as the distance
approaches 1 km, that number drops to
zero (Barlow and Gisiner, 2006).
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s visual monitoring efforts
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is successful for detecting marine
mammals. In addition to extra MMOs
and high-powered binoculars, L–DEO
will be using a PAM system for
acoustically detecting marine mammals
in the vicinity of the Langseth. NMFS
expects that the impacts of the seismic
survey action on marine mammals will
be temporary in nature and not result in
substantial impact to marine mammals
or to their role in the ecosystem. The
IHA anticipates, and would authorize,
Level B harassment only, in the form of
temporary behavioral disturbance, of
species of cetaceans. Neither Level A
harassment (injury), serious injury, nor
mortality is anticipated or authorized,
and the Level B harassment is not
expected to affect biodiversity or
ecosystem function. NMFS believes that
L–DEO’s revised survey as well as the
implementation of the required
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected species
or stocks of marine mammals in the
study area. See Monitoring, Mitigation,
and L–DEO’s Supplemental EA.
Comment 134: NRDC urges NMFS to
restrict L–DEO’s access to submarine
canyons off of southwest Taiwan (due to
probable sperm and beaked whale
habitat); and marine protected areas.
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures in the study area. If
concentrations of groups of sperm
whales and/or beaked whales are
observed (by visual or passive acoustic
detection) at a site such as on the
continental slope, submarine canyon,
seamount, or other underwater geologic
feature just prior or during the airgun
operations, those operations will be
powered/shut-down and/or moved to
another location, if possible based on
recommendations by the on-duty MMO
aboard the Langseth. When operating
the sound source(s), minimize
approaches to slopes, submarine
canyons, seamounts, and other
underwater geologic features, if
possible, because of sensitivity of
beaked whales. NMFS expects NSF and
L–DEO to adhere to local conservation
laws and regulations of nations while in
foreign waters, and known rules and
boundaries of Marine Protected Areas.
In the absence of local conservation
laws and regulations or Marine
Protected Area rules, L–DEO will
continue to use the monitoring and
mitigation measures identified in the
IHA. NMFS has included requirements
to these effects in the IHA issued to L–
DEO. See Species of Particular Concern
below.
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Comment 135: NRDC urges NMFS to
restrict L–DEO’s access to the coastal
waters of the South China Sea out to 200
m depth, >20 km including islands from
April through June (because of the
presence of beaked whales and potential
gray whale breeding sites).
Response: L–DEO will limit seismic
survey lines to water depths greater than
200 m in the South China Sea, and as
far east as possible from the mainland
China side of the Taiwan Strait, to
reduce potential for effects on Western
Pacific gray whales, Indo-Pacific
humpback dolphins, and finless
porpoises. L–DEO will avoid shallow
water areas near the mainland China
coast and western part of the Taiwan
Strait during the Western Pacific gray
wintering period and migration
(December to April). L–DEO will avoid
shallow, coastal waters of the South
China Sea to avoid populations of
finless porpoises. NMFS has included
requirements to these effects in the IHA
issued to L–DEO.
Mitigation—Tracklines
Comment 136: Several interested
parties state that with tracklines
overlapping known and suspected
important habitat for beaked whales,
which are known to be particularly
sensitive to acoustic impacts, extremely
difficult to detect visually, and already
facing numerous threats (including
acoustic) within their habitat at least in
Taiwanese waters, and with almost no
data on abundance for beaked whales in
SE Asia (as reflected by the IUCN Red
List status of three species in the region
as ‘‘Data Deficient’’), there is a clear
potential for significant impacts on
beaked whales, and hence a need for
great precaution.
Waters along the edge of the
continental shelf (especially where the
strong, warm, and oligotrophic Kuroshio
Current meets the shelf edge and
nutrient input from terrestrial sources)
are particularly productive and appear
to attract cetaceans, including beaked
whales. Tracklines that run near and
parallel to the edge of the continental
shelf around Taiwan will have the
greatest impact on cetaceans, being
possibly most damaging to beaked
whales. However, without more
cetacean survey information it is
uncertain if just moving tracklines
offshore from the shelf edge would be
effective in reducing impacts on beaked
whales or if the relocation of tracklines
would harm different species or other
populations offshore.
Response: During the public comment
period, concerns were expressed about
the survey line that was parallel to and
within a few km of the east coast of
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Taiwan because of potential effects on
coastal species and those that frequent
the narrow continental shelf break and
steep slopes (e.g., beaked whales and
sperm whales). After the issuance of the
proposed IHA, L–DEO has moved the
survey line further offshore by more
than 20 km to decrease potential
impacts on species that occur in coastal
water and over the continental slope,
such as beaked whales. When operating
the sound source(s), L–DEO will
minimize approaches to slopes,
submarine canyons, seamounts, and
other underwater geologic features, if
possible, because of sensitivity of
beaked whales. Also, if concentrations
of groups of beaked whales are observed
(by visual or passive acoustic detection)
prior to or during airgun operations,
those operations will be powered-down
or shut-down and/or moved to another
location along the site, if possible, based
on recommendations by the on-duty
MMO aboard the Langseth. NMFS has
included requirements to this effect in
the IHA issued to L–DEO.
Comment 137: Dr. John Wang states
that many of the proposed tracklines
appear to maximize risk to cetacean
populations in the waters of Taiwan,
some of which are critically endangered
under the 2008 IUCN Red List.
Response: NMFS does not authorize
the incidental take of marine mammals
in the territorial sea of foreign nations,
as the MMPA does not apply in those
waters. However, NMFS still calculates
the level of incidental take in territorial
seas as part of the analysis supporting
issuance of an IHA in order to
determine the biological accuracy of the
small numbers and negligible impact
determinations for species which cross
boundaries. In this case, after the
issuance of the proposed IHA, L–DEO
modified the cruise plan and adopted
more precautionary mitigation
measures, especially for species of
particular concern. See responses to
comments discussed within this
document as well as L–DEO’s
Supplemental EA.
Comment 138: Dr. John Wang states
that several tracklines of the proposed
seismic survey immediately standout as
being very likely to cause great risk to
marine mammals in the region. Some of
the problematic tracklines include: (1)
Coastal waters of western Taiwan; (2)
approaches to the mainland of China;
(3) the shelf edge along eastern Taiwan
and oceanic islands off eastern and
northern Taiwan, northern Philippines
and the Ryuku archipelago; (4) the shelf
edge along the eastern side of the
Penghu Channel; and (5) all waters of
the Taiwan Strait.
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Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures to reduce potential
effects to marine mammals in the
region. NMFS has included
requirements to these effects in the IHA
issued to L–DEO. See responses to
comments in this document for further
information, as well as L–DEO’s
Supplemental EA.
Comment 139: Dr. John Wang states
L–DEO claimed that when conducting
the Luzon Strait/Philippine sea leg of
their survey, they will ‘‘attempt to avoid
these [for humpback whale] wintering
areas at the time of peak occurrence by
surveying a * * * slate as possible
during each leg of the cruise’’. However,
the proposed survey schedule overlaps
with the peak period of humpback
whales in the Babuyan waters (the latter
portion of the peak period being April)
and a considerable number of
humpback whales will still be in the
survey area throughout the survey
period (many will also be migrating
through the waters at the same time the
seismic surveys are planned).
Although the exact migratory routes
of most humpback whales are unknown,
it is clear that at least some will follow
a path that is parallel and fairly close to
the shores of eastern Taiwan, which is
the same path of one of the proposed
survey tracklines of the Langseth. Some
females undertaking the migration at
this time will be accompanied by
neonatal calves, which are the most
sensitive individuals of the population
(McCauley et al., 2000). Such a frivolous
and empty statement by L–DEO
attempting to mitigate its impact is
concerning and raises questions about
the sincerity of its mitigation measure
proposed.
Response: Concerns were raised in
several comments about survey lines
scheduled for Leg 2 (April 20 to June 7,
2009) approaching humpback whale
breeding areas in the Babuyan and
Ryukyu Islands. In fact, the humpback
whales that winter and calve in the
Ryukyu Islands are near Okinawa
(Nishiwaki, 1959; Rice, 1989; Darling
and Mori, 1993), some 400 km north of
the most northerly survey. However, a
small population of humpbacks does
winter and calve in the Babuyan Islands
in Luzon Strait (Acebes and Lesaca,
2003; Acebes et al., 2007). The whales
may arrive in the area as early as
November and leave in May or even
June, with peak occurrence during
February through March or April
(Acebes et al., 2007).
To mitigate against the potential
effects of the surveys on humpbacks,
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particularly mothers and calves on the
breeding grounds or during the
beginning of migration to summer
feeding grounds, the surveys that
approach the Babuyan Islands have
been rescheduled as late as possible, to
Leg 4 (June 18 to July 20, 2009). L–DEO
will avoid areas (Ogasawara and Ryuku
Islands in southern Japan and the Batan
and Babuyan Islands in Luzon Strait in
the northern Philippines) at the time of
peak occurrence (February to April),
where concentrations of humpback
whales are known to winter, calve, and
nurse. Seismic survey lines will be
scheduled for as late as possible (June
to July) to avoid potential effects of the
surveys on humpback whales,
particularly mothers and calves on
breeding grounds or during the
beginning of migration to summer
feeding grounds. Also, if concentrations
or groups of humpback whales are
observed (by visual or passive acoustic
detection) prior to or during the airgun
operations, those operations will be
powered/shut-down and/or moved to
another location, if possible, based on
recommendations by the on-duty MMO
aboard the Langseth. If humpback whale
mother/calf pairs are visually sighted,
the airgun array will be shut-down
regardless of the distance of the
animal(s) to the sound source. The array
will not resume firing until 30 min after
the last documented whale visual
sighting. NMFS has included
requirements to these effects in the IHA
issued to L–DEO.
Comment 140: Dr. John Wang states
that there is a need for cetacean surveys
before seismic surveys. Clearly, all
tracklines over or near the shelf edge
will likely impact many cetaceans.
However, without more cetacean survey
information, it is uncertain if (a) just
moving tracklines away from the shelf
edge would be effective in reducing
impacts on beaked whales; or (b) if the
relocation of tracklines would harm
different species in waters further
offshore. Recent multiple sightings of
ginkgo-toothed beaked whales during
dedicated cetaceans surveys of waters
off southeast Taiwan demonstrate the
importance of such studies. Cetacean
surveys in the waters off southwest
Taiwan where the important deep
Penghu Channel exists are limited. This
channel has a steep eastern wall that
borders against the southwest shores of
Taiwan and helps to funnel a branch of
the Kuroshio Current or the South China
Sea current to the northern tip of the
channel ending in an important area of
complex seasonal mixing with the cold
China Coastal current (Jan et al., 2002).
Response: L–DEO has moved the
seismic survey line paralleling the east
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coat of Taiwan offshore at least 20 km
to decrease potential impacts on species
that occur in coastal waters and over the
continental slope. To the maximum
extent practicable, L–DEO will schedule
seismic operations in inshore and
shallow waters during daylight hours
and OBS operations to nighttime hours.
To the maximum extent practicable,
seismic surveys (especially inshore) will
be conducted from the coast (inshore)
and proceed towards the sea (offshore)
in order to avoid trapping marine
mammals in shallow water. When
operating the sound source(s), L–DEO
will minimize approaches to slopes,
submarine canyons, seamounts, or other
geologic features, if possible, because of
sensitivity of beaked whales. If
concentrations or groups of beaked
whales are observed (by visual or
passive acoustic detection) at a site such
as on the continental slope, submarine
canyon, seamount, or other underwater
geologic feature just prior to or during
the airgun operations, those operations
will be powered-down/shut-down and/
or moved to another location, if
possible, based on recommendations by
the on-duty MMO aboard the Langseth.
NMFS has included requirements to this
effect in the IHA issued to L–DEO.
Comment 141: ETSSTAWG
recommends that the section of Leg # 4
running along the western coast of
Taiwan should be removed from the L–
DEO survey as this represents core
habitat for the critically endangered
population of ETS Sousa.
Response: L–DEO will limit seismic
survey lines to take place at least 20 km
from the west coast of Taiwan, except
for in the passage between the Penghu
Islands and the Waishanding Jhou
(Wau-san-ting Chou) sandbar, where the
survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
μPa (rms). NMFS has included a
requirement to this effect in the IHA
issued to L–DEO.
Comment 142: Based on the map of
the proposed survey track lines found in
the L–DEO application (see Figure 1, p.
3 of the application), the survey vessel
Langseth will be operating in the known
and suspected habitat of at least two
critically endangered cetacean species,
the Western Pacific gray whale and the
ETS Sousa. L–DEO must provide better
justification for the track lines—if these
are the only tracklines that will
accomplish the goals of the research,
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then L–DEO must explain why and offer
a rationale that justifies exposing
critically endangered marine mammal
populations to Level B harassment and,
despite the applicant’s assurances to the
contrary, potentially Level A
harassment and serious injury.
Response: During the public comment
period, many concerns were expressed
about the potential effects of the
proposed survey on Western Pacific
gray whales and Indo-Pacific humpback
dolphins. After issuance of the proposed
IHA, L–DEO modified the cruise plan in
a number of ways: (1) L–DEO re-routed
the survey lines in the South China Sea
south of the Taiwan Strait so that they
are now located in water depths >200
m; (2) L–DEO dropped the seismic lines
in western Taiwan Strait, and (3) L–DEO
adopted more precautionary monitoring
and mitigation measures. For example,
L–DEO will also shut-down the airgun
array if a Western Pacific gray whale is
visually sighted at any distance from the
vessel. NMFS has included
requirements to this effect in the IHA.
See NMFS’ responses to comments for
more information regarding the ETS
sub-population of Indo-Pacific
humpback dolphins, as well as L–DEO’s
Supplemental EA. NMFS has not
authorized the incidental take of
Western Pacific gray whales or IndoPacific humpback dolphins.
Comment 143: CSI states that with the
exception of a very small area where the
proposed tracklines take the Langseth to
the mainland Chinese coast and back to
western Taiwan, the Langseth will
operate in waters within 1 km from the
shore of Taiwan and right through the
middle (longitudinally) of almost the
entire linear coastal distribution of the
ETS sub-population, i.e., the proposed
trackline almost completely overlaps
with the entire distribution of the ETS
sub-population. At this distance from
shore, the Langseth will subject the
entire ETS sub-population to noise
levels much greater than 180 dB.
CSI also states that even staying
greater than or equal to 2 km from the
coastline (a proposed mitigation
measure to reduce the impact on the
ETS sub-population) does absolutely
nothing to reduce the noise exposure to
these critically endangered dolphins.
Even at 8 to 10 km from shore, the
survey will still expose all animals to
greater than 160 dB and an unknown
number would still be exposed to
greater than 180 dB. The above
statements are conservative because
they are based on the predicted rms
distances for different levels of exposure
(Table 1 in the proposed IHA Federal
Register notice), which a)
underestimates actual exposure levels in
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shallow waters and b) does not consider
reverberations that are likely to occur as
a result of the solid concrete walls that
are found along much of the central
western coast of Taiwan, the very
shallow water depths of western Taiwan
(also, tidal fluctuation is up to about 5
to 6 m and can affect the depth in which
the dolphins are found during
exposure), or many sandbars that may
force animals to be further offshore from
the solid shoreline during lower tides.
The grouping of exposures into the very
broad category of ‘shallow’ water (being
less than 100 m) is not sufficient to
understand the exposure level for a
species that occupies water depths at
the lowest end of the ‘shallow’ water
category. It is expected that the
exposure levels will be much higher at
the any given distance from source than
the predicted values in the tables. The
distance to reduce exposure to noise
levels of 160 dB or greater is unknown
for dolphins in water depths less than
25 m and could be much greater.
HSI states that the only way to avoid
exposing these critically endangered
dolphins to Level A harassment (or
serious injury)—and also to avoid Level
B harassment, to which this fragile
population should arguably not be
exposed either—is to move the
proposed trackline considerably farther
offshore than 10 km. There is no way to
avoid them on the proposed trackline
seasonally, as they are year-round
residents. It is unacceptable that L–DEO
proposes to run the Langseth directly
through the only known habitat for this
critically endangered population,
employing mitigation measures that will
clearly be ineffective at preventing Level
A harassment and serious injury, let
alone Level B harassment.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO will limit
seismic survey lines to take place at
least 20 km from the west coast of
Taiwan, except for in the passage
between the Penghu Island and the
Waishanding Jhou sandbar, where the
survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
1 μPa (rms). Thus, L–DEO is
maintaining the precautionary buffer
recommended by ETSSTAWG in their
comments to NMFS, ‘‘at least 13 km and
perhaps a more precautionary 15 km of
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the ETS Sousa population—meaning up
to around 20 km from shore.’’ NMFS has
included requirements to this effect in
the IHA issued to L–DEO.
Comment 144: CSI states that
calculations of how far the Langseth
should be to prevent the ETS population
from being exposed to levels greater
than 160 dB should be based on at least
the recommended 5 km buffer boundary
(i.e., the waters from shore to 5 km
offshore should not be exposed to levels
greater than 160 dB). However, given
the population’s critical status and the
fact that Table 1 underestimates the
actual exposure levels in shallow water,
the recommended distance should be
even more precautionary, i.e., greater
than 13 km from shore based on the
values presented in Table 1 of the
Federal Register notice.
Response: After issuance of the
proposed IHA, L–DEO negotiated with
the project’s principal scientists to
modify the cruise plan and adopt more
precautionary mitigation measures. Off
Taiwan’s west coast the cruise tracks
have been re-routed by approximately
20 km, except for in the passage
between the Penghu Islands and the
Waishanding Jhou sandbar, where the
survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
of foreign nations, to protect the
critically endangered ETS Indo-Pacific
humpback dolphin sub-population and
the finless porpoise as well as ease
potential pressure on other coastal
species. Thus, L–DEO is maintaining the
precautionary buffer recommended by
ETSSTAWG in their public comments
to NMFS, ‘‘at least 13 km and perhaps
a more precautionary 15 km of the ETS
Sousa population—meaning up to
around 20 km from shore.’’
Comment 145: Dr. John Wang states
the predicted rms distances for different
levels of exposure (Table 1 of the
proposed IHA’s Federal Register
notice), underestimates actual exposure
levels in shallow waters and does not
consider the issues with: reflection,
reverberation, rarefaction, superposition
and constructive interference (see
Shapiro et al., 2009) of sound waves in
waters that abut concrete sea walls
found along much of the central western
coast of Taiwan; the very shallow water
depths of western Taiwan (with a tidal
fluctuation up to about 5–6 m that can
affect the depth in which the dolphins
are found during exposure); and the
many sandbars and some extensive
mudflats that can force animals to be
further ‘offshore’ during lower tides.
Response: NMFS believes that while
oceanographic conditions may alter
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sound levels, for purposes of this
seismic survey, the model used for
predicting received levels in L–DEO’s
IHA application and EA is the best
science available. After the issuance of
the proposed IHA, L–DEO has modified
the cruise plan and adopted more
precautionary monitoring and
mitigation measures to reduce impacts
on species and stocks of marine
mammals in the study area. See NMFS’
responses to comments in this
document for relevant information.
Comment 146: Dr. John Wang states
the water depths in the very broad
category of ‘‘shallow’’ water (being <100
m in the proposed IHA’s Federal
Register notice) are not sufficient to
understand the exposure level for a
species (e.g., ETS Indo-Pacific
humpback dolphins) that occupies
water depths at the lowest end of the
‘‘shallow’’ water category. It is expected
that the exposure levels will be much
higher at any given distance from the
source than the predicted values
suggested.
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. The revised survey
will maintain the precautionary buffer
recommended by ETSSTAWG in their
comments to NMFS, ‘‘at least 13 km and
perhaps a more precautionary 15 km of
the ETS Sousa population—meaning up
to around 20 km from shore.’’ See L–
DEO’s Supplemental EA for more
information.
Comment 147: Dr. John Wang states
the waters of western Taiwan are highly
dynamic with seasonal, monthly, daily
and diel changes in water salinity, tidal
fluctuations, water temperature and
surface conditions that can not be
explained by the simple model for
predicting levels that was used in the L–
DEO proposal. Given that a critically
endangered population (the ETS subpopulation of Sousa chinensis), two
vulnerable and very difficult species to
detect (i.e., finless porpoises) and the
Indo-Pacific bottlenose dolphin are
found in very shallow waters it is
crucial that sound levels under differing
conditions in shallow waters be better
understood before impacts to cetaceans
are trivialized.
Response: NMFS believes that while
oceanographic conditions may alter
sound levels, for purposes of this
seismic survey, the model used for
predicting received levels in L–DEO’s
IHA application and EA is the best
science available. After the issuance of
the proposed IHA, L–DEO has modified
the cruise plan and adopted more
precautionary monitoring and
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mitigation measures to reduce impacts
on species and stocks of marine
mammals in the study area. See NMFS’
responses to comments in this
document for more relevant
information.
MMPA Concerns
Comment 148: Dr. Robert Brownell
states that the possible numbers of
marine mammals exposed to sound
levels greater than or equal to 160 dB,
during the proposed L–DEO seismic
survey in SE Asia, should be considered
erroneous based on regional population
estimates from two main sources. Of the
37 cetacean populations listed in Table
2 of the Federal Register notice (78 FR
78294, December 22, 2008), 22 are from
the ETP and have no relationship at all
to the region to be surveyed in the
western North Pacific. Humpback
whales are correct. The minke whale
and Bryde’s whale estimates are
generally correct. Omura’s whale may
be common in some parts of the survey
area. Sei, fin, and blue whales are likely
to be rare at best in the survey area. For
the small cetacean, 15 of the 28
population estimates are from the ETP
and these should not be used for the
proposed survey area. Sperm whales
may be common as opposed to
‘‘uncommon’’ in deeper waters off the
eastern side of Taiwan and in some
parts of the Philippines. The estimate
for Pacific white-sided dolphins is for
the entire North Pacific and this species
as noted is rare or does not occur in
most of the proposed survey area. Most
of the estimated 5,220 to 10,220 finless
porpoise occur in the coastal waters of
Japan, not in Taiwan or along the coast
of China. In the case of Indo-Pacific
humpback dolphins, the estimate of
1,680 animals includes about 100 from
Taiwan. The IUCN has listed the
subpopulation of these dolphins along
the limited part of the western coast of
Taiwan as ‘‘critically endangered’’ and
the subpopulation is estimated at 100
individuals. Based on the problems of
the population estimates noted above,
the estimates of the possible number of
cetaceans exposed in Table 3 of the
Federal Register notice (78 FR 78294,
December 22, 2008) are unrealistic
either as the best estimate or maximum.
Response: NMFS acknowledges Dr.
Robert Brownell’s comment and the
information provided. The information
included in the proposed IHA has been
updated in this Federal Register notice
based on comments from the public. As
noted previously, when information is
unavailable on a local population size,
NMFS uses either stock or species
information on abundance. Since
NMFS, uses the best information that is
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available, estimating impacts on marine
mammals in this manner is appropriate.
See responses to comments below.
Comment 149: Dr. Robert Brownell
states the NMFS Permit Office appears
to have preliminarily determined that
the proposed seismic surveys will not
cause any death or serious injury to
cetaceans in the survey area. This is not
a precautionary approach and some
consideration should be given to the
possibility that some beaked whales or
schools of other small cetaceans may
mass strand in response to the surveys.
Brownell et al. (2008) reviewed the
numerous fisheries that have used
sounds to hunt cetaceans. The success
of these fisheries shows that numerous
species of small cetaceans avoid and
move away from a wide variety of
anthropogenic sounds, some as simple
as hitting two rocks together
underwater. Therefore, some advanced
plan must be made to respond to any
stranding of live animals during the
proposed seismic surveys.
Response: The preliminary
determination made by NMFS in L–
DEO’s proposed IHA was not a final
determination. NMFS requested
comments on its proposal to authorize
L–DEO to incidentally take, by Level B
harassment only, small numbers of
marine mammals during the marine
seismic survey in SE Asia during
March–July 2009. Based on comments
received from the public, L–DEO
revised the proposed seismic survey in
SE Asia. Conservative monitoring and
mitigation measures were enhanced, as
compared to those described in the
proposed IHA notice. The mitigation
and monitoring measures ensure the
least practicable adverse impact on
marine mammals in the SE Asia study
area. L–DEO is not using sound for
purposes of creating a drive fishery
targeted at hunting or capturing
cetaceans as discussed in Brownell et al.
(2008). Any takes of marine mammals
incidental to L–DEO’s seismic activities
would be Level B harassment due to the
implementation of the monitoring and
mitigation measures described in the
IHA and no injury, serious injury, or
mortality is authorized. L–DEO, to the
maximum extent practicable, will
schedule seismic operations in inshore
and shallow waters during daylight
hours and OBS operations in nighttime
hours; as well as conduct seismic
surveys (especially inshore) from the
coast (inshore) and proceed towards the
sea (offshore) in order to avoid trapping
marine mammals in shallow water.
Requirements to these effects have been
included in the NMFS-issued IHA.
NMFS believes L–DEO’s revised seismic
survey and the implementation of the
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required monitoring and mitigation
measures will have a negligible impact
on affected species and stocks of marine
mammals in the study area.
Comment 150: NRDC states that there
are two types of general exemptions
available through the MMPA for
activities that incidentally ‘‘take’’
marine mammals: permits and
incidental harassment authorizations.
Until 1994, the only exemptions
available under the MMPA were
permits, which require the wildlife
agencies to promulgate regulations
specifying permissible methods of
taking. In 1994, however, the MMPA
was amended to provide a streamlined
mechanism by which proponents can
obtain authorization for projects whose
takings are by incidental harassment
only. 16 U.S.C. 1371(a)(5)(D). Regardless
of which process is used, NMFS must
prescribe ‘‘methods’’ and ‘‘means of
effecting the least practicable impact’’
on protected species as well as
‘‘requirements pertaining to the
monitoring and reporting of such
taking.’’ 16 U.S.C. 1371(a)(5)(A)(ii),
(D)(vi).
Response: The mitigation measures
described in the proposed IHA notice
have been enhanced subsequently by
increased observer personnel, temporal
and spatial avoidance of areas, as well
as for species of particular concern.
NMFS believes that the mitigation and
monitoring measures that were imposed
under the IHA are complete to the
fullest extent practicable, and ensure
that the takings will be limited to Level
B harassment and will result in a
negligible impact on the affected species
or stocks of marine mammals in the
study area. The mitigation measures
described in the proposed IHA notice
have been enhanced subsequently by
increased observer personnel, temporal
and spatial avoidance of areas, as well
as for species of particular concern.
Comment 151: Dr. John Wang and CSI
state that it has been suggested that
recent mass strandings of melon-headed
whales were related to the use of naval
sonar (in Hawaiian waters—Southall et
al., 2006) and seismic surveys (in
Madagascan waters) so there is growing
concern about the potential impact of
such activities on this species. Melonheaded whales, although not a
commonly-observed species have been
sighted on several occasions in the
waters of eastern Taiwan and southwest
Taiwan, respectively (Wang et al.,
2001a). Seismic surveys along the shelf
edge of eastern Taiwan during the
daytime will likely have an impact.
Response: NMFS is also concerned
about potential impacts on this species
due to these recent events. The behavior
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of melon-headed whales near oceanic
islands was recently described in
Brownell et al. (2009). Due to concerns,
the survey line paralleling the east coast
of Taiwan was moved offshore by more
than 20 km after issuance of the
proposed IHA to decrease potential
impacts on species that occur in coastal
waters and over the continental slope.
L–DEO will also, to the maximum
extent practicable, schedule seismic
operations in inshore and shallow
waters during daylight hours and OBS
operations during nighttime hours.
Requirements to these effects have been
included in the NMFS-issued IHA. L–
DEO’s revised seismic survey
incorporating the implementation of the
required monitoring and mitigation
measures are expected to have a
negligible impact on the affected marine
mammal species and stocks in the study
area.
Comment 152: Dr. John Wang states
that seismic surveys should not be
conducted in the spring (when many
species give birth). The survey period
(from 21 March to 14 July) proposed by
L–DEO is probably the worst choice of
seasons if minimizing impacts to marine
mammals is sought. The above
scheduling overlaps almost entirely
with the confirmed presence of
humpback whales, likely presence of
gray whales and possible presence of
right whales in the region. Calving for
most cetacean species (including those
that are critically endangered—see
above) in this region appear to be in the
spring to early summer as evidenced by
sightings of many females with neonates
and other young calves during cetacean
surveys and the examination of
hundreds of carcasses (J.Y. Wang,
unpublished data). Seismic surveys
should not be conducted in the autumn
and winter until more information about
marine mammals in these waters during
these seasons is available.
Response: Conducting the seismic
survey during a different time of year is
not feasible, as the Langseth has other
research commitments after the TAIGER
cruise. Also there are concerns with
weather conditions associated with the
typhoon season. Due to concerns
regarding humpback whales, Western
Pacific gray whales, and other species,
L–DEO has revised their planned
survey, after issuance of the proposed
IHA, to avoid breeding and feeding
areas as well as migration routes. See L–
DEO’s Supplemental EA and relevant
discussions in this document. NMFS
has included temporal and spatial
avoidance restrictions to these effects in
the IHA. NMFS believes that the revised
survey as well as the implementation of
the required monitoring and mitigation
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measures will protect species of
particular concern in the study area.
Comment 153: CSI states that there is
an inappropriate use of data from other
areas. The use of data from the Eastern
Tropical Pacific for estimating the
densities and number of individuals
impacted by the proposed seismic
survey is completely inappropriate as
there is no evidence that the two sites
of the Pacific Ocean are comparable.
Such extrapolation would not be
acceptable to most cetacean scientists.
This should be re-examined carefully.
Response: NMFS agrees that impacts
should be assessed on the population or
stock unit whenever possible. L–DEO’s
application provides information on
stock abundance of some species in SE
Asia and larger water bodies (such as
the North Pacific Ocean). The data
source for each stock estimate is
provided. NMFS believes that these data
are the best scientific information
available for estimating impacts on
marine mammal species and stocks.
However, information on marine
mammal stock abundance may not
always be satisfactory. When
information is lacking to define a
particular population or stock of marine
mammals then impacts are assessed
with respect to the species as a whole
(54 FR 40338, September 29, 1989).
MMPA Concerns—Small Numbers
Comment 154: Minor and Wilson
state the summary in the Federal
Register listing says the proposal is to
take ‘‘small’’ numbers of marine
mammals. However, the actual
proposed ‘‘take authorization’’ by L–
DEO is for 71,669 cetaceans. Minor and
Wilson propose that a reasonable upper
bound for a small number is what can
be counted on their fingers and toes.
The Federal Register summary that
twice used the word ‘‘small’’ to describe
the number 71,669, while failing to
mention the actual number, so
misinformed the public that the
resulting public consultation process is
clearly invalid.
Response: NMFS disagrees with
Minor and Wilson’s comment. The
number stated by Minor and Wilson is
the total number of individuals
requested in the proposed IHA and must
be considered in the appropriate
context. An activity affects ‘‘small
numbers’’ of a species or stock when it
is determined that the total taking will
be small relative to the estimated
population size and relevant to the
behavior, physiology, and life history of
the species or stock. Furthermore, after
issuance of the proposed IHA, L–DEO
has revised its seismic tracklines and
reduced the estimates of the possible
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number of marine mammals exposed to
certain sound levels during the TAIGER
seismic survey. NMFS believes L–DEO’s
revised seismic survey and the
implementation of the required
monitoring and mitigation measures
will have a negligible impact on affected
species and stocks of marine mammals
in the study area.
Comment 155: Dr. John Wang
disagrees that the proposed survey will
have a negligible impact on local
species of stocks of marine mammals.
The estimated number of individuals
affected (>50,000 and with 68.7% of one
critically endangered population of
dolphins being affected) cannot be
considered ‘‘small.’’
Response: NMFS believes that the
revised seismic survey described in L–
DEO’s Supplemental EA incorporating
the implementation of the monitoring
and mitigation measures required in the
IHA will have a negligible impact on
affected local species and stocks of
marine mammals in the TAIGER study
area. NMFS believes that the monitoring
and mitigation measures described
below, which have been enhanced when
compared to the proposed IHA notice,
ensure the least practicable adverse
impact on marine mammals in the SE
Asia study area. See response to
comment above.
Comment 156: Several interested
parties are concerned about impacts of
any level of take on small or vulnerable
populations. Several cetaceans are in
such critically low numbers that even
minimal ‘takes’ can contribute greatly to
the demise of these populations. Most of
the values in Table 3 do not make any
sense to those who have experience
with local marine mammal populations
in the region (e.g., the take of 64
Cuvier’s beaked whales compared with
168 Blainville’s beaked whales; a take of
189 killer whales compared with only
68 finless porpoises). These numbers are
little better than random guesses. The
statement from the Federal Register
notice is incorrect. L–DEO estimated
that 68.7% of the critically endangered
ETS population of humpback dolphins
will be impacted. Although this is a
serious underestimate (explained
earlier), it is already a very high
proportion of this distinct population
and the mitigation measures proposed
do not minimize the exposure level to
these dolphins. The taking is also
expected to include Level A harassment
rather than just Level B as claimed by
L–DEO. The taking (both Level A and B)
of such a large proportion of the ETS
dolphins could have an irreversible
impact on the continued survival of the
population.
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Response: Since the issuance of the
proposed IHA, L–DEO has revised their
seismic survey and will implement
additional mitigation measures to
address concerns regarding several
species of cetaceans in the study area.
NMFS has included these as
requirements in the IHA. There have
been few, if any, systematic aircraft- or
ship-based surveys conducted for
marine mammals in waters near
Taiwan, and the species of marine
mammals that occur there is not well
known. In the absence of any other
density data, L–DEO used the survey
effort and sightings in Yang et al. (1999)
and Wang et al. (2001a) to estimate
densities of marine mammals in the
TAIGER study area. For other areas with
an absence of density data, density data
from the Eastern Tropical Pacific was
used. There is some uncertainty about
the representativeness of the density
data and the assumptions used in the
calculations. Furthermore, NMFS
believes that the data provided is the
best available information and likely
overestimates the potential number of
animals affected. NMFS believes that L–
DEO’s revised seismic survey
incorporating the implementation of the
monitoring and mitigation measures
described in the IHA will have a
negligible impact on the affected marine
mammal species and stocks in the study
area.
Comment 157: Several interested
parties have stated that the number of
ETS Indo-Pacific humpback dolphins
potentially affected by sound levels
greater than or equal to 160 dB in L–
DEO’s proposed IHA is an unacceptably
high proportion (68.7 percent of the subpopulation). This is by far the largest
proportion of any cetacean in the region
to be affected. This high proportion in
itself is a severe underestimation of the
population being impacted, as the
Langseth will transect the entire
distribution of the ETS sub-population.
The dolphins, which have no acoustic
shelters in these waters, are not capable
of escaping to quieter waters and will be
completely exposed for the duration of
the seismic survey. Over two-thirds
cannot be reasonably argued to
constitute a ‘‘small number’’ of dolphins
in any context, let alone the context of
there being less than 100 individuals in
existence, therefore, the requested level
of impacts of this survey exceeds the
coverage provided by IHAs. Also, given
the proposed tracklines, a likely large
but unknown number of ETS IndoPacific humpback dolphins will be
exposed to levels >180 dB, which may
result not only in Level A harassment,
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but also permanent injuries or even
death.
Response: Since the issuance of the
proposed IHA, L–DEO negotiated with
the project’s principal scientists to
modify the cruise plan and adopt more
precautionary monitoring and
mitigation measures. Off Taiwan’s west
coast, the cruise tracks have been rerouted offshore by approximately 20 km
to protect critically endangered ETS
Indo-Pacific humpback dolphins as well
as other coastal species. Thus, it is now
planned to maintain the precautionary
buffer recommended by ETSSTAWG in
their comments to NMFS, ‘‘at least 13
km and perhaps a more precautionary
15 km of the ETS Sousa population—
meaning up to around 20 km from
shore’’ (see L–DEO’s Supplemental EA).
L–DEO will also shut-down
immediately if there is a sighting of an
Indo-Pacific humpback dolphin sighted
at any distance from the vessel. Based
on the re-routed tracklines, has revised
estimates of the possible numbers of
ETS Indo-Pacific humpback dolphins
exposed to sound levels that would
constitute Level B harassment to zero (0
percent of the ETS sub-population).
NMFS considers zero to be a ‘‘small
number’’ and considered the revision in
its determinations towards the issuance
of the IHA.
L–DEO’s action is planned to take
place in the territorial seas and EEZ’s of
foreign nations, and will be continuous
with the activity that takes place on the
high seas. NMFS does not authorize the
incidental take of marine mammals in
the territorial seas of foreign nations, as
the MMPA does not apply in those
waters. However, NMFS still needs to
calculate the level of incidental take in
territorial seas as part of the analysis
supporting issuance of an IHA in order
to determine the biological accuracy of
the small numbers and negligible
impact determinations.
NEPA
Comment 158: WaH states the EA
contains several erroneous claims,
omissions, and unacceptable proposals
with regards to the critically endangered
ETS population of Indo-Pacific
humpback dolphins (Sousa chinensis).
Response: NMFS acknowledges
WaH’s concerns with the EA’s analysis
of the ETS population of Indo-Pacific
humpback dolphins. Because WaH did
not offer specific details, NMFS cannot
respond directly to this comment.
Please note that in response to public
comments received on the application
and EA, L–DEO has modified the survey
design (see L–DEO’s Supplemental EA)
and adopted more precautionary
mitigation measures to protect the
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critically endangered ETS population,
as well as ease potential pressure on
other coastal species.
Comment 159: Several commenters
believed that NSF violated the tenets of
the NEPA by committing resources for
the seismic survey before completing
the EA, which they described as predecisional, biased, and falling short of
the high standard of environmental
analysis prescribed by NEPA.
Response: In accordance with NEPA,
an irreversible or irretrievable
commitment of resources refers to
impacts on or losses to resources that
cannot be recovered or reversed, i.e.,
losses are permanent or effects to uses
of resources (e.g., mineral resources,
natural productivity) that are renewable
only over long periods of time. The
referenced discussion in the EA is
specific to the scheduling of the
Langseth to make the best use of the
vessel to support the NSF science
mission. Advance vessel scheduling
does not constitute an irreversible or
irretrievable commitment of resources
as that term is intended under NEPA.
Comment 160: The most
comprehensive study undertaken on the
impacts of seismic surveys on the
fishing industry in Norway in 1996
showed that fishing catches were
impacted to as far as 33 km from seismic
testing. I can only assume this is also
not good for marine mammals who have
a limited range, such as Sousa. The
paper can be found in Norwegian at
https://www.fiskeribladetfiskaren.no/
filarkiv/vedlegg/96.pdf.
Response: NMFS thanks the
commenter for providing the link to the
article. As the study is in Norwegian, it
is not appropriate to compare the size of
the airgun array, water depth, and zones
of influence between the two activities,
for marine mammals until NMFS is able
to obtain a translation of the article.
Engas et al. (1996) studied on the
effects of seismic shooting on local
abundance and catch rates of cod
(Gadus morhua) and haddock
(Melanogrammus aeglefinus) in the
Barents Sea (near Norway). Although
the authors reported that trawl catches
of cod and haddock and longline
catches of haddock declined on average
by about 50% (by mass) after seismic
operations commenced, they observed
that abundance and catch rates returned
to pre-shooting levels five days after the
cessation of seismic operations.
Finally, NMFS has reviewed L–DEO’s
EA and supplemental EA and has
determined that no more than Level B
harassment of marine mammals would
occur. Any marine mammal that could
be exposed to the seismic survey would
likely experience short-term disturbance
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as supported by prior studies. Marine
mammals are expected, at most, to show
an avoidance response to the seismic
pulses. Further, mitigation measures
such as controlled speed, course
alteration, visual and passive acoustic
marine mammal monitoring, and shutdowns when marine mammals are
detected within the defined ranges
should further reduce short-term
reactions to disturbance, and minimize
any effects on hearing sensitivity.
Comment 161: NSF’s EA and L–DEO’s
Assessment Report did not fully analyze
impacts on marine mammals; lacked
abundance and distribution data for
marine mammal species in the proposed
waters; failed to assess cumulative
impacts, reasonable alternatives, or
mitigation measures; and provided no
evidence of consultation with local
marine mammal experts.
Response: NMFS disagrees with the
commenter’s assertions. Please see
NMFS’ response to comments in the
Effects Analysis and Species of
Particular Concern sections.
Comment 162: NEPA requires
decision-makers to consider alternatives
to their proposed actions. Thus, L–DEO
must evaluate reasonable alternatives
that would avoid or minimize adverse
impacts to the proposed seismic
surveys. See, e.g., CFR 1502.1. Yet L–
DEO’s alternatives analysis analyzes
only the specified dates and does not
even consider conducting the proposed
study during an alternate season, such
as winter and fall, which would avoid
breeding, calving and migration for
many marine mammal species in the
proposed survey areas. As discussed in
Section II and Appendix A, temporal
and spatial avoidance is necessary in
order to minimize impacts on marine
mammals and therefore must be
considered by NMFS and L–DEO.
Response: NMFS disagrees with the
commenter’s assertion. NMFS has
reviewed NSF’s EA, and determined
that it contains an adequate description
of NMFS’ proposed action and
reasonable alternatives, including a No
Action and Another Time Alternative
Action (See pages 16 to 17 of the EA).
The impacts of the seismic survey
action on marine mammals are
specifically related to acoustic activities,
and these are expected to be temporary
in nature and not result in substantial
impact to marine mammals. The IHA
anticipates, and would authorize, Level
B harassment only, in the form of
temporary behavioral disturbance, of
several species of cetaceans. Neither
Level A harassment (injury), serious
injury, nor mortality is anticipated nor
authorized.
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For the purposes of NMFS’ Federal
action (i.e., the issuance of an MMPA
authorization) the alternatives are
adequate. Thus, for the reasons stated
throughout the text of this notice, NMFS
believes that the agency is in
compliance with both the MMPA and
NEPA.
Comment 163: Several commenters
disagreed with the EA’s conclusion that
the TAIGER seismic survey would add
little to the cumulative impacts of
anthropogenic noise in the survey area.
As such, they alleged that L–DEO: (1)
Did not assess the cumulative impacts
of multiple sources of noise; (2) failed
to consider the synergistic effects of
noise with other stressors in producing
or magnifying a stress-response; and (3)
presented an invalid argument that
impacts on marine mammals were
expected to be no more than minor and
short-term.
Response: NMFS has determined that
the EA adequately addressed the
cumulative impacts of a short-term, lowintensity seismic airgun survey in
relation to long-term noise and taking
events, such as vessel traffic, habitat
loss, oil and gas industry, pollution,
fisheries, and hunting.
NMFS endangered species scientists
have conducted a thorough review of
the best available information on the
cumulative effects of the proposed
project. As a result, NMFS issued a
BiOp on the proposed action on March
31, 2009 (NMFS, 2009), which stated
that the survey was not likely to
jeopardize the continued existence of
listed marine mammals in the survey
area.
L–DEO discusses cumulative effects
of noise in the EA (see pages 71–79) and
drew comparisons between TAIGER and
other sources of anthropogenic noise
(i.e., vessel traffic, habitat loss, oil and
gas industry, pollution, fisheries, and
hunting) in the proposed survey areas.
These multiple sources of
anthropogenic noise are considered to
be long-term, continuous activities
which are unaffected by NMFS’
issuance of an incidental take
authorization for Level B harassment
only, in the form of temporary
behavioral disturbance.
In regards to stating that the impacts
of seismic surveys are small compared
to other activities, NMFS believes that
the signals do not add appreciably to the
ambient noise levels, and therefore do
not accumulate, or collect, to greater
effects. The conclusion reached in the
EA that even when considered in
combination with other underwater
sounds, seismic sound does not add
appreciably to the underwater sounds
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that fish, sea turtles and marine
mammals are exposed to, remains valid.
Precautionary Approach
Comment 164: WaH states the
proposed mitigation measures are
inadequate, do not sufficiently allow for
local marine mammal observation
conditions, and are weaknesses which
augment the risk of impacts in a region
where cetacean status and distribution
are relatively poorly understood.
According to WaH, the lack of reliable
information from systematic surveys in
the relatively poorly-studied SE Asian
region, as in other regions, necessitates
the highest levels of precaution in
estimating and attempting to mitigate
potential impacts. WaH states that even
best practice marine mammal visual
observation, shut down, and other
measures can provide no guarantee
against significant impacts on
populations in these regions (citing
inherently low observation sighting
rates for species such as beaked whales
and evidence that some species decrease
or cease vocalizing in response to
seismic surveys). WaH states that L–
DEO has not attempted to adopt all
available precautionary measures that
may help to reduce impacts.
Response: NMFS disagrees with
WaH’s comments. NMFS believes that
the monitoring and mitigation measures
ensure the least practicable impacts and
ensure that any incidental takings will
be limited to Level B harassment and
will result in a negligible impact on the
affected species or stocks of marine
mammals in the study area. As
discussed elsewhere in this document,
after issuance of the proposed IHA, L–
DEO has modified the cruise plan and
adopted more precautionary monitoring
and mitigation measures to reduce
potential impacts on marine mammals.
NMFS believes that the implementation
of these monitoring and mitigation
measures described in the IHA issued to
L–DEO will ensure that the seismic
survey will have a negligible impact on
the affected species and stocks of
marine mammals in the study area. See
L–DEO’s Supplemental EA.
Comment 165: HSI states the agency
and the applicant focus in great detail
on specific results from the limited
number of scientific studies on acoustic
impacts on marine mammals (when, for
example, results show some marine
mammal species do not avoid vessels
conducting seismic surveys) in order to
support their conclusion that impacts
from the proposed surveys will be
negligible. When specific study results
do not support their conclusion of
negligible impacts (when, for example,
results show that some marine mammal
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species cease vocalizing when exposed
to seismic airguns), they pass over them
quickly with little discussion. Similarly,
the Federal Register notice frequently
emphasizes the lack of evidence for
impacts, in what seems to be an effort
to make the classic (and inappropriate)
argument that absence of evidence is
evidence of absence of impacts. At no
time does the Federal Register notice
take the position that a lack of
information should be treated as
grounds for a precautionary approach.
Response: NMFS disagrees with this
characterization of the Federal Register
notice. NMFS relies on the best
scientific information available. NMFS
believes that the mitigation and
monitoring measures that have been
imposed under the IHA issued to L–
DEO are conservative and ensure the
least practicable adverse impacts.
Mitigation measures such as powerdowns, shut-downs, speed and course
alterations, and the use of MMVO’s and
PAM for visual and acoustic detection
will ensure that marine mammals that
do not avoid the Langseth while
operating seismic sound sources will
not be potentially impacted during the
survey. The monitoring and mitigation
measures also ensure that the takings
will be limited to Level B harassment
and will result in a negligible impact on
the affected species or stocks of marine
mammals in the study area. After
issuance of the proposed IHA, L–DEO
modified the cruise plan and adopted
more precautionary monitoring and
mitigation measures. L–DEO has also
subsequently increased observer
personnel and re-routed survey
tracklines. See L–DEO’s Supplemental
EA.
Comment 166: ETTSTAWG states that
the project description must adopt a
‘precautionary approach’ when
extrapolating from the literature to the
particular acoustic environment of the
study area, and when considering
‘unknowns’ (‘absence of evidence is not
evidence of absence’).
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. NMFS believes
that L–DEO’s revised survey as well as
the implementation of the monitoring
and mitigation measures described in
the IHA will have a negligible impact on
the affected species or stocks of marine
mammals in the study area. See NMFS’
responses to comments in Precautionary
Approach above and other relevant
discussions throughout this document.
Comment 167: ETTSTAWG states that
since empirical data is not available for
L–DEO operations (and what is
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available at deep and shallow was from
shorter arrays) in intermediate
distances, the extrapolation in the EA
(‘‘On the expectation that results would
be intermediate between those from
shallow and deep water, a correction
factor of 1.1 to 1.5x was applied to the
estimates provided by the model for
deep-water situations to obtain
estimates for intermediate-depth sites.’’)
should be much more precautionary.
Perhaps L–DEO should use a mean
between the shallow and deep water
ranges, rather than one adjusted by the
apparently arbitrary correction factor.
See Table 1.
Response: L–DEO acknowledges in
their application the shortcomings of
the models for predicted sound levels in
shallow water. Regarding the model, L–
DEO conducted an acoustic calibration
study of the Ewing’s 20 airgun, 8600 in3
array in the Gulf of Mexico in 2003
(Tolstoy et al. 2004a,b). During the
study, researchers conducted calibration
measurements for a 6, 10, 12, and 20
airgun array configurations at a depth of
approximately 30 m (98 ft) to gather
empirical data on the measured values
(i.e., received sound level) for the 160 to
190 dB re 1 μPa (rms) radii. In the 2003
study, Tolstoy et al. (2004b) reported
that for the 20 airgun array, the 160-dB
radius in shallow water was 33% higher
than predicted (Predicted = 9 km [5.5
mi]; Measured = 12 km [7.4 mi]).
According to Tolstoy et al. (2004b), the
results indicated that reverberations
played a significant role in received
levels of sound in shallow water and
that previously estimated radii for 160
and 180 dB had not accounted for
bottom reverberations. Thus, the
predicted radii were underestimates of
the actual distances where the 160 and
180 dB levels occurred in shallow
water. The authors recommended that
L–DEO extend the radii by an
appropriate factor to account for this
underestimation. As a result, L–DEO
developed correction factors for water
depths 100 to 1,000 m (328–3,281 ft)
and less than 100 m (328 ft).
For the TAIGER cruise, L–DEO has
applied conservative correction factors
to develop appropriate shallow water
exclusion zones (see Table 1 in 72 FR
78294, December 22, 2008) to mitigate
for potential effects on marine
mammals. At this time, NMFS believes
that this is the best available scientific
data for estimating seismic sound
propagation and establishing isopleths
for the Langseth’s airgun configuration.
L–DEO has measured the Langseth’s
seismic source array, and initial results,
which do not significantly vary from
those stated here, will be published in
the future.
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Comment 168: Dr. John Wang states
the applicant has not attempted to
minimize the impacts of its survey; has
not taken a precautionary approach in
addressing potential impacts, and has
not adopted mitigation measures that
are effective. Wherever uncertainties in
impacts and knowledge exist, the
applicant consistently interpreted the
uncertainties as supporting its position
of little or no impact. Not only are such
interpretations biased, misleading and
contradictory, but they are scientifically
incorrect. Absence of evidence is not
evidence of absence of impacts.
Response: After issuance of the
proposed IHA, L–DEO revised its
seismic survey and adopted more
precautionary mitigation measures.
NMFS believes that the monitoring and
mitigation measures that have been
imposed under the IHA issued to L–
DEO ensure that the takings will be
limited to Level B harassment and will
result in a negligible impact on the
affected species or stocks of marine
mammals in the study area. See L–
DEO’s Supplemental EA.
Effects Analysis
Comment 169: The concern over
anthropogenic noise and its potential
effect on cetaceans has led to repeated
resolutions by multinational groups and
organizations including the Agreement
on the Conservation of Small Cetaceans
of the Baltic and North Seas
(ASCOBANS, 2006), the Agreement on
the Conservation of Cetaceans of the
Black and Mediterranean Seas
(ACCOBAMS, 2004), and the European
Commission (2004), for member
countries to take precautionary
mitigating measures, although to date
there has been a continuing failure of
most countries to do so (Parsons et al.,
2008).
Response: The MMPA requires NMFS
to prescribe mitigation measures to
achieve the least practicable adverse
impact whenever NMFS authorizes take
of marine mammals. In this IHA, NMFS
prescribed mitigation measures that
achieve the least practicable adverse
impact, such as: re-routing the cruises
tracklines further offshore by
approximately 20 km to protect the
critically endangered ETS Indo-Pacific
humpback dolphins and the finless
porpoise; visual marine mammal
monitoring, and shut-downs when
marine mammals are detected within
the defined ranges should further
reduce short-term reactions to
disturbance, and minimize any effects
on hearing sensitivity. The best
available scientific information
demonstrates that shut-down at 180 dB
is conservative. (Southall et al., 2007).
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Comment 170: WAHLDA states that
even the high number of dolphins
estimated in the EA to be potentially
harassed does not accurately reflect the
potential impact, as the entire ETS
humpback dolphin habitat could be
ensonified at received levels of >160 dB
re 1 μPa (rms), with some dolphins
being exposed to received levels of
>180dB (rms), with some dolphins
being exposed to received levels of >180
dB (rms), given that the survey
tracklines pass within 1 km of shore (or
2 km if proposed mitigation measures
are applied) [as described in 73 FR
78294, December 22, 2008]; and
therefore directly through the shallow,
narrow, linear coastal ETS humpback
dolphin habitat which extends to 5 km
from shore.
Response: The exposure estimates
produced by the EA model: (1) Do not
take into consideration the
implementation of mitigation measures
to avoid incidentally harassing marine
mammals; (2) assume that the animals
do not move away from the Langseth
before ensonification at received levels
greater than or equal to 160 dB; and (3)
are based on overestimated densities of
several species of marine mammals. As
a result, NMFS believes that the
exposure estimates are conservative and
that the seismic survey may actually
affect far fewer marine animals that
predicted.
In response to comments received
from the public, L–DEO has completed
a Supplemental EA for the TAIGER
survey. As a result of changes made to
the location and timing of survey lines
made after the publication of the
proposed IHA and Federal Register
notice, L–DEO has revised take
estimates of the possible numbers of
marine mammals exposed to different
sound levels during L–DEO’s proposed
TAIGER seismic survey.
L–DEO and TAIGER’s principal
investigators have modified the cruise
plan and survey design, adopted more
precautionary mitigation measures to
protect the critically endangered ETS
population, as well as ease potential
pressure on other coastal species. They
have re-routed the cruise’s tracklines
offshore Taiwan’s west coast by
approximately 20 km (10.8 nautical mi)
to protect the critically endangered
Sousa population and the finless
porpoise (except for in the passage
between the Penghu Islands and the
Waishanding Jhou (Wau-san-ting Chou)
sandbar, where the survey will pass
through the 17.1 km (9.2 nautical mi)
mid-line distance between the two
possibly sensitive areas); and are
restricted to conducting seismic surveys
in water depths greater than 200 m (656
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ft) in the South China Sea, and as far
east as possible from the mainland
China side of the Taiwan Strait, to
reduce potential for effects on western
Pacific gray whales, Indo-Pacific
humpback dolphins, and finless
porpoises. In response to concerns about
marine mammal species of special
concern because of their low population
sizes, L–DEO will shut down the airgun
array immediately if there is a sighting
at any distance of the Indo-Pacific
humpbacked dolphin or finless
porpoise. Correspondingly, take
estimates of most of the other species
will be lower because of the reduction
in the ensonified area.
Comment 171: Many of the
commenters expressed concern on the
possible effects of the seismic surveys
on the small population of Indo-Pacific
humpback dolphins. They believed that
the proposed survey: would cause
minor impacts to individuals which
may lead to threats to the existence of
the ETS population; would expose
individuals to noise levels greater than
180 dB leading to serious injury or
death; and expose individual to noise
levels that may increase the likelihood
of negative interactions with boats and
gillnets.
Response: NMFS appreciates the
outpouring of concern for the well-being
of the marine mammals in and around
the Taiwan Strait and South China Sea.
For reasons discussed in the Federal
Register notice of receipt of the
application (73 FR 78294, December 22,
2009), L–DEO only requested Level B
harassment (behavioral harassment) of
small numbers of marine mammals, not
Level A (injury).
NMFS does not believe that there is
any potential for marine mammal
mortality to occur incidental to
conducting the TAIGER seismic surveys
in 2009. NMFS does not expect, nor did
it authorize take by mortality or for this
proposed activity. Incidental taking will
be limited to a temporary and localized
disturbance of animals from elevated
sound levels from seismic airguns only.
The incidental harassment authorization
includes mitigation and monitoring
measures to reduce the potential for
injury or mortality, as well as instituting
immediate shutdown protocols for the
North Pacific right whale, Western
Pacific gray whale, Indo-Pacific
humpbacked dolphin, or finless
porpoise.
The 160 dB isopleth is currently used
for estimating the onset of Level B
behavioral harassment for impulse noise
sounds. However, as NMFS shows in
this document, mortality and serious
injury are not expected to occur during
this seismic survey cruise due to
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implementation of mitigation measures
(e.g., ramp-up, passive acoustic and
visual monitoring, and quiet acoustic
periods). NMFS believes that it is highly
unlikely that a marine mammal will be
exposed to levels of sound likely to
result in Level A harassment or
mortality given the mitigation measures.
Cetaceans are expected, at most, to show
an avoidance response to the seismic
pulses. Mitigation measures such as
visual marine mammal monitoring, and
shut-downs when marine mammals are
detected within the defined ranges
should further reduce short-term
reactions to disturbance, and minimize
any effects on hearing sensitivity.
Finally, detecting and scientifically
validating a change in a marine mammal
population (e.g., trend, demographics) is
extremely difficult. It is also unrealistic
to expect a single factor to explain
population changes. To date, there is no
evidence that seismic sound has an
effect on individual survival or
reproductive success, or population
trends or demographics. However,
because research on the appropriate
temporal and spatial scales has not been
conducted, questions concerning the
level of impact at such scales remain.
NMFS relies on the best available
scientific information in determining
whether to issue incidental take
authorizations and in developing
appropriate mitigation and monitoring
measures.
Comment 172: Seismic airgun noise
has been shown to impact a variety of
species from cetaceans, to fish species,
to squid, to even invertebrates. The fact
that this noise covers a large area at high
levels makes this survey potentially
dangerous to marine life. There are
indications that similar surveys have
caused fatal giant squid and beaked
whale strandings. While I understand
that the Langseth probably has a better
airgun configuration (safer for marine
life) than its predecessor, the Ewing, it
appears very little was learned from past
experience.
Response: The IHA issued to L–DEO,
under section 101(a)(5)(D) of the
MMPA, provides mitigation and
monitoring requirements that will
protect marine mammals from any
injury or mortality. L–DEO is required
to comply with the IHA’s requirements.
Detailed analyses of underwater noise,
especially those from airguns, and
impacts to cetaceans, fish, and
invertebrates are provided in various
documents related to the proposed
project. These include: (1) The Federal
Register notice for the receipt of L–
DEO’s application (73 FR 78294,
December 22, 2008); (2) the EA and SEA
for the TAIGER seismic; (3) and the
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BiOp and ITS. These analyses are
supported by extensive scientific
research and data. These reviews have
led NMFS to conclude that the proposed
seismic surveys would have a negligible
impact on the affected species or stocks
of marine mammals and are not likely
to jeopardize the continued existence of
any ESA listed species.
The evidence linking giant squid
(Architeuthis dux) strandings and
seismic surveys remains inconclusive at
best. Most of the information on
acoustic effects on squid is derived from
non-peer reviewed sources such as
industry reports, government reports,
conference proceedings, and news
articles. NMFS is aware of two sources
that attempted to link giant squid
strandings and seismic surveys. The
first is a presentation given at the
International Council for Exploration of
the Sea (ICES) Annual Science
Conference in 2004 (Geurra et al., 2004).
The authors reported that a total of nine
squid stranded or surfaced in the Bay of
Biscay in 2001 and 2003 and conducted
necropsies on seven of the specimens
which were previously frozen and then
thawed for examination. In that
presentation, Guerra et al. (2004)
speculated that the mortalities were the
result of geologists conducting marine
geophysical surveys in the vicinity.
However, the authors failed to describe
the seismic sources, locations, and
durations of the surveys which resulted
in a lack of knowledge regarding the
spatial and temporal correlation
between the squid and the sound
source. In addition, there were no
controls and the examined animals had
been dead long enough for
commencement of tissue degradation.
The second source, an article in New
Scientist magazine (MacKenzie, 2004),
only summarizes and repeats Guerra et
al. (2004) claims without additional
empirical evidence. Thus, it cannot be
used as the best available information
for assessing impacts of airgun sounds
on marine invertebrates.
As in the case of the giant squid, the
scientific evidence linking beaked
strandings and seismic surveys still
remains inconclusive. However, the
association of mass strandings of beaked
whales with naval exercises (Malakoff,
2002), has raised the possibility that
beaked whales exposed to strong
‘‘pulsed’’ sounds may be susceptible to
injury and/or behavioral reactions that
can lead to stranding (e.g., Hildebrand,
2005; Southall et al., 2007). Suggestions
that there was a link between seismic
surveys and strandings of humpback
whales in Brazil (Engel et al., 2004)
were not well founded (IAGC, 2004;
IWC, 2007). In September, 2002, two
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Cuvier’s beaked whales stranded in the
Gulf of California, Mexico. The Ewing
had been operating a 20 airgun, 8,490in 3 airgun array 22 km offshore the
general area at the time that strandings
occurred. The link between the
stranding and the seismic surveys was
inconclusive and not based on any
physical evidence (Hogarth, 2002;
Yoder, 2002) as some vacationing
marine mammal researchers who
happened upon the stranding were illequipped to perform an adequate
necropsy. Furthermore, the small
numbers of animals involved and the
lack of knowledge regarding the spatial
and temporal correlation between the
beaked whales and the sound source
underlies the uncertainty regarding the
linkage between seismic sound sources
and beaked whale strandings (Cox et al.,
2006).
No injuries of beaked whales are
anticipated during the proposed study
because of: (1) The high likelihood that
any beaked whales nearby would avoid
the approaching vessel before being
exposed to high sound levels; (2) the
proposed monitoring and mitigation
measures; and (3) differences between
the sound sources operated by the
Langseth and the Ewing, as the
Langseth’s source arrays have a smaller
airgun volume than the Ewing’s.
Comment 173: The possibility of
trophic cascades was also unaddressed.
Most marine animals are acoustically
sensitive. Since components in the
marine ecosystem are particularly
interlinked, such effects cannot be
discounted. It is time serious
consideration be given to (possibly)
subtle, long-term impacts at the level of
the population and ecosystem. These
are the effects we should be most
concerned about, yet they barely receive
any attention in this application.
Response: NMFS acknowledges the
public’s concern about the effects of
seismic sound on prey items of marine
mammals. However, NMFS would refer
the commenter to Chapter 4 section 5 of
the final EA titled ‘‘Direct Effects on
Fish and Their Significance’’; section 6
titled ‘‘Direct Effects on Invertebrates
and Their Significance’’; Appendix D:
Review Of Potential Impacts Of Airgun
Sounds On Fish; and Appendix E:
Review Of Potential Impacts Of Airgun
Sounds on Marine Invertebrates to see
the applicant’s analysis and
consideration of potentially affected
trophic species. NMFS believes that L–
DEO sufficiently analyzed the current
research on the effects of seismic sound
sources on fish and invertebrates.
Comment 174: Minor and Wilson
have read the IHA request and are
disappointed about the lack of balance
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in its presentation. The numerous
graphs and tables that describe the
activity and levels of take are not well
supported with data. ‘‘Little is known
about’’ is a common refrain concerning
biological effects, and the document
notes that models used underestimate
the actual sound levels by as much as
15x (which is a 1,500 percent modeling
error).
Response: The L–DEO application,
the NSF’s EA and SEA, and the BiOp
and ITS provided the necessary
information and analyses needed for
NMFS to determine whether the
proposed incidental harassment takings
would be of small numbers of marine
mammals and would have no more than
a negligible impact on marine mammals
pursuant to the MMPA. Because Minor
and Wilson did not offer specific details
on the specific graphs and tables in
question, NMFS cannot respond directly
to their concerns on the lack of
supported data.
NMFS disagrees with the
commenters’ assertions about the lack of
balance in the application. NMFS
published the proposed regulations on
December 22, 2008 (72 FR 78294) and
on January 16, 2009 (74 FR 2995),
providing required notice and
opportunity for the public to address
concerns and submit comments on the
application and EA. By its very nature,
the process of public review ensures
that NMFS’ analyses will be balanced
and would incorporate the best
available scientific information. In
response to the public comments
received during the public comment
period, L–DEO has modified the survey
design (see L–DEO’s Supplemental EA)
and enhanced mitigation measures
included in the proposed IHA. Finally,
NMFS has incorporated additional
mitigation measures to the IHA.
As Minor and Wilson point out in
their letter, L–DEO acknowledges in
their application the shortcomings of
the models for predicted sound levels in
shallow water. Regarding the model, L–
DEO conducted an acoustic calibration
study of the Ewing’s 20 airgun 8,600-in3 array in the Gulf of Mexico in 2003
(Tolstoy et al., 2004a,b). During the
study, researchers conducted calibration
measurements for a 6-, 10-, and 12-, and
20-airgun array configurations at a
depth of approximately 30 m (98 ft) to
gather empirical data on the measured
values (i.e., received sound level) for the
160–190-dB re 1 μPa (rms) radii. In the
2003 study, Tolstoy et al. (2004b)
reported that for the 20 airgun array, the
160 dB radius in shallow water was 33
percent higher than predicted (predicted
= 9 km (5.5 mi); measured = 12 km (7.4
mi)). According to Tolstoy et al. (2004b),
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the results indicated that reverberations
played a significant role in received
levels of sound in shallow water and
that previously estimated radii for 160
and 180 dB had not accounted for
bottom reverberations. Thus, the
predicted radii were underestimates of
the actual distances where the 160 and
180 dB levels occurred in shallow
water. The authors recommended that
L–DEO extend the radii by an
appropriate factor to account for this
underestimation. As a result, L–DEO
developed correction factors for water
depths 100 to1,000 m (328 to 3,281 ft)
and less than 100 m (328 ft).
For the TAIGER cruise, L–DEO has
applied conservative correction factors
to develop appropriate shallow-water
exclusion zones (see Table 1 in 72 FR
78294, December 22, 2008) to mitigate
effects on marine mammals. At this
time, this is the best available scientific
data for estimating seismic sound
propagation for the Langseth’s airgun
configuration. L–DEO has measured the
Langseth’s seismic source array, and has
stated that initial results, which do not
significantly vary from those stated
here, will be published in the future.
Comment 175: The problem that
permeates the EA and IHA documents
(and the Federal Register listing) is the
silly assumption that since nobody has
done this (impossible) task that there is
no reason to suspect that sending 170
dB pulses out for 7,808 m either side of
a boat traveling for 1,113 km through
the shallow water critical habitat of
several endangered species is wrong.
Response: To clarify, NMFS has
determined that safety zones should be
established at 180 dB (rms) for cetaceans
not, 170 dB (rms). The commenter is
referring to L–DEO’s predicted root
mean square (rms) distance for the
safety radius/exclusion zone at 170 dB
shown in Table 1 of the application (see
also Table 1 in 72 FR 78294, December
22, 2008). The predicted rms distance of
7,808 m (4.8 mi) is the most
precautionary distance which the 170
dB sound level is expected to be
received from the 36-airgun array in
shallow water.
L–DEO establishes and closely
monitors safety zones to ensure, to the
greatest extent practicable, that no
marine mammals would be injured by
the proposed activity. NMFS recognizes
that absence of evidence is not the same
as having no effect or impact on the
marine mammal species. However,
NMFS is not relying solely on absence
of evidence. All parties involved have
used the best information currently
available to analyze the impacts to
marine mammals as shown in: (1) The
Federal Register notice for the receipt of
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L–DEO’s application (73 FR 78294,
December 22, 2008); (2) the EA and SEA
for the TAIGER seismic; (3) the BiOp
and ITS; and (4) numerous and salient
public comments received by NMFS
during the public comment period.
Some of the new information used by
NMFS to make its determinations under
the MMPA are discussed and
summarized in this Federal Register
notice. Based on the evidence cited,
NMFS concludes that the proposed
seismic surveys would have a negligible
impact on the affected species or stocks
of marine mammals and are not likely
to jeopardize the continued existence of
any ESA-listed species.
Comment 176: The notice in the
Federal Register states in several places
that scientific information on marine
mammal species in the SE Asia survey
area is minimal or even non-existent. It
also notes that data on the impacts of
seismic airgun sounds on marine
mammals are minimal or lacking.
Nevertheless, the NMFS and L–DEO
inexplicably and without basis or
precaution conclude that the surveys
will have negligible impacts on marine
mammals. This is unacceptable.
Response: The NMFS recognizes that
absence of evidence is not the same as
having no effect or impact on the marine
mammal species. However, NMFS is not
relying solely on absence of evidence to
support its determinations. All parties
involved have used the best information
currently available to analyze the
impacts to marine mammals as shown
in: (1) The Federal Register notice for
the receipt of L–DEO’s application (73
FR 78294, December 22, 2008); (2) the
EA and SEA for the TAIGER seismic; (3)
the BiOp and ITS; and (4) numerous and
salient public comments received by
NMFS during the public comment
period. NMFS has incorporated new
information to make its determinations
under the MMPA are discussed and
summarized in this Federal Register
notice. Based on the evidence cited,
NMFS concludes that the proposed
seismic surveys would have a negligible
impact on the affected species or stocks
of marine mammals and are not likely
to jeopardize the continued existence of
any ESA-listed species.
Comment 177: The discussion of the
critically endangered Western Pacific
gray whale (Eschrichtius robustus) is
similarly problematic and does not
adequately consider that the surveys
will occur in waters presumed to
include the population’s breeding
grounds and migration pathways (which
are currently unknown but are placed
by expert opinion in the South China
Sea). Any resubmission of this
application must do a far better job of
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evaluating the region’s marine mammal
populations, especially those that are
critically endangered.
Response: Please see NMFS’
responses to comments under the
Species of Particular Concern section.
Because of concerns about effects of the
proposed survey lines on Western
Pacific gray whales, L–DEO has rerouted the survey lines in the South
China Sea, south of the Taiwan Strait.
The survey lines are now located in
water depths greater than 200 m.
Comment 178: The NMFS and L–DEO
also ignore the growing body of
literature addressing the possible
infliction of stress on animals, including
marine mammals, due to exposure to
noise and how this stress can have
significant impacts on individuals and
populations (e.g., Wright and Kuczaj,
2007). The discussion in the notice and
application (and no doubt the EA) still
relies overmuch on observable
behavioral reactions, when in fact
research (also not cited in the L–DEO
documentation) is available that
suggests already stressed animals or
animals in poor condition may not
observably react in the face of human
disturbance when more robust animals
will (e.g., Beale and Monaghan, 2004).
Any resubmission of this request for
authorization must expand and improve
its discussion of the relevant scientific
literature.
Response: The Beale and Monaghan
study investigated the effects of
disturbance on cliff-dwelling birds.
NMFS is aware of only two studies that
directly address the physiological stress
responses of marine mammals when
exposed to sound. Thomas et al. (1990)
examined behavioral responses of four
captive belugas (Delphinapterus leucas)
to playbacks of noise from SEDCO 708,
a semi-submersible drilling platform.
Results indicated no elevation in blood
epinephrine and norepinephrine levels
immediately after the playback. The
authors observed no differences in swim
patterns, social groupings, and
respiration/dive rates before and during
playbacks. In the second study, Romano
et al. (2004) investigated nervous system
activation and immune function in two
species of captive marine mammals after
exposure to a seismic water gun and/or
single pure tones and observed that
norepinephrine, epinephrine, and
dopamine levels increased with
increasing sound levels. However,
Wright et al. (2007) noted that
extrapolating these results to wild
species should proceed with caution
due to the study’s small sample sizes,
use of captive animals, and other
technical limitations with the baseline
measurements.
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L–DEO’s EA (see Chapter 3) provided
information on non-auditory
physiological effects (including stress)
in relation to seismic survey sounds in
the EA. However, few studies exist on
the quantification of a specific exposure
level above which non-auditory effects
can be expected. At present, NMFS is
unaware of quantitative predictions of
the numbers of marine mammals that
might exhibit stress when exposed to
seismic sounds. NMFS believes that
these data presented in the EA were the
best scientific information available for
estimating impacts on marine mammal
species and stocks. [Romano, T. A.,
Keogh, M. J., Kelly, C., Feng, P., Berk,
L., Schlundt, C. E., Carder, D. A. &
Finneran, J. J. (2004). Anthropogenic
sound and marine mammal health:
Measures of the nervous and immune
systems before and after intense sound
exposure. Canadian Journal of Fisheries
and Aquatic Sciences, 61, 1,124 to
1,134].
Comment 179: The assumption
(repeated several times in the Federal
Register notice) that animals will move
away from the approaching Langseth is
simply wishful thinking—there is no
evidence that this will occur for most
species and in some cases (again, e.g.,
ETS Sousa), this is not even an option,
as there is essentially nowhere for the
animals to move to that will allow them
to escape exposure to high levels of
seismic sound. These issues are all
discussed at greater length by other
parties submitting comments and we
urge the NMFS to require L–DEO to
address these concerns in any
resubmission of the application.
Response: Several studies have
reported observations of marine
mammals exhibiting localized
avoidance from areas with operating
seismic airgun arrays. L–DEO provides
this information in the Chapter 4 and
Appendix B of the EA. In the case of
critically endangered ETS population
and other coastal species, L–DEO and
TAIGER’s principal investigators have
modified the cruise plan and survey
design by re-routing the cruise’s
tracklines offshore Taiwan’s west coast
by approximately 20 km to protect the
ETS and the finless porpoise
populations (except for in the passage
between the Penghu Islands and the
Waishanding Jhou (Wau-san-ting Chou)
sandbar, where the survey will pass
through the approximately 17.1 km (9.2
nautical mi) mid-line distance between
the two possibly sensitive areas); rerouting the proposed survey lines in the
South China Sea south of the Taiwan
Strait to water depths greater than 200
m; and eliminating survey tracklines in
the western Taiwan Strait.
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Comment 180: The applicant and the
agency must improve their consultation
with regional experts on the protected
species in the region(s) of interest. Many
of the omissions and inaccuracies of the
application (and, quite frankly, much of
the local resistance to this proposed
research) could have been avoided if the
applicants had sought out and consulted
with regional scientific experts and
regional non-governmental
organizations (NGO) with relevant
expertise.
Response: The conditions of the IHA
encourage NSF and L–DEO to
coordinate with the Taiwanese
government regarding the proposed
seismic activity. In December 2008,
NMFS published notice of the proposed
IHA in the Federal Register. During the
public comment period, regional
scientific experts and regional NGOs
with relevant expertise were free to
provide comments on the survey. NMFS
considered these requests during the 30
day public comment period and
published a notice in the Federal
Register (74 FR 2995, January 16, 2009)
extending the public comment period
for the proposed IHA to facilitate
additional review by regional scientific
experts. If a regional expert or regional
NGO representative requests to consult
on the effects of the seismic survey on
protected species in the region, NMFS
encourages them to discuss this directly
with a representative from L–DEO or
NSF.
Finally, based on comments received
from the public, including regional
experts, L–DEO completed a
Supplemental EA for the TAIGER
survey. NMFS believes that the
monitoring and mitigation measures,
which have been enhanced when
compared to the proposed IHA notice,
ensure the least practicable adverse
impact on marine mammals in the SE
Asia study area.
Comment 181: According to the tables
within the EA, more Sousa will be
impacted than there actually are Sousa
in the area. I am unclear on how this
meets the ‘‘small number’’ criteria. This
number would, of course, go up further
if the distances reported by Madsen et
al. (2006—noted above) were taken into
account. Of course, these distances
would increase the take numbers for all
animals in the area.
Response: Since the issuance of the
proposed IHA notice, L–DEO negotiated
with the project’s principal scientists to
modify the cruise plan and adopt more
precautionary monitoring and
mitigation measures. Based on the rerouted tracklines, L–DEO has revised
estimates of the possible numbers of
ETS Indo-Pacific humpback dolphins
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exposed to sound levels that would
constitute Level B harassment to zero
(zero percent of the ETS subpopulation). NMFS took the revised
tracklines into account when making
the necessary MMPA determinations,
including small numbers, towards the
issuance of the IHA.
Comment 182: The Langseth will
deploy an 8 km long streamer for most
transects requiring a streamer; however,
a shorter streamer (500 m to 2 km) will
be used during surveys in Taiwan
(Formosa) Strait (EA2). Do the effective
source levels offered in the EA pertain
to the longer or shorted streamers?
Response: The effective source level
output from the Langseth’s airgun array
pertains to both the longer and shorter
streamers. Streamer lengths generally
relate to hydrophones, not airguns, and
changes are often due to convenience,
particularly to improve
maneuverability.
Comment 183: According to the EA,
the Multibeam Echosounder and Subbottom Profiler have outputs up to 204
dB re 1 μPa m, at the dominant
frequency of 3.5 kHz. This is perilously
close to the US Navy’s AN/SQS–53C
tactical mid-frequency sonar system
implicated in many of the mass
strandings of beaked whales and other
cetaceans, which produces ‘pings’
primarily in the 2.6 to 3.3 kHz range.
Another LDEO survey has been
associated with a stranding (as
acknowledged in the EA: ‘‘* * *
association of mass strandings of beaked
whales with naval exercises and, in one
case, an L–DEO seismic survey
(Malakoff, 2002)’’). There may thus also
be concern for beaked whales and other
animals, because, while ‘‘[t]here is no
conclusive evidence of cetacean
strandings or deaths at sea as a result of
exposure to seismic surveys’’ (EA), there
is also no conclusive evidence that
seismic surveys do not lead to
strandings or death either.
Response: The evidence linking
beaked whale strandings and seismic
surveys remains inconclusive at best. In
September, 2002, two Cuvier’s beaked
whales stranded in the Gulf of
California, Mexico. The Ewing had been
operating a 20-airgun, 8,490-in3 airgun
array 22 km offshore the general area at
the time that strandings occurred.
However, the link between the stranding
and the seismic surveys was
inconclusive and not based on any
physical evidence (Hogarth, 2002;
Yoder, 2002) as some vacationing
marine mammal researchers who
happened upon the stranding were illequipped to perform an adequate
necropsy. In addition, Cox et al. (2006)
noted the ‘‘lack of knowledge regarding
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41303
the temporal and spatial correlation
between the [stranding] and the sound
source.’’ Finally, Hildebrand (2005)
illustrated the approximate temporalspatial relationships between the
stranding and the Ewing’s tracks, but
noted that the time of the stranding was
not known with sufficient precision for
accurate determination of the closest
point of approach (CPA) distance of the
whales to the Ewing.
The MBES and SBP have anticipated
radii of influence significantly less than
that for the airgun array. For reasons
noted in the EA, the 160 dB and 180 dB
isopleths of the MBES and SBP are
either too small or the acoustic beams
are very narrow, making the duration of
the exposure and the potential for taking
marine mammals by harassment small
to non-existent. NMFS believes that it is
unlikely that marine mammals would be
affected by sub-bottom profiler signals
whether operating alone or in
conjunction with other acoustic devices
since the animals would need to be
swimming immediately adjacent to the
vessel or directly under the vessel.
Additionally, NMFS believes that the
MBES and SBP are not likely to be
capable of causing marine mammal
strandings because of their short
duration and brief pings
Comment 184: Several commenters
expressed that the impacts of masking
(including the physiological and
psychological consequences potentially
resulting from masking) were likely to
be greatest for baleen whales throughout
the survey area and requested that the
Langseth should avoid calving grounds
at breeding season, and feeding and
migratory habitat for several species of
threatened and endangered marine
mammals. Several expressed concern
for the range of the critically endangered
Eastern Taiwan Strait (ETS) population
of Indo-Pacific humpbacked dolphin;
the partial range of Jiulong River Estuary
(JRE) population of Indo-Pacific
humpbacked dolphin; calving and
migratory habitat for western Pacific
humpback whales; a migratory pathway
for the critically endangered western
Pacific gray whale; and beaked and
sperm whale habitat in southeastern and
southwestern Taiwan.
Response: Please see NMFS’
responses to comments under the
Species of Particular Concern section
and the response to Comment EA2
under this section. The IHA contains
measures to mitigate against the
potential effects of the surveys on
mother/calf pairs, ETS and JRE
humpbacked dolphins, and western
Pacific gray whales.
Comment 185: NMFS has determined
that the proposed activity ‘‘may result,
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at worst, in a temporary modification in
behavior (Level B harassment) of small
numbers of marine mammals’’ and
proposes to issue an IHA, which
demonstrates that either the reviewers
of the proposal lacked knowledge of SE
Asian marine mammals or chose to
ignore the potential damage such
seismic surveys can have on small and
critically endangered populations of
marine mammals in the region. With a
lack of knowledge about even the most
basic biology of marine mammals in the
region, any determination of the level of
impact of the seismic surveys would be
little more than a random guess.
Response: Please see NMFS response
to Comment EA2 (above) in this section.
Comment 186: The principal
investigators responded that the bulk of
the energy produced by the Langseth
sound source is below a frequency of
200 Hz. They also noted that
odontocetes communicate in a much
higher band of frequencies, typically in
the range of 10,000 Hz to several
100,000 Hz. Thus there is very little, if
any, overlap in the frequency bands of
acoustic energy used by these marine
mammals and that of the seismic
system. In summary, the investigators
agreed with the EA that the surveys
were not likely to result in any
significant impact on marine life in the
area.
Response: NMFS acknowledges the
comments from the principal
investigators.
Comment 187: NMFS is charged with
implementing the MMPA and, to that
end, must prescribe methods and means
of effecting the least practicable adverse
impact on marine mammals. NMFS’
proposed IHA falls short of the mark.
Response: Please see NMFS’ response
to comments (above) under this section.
In this IHA, NMFS prescribed
mitigation measures that achieve the
least practicable adverse impact, such
as: re-routing the cruises tracklines
further offshore by approximately 20 km
(10.8 nautical mi) to protect the
critically endangered Sousa population
and the finless porpoise (except for in
the passage between the Penghu Islands
and the Waishanding Jhou (Wau-santing Chou) sandbar, where the survey
will pass through the 17.1 km (9.2
nautical mi) mid-line distance between
the two possibly sensitive areas); visual
marine mammal monitoring, and shutdowns when marine mammals are
detected within the defined ranges
should further reduce short-term
reactions to disturbance, and minimize
any effects on hearing sensitivity. The
IHA includes mitigation and monitoring
measures to reduce the potential for
injury or mortality, as well as instituting
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immediate shutdown protocols for the
North Pacific right whale, western gray
whale, Indo-Pacific humpbacked
dolphin, or finless porpoise. No injury,
serious injury, or mortality of any
marine mammal is anticipated nor is
authorized.
Comment 188: Several other baleen
whales have been recorded from
Taiwanese waters. However, due to
almost no survey effort in the waters
beyond about 20 km from shore and
surveys being most in summer months,
little is known about these species,
which include: fin, sei, minke, Bryde’s
and Omura’s whales. There are reports
of several distinct stocks of some of
these species. As a minimum, the
impact on each stock of each species
should be assessed rather than just at
the species level and more work is
needed on understanding stock
structure before impacts can be
understood.
Response: Please see NMFS’ response
to comments above. Detailed analyses of
underwater noise, especially those from
airguns, and impacts to cetaceans, fish,
and invertebrates are provided in
various documents related to the
proposed project. NMFS’ review of
these documents have led to the
determination that the proposed seismic
surveys would have a negligible impact
on the affected species or stocks of
marine mammals and are not likely to
jeopardize the continued existence of
any ESA listed species.
Comment 189: Consideration of
cumulative noise impacts. The exposure
of these dolphins to total cumulative
noise has not been considered. The ETS
dolphins live in an environment which
is already very noisy (e.g., pile driving
and other noise-generating activities
during coastal construction, shipping,
other seismic surveys (oil and gas, local
researchers, etc.). The cumulative
impact of all noise sources needs to be
examined in context of the
contributions by the intense sounds
source of the airguns.
Response: Please NMFS’ response to
NEPA comments. NMFS has determined
that the EA adequately addressed the
cumulative impacts of a short-term, lowintensity seismic airgun survey in
relation to long-term noise and taking
events, such as vessel traffic, habitat
loss, oil and gas industry, pollution,
fisheries, and hunting. NMFS’
endangered species scientists have
conducted a thorough review of the best
available information on the cumulative
effects of the proposed project. As a
result, NMFS issued a BiOp on the
proposed action on March 31, 2009
(NMFS, 2009), which stated that the
survey was not likely to jeopardize the
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continued existence of ESA-listed
marine mammals in the survey area.
Comment 190: The blue whale is
given the highest level of legislative
protection by the Wildlife Conservation
Act of Taiwan. If small numbers of
western North Pacific blue whales still
exist, seismic surveys can have a large
impact on the few remaining
individuals.
Response: Please see NMFS’ response
to comments under the Species of
Particular Concern section. L–DEO’s
revised seismic survey is expected to
have a negligible impact on populations
of blue whales in the study area. Blue
whales can be easily detected visually
so that L–DEO may implement
appropriate mitigation measures.
Comment 191: The project description
does not adequately consider the
relevant scientific literature on risks of
seismic activities to cetaceans. Also, L–
DEO completely overlooked
physiological impacts on cetaceans (see
Wright et al., 2007a,b).
Response: L–DEO’s EA (see Chapter 3)
provided information on non-auditory
physiological effects (including stress)
in relation to seismic survey sounds in
the EA. However, few studies exist on
the quantification of a specific exposure
level above which non-auditory effects
can be expected. At present, NMFS is
unaware of quantitative predictions of
the numbers of marine mammals that
might exhibit stress when exposed to
seismic sounds. NMFS believes that
these data presented in the EA were the
best scientific information available for
estimating impacts on marine mammal
species and stocks.
All parties involved have used the
best information currently available to
analyze physiological impacts to marine
mammals as shown in: (1) The Federal
Register notice for the receipt of L–
DEO’s application (73 FR 78294,
December 22, 2008); (2) the EA and SEA
for the TAIGER seismic; (3) the BiOp
and ITS; and (4) numerous and salient
public comments received by NMFS
during the public comment period.
International Legal Compliance
Comment 192: L–DEO has stated that
it will ‘‘coordinate with Taiwan, China,
Japan, and the Philippines, as well as
applicable U.S. agencies (e.g., NMFS)
and will comply with their
requirements’’ (p. 78316). This is a
promise of action but there is no
indication in the Federal Register notice
how fulfillment of this promise will be
verified. HSI and other interested
parties state that before NMFS issues an
authorization, NMFS must verify that L–
DEO has complied with all relevant
laws and regulations of the countries
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within whose EEZs it will be
conducting surveys. NMFS must request
and receive the relevant paperwork from
the applicant, that L–DEO has a
minimum initiated and preferably
completed. It cannot take at face value
the assurances of L–DEO that such
compliance will occur. It is a longstanding concern of HSUS/HSI (and
other NGOs, both domestic and
international) that U.S. agencies issue
environmental permits and
authorizations for activities that will in
part be conducted within foreign
jurisdictions without first verifying that
the applicant has complied or even
initiated compliance with local laws
and regulations of these four nations.
Response: NMFS has communicated
with NSF and L–DEO regarding the
seismic survey in SE Asia. NMFS has
received copies of L–DEO’s foreign
clearances from Taiwan, Japan, and the
Philippines. L–DEO has been denied
access to the waters of China. NMFS
expects NSF and L–DEO to coordinate
with the governments of Taiwan, Japan,
and the Philippines, as well as adhere
to local conservation laws and
regulations of nations while in foreign
waters, and known rules and boundaries
of Marine Protected Areas (MPA),
regarding the marine geophysical
activity in SE Asia. In the absence of
local conservation laws and regulations
or MPA rules, L–DEO will continue to
use the monitoring and mitigation
measures identified in the IHA. NMFS
has included conditions to these effects
in the IHA. L–DEO is required to submit
a draft report on all activities and
monitoring results to the Office of
Protected Resources, NMFS, within 90
days of the completion of the Langseth’s
SE Asia cruise (see ‘‘Reporting’’ section
below).
Comment 193: HSI states that far too
often, applicants for MMPA Incidental
Harassment Authorizations, who are
working on geophysical and other
projects that do not directly concern
marine mammals, but result in their
incidental harassment and that will
occur at least partially within foreign
jurisdictions, fail to consult much or at
all with regional entities who can be
considered stakeholders in the decisions
to authorize such projects. The
authorizing agency compounds this
failing by accepting the applicant’s
assurances at face value that sufficient
consultation has occurred or will occur.
HSI strongly advises the NMFS (and
applicants such as L–DEO) to rectify
this problem in the future.
Response: NMFS acknowledges HSI’s
recommendation and expects applicants
to comply with all foreign and domestic
laws. NMFS encourages applicants to
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consult with all stakeholders regarding
projects in a specified region.
Recommendations for Consultation and
Research
Comment 194: Dr. McIntosh and Dr.
Wu state they have already contacted
marine biologists highly knowledgeable
and very concerned about the ecology of
all marine mammals in the National
Taiwan University, Academica Sinica
and the National Taiwan Ocean
University. They will continue to
provide guidance to the planning of the
TAIGER program.
Response: NMFS acknowledges the
principal investigators comment.
Comment 195: CSI states that in
December, 2008, for the ETSSTAWG (an
international working group established
in early 2008 to provide scientific
guidance and advice to all interest
groups) recommended that a buffer for
noise threats be out to at least 5 km from
shore for the ETS population after
reviewing a proposal for designation of
Majore Wildlife Habitat for the ETS
population (review letter to Wild At
Heart Legal Defense Association—dated
29 December, 2008).
Response: After issuance of the
proposed IHA, L–DEO negotiated with
the project’s principal scientists to
modify the cruise plan and adopt more
precautionary mitigation measures. Off
Taiwan’s west coast, the cruise tracks
have been re-routed offshore by
approximately 20 km to protect the
‘critically endangered’ ETS Indo-Pacific
humpback dolphin population and the
finless porpoise, as well as ease
potential pressure on other coastal
species. Thus, the precautionary buffer
recommended by ETSSTAWG in their
comments to NMFS, ‘‘at least 13 km and
perhaps a more precautionary 15 km of
the ETS Indo-Pacific humpback dolphin
subpopulation—meaning up to around
20 km from shore’’ will be adopted. L–
DEO will limit seismic survey lines to
take place at least 20 km from the west
coast of Taiwan, expect for in the
passage between the Penghu Islands and
the Waishanding Jhou (Wau-san-ting
Chou) sandbar, where the survey will
pass through the approximately 17.1 km
mid line distance between the two
possibly sensitive areas, subject to the
limitations imposed by other foreign
nations, to minimize the potential for
exposing the ETS sub-population and
other coastal species to SPLs greater
than or equal to 160 dB re 1 μPa (rms).
NMFS has included conditions to this
effect in the IHA as well.
Comment 196: CSI recommends that
activities that would increase the risk of
extinction of Sousa chinensis
populations, including physiological
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41305
and behavioral impacts, not be
permitted.
Response: NMFS disagrees with CSI’s
recommendations. NMFS believes that
L–DEO’s revised seismic survey as well
as the implementation of the required
monitoring and mitigation measures
will have a negligible impact on the
affected species or stocks of marine
mammals in the planned study area. L–
DEO will limit seismic survey lines to
water depths greater than 200 m in the
South China Sea, and as far east as
possible from the mainland China side
of the Taiwan Strait, to reduce potential
for effects on Western Pacific gray
whales, Indo-Pacific humpback
dolphins, and finless porpoises. L–DEO
will limit seismic survey lines to take
place at least 20 km from the west coast
of Taiwan, except for in the passage
between the Penghu Islands and the
Waishanding Jhou sandbar, where the
survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
1 μPa (rms).
Comment 197: Several interested
parties recommend dedicated marine
mammal systematic surveys in waters
off eastern Taiwan (particularly in
waters beyond 20 km from shore where
almost no cetacean survey effort exists)
and of the Penghu Channel to better
understand the region’s waters,
determine concentrations of beaked
whales, and reduce impacts on other
cetaceans. Systematic cetacean surveys
of the waters of these waters are needed
before seismic surveys are conducted so
that better planning with adequate
information can reduce impacts on
marine mammals. Better coverage of the
region’s waters by cetaceans surveys can
also allow fine turning of spatial and
temporal avoidance of humpback
whales by seismic surveys. Simple
strategic scheduling of seismic surveys
can eliminate or at least greatly reduce
the impacts on this population.
Response: In this case, NMFS does
not agree that marine mammal
assessment surveys are needed prior to
issuing an IHA. When information is
unavailable on a local marine mammal
population size, NMFS uses either stock
or species information on abundance.
Also, while information may be lacking
for many species of cetaceans,
information on some of the locallyfound species is found in the L–DEO’s
IHA application, EA, and Supplemental
EA. See L–DEO’s IHA application, EA,
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and Supplemental EA for more
information.
In order to reduce impacts on marine
mammals, NMFS has included temporal
and spatial avoidance requirements in
the IHA. See the information in the
Monitoring and Mitigation sections
below. Also, after the issuance of the
proposed IHA, L–DEO has revised the
planned seismic survey to reduce
potential impacts on marine mammal
populations in the study area.
Comment 198: Several interested
parties recommend greater local
consultation. Extensive consultation
with experts on these regions and more
studies to better understand the biology
of cetaceans in this region can provide
expert guidance to greatly reduce the
impacts on the seismic surveys. More
information exists in publications in
local languages that have not been
considered by this proposal. Conduct a
consultation workshop with scientists
who have expertise in local marine
mammals, reptiles, fish, and
invertebrates to understand better the
local sensitive species and waters.
Consultation with ETSSTAWG is
needed.
Response: L–DEO and NSF have
formally consulted with NMFS’ Permits,
Conservation, and Education Division
regarding the IHA and NMFS’
Endangered Species Division regarding
a Biological Opinion under Section 7 of
the ESA for the marine geophysical
survey in SE Asia. L–DEO and NSF have
also consulted with numerous persons
and organizations in the SE Asia region.
Below is a timeline of L–DEO’s
consultation process and issues
discussed:
• December 18, 2007—Initial
consultation began with LGL Ltd. when
Dr. John Richardson contacts Dr. John
Wang for a reprint. Dr. John Wang
expresses concerns about seismics and
mentions that the Indo-Pacific
humpback dolphin is being reviewed for
critically endangered status.
• August 9, 2008—Meike Holst of
LGL Limited contacts Dr. John Wang for
reprints. The L–DEO program is
discussed via e-mail.
• August 14, 2008—Dr. John Wang
copies Robin Winkler of WaH and asks
for details on the cruise.
• August 19, 2008—Meike Holst
shared details with Dr. John Wang and
consults with him further.
• August 20, 2008—Meike Holst
assures Robin Winkler of the planned
mitigation measures in place and asks
about relevant local laws.
• August 30, 2008—Chao-Shing Lee
referred Meagan Cummings of L–DEO to
Dr. Lien-Siang Chou. Meagan Cummings
e-mailed Dr. Lien-Siang Chou and
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informed her that she planned to send
copies of the EA when it became
available.
• September 19, 2008—Robin
Winkler responds to Meike Holst and
copies Dr. Peter Ross. Meike Holst never
hears back from Dr. Peter Ross.
• October 2, 2008—Hong Young, Prof.
K. T. Shao from the Center for
Biodiversity Research (Academica
Sinica), and Prof. F. C. Chiu, Director of
the Taiwan Ocean Research Institute are
contacted by Claudio Fossati, one of L–
DEO’s lead bioacousticians and MMOs.
• January 13, 2009—Dr. Randall
Reeves reviews the EA and recommends
contacting Dr. Lien-Siang Chou or
Benjamin Kahn based in Cairns,
Australia.
• January 19, 2009—Dr. Francis Wu
recommends Dr. Lien-Siang Chou.
https://ecology.lifescience.ntu.edu.tw/
english/faculty_chou_ls.htm.
• February 27, 2009—Meagan
Cummings contacts Dr. Peter Ross. Dr.
Peter Ross recommended an
independent review of the program.
Meagan Cummings assured him that
NMFS was the reviewing agency and
they wrote back and forth a few times
and was informed that there was a
regional expert.
• February 27, 2009 to present—L–
DEO has been consulting mainly with
Dr. Lien-Siang Chou and her
department’s graduate students. Meagan
Cummings met with Dr. Lien-Siang
Chou on March 21, 2009 in Taiwan. L–
DEO scheduled a workshop for March
27, 2009 to discuss mitigation measures
and visual sighting techniques for
finless porpoises.
• March 27, 2009—L–DEO met with
Dr. Lien-Siang Chou and her graduate
students at National Taiwan University.
The discussion points during the
meeting included: MMO operations
(Big-eye and 7x50 binoculars, visible
distances from the observation tower,
safety radii, ramp-up, power-down, and
shut-down explanations), the
Supplemental EA (revised tracklines,
proximity to Taiwan, the ETS IndoPacific humpback dolphins, finless
porpoises), possible carcass and
stranding procedures (stranding density
and locations during the past 10 years,
current protocols for live and dead
animals, reporting protocols and
notification of the Taiwan Cetacean
Society, funding to conduct necropsies,
investigate resources to process more
animals if there are a significant number
of strandings, possible MRI of smaller
cetaceans to look at possible effects of
sound or pressure, fewer recent
strandings than average, public concern
has dropped, Taiwan’s marine mammal
stranding response team, stranding
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teams divided up between the north and
south of Taiwan, discovery and
reporting of possible carcasses at sea,
and taking carcass samples for DNA
analysis), NMFS notification
requirements, finless porpoise sighting
techniques, current MMO protocols,
sampling considerations, regions of
concern, beaked whales in Taiwan,
population and density of Taiwanese
cetaceans, and addressing the media.
Comment 199: Recent estimates of
habitat boundaries and noise buffer
zones specifically for the ETS IndoPacific humpback dolphins are not
referred to yet could have easily been
acquired through consultation with the
ETSSTAWG. The existence of this
expert advisory team dedicated to ETS
humpback dolphin matters was brought
to the attention of one of the principal
preparers of the EA by the directors of
Wild at Heart Legal Defense Association
in an e-mail dated September 19, 2008.
Response: After the issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO will
maintain the precautionary buffer
recommended by ETSSTAWG in their
comments to NMFS, ‘‘at least 13 km and
perhaps a more precautionary 15 km of
the ETS Sousa population—meaning up
to around 20 km from shore.’’ L–DEO
will limit seismic survey lines to take
place at least 20 km from the west coast
of Taiwan, except for in the passage
between the Penghu Islands and the
Waishanding Jhou (Wau-san-ting Chou)
sandbar, where the survey will pass
through the approximately 17.1 km midline distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
1 μPa (rms). See relevant responses to
comment above for information on
consultation.
Comment 200: WaH states that in the
event that no attempt was made by LGL
to consult with the ETSSTAWG prior to
completion of the EA, WaH would
recommend that this is done
immediately with a view to clarifying
some of the concerns relating to
harassment of Indo-Pacific humpback
dolphins, and that similar consultations
be held with other experienced
researchers through the region in
question.
Response: During the preparation of
the IHA application and EA, LGL Ltd.
contacted and consulted with regional
experts. After the issuance of the
proposed IHA, L–DEO modified the
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cruise plan and adopted more
precautionary monitoring and
mitigation measures to address concerns
for species of particular concern (e.g.,
ETS sub-population of Indo-Pacific
humpback dolphins). L–DEO also
prepared a Supplemental EA. The
Supplemental EA is in response to the
comments received by NMFS through
the public comment period associated
with the IHA process. See relevant
discussions in this document as well as
L–DEO’s Supplemental EA.
Species of Particular Concern
Comment 201: NRDC states many
genetically distinct populations of
cetaceans are found within the enclosed
seas of the western Pacific, including
the ETS population of Indo-Pacific
humpbacked dolphin, South China Sea
population of finless porpoise, fin
whales, gray whales, and humpback
whales. Take estimates should use
abundance and density estimates for
these distinct populations (rather than
estimates for the entire North Pacific)
where appropriate.
Response: NMFS agrees that impacts
should be assessed on the population or
stock unit whenever possible. Due to the
lack of systematic aircraft- or ship-based
surveys conducted for marine mammals
in waters near Taiwan, the species of
marine mammals that occur there are
not well known. A few surveys have
been conducted from small vessels with
low observation platforms. In the
absence of any other density data, L–
DEO used the survey effort and
sightings in Yang et al. (1999) and Wang
et al. (2001a) to estimate densities of
marine mammals in the TAIGER study
area. L–DEO’s application provides
information on stock abundance and
local and regional populations. The data
source for each stock estimate is
provided in Table 2 of L–DEO’s IHA
application. There is some uncertainty
about the representatives of the density
data and the assumptions used in the
calculations. Perhaps the greatest
uncertainty results from using survey
results from the northeast Pacific Ocean.
NMFS believes that this approach and
these data are the best scientific
information available for estimating
impacts on marine mammal species and
stocks. However, information on marine
mammal stock abundance may not
always be complete. When information
is lacking to define a particular
population or stock of marine mammals
then impacts are assessed with respect
to the species as a whole (54 FR 40338,
September 29, 1989).
Comment 202: Dr. John Wang states
that for gray, right, and humpback
whales, some common issues arise from
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the seismic surveys. The timing of the
L–DEO surveys overlaps, spatially and
temporally, with whales wintering
(calving and nursing) in the region’s
waters (see above) and during the
northward migrations of mothers with
neonatal or other young calves from
these calving/nursing grounds.
Response: After issuance of the
proposed IHA, L–DEO revised their
seismic survey to include temporal and
spatial concerns regarding marine
mammals in the study area. Because of
concerns about effects of the proposed
survey lines on gray whales, the
proposed survey lines in the South
China Sea south of the Taiwan Strait
were re-routed so that they are now
located in water depths >200 m. To
mitigate against the potential effects of
the surveys on humpback whales,
particularly mothers and calves on the
breeding grounds or during the
beginning of migration to summer
feeding grounds, the surveys that
approach the Babuyan Islands have
been rescheduled as late as possible, to
Leg 4. Also, L–DEO will shut-down the
airgun array immediately if a Western
Pacific gray, North Pacific right, and/or
humpback whale mother/calf pair are
visually sighted at any distance.
Requirements to these effects have been
included in the NMFS-issued IHA. See
responses to comments pertaining to
Western Pacific gray and humpback
whales below.
Comment 203: CSI states that if small
numbers of Western North Pacific blue
whales still exist in the region’s waters,
seismic surveys can have a large impact
on the few remaining individuals (even
if only a very few whales are disturbed).
Response: After issuance of the
proposed IHA, L–DEO modified the
cruise plan and adopted more
precautionary monitoring and
mitigation measures. L–DEO’s revised
seismic survey is expected to have a
negligible impact on populations of blue
whales in the study area. Blue whales
can be easily detected visually so that
the proper mitigation measures may be
implemented.
Species of Particular Concern—Pearl
River Estuary (PRE), Jiulong River
Estuary (JRE), and Eastern Taiwan Strait
(ETS) Indo-Pacific Humpback Dolphins
Comment 204: Several interested
parties are concerned about the acoustic
disturbance that can seriously affect
several coastal populations of IndoPacific humpback dolphins, notably the
ones at the PRE in Guangdong Province,
the JRE in Fujian Province (near
Xiamen), and along the coastal waters of
the ETS. The JRE sub-population of
Indo-Pacific humpback dolphins is
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41307
estimated to be less than 90 individuals
(Chen et al., 2008) and faces similar
threats. The JRE sub-population is
distinct from the ETS sub-population
(Wang et al., 2008a), but the level of
exchange (if any) with other provisional
populations along the mainland Chinese
coast is unknown. Other Chinese subpopulations have been studied and have
a distribution in adjacent waters of the
Chinmen islands and further east are
completely unknown and were not
surveyed by Chen et al. (2008) due to
political border issues. Not enough is
known about this population to estimate
what proportion of dolphins in this
small sub-population will be impacted,
but it is clear that some will be
impacted and with such a small
population size, even minimal
disturbance can have a large impact on
the sub-population. Far less is known
about Sousa chinensis in other regions
so the impact on these dolphins cannot
be estimated. However, given the
proposed trackline which meets the
mainland Chinese coast perpendicularly
and closes near the area of Xiamen/
Chinmen Islands and near Pingtan
(where records of Sousa chinensis also
exist—see Wang, 1999; Zhou, 2004),
dolphins of these coastal waters would
be expected to be impacted.
The proposed tracklines of these
seismic surveys will traverse through
areas that will overlap or are in close
proximity to these resident humpback
dolphin populations, posing serious
risks and threats to the livelihood of
their daily lives. One of the Langseth’s
proposed tracklines approaches to the
mainland Chinese coast is directly in
line with the heart of the JRE
population. At a distance of 10 km from
shore, dolphins using waters east of the
Chinmen islands may be exposed to
levels greater than 160 dB and some
may be exposed to greater than 180 dB
depending on where the dolphins are
found in their distribution and how
close the Langseth is to the 25–30 m
isobath (which appears to be the depth
limit for the species—see Jefferson and
Karczmarski, 2001). Not enough is
known about this population to estimate
the numbers of dolphins that will be
impacted. Given such a small
population size, even minimal
disturbance can have a large impact on
the lives of the populations. The
animals may be exposed to received
levels >180 dB, which would exceed the
type of take which L–DEO has applied
for.
Response: Because of these concerns
about effects of the proposed surveys on
Western Pacific gray whales,
populations of Indo-Pacific humpback
dolphins, and finless porpoises, the
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proposed survey lines in the South
China Sea south of the Taiwan Strait
were re-routed after the issuance of the
proposed IHA so that they are now
located in water depths >200 m, as
recommended by NRDC. The seismic
lines in the western Taiwan Strait were
dropped. Requirements to these effects
have been included in the IHA and no
takes of any of the three sub-populations
of Indo-Pacific humpback dolphins
found in the SE Asia study area is
authorized for this seismic survey.
Comment 205: Several interested
parties have expressed concern with the
safety of the ETS Indo-Pacific humpback
dolphin. This ‘critically endangered’
sub-population is very small at <100
individuals. The distinct population is a
year-round resident of a very restricted
stretch of shallow coastal waters along
western Taiwan (i.e., the ETS). Any
single threat (e.g., loss of habitat,
pollution, bycatch, and noise) has the
potential to be the final cause of
extinction. Unless effective mitigation
measures are taken to reduce these
threats, it is unlikely that the population
will continue to exist. Mortality (by
human causes) of even a single
individual per year from this population
is not sustainable.
Seismic surveys in June and July (as
well as any other time of the year) will
have a serious impact on this critically
endangered population. Given their year
round residency, there is no season that
will reduce the serious impacts of
seismic surveys in inshore waters on
this population. In June and July, large
numbers of cetaceans are found along
and near the shelf edge of eastern
Taiwan. Conducting seismic surveys
close to the shores of Taiwan risks
greatly impacting on these cetaceans.
Response: After the issuance of the
proposed IHA, L–DEO negotiated with
the project’s principal scientists to
modify the cruise plan and adopt more
precautionary mitigation measures. Off
Taiwan’s west coast, the cruise tracks
have been re-routed offshore by
approximately 20 km to protect the
critically endangered ETS Indo-Pacific
humpback dolphins and the finless
porpoise, as well as ease potential
pressure on other coastal species. Thus,
the revised survey will maintain the
precautionary buffer recommended by
ETSSTAWG in their comments to
NMFS, ‘‘at least 13 km and perhaps a
more precautionary 15 km of the ETS
Sousa population—meaning up to
around 20 km from shore.’’ See L–DEO’s
Supplemental EA.
Concerns were expressed about the
survey line that was parallel to and
within a few km of the east coast of
Taiwan because of potential effects on
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coastal species and those that frequent
the shelf break and steep slopes, where
the continental shelf is narrow. Due to
these concerns, the survey line has been
moved offshore by more than 20 km to
decrease potential impacts on species
that occur there.
Requirements to these effects have
been included in the IHA. No injury,
serious injury, or mortality has been
authorized.
Comment 206: HSI states the
application and the Federal Register
notice never indicate that the Eastern
Taiwan Strait (ETS) population of the
Indo-Pacific humpback dolphin, Sousa
chinensis, is listed as ‘‘critically
endangered’’ on the International Union
for Conservation of Nature (IUCN) Red
List. Instead these two documents lump
the entire region’s Sousa populations
together. While the IUCN did list the
larger regional Sousa population as
‘‘near threatened,’’ it specifically
identified the ETS population as
separate and ‘‘critically endangered.’’
This designation was made well before
the December publication of the Federal
Register notice. The failure to note this,
to address the fact that two-thirds of this
population (the maximum proportion
the notice indicates could be taken—see
p. 78311) cannot be considered a ‘‘small
number,’’ or to address the fact that the
survey track lines cover the entire
length of this imperiled population’s
home range is unacceptable and must be
rectified by a resubmission of the
application.
Response: NMFS acknowledges HSI’s
comment. L–DEO’s Supplemental EA
states the ETS sub-population of IndoPacific humpback dolphins is
considered ‘critically endangered’ on
the IUCN Red List of Threatened
Species (IUCN, 2008). See L–DEO’s
Supplemental EA for a detailed
description of the revised survey as well
as monitoring and mitigation measures.
No takes of the ETS Indo-Pacific
humpback dolphin sub-population are
authorized under the NMFS-issued IHA.
See response to comment below.
Comment 207: Dr. John Wang and CSI
states that Sousa chinensis is considered
a slow swimming species with average
speeds between 3.6 and 7.2 km/hr
(Saayman and Tayler, 1979; Jefferson,
2000) but much slower during resting
periods (Saayman and Tayler, 1979)—
observations of the ETS population
(unpublished data) are consistent. As
such, the ETS Indo-Pacific humpback
dolphins will not be able to outrun the
Langseth (even while towing airguns,
the operating speed is reported to be
between 7.4–9.3 km/hr) for extended
periods. Even if they were able to
outrun the Langseth, there would be no
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escape within their distribution
because: (a) The tracklines cover nearly
the entire longitudinal length of the ETS
sub-population’s total distribution and
beyond, and (b) no safe acoustic shelters
exist. Therefore, nearly the entire
population (especially the most
vulnerable members: mothers with
young calves and other compromised
individuals) will be affected by the
seismic surveys along western Taiwan
regardless of where the dolphins are in
their distribution and an unknown but
substantial number will be exposed to
levels >180dB. Clearly, the proportion
of the ETS sub-population to be
impacted by the seismic survey (and at
dangerous exposure levels) is far too
high for any cetaceans let alone one that
is critically endangered.
Response: After issuance of the
proposed IHA, L–DEO has negotiated
with the project’s principal scientists to
modify the cruise plan and adopt more
precautionary mitigation measures. L–
DEO will limit seismic survey lines to
take place at least 20 km from the west
coast of Taiwan, except for in the
passage between the Penghu Islands and
the Waishanding Jhou sandbar, where
the survey will pass through the
approximately 17.1 km mid-line
distance between the two possibly
sensitive areas, subject to the limitations
imposed by other foreign nations, to
minimize the potential for exposing
Indo-Pacific humpback dolphins, finless
porpoises, and other coastal species to
SPLs greater than or equal to 160 dB re
1 μPa (rms). The buffer zone will reduce
the potential impacts to animals,
especially to protect the ‘critically
endangered’ ETS Indo-Pacific
humpback dolphin sub-population.
Requirements to this effect have been
included in the NMFS-issued IHA.
Comment 208: Dr. McIntosh and Dr.
Wu state that a specific concern
expressed by Dr. John Wang is with the
safety of the ETS Indo-Pacific humpback
dolphin; this species is considered
critically endangered. The principal
scientists share Dr. Wang’s desire to
protect this species and plan to avoid
seismic work in or near its habitat. This
species is known to live in very shallow
water environments, primarily in water
depths less than 25 meters and typically
close to the coast. Dr. McIntosh and Dr.
Wu expect seismic operations to occur
generally in water depths of 50 m or
greater, especially along Taiwan’s west
coast. With the generally shallow slope
of the seafloor in this area this means
that our work will typically be farther
than 10 km from the coast. Furthermore,
we are willing to adjust line positions to
provide an adequate buffer zone for the
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coastal habitat of these humpback
dolphins.
Response: NMFS acknowledges the
principal investigators comments. A
description of the revised seismic
survey can be found in L–DEO’s
Supplemental EA.
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Species of Particular Concern—Deep
Diving Species
Comment 209: ETTSTAWG states
beaked whales can be expected to be at
heightened risk from the L–DEO project,
in part because their extended dives
make it exceedingly difficult for even
trained personnel to spot them.
Response: NMFS agrees that beaked
whales are difficult to detect visually,
even by trained and experienced
MMVOs. In order to minimize potential
effects of the seismic surveys, L–DEO
will (when operating the sound source),
minimize approaches to slopes,
submarine canyons, seamounts, an other
underwater geologic features, if
possible, because of sensitivity to
beaked whales. If concentrations of
beaked whales are observed (by visual
or passive acoustic detection) at a site
such as on the continental slope,
submarine canyon, seamount, or other
underwater geologic feature just prior to
or during the airgun operations, those
operations will be moved to another
location along the site based on
recommendations by the on-duty
MMVO aboard the Langseth. After the
issuance of the proposed IHA, L–DEO
also re-routed the seismic survey line
paralleling the east coast of Taiwan
further offshore to decrease potential
impacts on species (including beaked
whales) over the continental slope, and
seismic surveys (to the maximum extent
practicable) will be conducted from the
coast (inshore) and proceed towards the
sea (offshore) in order to avoid trapping
marine mammals in shallow water.
NMFS believes these mitigation
measures should lessen the potential
risks to beaked whales.
Species of Particular Concern—Finless
Porpoises
Comment 210: Several interested
parties have stated that finless porpoises
are arguably one of the most difficult
species to detect at sea by observers,
even in calm conditions, because of its
small size, lack of dorsal fin, brief
surface time, and usually occurring
individually or in small groups, so
many will be missed by MMVOs during
seismic operations. Depending on the
behavior of the animals, they can be
near impossible to detect. Jefferson et al.
(2002) reported that during calm
sighting conditions, finless porpoises
were observed primarily within 300 m
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from the trackline (perpendicular
distance) and none were observed
beyond about 700 m. In low light
conditions or even slight seas, detecting
finless porpoises is challenging even for
researchers experienced with the
species. MMVOs will be ineffective at
detecting animals within the predicted
distance, therefore, an unknown
(potentially large) number of finless
porpoises will be exposed to much
greater noise levels than suggested by L–
DEO (especially since detection is
effectively zero beyond 1 km, yet the
predicted distance for received levels
>190 dB is more than 2 km from the
source).
Response: NMFS agrees that finless
porpoises are arguably one of the most
difficult species to detect at sea by
observers. NMFS has not authorized any
takes of finless porpoises in the IHA
issued to L–DEO for this survey. Take
estimates for finless porpoises have
been reduced to zero because of the
elimination of seismic tracklines in
shallow water areas where they are
likely to occur. In addition to having
additional MMVOs and the use of PAM
onboard the Langseth to detect animals,
L–DEO will also shut-down
immediately if there is a sighting at any
distance of finless porpoises. See
responses to previous comments and L–
DEO’s Supplemental EA.
Comment 211: Dr. John Wang states
finless porpoises are arguably the most
difficult cetacean to detect at sea by
observers, so many will be missed by
MMVOs during seismic operations.
Therefore, an unknown (potentially
large) number of finless porpoises will
be exposed to much greater noise levels
than suggested by L–DEO (especially
since detection is effectively zero
beyond 1 km, yet the predicted distance
for received levels >190 dB is more than
2 km from the source.
Response: NMFS agrees that finless
porpoises are arguably the most difficult
cetacean to detect by MMVOs due to
their small body size, lack of a dorsal
fin, and shy behavior. However, the
PAM system onboard the Langseth is
capable of detecting the clicks of finless
porpoises. Finless porpoises are
unlikely to be encountered during the
survey as L–DEO will avoid shallow
water areas near the China coast,
western Taiwan Strait, and South China
Sea in order to avoid this species. L–
DEO will also limit seismic survey lines
to water depths greater than 200 m (656
ft) in the South China Sea and as far east
as possible from the mainland side of
the Taiwan Strait, to reduce potential
for effects on finless porpoises. L–DEO
is not authorized incidental take of
finless porpoise and will shut-down the
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41309
airgun array if any finless porpoises are
visually sighted.
Comment 212: Dr. John Wang states
finless porpoises appear to go undergo
inshore-offshore migrations seasonally
(see Jefferson and Hung, 2004) but this
is not well understood. During the
timing of the proposed seismic surveys,
many finless porpoises will be in the
Taiwan Strait (as evidenced by bycatch
records and some sighting data—J.Y.
Wang, unpublished data) and an
unknown (but potentially large) number
will be exposed to the airgun sounds.
Furthermore, the timing also coincides
with the presence of many female with
newborn calves in these waters. These
will be the most vulnerable individuals
as they will be less able to escape the
wide range of the airguns in shallow
waters. The potential impact on finless
porpoises is far from negligible and
none of the mitigation measures
proposed would be effective in reducing
the harm.
Response: After issuance of the
proposed IHA, L–DEO has negotiated
with the project’s principal scientists to
modify the cruise plan and adopt more
precautionary monitoring and
mitigation measures. Off Taiwan’s west
coast, the cruise tracks have been rerouted offshore by approximately 20 km
to protect finless porpoise. Because of
concerns about effects of the proposed
surveys on finless porpoises, the
proposed survey lines in the South
China Sea south of the Taiwan Strait
were also re-routed so that they are now
located in water depths >200 m, as
recommended by NRDC. The seismic
lines in the western Taiwan Strait have
been dropped. The proposed survey line
paralleling the east coast of Taiwan has
also been moved offshore by more than
20 km to decrease potential impacts on
species that occur in coastal waters and
over the continental slope. The airgun
array will be shut-down immediately if
there is a sighting at any distance of
finless porpoises. Requirements to this
effect have been included in the IHA.
Comment 213: CSI and WaH states the
anticipated presence of female finless
porpoises and their (neonatal) calves in
the survey region during the proposed
seismic surveys is of great concern,
particularly given the fact that these
animals will likely be difficult if not
completely impossible to detect visually
at distances at which they may still be
exposed to noise levels >180 dB (rms),
and do not vocalize at all times. These
will be the most vulnerable individuals
as they will be less able to maintain
swimming speeds that will allow them
to escape the range of the airguns.
Finless porpoises are generally slowswimmers, but are capable of high speed
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bursts. However it is unlikely that such
speeds can be maintained for more than
a few minutes.
Response: See responses to previous
comments pertaining to finless
porpoises.
Species of Particular Concern—Western
Pacific Gray Whales
Comment 214: CSI states the route(s)
and months when Western Pacific gray
whales may undertake their migration
from a suspected wintering ground(s) in
the South China Sea are unknown.
However, it is likely that the period for
the migration is in the spring. The
proposed L–DEO surveys overlap with
the period during which these gray
whales are expected to be either in their
wintering grounds or are undergoing
their northward migration through the
Taiwan Strait. Scheduling the seismic
surveys in the South China Sea to be
conducted in March and April will
likely coincide with at least some
migrating gray whales, and are an
additional threat to these highly
threatened gray whales. L–DEO did not
address this possibility and have not
proposed any mitigation measures to
avoid this likely overlap of seismic
surveys and migrating gray whales.
Even the take of a few individuals is
projected to cause a continuing decline
in the population towards extinction
(Cooke et al., 2006).
Response: Winter breeding grounds of
the Western Pacific gray whale are not
known, but are thought to be located in
the South China Sea, along the coast of
Guangdong province and Hainan (Wang,
1984; and Zhu, 1998 in Weller et al.,
2002a; Rice, 1998). Also, the migration
route of the gray whale is ill defined,
but very likely extends through
Taiwanese waters, probably through the
Taiwan Strait. Their occurrence there is
possible from December to April. If
migration timing is similar to that of the
better-known Eastern Pacific gray whale
through similar latitudes, southbound
migration probably occurs mainly in
December to January, and northbound
migration mainly in February to April,
with northbound migration of newborn
calves and their mothers probably
concentrated toward the end of that
period. Even during migration, gray
whales are found primarily in shallow
coastal waters. Because of these
concerns about the effects of the
proposed surveys on gray whales, the
proposed survey lines in the South
China Sea south of the Taiwan Strait
were re-routed after the issuance of the
proposed IHA so that they are now
located in water depths >200 m, as
recommended by NRDC. The seismic
lines in the western Taiwan Strait have
VerDate Nov<24>2008
17:44 Aug 13, 2009
Jkt 217001
been dropped. L–DEO will also
immediately shut-down the airgun array
if there is a sighting of a Western Pacific
gray whale at any distance (see L–DEO’s
Supplemental EA).
Comment 215: In its discussion of
disturbance reactions, HSI also notes the
proposed IHA’s Federal Register notice
(73 FR 78294, December 22, 2008) use
of the Eastern Pacific gray whale’s status
as an example of a species experiencing
‘‘no impact’’ despite living in a noisy
environment. The notice states that the
whales ‘‘continued to migrate annually
* * * with substantial increases in the
population over recent years, despite
intermittent seismic exploration and
much ship traffic’’ (73 FR 78302,
December 22, 2008). However, the
notice ignores the drastic drop in
Eastern Pacific gray whale numbers
between 1998 and 2000, by perhaps as
many as 9,000 animals (Angliss and
Outlaw, 2007). While it is certainly
debatable to what (if any) degree
exposure to various noise sources
contributed to this population’s decline,
to ignore the decline when using the
population as an example of a
population’s increase in the face of
exposure to various noise sources is
simply bad science.
Response: As a coastal population, the
Eastern North Pacific stock of gray
whales, are subject to a wide variety of
direct and indirect anthropogenic effects
off of Mexico, California, Oregon,
Washington, Canada, and Alaska. Some
of the effects include pollution from
chemical contaminants, subsistence
harvesting, fishery interactions, ship
strikes, and potentially impacts from
noise. The population size of the
Eastern North Pacific gray whale stock
has been increasing over the past several
decades. Due to the steady increases in
population abundance, this stock of gray
whales was removed from the List of
Endangered and Threatened Wildlife in
1994, as it was no longer considered
Endangered or Threatened under the
ESA.
The decline in Eastern Pacific gray
whale numbers between 1998 and 2000
may be an indication that the
abundance was responding to
environmental limitations as the
population approaches the carrying
capacity of its environment. Visibly
emaciated whales (LeBoeuf et al., 2000;
Moore et al., 2001) suggest a decline in
food resources associated with
unusually high sea temperatures in 1997
(Minobe, 2002), which may factor in to
the high mortality rates observed in
1999 and 2000 (Gulland et al., 2005).
Several factors since this mortality event
suggest that the high mortality rate was
a short-term acute event and not a
PO 00000
Frm 00052
Fmt 4701
Sfmt 4703
chronic situation or trend: (1) Counts of
stranded dead gray whales dropped to
levels below those seen prior to this
event, (2) in 2001 living whales no
longer appeared to be emaciated, and (3)
calf counts in 2001–2002, a year after
the event ended, were similar to
averages for previous years (NMFS,
2007; Rugh et al., 2005). It is expected
that a population close to or at the
carrying capacity of the environment
will be more susceptible to fluctuations
in the environment (Moore et al., 2001),
and assessments indicated that the
population is likely close to or above its
unexploited equilibrium level (IWC,
2002). It can be predicted that the
population will undergo fluctuations in
the future that may be similar to the 2year event that occurred in 1999–2000
(Norman et al., 2000; Perez-Cortes et al.,
2000; Brownell et al., 2001; Gulland et
al., 2005).
Species of Particular Concern—
Humpback Whales
Comment 216: CSI states the schedule
for surveying the Luzon Strait and the
Philippine Sea overlaps completely
with the period when humpback whales
are still in the area (and includes the
latter portion of the peak period (April)
for humpback whale concentrations in
the Babuyan Islands). Therefore it is
unclear how the timing of the surveys
reduces the impacts on humpback
whales as claimed by L–DEO. A large
portion of this population of humpback
whales will also be migrating through
the Philippine Sea to northern waters at
the same time as the proposed surveys.
Although the exact migratory routes of
most humpback whales are unknown, it
is clear that at least some will follow a
path that is parallel and fairly close to
the shores of eastern Taiwan. One of the
proposed survey tracklines of the
Langseth also follows this course. Many
females undertaking the migration at
this time will also be accompanied by
neonatal calves and these are the most
sensitive individuals of the population
(McCauley et al., 2000).
Response: Several commenters raised
concerns about survey lines scheduled
for Leg 2 (April 20 to June 7, 2009)
approaching humpback whale breeding
areas in the Babuyan and Ryuku Islands.
In fact, the humpback whales that
winter and calve in the Ryuku Islands
are near Okinawa (Nishiwaki, 1959;
Rice, 1989; Darling and Mori, 1993),
some 400 km north of the most
northerly survey. However, a small
population of humpback whales does
winter and calve in the Babuyan Islands
in Luzon Strait (Acebes and Lesaca,
2003; Acebes et al., 2007). The whales
may arrive in the area as early as
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November and leave in May or even
June, with peak occurrence during
February through March or April
(Acebes et al., 2007).
To mitigate against the potential
effects of the surveys on humpback
whales, particularly mothers and calves
on the breeding grounds or during the
beginning of migration to summer
feeding grounds, the surveys that
approach the Babuyan Islands have
been rescheduled as late as possible, to
Leg 4 (June 18 to July 20, 2009). L–DEO
will also be required to shut-down
immediately if there is a visual sighting
at any distance for mother/calf pairs of
humpback whales.
Description of Marine Mammals in the
Proposed Activity Area
A total of 34 cetacean species,
including 25 odontocete (dolphins and
small- and large-toothed whales) species
and 9 mysticetes (baleen whales) are
known to occur in the proposed
TAIGER study area (see Table 2 of L–
DEO’s application). Cetaceans and
pinnipeds are managed by NMFS and
are the subject of this IHA application.
Information on the occurrence,
distribution, population size, and
conservation status for each of the 34
marine mammal species that may occur
in the proposed project area is presented
in the Table 2 of L–DEO’s application as
well as here in the table below (Table 2).
The status of these species is based on
the U.S. Endangered Species Act (ESA),
the International Union for
Conservation of Nature (IUCN) Red List
of Threatened Species, and Convention
on International Trade in Endangered
Species (CITES). Several species are
listed as Endangered under the ESA,
including the Western North Pacific
gray, North Pacific right, sperm,
humpback, fin, sei, and blue whales,
and the dugong (Dugong dugon). In
addition, the Indo-Pacific humpback
dolphin is listed as Near Threatened
and the finless porpoise is listed as
Vulnerable under the 2008 IUCN Red
List of Threatened Species (IUCN,
2008).
Although the dugong may have
inhabited waters off Taiwan, it is no
longer thought to occur there (March et
al., n.d.; Chou, 2004; Perrin et al., 2005).
Similarly, although the dugong was
once widespread through the
Philippines, current data suggest that it
does not inhabit the Batan or Babuyan
Islands or northwestern Luzon (Marsh et
al., n.d.; Perrin et al., 2005), where
seismic operations will occur. However,
the dugong does occur off northeastern
Luzon (Marsh et al., n.d.; Perrin et al.,
2005) outside the study area. In China,
it is only known to inhabit the waters
off Guangxi and Guangdong and the
west coast of Hanain Island (Marsh et
al., n.d.; Perrin et al., 2005), which do
not occur near the study area. It is rare
in the Ryuku Islands, but can be sighted
in Okinawa, particularly off the east
coast of the island (Yoshida and Trono,
2004; Shirakihara et al., 2007); some
individuals may have previously
occurred in the southernmost of the
Ryuku Islands, Yaeyama (Marsh et al.,
n.d.), but these animals have not been
documented there recently (Shirakihara
et al., 2007). The dugong is managed
under the jurisdiction of the U.S. Fish
and Wildlife Service (USFWS). The
USFWS concurred with L–DEO’s
determination that the survey is likely
to have no effects on the species and no
consultation under Section 7 of the ESA
is required, therefore, it is not
considered further in this analysis.
Wang et al. (2001a) noted that during
the spring/summer off southern Taiwan,
the highest number of marine mammal
sightings and species occur during April
and June. The number of sightings per
survey effort and the number of species
were highest directly west of the
southern tip of Taiwan and northeast off
the southern tip.
Table 2 (below) outlines the cetacean
species, their habitat and abundance in
the proposed project area, and the
requested take levels. Additional
information regarding the distribution of
these species expected to be found in
the project area and how the estimated
densities were calculated was included
in the notice of the proposed IHA (73 FR
78294, December 22, 2008) and may be
found in L–DEO’s application.
The occurrence, habitat, regional
abundance, conservation status, best
and maximum density estimates,
number of marine mammals that could
be exposed to sound level at or above
160dB re 1μPa, best estimate of number
of individuals exposed, and best
estimate of number of exposures per
marine mammal in or near the proposed
seismic survey area in SE Asia. See
Tables 2–4 in L–DEO’s application for
further detail.
TABLE 2
mstockstill on DSKH9S0YB1PROD with NOTICES2
Species
Mysticetes
Western Pacific gray whale
(Eschrichtius robustus).
North Pacific right whale
(Eubalaena japonica).
Humpback whale
(Megaptera
novaeangliae).
Minke whale (Balaenoptera
acutorostrata).
Bryde’s whale
Balaenoptera brydei).
Omura’s whale
(Balaenoptera omurai).
Sei whale (Balaenoptera
borealis).
Fin whale (Balaenoptera
physalus).
VerDate Nov<24>2008
17:44 Aug 13, 2009
Number of
indiv.
exposed to
≥ 160 dB
Percent of
estimated
population
exposed to
≥ 160 dB
0
0
0
0
0
0
0
938–1107 f ......
0.89
1.33
6
0.60
25,000 g ...........
0.03
0.04
0
0
20,000–
30,000 e h.
N.A. .................
0.27
0.41
43
0.17
0.03
0.04
4
N.A.
7,260–12,620 i
0.03
0.04
4
0.04
13,620–18,680 j
0.03
0.04
4
0.03
Occurrence in
study area in
SE Asia
Habitat
Regional
population size
Rare ................
Coastal ...........
131 d ................
0
Rare ................
Pelagic and
coastal.
Mainly near
shore waters
and banks.
Pelagic and
coastal.
Pelagic and
coastal.
Pelagic and
coastal.
Primarily offshore, pelagic.
Continental
slope, mostly
pelagic.
Less than 100 e
Uncommon .....
Uncommon .....
Common .........
Common? .......
Rare ................
Rare ................
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Density/
1000km b
(best)
Density/
1000km c
(max)
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TABLE 2—Continued
Species
Blue whale (Balaenoptera
musculus).
Odontocetes:
Sperm whale (Physeter
macrocephalus).
Occurrence in
study area in
SE Asia
Rare ................
Pelagic and
coastal.
N.A. .................
0.03
0.04
4
N.A.
Common? .......
Usually pelagic
and deep
seas.
Deep waters ...
26,674 k ...........
0.03
0.04
4
0.01
N.A. .................
0
0
....................
N.A.
11,200 e ...........
4.25
6.68
703
6.28
Common? .......
Likely Common
Deep waters
off shelf.
Deep waters ...
Pelagic ............
N.A. .................
20,000 e ...........
0.26
0.34
0.40
0.75
38
58
N.A.
0.29
Rare ................
Deep water .....
N.A. .................
N.A.
N.A.
....................
N.A.
Uncommon? ...
Pelagic ............
25,300 l ...........
0.89
1.60
153
0.61
Rare ................
Pelagic ............
N.A. .................
N.A.
N.A.
....................
N.A.
Uncommon? ...
Pelagic ............
N.A. .................
1.55
1.60
268
N.A.
Rare ................
Common .........
Pelagic ............
Deep water .....
N.A. .................
146,000 ETP e
0.72
1.33
0.94
5.44
118
212
N.A.
0.14
Uncommon .....
Coastal ...........
24.30
35.36
0
0
Common .........
Coastal and
oceanic,
shelf break.
Coastal and
shelf waters.
Coastal and
pelagic.
1,680 China +
Taiwan e.
243,500 ETP e
24.30
35.36
4,021
1.65
N.A. .................
43.60
65.40
0
N.A.
N.A.
N.A.
0
0
Uncommon .....
Indo-Pacific bottlenose dolphin (Tursiops aduncus).
Pacific white-sided dolphin
(Lagenorhynchus
obliquidens).
Pantropical spotted dolphin
(Stenella attenuata).
Spinner dolphin (Stenella
longirostris).
Striped dolphin (Stenella
coeruleoalba).
Fraser’s dolphin
(Lagenodelphis hosei).
Short-beaked common dolphin (Delphinus delphis).
Common? .......
mstockstill on DSKH9S0YB1PROD with NOTICES2
False killer whale
(Pseudorca crassidens).
Killer whale (Orcinus orca)
Short-finned pilot whale
(Globicephala
macrorhynchus).
Finless porpoise
(Neophocaena
phocaenoides).
Sirenians:
VerDate Nov<24>2008
20:00 Aug 13, 2009
Percent of
estimated
population
exposed to
≥ 160 dB
Habitat
Pygmy sperm whale
(Kogia breviceps).
Dwarf sperm whale (Kogia
sima).
Kogia sp. (unidentified) .....
Cuvier’s beaked whale
(Ziphius cavirostris).
Longman’s beaked whale
(Indopacetus pacificus).
Blainville’s beaked whale
(Mesoplodon
densirostris).
Ginkgo-toothed beaked
whale (Mesoplodon
ginkgodens).
Mesoplodon sp. (unidentified).
Unidentified beaked whale
Rough-toothed dolphin
(Steno bredanensis).
Indo-Pacific humpback dolphin (Sousa chinensis).
Common bottlenose dolphin (Tursiops truncatus).
Long-beaked common dolphin (Delphinus
capensis).
Risso’s dolphin (Grampus
griseus).
Melon-headed whale
(Peponocephala electra).
Pygmy killer whale (Feresa
attenuata).
Number of
indiv.
exposed to
≥ 160 dB
Density/
1000km c
(max)
Density/
1000km b
(best)
Regional
population size
Common? .......
Rare, Likely
Absent.
930,000–
990,000 e.
800,000 ETP e
120.80
140.97
20,169
2.52
800,000 ETP e
54.84
88.89
9,485
1.19
1,000,000
ETP e.
289,000 ETP e
0.20
0.32
38
0.01
96.84
124.14
16,749
5.80
3,000,000
ETP e.
N.A.
N.A.
0
0
Uncommon .....
Coastal and
pelagic.
Coastal and
pelagic.
Coastal and
pelagic.
Waters greater
than 1,000 m.
Shelf and pelagic,
seamounts.
Coastal ...........
N.A. .................
0.05
0.12
10
N.A.
Common .........
Pelagic ............
175,000 ETP e
41.88
67.18
7,209
4.12
Common? .......
Oceanic ...........
45,000 ETP e ..
13.37
20.86
2,173
4.83
Uncommon .....
Deep,
pantropical
waters.
Pelagic ............
39,000 ETP e ..
2.01
3.16
327
0.84
40,000 n ...........
4.56
4.77
789
1.97
Widely distributed.
Mostly pelagic,
relief topography.
Coastal ...........
8,500 ETP e ....
1.00
1.73
166
1.95
500,000 ETP e
3.83
6.43
630
0.13
5,220–10,220
Japan + HK e.
4.36
6.54
0
0
Common .........
Common .........
Common .........
Common .........
Rare ................
Common? .......
Uncommon? ...
Common? .......
Common? .......
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TABLE 2—Continued
Species
Dugong (Dugong dugon) ..
Occurrence in
study area in
SE Asia
Habitat
Regional
population size
Uncommon? ...
Coastal ...........
Density/
1000km b
(best)
N.A. .................
N.A.
Density/
1000km c
(max)
N.A.
Number of
indiv.
exposed to
≥ 160 dB
Percent of
estimated
population
exposed to
≥ 160 dB
N.A.
N.A.
N.A.—Data not available or species status was not assessed, ETP—Eastern Tropical Pacific, HK = Hong Kong.
a U.S. Endangered Species Act: EN = Endangered, T = Threatened, NL = Not listed.
b Best estimate as listed in Table 3 of the application.
c Maximum estimate as listed in Table 3 of the application.
d Vladimirov et al. (2008).
e North Pacific unless otherwise indicated (Jefferson et al., 2008).
f Western North Pacific (Calambokidis et al., 2008).
g Northwest Pacific and Okhotsk Sea (IWC, 2007a).
h Kitakado et al. (2008).
i Tillman (1977).
j Ohsumi and Wada (1974).
k Western North Pacific (Whitehead, 2002b).
l ETP; all Mesoplodon spp. (Wade and Gerrodette, 1993).
m IUCN states that this species should be re-assessed following taxonomic classification of the two forms. The chinensis-type would be considered vulnerable (IUCN, 2008).
n ETP (Wade and Gerrodette, 1993).
Potential Effects on Marine Mammals
mstockstill on DSKH9S0YB1PROD with NOTICES2
Potential Effects of Airguns
The sounds from airguns might result
in one or more of the following:
tolerance, masking of natural sounds,
behavioral disturbances, temporary or
permanent hearing impairment, and
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). With the possible exception of
some cases of temporary threshold shift
in harbor seals, it is unlikely that the
project would result in any cases of
temporary or especially permanent
hearing impairment, or any significant
non-auditory physical or physiological
effects. Some behavioral disturbance is
expected, but this would be localized
and short-term.
The notice of the proposed IHA (73
FR 78294, December 22, 2008) included
a discussion of the effects of sounds
from airguns on mysticetes,
odontocetes, and pinnipeds, including
tolerance, masking, behavioral
disturbance, hearing impairment, and
other non-auditory physical effects.
Additional information on the
behavioral reactions (or lack thereof) by
all types of marine mammals to seismic
vessels can be found in L–DEO’s
application and associated EA.
The notice of the proposed IHA also
included a discussion of the potential
effects of the multibeam echosounder
(MBES) and the sub-bottom profiler
(SBP). Because of the shape of the
beams of these sources and their power,
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17:44 Aug 13, 2009
Jkt 217001
NMFS believes it unlikely that marine
mammals will be exposed to either the
MBES or the SBP at levels at or above
those likely to cause harassment.
Further, NMFS believes that the brief
exposure of cetaceans to a few signals
from the multi-beam bathymetric sonar
system is not likely to result in the
harassment of marine mammals.
Estimated Take by Incidental
Harassment
The notice of the proposed IHA (73
FR 78294, December 22, 2008) included
an in-depth 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
L–DEO’s application. A summary is
included here.
All anticipated ‘‘takes by harassment’’
authorized by this IHA are Level B
harassment only, involving temporary
changes in behavior. The mitigation
measures are expected to minimize the
possibility of injurious takes. Take
calculations were based on maximum
exposure estimates (based on maximum
density estimates) vs. best estimates and
are based on the 160 dB isopleths of a
larger array of airguns. Given these
considerations, the predicted number of
marine mammals that might be exposed
to sounds 160 dB or greater may be
somewhat overestimated.
No systematic aircraft- or ship-based
surveys have been conducted for marine
mammals in waters near Taiwan, and
the species of marine mammals that
occur there are not well known. A few
surveys have been conducted from
small vessels (approximately 10–12 m
or 33–40 ft long) with low observation
PO 00000
Frm 00055
Fmt 4701
Sfmt 4703
platforms (approximately 3 m or 10 ft
above sea level) as follows:
• Off the east central coast of Taiwan
to a maximum of approximately 20 km
(12.4 mi) from shore in water depths up
to approximately 1,200 m deep between
June 1996 and July 1997 (all cetacean;
Yang et al., 1999);
• Off the south coast of Taiwan to a
distance of approximately 50 km (mi)
and depths greater than 1,000 m (3,280
ft) during April 13–September 9, 2000
(all cetaceans; Wang et al., 2001a);
• Off the west coast of Taiwan close
to shore during early April–early
August, 2002–2006 (Indo-Pacific
humpback dolphins; Wang et al., 2007);
and
• Around and between the Babuyan
Islands off northern Philippines in
waters less than 1,000 m deep during
late February-May 2000–2003
(humpback whales; Acebes et al., 2007).
The only density calculated by the
authors was for the Indo-Pacific
humpback dolphin (Wang et al., 2007).
In addition, a density estimate was also
available for the Indo-Pacific bottlenose
dolphin (Yang et al., 2000 in Perrin et
al., 2005).
In the absence of any other density
data, L–DEO used the survey effort and
sightings in Yang et al. (1999) and Wang
et al. (2001a) to estimate densities of
marine mammals in the TAIGER study
area. To correct for detection bias (bias
associated with diminishing sightability
with increasing lateral distance from the
trackline), L–DEO used mean group
sizes given by or calculated from Wang
et al. (2001a, 2007) and Yang et al.,
(1999), and a value for ƒ(0) of 5.32
calculated from the data and density
equation in Wang et al. (2007); Yang et
al. (1999), and Wang et al. (2001a) did
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not give a value for ƒ(0), but they used
a vessel and methods similar to those of
Wang et al. (2007). To correct for
availability and perception bias, which
are attributable to the less than 100
percent probability of sighting an
animals present along the survey
trackline, L–DEO used g(0) values
calculated using surfacing and dive data
from Erickson (1976), Barlow and
Sexton (1996), Forney and Barlow
(1998), and Barlow (1999): 0.154 for
Mesoplodon sp., 0.102 for Cuvier’s
beaked whale, 0.193 for the dwarf sperm
whale and Kogia sp., 0.238 for the killer
whale, and 1.0 for delphinids.
The surveys of Yang et al. (1999) and
Wang et al. (2001a) were carried out in
areas of steep slopes and complex
bathymetric features, where many
cetacean species are known to
concentrate. It did not seem reasonable
to extrapolate those densities to the
overall survey area, which is
predominantly in areas of deep water
without complex bathymetry. For latter
areas, L–DEO used density data from
two 5° x 5° blocks in the eastern tropical
Pacific Ocean (ETP) surveyed by
Ferguson and Barlow (2001): Blocks 87
and 882, bounded by 20° N to 25° N (the
same latitudes as the proposed survey
area and 115° W to 125° W, in deep
water and just offshore from Mexico. L–
DEO then calculated an overall estimate
weighted by the estimated lengths of
seismic lines over complex bathymetry
or slope (approximately 1,200 km or 746
mi) and over deep, flat, or gently sloping
bottom (approximately 12,934 km or
8,037 mi).
The density estimate for the IndoPacific hump-backed dolphin is from
Wang et al. (2007) and applies only to
the population’s limited range on the
west coat of Taiwan. No density data
were available for the Pacific whitesided or short-beaked common dolphin
for the study area. As these species are
rare in the area, densities are expected
to be near zero. In addition, density data
were unavailable for striped and longbeaked common dolphins. As these two
species were not seen during the abovementioned surveys and are considered
uncommon in the TAIGER study area,
L–DEO assigned these two species 10
percent of the density estimate of the
delphinid occurring in similar habitat in
the area with the lowest density (i.e.,
pygmy killer whale). Also no density
estimate was available for finless
porpoise. As this species was not
sighted during surveys of southern
Taiwan in 2000 (Wang et al., 2001a), L–
DEO assigned it 10 percent of the lowest
density (i.e., Indo-Pacific bottlenose
dolphin). Density data were unavailable
for Longman’s beaked and ginkgo-
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Jkt 217001
toothed beaked whales; however, these
two species are represented by densities
for unidentified beaked whales.
Large whales were not sighted during
the surveys by Yang et al. (1999) or
Wang et al. (2001a). The only available
abundance estimate for large whales in
the area (except that for humpbacks, see
below) is that of Shimada et al. (2008),
who estimated abundances of Bryde’s
whales in several blocks in the
northwestern Pacific based on surveys
in 1998–2002, the closest of which to
the proceed survey area is the block
bounded by 10° N–25° N and 130° E–
137.5° E. The resulting abundance and
area were used to calculate density.
Sperm, sei, Omura’s, fin, minke, and
blue whales are less common than
Bryde’s whales in these waters, so L–
DEO assigned a density of 10 percent of
that calculated for Bryde’s whale. North
Pacific right, and Western Pacific gray
whales are unlikely to occur in the
TAIGER study area, thus, densities were
estimated to be zero.
For humpback whales in the Babuyan
Islands, L–DEO used the population
estimate of Acebes et al. (2007) and
applied it to an area of approximately
78,000 km2, extending from the north
coast of Luzon to just south of Orchid
Island to derive a density estimate. That
area is a historically well-documented
breeding ground that whaling records
indicate was used until at least the
1960s (Acebes et al., 2007), and an area
where humpbacks have been sighted
more recently.
There is some uncertainty about the
representatives of the density data and
the assumptions used in the
calculations. For example, the timing of
the surveys of Indo-Pacific humpback
dolphins (early April-early August) and
humpback whales (late February–May)
overlaps the timing of the proposed
surveys, but the Bryde’s whale surveys
(August and September), and those of
Yang et al. (1999) (year-round) include
different seasons, and would not be as
representative if there are seasonal
density differences. Perhaps the greatest
uncertainty results from using survey
results from the northeast Pacific Ocean.
However, the approach used here is
believed to be the best available
approach. Also, to provide some
allowance for these uncertainties,
‘‘maximum estimates’’ as well as ‘‘best
estimates’’ of the densities present and
numbers of marine mammals potentially
affected have been derived. Best
estimates for most species are based on
average densities from the surveys of
Yang et al. (1999), Wang et al. (2001a),
and Ferguson and Barlow (2001),
weighted by effort, whereas maximum
estimates are based on the higher of the
PO 00000
Frm 00056
Fmt 4701
Sfmt 4703
two densities from the Taiwan surveys
and the eastern Pacific survey blocks.
For the sperm whales, mysticetes, two
delphinids (Indo-Pacific humpback and
Indo-Pacific bottlenose dolphins), as
well as for the finless porpoise, the
maximum estimates are the best
estimates multiplied by 1.5. Densities
calculated or estimated as described
above are given in Table 3 of L–DEO’s
application.
The estimated numbers of individuals
potentially exposed on each leg of the
survey are based on the 160 dB re 1 μPa
(rms) Level B harassment exposure
threshold for cetaceans and pinnipeds.
It is assumed that marine mammals
exposed to airgun sounds at these levels
might experience disruption of
behavioral patterns.
It should be noted that the following
estimates of takes by harassment assume
that the surveys will be fully completed.
As is typical during offshore ship
surveys, inclement weather and
equipment malfunctions are likely to
cause delays and may limit the number
of useful line-km to seismic operations
that can be undertaken. Furthermore,
any marine mammal sightings within or
near the designated EZ will result in the
power-down or shut-down of seismic
operations as a mitigation measure.
Thus, the following estimates of the
numbers of marine mammals exposed to
160 dB sounds probably overestimate
the actual numbers of marine mammals
that might be involved. These estimates
assume that there will be no weather,
equipment, or mitigation delays, which
is highly unlikely.
The number of different individuals
that may be exposed to airgun sounds
with received levels ≥160 dB re 1 μPa
(rms) on one or more occasions was
estimated by considering the total
marine area that would be within the
160 dB radius around the operating
airgun array on at least one occasion.
The number of possible exposures
(including repeated exposures of the
same individuals) can be estimated by
considering the total marine area that
would be within the 160 dB radius
around the operating airguns, including
areas of overlap. The seismic lines are
widely spaced in the survey area, and
are further spaced in time because the
survey is planned in discrete legs
separated by several days. Thus, an
individual mammal would not be
exposed numerous times during the
survey; the areas including overlap are
1.1 to 1.3 times the areas excluding
overlap, depending on the leg, so the
numbers of exposures are not discussed
further. Moreover, it is unlikely that a
particular animal would stay in the area
during the entire survey.
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The number of different individuals
potentially exposed to received levels
≥160 dB re 1 μPa (rms) was calculated
by multiplying:
• The expected species density, either
‘‘mean’’ (i.e., best estimate) or
‘‘maximum,’’ times
• The anticipated minimum area to
be ensonified to that level during airgun
operations excluding overlap.
The area expected to be ensonified
was determined by entering the planned
survey lines into a MapInfo Geographic
Information System (GIS), using the GIS
to identify the relevant areas by
‘‘drawing’’ the applicable 160 dB buffer
around each seismic line (depending on
water and tow depth) and then
calculating the total area within the
buffers. Areas where overlap occurred
were limited and included only once to
determine the area expected to be
ensonified when estimating the number
of individuals exposed.
Applying the approach described
above and in L–DEO’s Supplemental
EA, approximately 160,132 km2 (61,827
mi2), which is approximately 5 percent
less than the original 168,315 km2,
would be within the 160 dB isopleth on
one or more occasions during the
survey. Because this approach does not
allow for turnover in the mammal
populations in the study area during the
course of the survey, the actual number
of individuals exposed could be
underestimated. However, the approach
assumes that no cetaceans will move
away from or toward the trackline as the
Langseth approaches in response to
increasing sound levels prior to the time
the levels reach 160 dB, which will
result in overestimates for those species
known to avoid seismic vessels.
Table 3 (see below) outlines the
species, estimated stock population
(minimum and best), and estimated
percentage of the stock exposed to
seismic pulses in the project area.
Additional information regarding the
status, abundance, and distribution of
the marine mammals in the area and
how densities were calculated was
included in Table 2 (see above), the
notice of the proposed IHA (73 FR
78294, December 22, 2008) and may be
found in L–DEO’s application.
The estimates of the possible numbers
of marine mammals exposed to sound
levels greater than or equal to 160 dB
during L–DEO’s proposed seismic
survey in SE Asia in March–July 2009.
The proposed sound source consists of
a 36-airgun, 6,600 in3 array. 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 2–4 in L–DEO’s application for
further detail.
TABLE 3
mstockstill on DSKH9S0YB1PROD with NOTICES2
Mysticetes:
Western Pacific gray whale ..................................................................................................
(Eschrichtius robustus) .........................................................................................................
North Pacific right whale ......................................................................................................
(Eubalaena japonica) ............................................................................................................
Humpback whale ..................................................................................................................
(Megaptera novaeangliae) ....................................................................................................
Minke whale ..........................................................................................................................
(Balaenoptera acutorostrata) ................................................................................................
Bryde’s whale .......................................................................................................................
(Balaenoptera brydei) ...........................................................................................................
Omura’s whale ......................................................................................................................
(Balaenoptera omurai) ..........................................................................................................
Sei whale ..............................................................................................................................
(Balaenoptera borealis) ........................................................................................................
Fin whale ..............................................................................................................................
(Balaenoptera physalus) .......................................................................................................
Blue whale ............................................................................................................................
(Balaenoptera musculus) ......................................................................................................
Odontocetes:
Sperm whale .........................................................................................................................
(Physeter macrocephalus) ....................................................................................................
Pygmy sperm whale .............................................................................................................
(Kogia breviceps) ..................................................................................................................
Dwarf sperm whale ...............................................................................................................
(Kogia sima) .........................................................................................................................
Kogia sp. ...............................................................................................................................
(unidentified) .........................................................................................................................
Cuvier’s beaked whale .........................................................................................................
(Ziphius cavirostris) ..............................................................................................................
Longman’s beaked whale .....................................................................................................
(Indopacetus pacificus) .........................................................................................................
Blainville’s beaked whale .....................................................................................................
(Mesoplodon densirostris) ....................................................................................................
Ginkgo-toothed beaked whale ..............................................................................................
(Mesoplodon ginkgodens) ....................................................................................................
Mesoplodon sp. ....................................................................................................................
(unidentified) 3 .......................................................................................................................
Unidentified beaked whale 4 .................................................................................................
Rough-toothed dolphin .........................................................................................................
(Steno bredanensis) .............................................................................................................
VerDate Nov<24>2008
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Jkt 217001
PO 00000
Number of
individuals
exposed
(max)1
Number of
individuals
exposed
(best)1
Species
Frm 00057
Fmt 4701
Sfmt 4703
Approx. percent regional
population
(best) 2
0
0
0
0
0
0
6
9
0.60
0
0
0
43
65
0.17
4
6
N.A.
4
6
0.04
4
6
0.03
4
6
N.A.
4
6
0.01
........................
........................
N.A.
703
1,124
6.28
38
58
N.A.
58
131
0.29
........................
........................
N.A.
153
276
0.61
........................
........................
N.A.
268
118
276
155
1.06
N.A.
212
865
0.14
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TABLE 3—Continued
Number of
individuals
exposed
(best)1
Species
Indo-Pacific humpback dolphin ............................................................................................
(Sousa chinensis) .................................................................................................................
Common bottlenose dolphin .................................................................................................
(Tursiops truncatus) ..............................................................................................................
Indo-Pacific bottlenose dolphin ............................................................................................
(Tursiops aduncus) ...............................................................................................................
Pacific white-sided dolphin ...................................................................................................
(Lagenorhynchus obliquidens) .............................................................................................
Pantropical spotted dolphin ..................................................................................................
(Stenella attenuata) ..............................................................................................................
Spinner dolphin .....................................................................................................................
(Stenella longirostris) ............................................................................................................
Striped dolphin ......................................................................................................................
(Stenella coeruleoalba) .........................................................................................................
Fraser’s dolphin ....................................................................................................................
(Lagenodelphis hosei) ..........................................................................................................
Short-beaked common dolphin ............................................................................................
(Delphinus delphis) ...............................................................................................................
Long-beaked common dolphin .............................................................................................
(Delphinus capensis) ............................................................................................................
Risso’s dolphin .....................................................................................................................
(Grampus griseus) ................................................................................................................
Melon-headed whale ............................................................................................................
(Peponocephala electra) ......................................................................................................
Pygmy killer whale ................................................................................................................
(Feresa attenuata) ................................................................................................................
False killer whale ..................................................................................................................
(Pseudorca crassidens) ........................................................................................................
Killer whale ...........................................................................................................................
(Orcinus orca) .......................................................................................................................
Short-finned pilot whale ........................................................................................................
(Globicephala macrorhynchus) .............................................................................................
Finless porpoise ...................................................................................................................
(Neophocaena phocaenoides) .............................................................................................
Sirenians
Dugong .................................................................................................................................
(Dugong dugon) ....................................................................................................................
Approx. percent regional
population
(best) 2
Number of
individuals
exposed
(max)1
0
0
0
4,021
5,886
1.65
0
0
N.A.
0
0
0
20,169
23,646
2.52
9,485
15,373
1.19
38
60
0.01
16,749
21,470
5.80
0
0
0
10
23
0.01
7,209
11,478
4.12
2,173
3,424
4.83
327
520
789
789
825
1.97
171
297
2.01
630
1,069
0.13
0
0
0
........................
........................
N.A.
mstockstill on DSKH9S0YB1PROD with NOTICES2
N.A.—Data not available or species status was not assessed.
1 Best estimate and maximum estimate density are from Table 3 of L–DEO’s application. There will be no seismic acquisition data during Leg 3
of the survey; this, it is not included here in this table.
2 Regional population size estimates are from Table 2.
3 Requested takes include Blainville’s, and ginkgo-toothed beaked whales.
4 Requested takes include Cuvier’s, Blainville’s, ginkgo-toothed, and Longman’s beaked whales.
Table 1 of L–DEO’s Supplemental EA
shows the best and maximum estimates
of the number of exposures and the
number of individual marine mammals
that potentially could be exposed to
greater than or equal to 160 dB re 1 μPa
(rms) during the different legs of the
seismic survey if no animals moved
away from the survey vessel.
The ‘‘best estimate’’ of the number of
individual marine mammals that could
be exposed to seismic sounds with
received levels greater than or equal to
160 dB re 1 μPa (rms) (but below Level
A harassment thresholds) during the
survey is shown in Table 1 of L–DEO’s
Supplemental EA and Table 3 (shown
above). The ‘‘best estimate’’ total
includes 65 baleen whale individuals,
25 of which are listed as Endangered
under the ESA: 6 humpback whales
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Jkt 217001
(0.60 percent of the regional
population), 4 sei whales (0.04 percent),
4 fin whales (0.03 percent), and 4 blue
whales (regional population unknown).
These estimates were derived from the
best density estimates calculated for
these species in the area (see Table 1 of
L–DEO’s Supplemental EA). In addition,
4 sperm whales (0.01 percent of the
regional population), as well as 0 IndoPacific humpback dolphins (0 percent
population, and 0 percent of the eastern
Taiwan Strait (ETC) population), 0
finless porpoise (0 percent), and 597
beaked whales (including Longman’s
and ginkgo-toothed beaked whales) are
included in the ‘‘best estimate’’ total.
Most (97.8 percent) of the cetaceans
potentially exposed are delphinids;
pantropical spotted, Fraser’s, and
spinner dolphins are estimated to be the
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Frm 00058
Fmt 4701
Sfmt 4703
most common species in the area, with
best estimates of 20,169 (2.52 percent of
the regional population), 16,749 (5.80
percent), and 9,485 (1.19 percent)
individuals exposed to greater or equal
to 160 dB re μPa (rms) respectively.
Potential Effects on 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 (73 FR 78294, December
22, 2008). 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
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mammals or their populations or stocks.
Similarly, any effects to food sources are
expected to be negligible.
The L–DEO seismic survey 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
proposed activity will be temporarily
elevated noise levels and the associated
direct effects on marine mammals, as
described above. The following sections
briefly review effects of airguns on fish
and invertebrates, and more details are
included in L–DEO’s application and
EA, respectively.
Subsistence Activities
There is no legal subsistence hunting
for marine mammals in the waters of
Taiwan, China, or the Philippines, so
the proposed activities will not have
any impact on the availability of the
species or stocks for subsistence users.
Today, Japan still hunts whales and
dolphins for ‘‘scientific’’ purposes. Up
until 1990, a drive fishery of false killer
whales occurred in the Penghu Islands,
Taiwan, where dozens of whales were
taken. Although killing and capturing of
cetaceans has been prohibited in
Taiwan since August 1990 under the
Wildlife Conservation Law (Zhou et al.,
1995; Chou, 2004), illegal harpooning
still occurs (Perrin et al., 2005). Until
the 1990’s, there was a significant hunt
of around 200 to 300 dolphins annually
in the Philippines. Catches included
dwarf sperm, melon-headed, and shortfinned pilot whales, as well as
bottlenose, spinner, Fraser’s, and Risso’s
dolphins (Rudolph and Smeenk, 2002).
Reports also indicate that perhaps 5
Bryde’s whales were caught annually
(Rudolph and Smeenk, 2002), although
the last Bryde’s whales were caught in
1996 (Reeves, 2002). Successive bans on
the harvesting of whales and dolphins
were issued by the Philippine
Government during the 1990’s.
mstockstill on DSKH9S0YB1PROD with NOTICES2
Mitigation and Monitoring
Mitigation and monitoring measures
for the seismic survey have been
developed and refined during previous
L–DEO seismic studies and associated
environmental assessments (EAs), IHA
applications, and IHAs. The mitigation
and monitoring measures described
herein represent a combination of
procedures required by past IHAs for
other similar projects and on
recommended best practices in
Richardson et al. (1995), Pierson et al.
(1998), and Weir and Dolman (2007).
The measures are described in detail
below.
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Mitigation measures that will be
adopted during the TAIGER survey
include:
(1) Speed or course alteration,
provided that doing so will not
compromise operational safety
requirements;
(2) Power-down procedures;
(3) Shut-down procedures;
(4) Ramp-up procedures;
(5) Temporal and spatial avoidance of
sensitive species and areas, provided
that doing so will not compromise
operational safety requirements (see
‘‘temporal and spatial avoidance,’’
below);
(6) Special procedures for situations
or species of particular concern, e.g.,
emergency shutdown procedures if a
North Pacific right whale, Western
Pacific gray whale, humpback whale
mother/calf pairs, Indo-Pacific
humpback and bottlenose dolphins, and
finless porpoise are sighted from any
distance (see ‘‘shut-down procedures’’
and ‘‘special procedures for species of
particular concern’’ below); and
minimization of approaches to slopes
and submarine canyons, if possible,
because of sensitivity for beaked whales;
and
(7) Additional mitigation measures
(see ‘‘additional mitigation measures’’
below). The thresholds for estimating
take are also used in connection with
mitigation.
Vessel-Based Visual Monitoring
Vessel-based Marine Mammal Visual
Observers (MMVOs) will be based
aboard the seismic source vessel and
will watch for marine mammals near the
vessel during daytime airgun operations
and during start-ups of airguns at night.
MMVOs will also watch for marine
mammals near the seismic vessel for at
least 30 minutes prior to the start of
airgun operations and after an extended
shutdown of the airguns (i.e., 8
minutes). When feasible, MMVOs will
also make observations during daytime
periods when the seismic system is not
operating for comparison of sighting
rates and animal behavior with vs.
without airgun operations. Based on
MMVO observations, the airguns will be
powered-down, or if necessary, shutdown completely (see below), when
marine mammals are detected within or
about to enter a designated EZ. The
MMVOs will continue to maintain
watch to determine when the animal(s)
are outside the safety radius, and airgun
operations will not resume until the
animal has left that zone. The predicted
distances for the safety radius are listed
according to the sound source, water
depth, and received isopleths in
Table 1.
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Sfmt 4703
41317
During seismic operations in SE Asia,
at least four MMOs and one
bioacoustician will be based aboard the
Langseth (five total MMOs). MMVOs
will be appointed by L–DEO with NMFS
concurrence. At least two MMVOs
(except during meal times) will monitor
the EZ from the observation tower for
marine mammals during ongoing
daytime operations and nighttime
startups of the airguns. Three MMOs are
typically on watch at a time, two on the
observation tower conducting and the
third monitoring the PAM equipment.
Use of two simultaneous MMVOs and
one bioacoustician will increase the
effectiveness of detecting animals near
the sound source. MMVOs typically
visually observe for one to three hours,
and MMVOs will be on duty in shifts of
duration no longer than three hours.
MMOs and/or the lead bioacoustician
will monitor the PAM equipment at all
times in shifts of one to six hours. L–
DEO has employed a regional expert as
at least one of the MMOs, and has
negotiated with experts from National
Taiwan University, Academia Sinica,
and the National Taiwan Ocean
University. L–DEO is carrying an
additional MMO (six total MMOs), who
is a Taiwan regional expert from Dr.
Lien-Siang Chou’s team, during Leg 2 of
the seismic survey (and during Leg 4 as
well). The vessel crew will also be
instructed to assist in detecting marine
mammals and implementing mitigation
measures (if practical). Before the start
of the seismic survey the crew was
given additional instruction regarding
how to do so.
The Langseth is a suitable platform for
marine mammal observations. When
stationed on the observation platform,
the eye level will be approximately 18
m (58 ft) above sea level, and the
observer will have a good view around
the entire vessel. During the daytime,
the MMVO(s) will scan the area around
the vessel systematically with reticle
binoculars (e.g., 7x50 Fujinon), Big-eye
binoculars (25x150), and with the naked
eye to avoid eye fatigue. During
darkness, night vision devices will be
available (ITT F500 Series Generation 3
binocular-image intensifier or
equivalent), when required. Laser
rangefinding binoculars (Leica LRF 1200
laser rangefinder or equivalent) will be
available to assist with distance
estimation. Those are useful in training
MMVOs to estimate distances visually,
but are generally not useful in
measuring distances to animals directly;
that is done primarily with the reticles
on the binocular’s lenses.
Speed or Course Alteration—If a
marine mammal is detected outside the
safety radius and based on its position
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and the relative motion, is likely to
enter the EZ, the vessel’s speed and/or
direct course may be changed. This
would be done if practicable while
minimizing the effect on the planned
science objectives. The activities and
movements of the marine mammal(s)
(relative to the seismic vessel) will then
be closely monitored to determine
whether the animal(s) is approaching
the applicable EZ. If the animal appears
likely to enter the EZ, further mitigative
actions will be taken, i.e., either further
course alterations or a power-down or
shut-down of the airguns. Typically,
during seismic operations, major course
and speed adjustments are often
impractical when towing long seismic
streamers and large source arrays, thus
alternative mitigation measures (see
below) will need to be implemented.
Power-down Procedures—A powerdown involves reducing the number of
airguns in use such that the radius of
the 180 dB or 190 dB zone is 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
will be operated. The continued
operation of one airgun is intended to
alert marine mammals to the presence of
the seismic vessel in the area. 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 it,
and if the vessel’s speed and/or course
cannot be changed to avoid the
animal(s) entering the EZ, the airguns
will be powered down 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.
During a power-down of the airgun
array, the 40 in3 airgun will be operated.
If a marine mammal is detected within
or near the smaller EZ around that
single airgun (see Table 1 of L–DEO’s
application and Table 1 above), all
airguns will be shut down (see next
subsection).
Following a power-down, airgun
activity 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 of species
with shorter dive durations—small
odontocetes and pinnipeds; or
(3) Has not been seen within the EZ
for 30 minutes in the case of species
with longer dive durations—mysticetes
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and large odontocetes, including sperm,
pygmy sperm, dwarf sperm, killer, and
beaked 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 airgun(s) will be shut down if
a marine mammal is detected within or
approaching the EZ for a single airgun
source. Shut-downs will be
implemented (1) if an animal enters the
EZ of the single airgun after a powerdown 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 MMVO is
confident that the animal has left the
vicinity of the vessel. Criteria for
judging that the animal has cleared the
EZ will be as described in the preceding
subsection.
Considering the conservation status
for North Pacific right whales and
Western Pacific gray whales, and IndoPacific humpback dolphins, the
airgun(s) will be shut-down
immediately if either of these species
are observed, regardless of the distance
from the Langseth. Due to additional
concerns, shut-downs will also occur for
visual sightings of humpback whale
mother/calf pair, Indo-Pacific bottlenose
dolphins and/or finless porpoises.
Ramp-up will only begin 30 min after
the last documented whale visual
sighting, and 15 min after the last
documented dolphin/porpoise sighting.
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 has
exceeded that period. It is proposed
that, for the present cruise, this period
would be approximately 8 minutes. This
period is based on the largest modeled
180 dB radius for the 36-airgun array
(see Table 1 of L–DEO’s application and
Table 1 here) in relation to the planned
speed of the Langseth while shooting.
Similar periods (approximately 7–10
minutes) were used during previous L–
DEO surveys.
Ramp-up will begin with the smallest
airgun in the array (40 in3). 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 35 minutes. During
ramp-up, the MMVOs will monitor the
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EZ, and if marine mammals are sighted,
a course/speed change, power-down, or
shut-down will be implemented as
though the full array were operational.
If the complete 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 (40 in3 or
similar) has been operating during the
interruption of seismic survey
operations. Given these provisions, it is
likely that the airgun array will not be
ramped up from a complete shut-down
at night or in thick fog, because the
other part of the EZ for that array will
not be visible during those conditions.
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. Ramp-up of
the airguns will not be initiated if a
marine mammal is sighted within or
near the applicable EZ during the day or
close to the vessel at night.
Temporal and Spatial Avoidance—
The Langseth will not acquire seismic
data in the humpback winter
concentration areas during the early part
of the seismic program. North Pacific
humpback whales are known to winter
and calve around Ogasawara (400 km
north of the most northerly survey) and
Ryuku Islands in southern Japan and in
the Babuyan Islands in Luzon Strait in
the northern Philippines (Perry et al.,
1999a; Acebes et al., 2007;
Calambokidis et al., 2008). In the Luzon
Strait, a small population of humpback
whales may arrive in the area as early
as November and leave in May or even
June, with a peak occurrence during
February through March or April
(Acebes et al., 2007). To mitigate against
the potential effects of the surveys on
humpback whales, particularly mothers
and calves on the breeding grounds or
during the beginning of migration to
summer feeding grounds, the Langseth
will avoid these wintering areas at the
time of peak occurrence, by surveying
the lines that approach the Babuyan
Islands as late as possible to Leg 4 (June
18 to July 20).
Due to the conservation status of
Indo-Pacific humpback dolphins in the
Taiwan Strait, particularly the central
western coast off Taiwan’s west coast
(including the Waishanding Jhou
sandbar), the cruise tracks will be
approximately 20 km (12.4 mi) offshore
to protect this sub-population and
finless porpoises, as well as to ease
potential pressure on other coastal
species. This is consistent with the
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conservative buffer recommended by
ETSSTAWG in their comments to
NMFS, ‘‘at least 13 km (8.1 mi) and
perhaps a more precautionary 15 km
(9.3 mi) to the ETS Sousa population
(Indo-Pacific humpback dolphin)—
meaning up to 20 km from shore’’ to
minimize the potential of exposing
these threatened dolphins to SPLs
greater than 160 dB re 1 μPa (rms),
subject to the limitations imposed by
other foreign nations. Regarding the
buffer for the area between the Penghu
Islands and the Waishanding Jhou
sandbar, the widest point between the
closest Penghu island and the sandbar is
34.2 km (21.3); therefore the mid-line
for the planned survey is 17.1 km (10.6
mi). The total distance between Taiwan
and the Penghu Islands is
approximately 45 km and the planned
seismic survey line off the west coast of
Taiwan is within the territorial sea of
Taiwan.
Because of the concerns about
potential effects of the seismic surveys
on Western Pacific gray whales
(wintering areas and migration), IndoPacific humpback dolphins, and finless
porpoises, the seismic survey lines in
the South China Sea south of the
Taiwan Strait have been re-routed so
that they are now located in water
depths greater than 200 m (656 ft), as
recommended by NRDC. Those in the
Taiwan Strait will be as far east as
possible from the mainland China side.
The seismic lines that were proposed in
the IHA application in the western
Taiwan Strait have been dropped.
Because of concerns about potential
effects of the seismic surveys on coastal
species and those that frequent the
continental shelf break and steep slopes
(e.g., beaked and sperm whales), the
proposed survey line paralleling the east
coast of Taiwan (the continental shelf is
narrow there) has also been moved
offshore by more than 20 km to decrease
potential impacts on these species (see
Figure 1 of L–DEO’s Supplemental EA).
Procedures for Species of Particular
Concern—Several species of particular
concern could occur in the study area.
Special mitigation procedures will be
used for these species as follows:
(1) The airguns will be shut-down if
a North Pacific right whale, Western
Pacific gray whale, humpback whale
mother/calf pair, Indo-Pacific humpback
and bottlenose dolphin, and/or finless
porpoise is sighted at any distance from
the vessel;
(2) Because of the sensitivity of
beaked whales, approach to slopes,
submarine canyons, and other
underwater geologic features will be
minimized, if possible, during the
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survey (Figure 1 of L–DEO’s
application); and
(3) If visually sighted, avoidance of
concentrations of humpback, sperm,
and beaked whales, and dugongs.
Additional Mitigation Measures
(1) To the maximum extent
practicable, L–DEO will schedule
seismic operations in inshore or shallow
waters during daylight hours and OBS
operations to nighttime hours.
(2) To the maximum extent
practicable, inshore seismic surveys will
be conducted from the coast (inshore)
and proceed towards the sea (offshore)
in order to avoid trapping marine
mammals in shallow water.
(3) NSF and L–DEO have coordinated
with the governments of Taiwan, Japan,
and the Philippines regarding the
marine geophysical activity.
(4) NMFS expects NSF and L–DEO to
adhere to conservation laws and
regulations of nations while in foreign
waters, and known rules and boundaries
of Marine Protected Areas (MPA). In the
absence of local conservation laws and
regulations or MPA rules, L–DEO will
continue to use the monitoring and
mitigation measures identified in the
IHA.
Passive Acoustic Monitoring
Passive Acoustic Monitoring (PAM)
will take place to complement the visual
monitoring program, if practicable.
Visual monitoring typically is not
effective during periods of poor
visibility (e.g., bad weather) or at night,
and even with good visibility, is unable
to detect marine mammals when they
are below the surface or beyond visual
range. Acoustical monitoring can be
used in addition to visual observations
to improve detection, identification,
localization, and tracking of cetaceans.
The acoustic monitoring will serve to
alert visual observers (if on duty) when
vocalizing cetaceans are detected. It is
only useful when marine mammals call,
but it can be effective either by day or
by night and does not depend on good
visibility. It will be monitored in real
time so visual observers can be advised
when cetaceans are detected. When
bearings (primary and mirror-image) to
calling cetacean(s) are determined, the
bearings will be relayed to the visual
observer to help him/her sight the
calling animal(s).
The PAM system consists of hardware
(i.e., hydrophones) and software. The
‘‘wet end’’ of the system consists of a
low-noise, towed hydrophone array that
is connected to the vessel by a ‘‘hairy’’
faired cable. The array will be deployed
from a winch located on the back deck.
A deck cable will connect from the
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winch to the main computer lab where
the acoustic station and signal condition
and processing system will be located.
The lead-in from the hydrophone array
is approximately 400 m (1,312 ft) long,
and the active part of the hydrophone is
approximately 56 m (184 ft) long. The
hydrophone array is typically towed at
depths less than 20 m (65.6 ft).
The towed hydrophone array will be
monitored 24 hours per day while at the
survey area during airgun operations,
and also during most periods when the
Langseth is underway while the airguns
are not operating. One MMO will
monitor the acoustic detection system at
any one time, by listening to the signals
from two channels via headphones and/
or speakers and watching the real time
spectrographic display for frequency
ranges produced by cetaceans. MMOs
monitoring the acoustical data will be
on shift for 1–6 hours. Besides the
‘‘visual’’ MMOs, an additional MMO
with primary responsibility for PAM
will also be aboard. However, all MMOs
are expected to rotate through the PAM
position, although the most experienced
with acoustics will be on PAM duty
more frequently.
When a vocalization is detected, the
acoustic MMO will, if visual
observations are in progress, contact the
MMVO immediately to alert him/her to
the presence of the cetacean(s) (if they
have not already been seen), and to
allow a power down or shutdown to be
initiated, if required. The information
regarding the call will be entered into a
database. The data to be entered include
an acoustic encounter identification
number, whether it was linked with a
visual sighting, date, time when first
and last heard and whenever any
additional information was recorded,
position and water depth when first
detected, bearing if determinable,
species or species group (e.g.,
unidentified dolphin, sperm whale),
types and nature of sounds heard (e.g.,
clicks, continuous, sporadic, whistles,
creaks, burst pulses, strength of signal,
etc.), and any other notable information.
The acoustic detection can also be
recorded for further analysis.
L–DEO will coordinate the planned
marine mammal monitoring program
associated with the TAIGER seismic
survey in SE Asia with other parties that
may have interest in the area and/or be
conducting marine mammal studies in
the same region during the proposed
seismic survey. L–DEO and NSF will
coordinate with Taiwan, Japan, and the
Philippines, as well as applicable U.S.
agencies (e.g., NMFS), and will comply
with their requirements.
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Reporting
MMVO Data and Documentation
MMVOs will record data to estimate
the numbers of marine mammals
exposed to various received sound
levels and to 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 shut-down of the
seismic source when a marine mammal
or sea turtle 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, cloud cover, and sun glare.
The data listed (time, location, etc.)
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
shutdown, will be recorded in a
standardized format. Data accuracy will
be verified by the MMVOs at sea, and
preliminary reports will be prepared
during the field program and summaries
forwarded to the operating institution’s
shore facility and to NSF weekly or
more frequently. MMVO observations
will provide the following information:
(1) The basis for decisions about
powering down or shutting down airgun
arrays.
(2) Information needed to estimate the
number of marine mammals potentially
‘taken by harassment.’ These data will
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) Data on the behavior and
movement patterns of marine mammals
seen at times with and without seismic
activity.
A report 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
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of methods, results, and interpretation
pertaining to all 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 report will also
include estimates of the amount and
nature of potential ‘‘take’’ of marine
mammals by harassment or in other
ways.
All injured or dead marine mammals
(regardless of cause) will be reported to
NMFS as soon as practicable. Report
should include species or description of
animal, condition of animal, location,
time first found, observed behaviors (if
alive) and photo or video, if available.
Monitoring to Date
During Leg 1 of the TAIGER survey,
L–DEO’s MMOs onboard the Langseth
have reported four visual sightings and
four acoustic detections during
operations in the study area. MMOs
have visually sighted a group of sperm
whales (approximately 3 individuals), a
group of short-finned pilot whales
(approximately 36 individuals), an
unidentified toothed whale, and a single
unidentified sea turtle during the four
visual sightings. For the four acoustic
detections made, spectrograms
resembling known sounds made by
sperm whales and melon-headed whales
were recorded during visual
observations of the sperm whale and
unidentified toothed whale,
respectively. Spectrograms resembling a
call of a melon-headed whale and an
unidentified whistle were recorded on
different nights. Two of the visual
sightings of cetaceans occurred while
one airgun was in operations and did
not require additional mitigation action.
The visual sighting of a group of pilot
whales occurred during a period of no
seismic activity. A power-down was
initiated for the sighting of the single
unidentified sea turtle.
During Leg 2 of the TAIGER survey,
L–DEO’s MMOs onboard the Langseth
have reported 11 visual sightings and 8
acoustic detections during operations in
the study area. No visual or acoustic
detections were made during week one
of Leg 2. During week two of the Leg 2,
MMOs on the Langseth recorded six
visual sightings of marine mammals (all
during seismic operations), two of
which sightings required a power-down.
MMOs have visually sighted two groups
of unidentified dolphins, two groups of
unidentified toothed whales (both
probable false killer whales), a group of
pantropical (approximately 100
individuals), and a group of Fraser’s
dolphins (approximately 50
individuals). A total of five acoustic
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detections were of unidentified toothed
whales and three of unidentified
dolphins. Only one of those acoustic
detections was concurrent with a visual
sighting (unidentified toothed whale).
During week three of Leg 2, MMOs on
the Langseth recorded four visual
sightings of marine mammals (all during
seismic operations), one of which
required a power-down. MMOs have
visually sighted four groups of
unidentified dolphins (one probably
bottlenose dolphin group). The groups
ranged from approximately 12 to 75
individuals. No acoustic detections
were made during week three.
During week four of Leg 2, MMOs on
the Langseth recorded one visual
sighting of spinner dolphins
(approximately 75 individuals), and
implemented a power-down during the
sighting. No other sightings were made
during week four. Three acoustic
detections of delphinids were made
during week three, all on the same day.
No monitoring for marine mammals
was conducted during Leg 3 of the
TAIGER survey, as it only consisted of
OBS operations. During week one of Leg
4, three marine mammal sightings were
made. No sightings occurred during
seismic periods; thus, not shut-downs or
power-downs of the airgun array were
required. The sightings included an
unidentified sea turtle, sperm whales
(approximately two individuals), melonheaded whales (approximately 20
individuals), and unidentified dolphins
(approximately 12 individuals). On June
23, 2009, two acoustic detections of
delphinids were made, and another
delphinid acoustic detection was made
on June 28, 2009. All acoustic
detections occurred during seismic
activity, but none required mitigation
measures.
During week one of Leg 4, MMOs on
the Langseth recorded three marine
mammal sightings and an unidentified
sea turtle. No sightings occurred during
seismic periods; thus, no shut-downs or
power-downs of the airgun array were
required. The marine mammal sightings
included one of sperm whales
(approximately 2 individuals), a group
of melon-headed whales (approximately
20 individuals), and a group of
unidentified dolphins (approximately
12 individuals). On June 23, 2009, two
acoustic detections of delphinids were
made. On June 28, 2009, an additional
delphinid acoustic detection was made.
All acoustic detections occurred during
seismic activity, but none required
mitigation measures.
During week two of Leg 4, MMOs on
the Langseth recorded two marine
mammal sightings. Both sightings of
unidentified dolphins (approximately 2
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and 100 individuals) occurred during
seismic activity, but only one sighting
required a power-down of the airgun
array. There were no shut-downs due to
marine mammal sightings during this
period. There were four acoustic
detections, all of which occurred during
seismic activity.
During week three of Leg 4, MMOs on
the Langseth recorded one marine
mammal sighting. The group of five
individual sperm whales consisted of
four adults and one calf. This sighting
occurred during seismic activity, but
did not require the implementation of
any mitigation measures. No acoustic
detections were made during this
period.
During week four of Leg 4, MMOs on
the Langseth recorded one marine
mammal sighting. One sighting of 36
pantropical spotted dolphins (24 adults
and 12 calves) was made during this
period. This sighting occurred during
seismic activity, but did not require the
implementation of any mitigation
measures. There were two acoustic
detections made during this period,
both of which occurred during seismic
activity.
IHA Modifications
On March 31, 2009, NMFS issued an
IHA to L–DEO to take small numbers of
marine mammals incidental to
conducting a marine geophysical survey
in SE Asia, under a cooperative
agreement with NSF, as part of the
TAIGER program from March–July,
2009. On April 21, 2009, NMFS
received a request from L–DEO, asking
that IHA conditions (10(u) and 10(w)) be
modified for clarification because as
currently written, the conditions would
effectively preclude the complete
execution of Leg 2—the seismic survey
line along the west coast of Taiwan.
Specifically, condition 10(u) only
allowed the survey to occur if the
Taiwan Strait were more than 170 km
wide throughout its entire length or
only in the southern portion of the area.
The area between Taixi and Tongshiao,
which demarcates the primary
distribution of the ‘critically
endangered’ (IUCN, 2008) Indo-Pacific
humpback dolphin Eastern Taiwan
Strait sub-population, is typically
narrower than 170 km. L–DEO stated
that the 150 km distance probably
originated as an error with an early draft
of the Supplemental EA.
Condition 10(w) did not specifically
address the maintenance of a
conservative buffer from the Penghu
Islands and the Waishanding Jhou
sandbar. Under the modification to
condition 10(w) the planned seismic
survey line will only change in the area
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Jkt 217001
between the Penghu Islands and the
Waishanding Jhou sandbar. The widest
point between the closest Penghu island
and the sandbar is 34.2 km (21.3 mi);
therefore the mid-line for the planned
survey is 17.1 km (10.6 mi). The total
distance between Taiwan and the
Penghu Islands is approximately 45 km
and the planned seismic survey line off
the west coast of Taiwan is within the
territorial sea of Taiwan. Additionally,
as requested by L–DEO, distances stated
in the IHA now include nautical miles
for navigational purposes.
In addition, NMFS clarified condition
10(s). Condition 10(s) needed to be
modified to more specifically describe
the geographical area of the Taiwan
Strait where the first and second legs of
the TAIGER survey are being conducted.
Prior to the issuance of the original IHA,
L–DEO voluntarily dropped the seismic
survey tracklines in the western Taiwan
Strait for a number of reasons, including
concerns about the effects of the surveys
on Western Pacific gray whales, IndoPacific humpback dolphins, and finless
porpoises, and because China denied L–
DEO access to their waters. Condition
10(s), as modified, better reflects these
circumstances.
A copy of the modified IHA can be
found online at: https://
www.nmfs.noaa.gov/pr/pdfs/permits/
taiger_iha_modified.pdf.
On July 13, 2009, NMFS received a
request from L–DEO for an additional 16
authorized takes of sperm whales for the
remainder of the seismic survey. It is
unlikely that his many animals will be
exposed to these sound levels, but with
the group dynamic for this particular
species, additional numbers have been
requested to allow for a chance
encounter of a large sperm whale group.
During vessel operations in the TAIGER
study area, there have been 13
individual sperm whales sighted in
three groups. On July 8, 2009, five
individuals were identified by MMOs to
have been exposed to sound levels
greater than or equal to 160 dB re 1 μPa
(rms) in the study area. These five
animals were observed in a single group
about 2 km (1.24 mi) from the MMO
observation tower (approximately 2.2
km [1.37 mi] from the closest airgun)
onboard the Langseth. These animals
showed similar movement and
behavioral responses as those observed
outside the 160 dB isopleths. L–DEO
has provided additional sighting data as
well. Authorized takes of 20 sperm
whales (0.08 percent of the regional
population) are included in the IHA
modified on July 15, 2009.
PO 00000
Frm 00063
Fmt 4701
Sfmt 4703
41321
Endangered Species Act (ESA)
Pursuant to Section 7 of the ESA, NSF
has consulted with the NMFS, Office of
Protected Resources, Endangered
Species Division on this seismic survey.
NMFS has also consulted internally
pursuant to Section 7 of the ESA on the
issuance of an IHA under section
101(a)(5)(D) of the MMPA for this
activity. On March 31, 2009, NMFS
concluded consultation with NMFS and
NSF and issued a Biological Opinion
(BiOp), which concluded that the
proposed action and issuance of an IHA
are not likely to jeopardize the
continued existence of North Pacific
right, Western Pacific gray, blue, fin, sei,
humpback, and sperm whales, and
leatherback (Dermochelys coriacea),
green (Chelonia mydas), loggerhead
(Caretta caretta), hawksbill
(Eretmochelys imbricata), and olive
ridley (Lepidochelys olivacea) sea
turtles. The BiOp also concluded that
designated critical habitat for these
species does not occur in the action area
and would not be affected by the survey.
Relevant Terms and Conditions of the
Incidental Take Statement in the BiOp
have been incorporated into the IHA.
Since NMFS modified the IHA issued
to L–DEO, a review under Section 7 was
conducted. On May 1, 2009, NMFS
concluded that the proposed revisions
to the IHA would not cause adverse
effects on species or designated critical
habitat. Given this, the consultation
requirements have been met and no
additional consultation is required for
the issuance of the revised IHA.
National Environmental Policy Act
(NEPA)
NSF prepared an EA titled ‘‘Marine
Seismic Survey in Southeast Asia,
March–July 2009’’ that references L–
DEO’s EA and Supplemental EA of a
Marine Geophysical Survey by the R/V
Marcus G. Langseth in Southeast Asia,
March–July 2009. LGL Limited,
Environmental Research Associates,
prepared the EA and Supplemental EA
on behalf of L–DEO and NSF. NMFS has
adopted NSF’s EA and issued a Finding
of No Significant Impact (FONSI) for the
issuance of the IHA. The modification of
the IHA was within the scope of the
impacts considered in the EA and used
to support the FONSI.
Determinations
NMFS has determined that the impact
of conducting the seismic survey in SE
Asia may result, at worst, in a temporary
modification in behavior (Level B
harassment) of small numbers of marine
mammals. Further, this activity is
expected to result in a negligible impact
E:\FR\FM\14AUN2.SGM
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mstockstill on DSKH9S0YB1PROD with NOTICES2
on the affected species or stocks. The
provision requiring that the activity not
have an unmitigable impact on the
availability of the affected species or
stock for subsistence uses is not
implicated for this action.
For reasons stated previously in this
document, this negligible impact
determination is supported by:
(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 marine mammals
would have to be closer than 40 m (131
ft) in deep water, 60 m (197 ft) at
intermediate depths, or 296 m (971 ft)
in shallow water when a single airgun
is in use from the vessel to be exposed
to levels of sound (180 dB) believed to
have even a minimal chance of causing
TTS;
(3) The fact that cetaceans would have
to be closer than 950 m (0.6 mi) in deep
water, 1,425 m (0.9 mi) at intermediate
depths, and 3,694 m (2.3 mi) in shallow
water when the full array is in use at a
9 m (29.5 ft) tow depth from the vessel
to be exposed to levels of sound (180
dB) believed to have even a minimal
chance of causing TTS;
VerDate Nov<24>2008
17:44 Aug 13, 2009
Jkt 217001
(4) The fact that marine mammals
would have to be closer than 6,000 m
(3.7 mi) in deep water, 6,667 m (4.1 mi)
at intermediate depths, and 8,000 m (4.9
mi) in shallow water when the full array
is in use at a 9 m (29.5 ft) tow depth
from the vessel to be exposed to levels
of sound (160 dB) believed to have even
a minimal chance at causing TTS;
(5) The likelihood that marine
mammal detection ability by trained
observers is high at that short distance
from the vessel;
(6) The use of PAM, which is effective
out to tens of km, will assist in the
detection of vocalizing marine mammals
at greater distances from the vessel;
(7) The incorporation of other
required mitigation measures (i.e.,
ramp-up, power-down, shut-down,
temporal and spatial avoidance, special
measures for species of particular
concern, and additional mitigation
measures); and
(8) The relatively limited duration
and geographically widespread
distances of the seismic survey in the SE
Asia study area (approximately 103
days). As a result, no take by injury or
death is anticipated, and the potential
for temporary or permanent hearing
impairment is very low and will be
avoided through the incorporation of
PO 00000
Frm 00064
Fmt 4701
Sfmt 4703
the required monitoring and mitigation
measures.
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
harassment takings is estimated to be
small, relative to the affected species
and stock sizes (less than a few percent
of any of the estimated population
sizes), and has been mitigated to the
lowest level practicable through
incorporation of the measures
mentioned previously in this document.
Authorization
As a result of these determinations,
NMFS issued and modified an IHA to
L–DEO for conducting a marine
geophysical survey in SE Asia from
March–July, 2009, including the
previously mentioned mitigation,
monitoring, and reporting requirements.
James H. Lecky,
Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. E9–19459 Filed 8–13–09; 8:45 am]
BILLING CODE 3510–22–P
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Agencies
[Federal Register Volume 74, Number 156 (Friday, August 14, 2009)]
[Notices]
[Pages 41260-41322]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-19459]
[[Page 41259]]
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Part III
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
Geophysical Survey in Southeast Asia, March-July 2009; Notice
Federal Register / Vol. 74 , No. 156 / Friday, August 14, 2009 /
Notices
[[Page 41260]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XL89
Incidental Takes of Marine Mammals During Specified Activities;
Marine Geophysical Survey in Southeast Asia, March-July 2009
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; issuance and modification of an incidental take
authorization.
-----------------------------------------------------------------------
SUMMARY: In accordance with the Marine Mammal Protection Act (MMPA)
regulations, notification is hereby given that NMFS issued and modified
an Incidental Harassment Authorization (IHA) to Lamont-Doherty Earth
Observatory (L-DEO), a part of Columbia University, for the take small
numbers of marine mammals, by harassment, incidental to conducting a
marine seismic survey in Southeast (SE) Asia during March-July 2009.
DATES: Effective March 31, 2009, through August 20, 2009.
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 20910-3235 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 online
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 Ken Hollingshead,
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 to allow, upon request, the
incidental, but not intentional, taking 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.
Authorization for incidental taking shall be granted if NMFS finds
that the taking will have a negligible impact on the species or
stock(s), will not have an unmitigable adverse impact on the
availability of the species or stock(s) for subsistence uses (where
relevant), and if the permissible methods of taking and requirements
pertaining to the mitigation, monitoring and reporting of such takings
are set forth. NMFS has defined ``negligible impact'' in 50 CFR 216.103
as `` * * * an impact resulting from the specified activity that cannot
be reasonably expected to, and is not reasonably likely to, adversely
affect the species or stock through effects on annual rates of
recruitment or survival.''
Section 101(a)(5)(D) of the MMPA established an expedited process
by which citizens of the U.S. can apply for an authorization 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 on any proposed authorizations for the incidental harassment of
small numbers 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 October 27, 2008, NMFS received an application from L-DEO for
the taking, by Level B harassment only, of small numbers of marine
mammals incidental to conducting, under cooperative agreement with the
National Science Foundation (NSF), a marine seismic survey in SE Asia.
The funding for the Taiwan Integrated Geodynamics Research (TAIGER)
survey is provided by the NSF. The proposed survey will encompass the
area 17[deg]30'-26[deg]30' N, 113[deg]30'-126[deg] E within the
Exclusive Economic Zones (EEZ) of Taiwan, Japan, and the Philippines,
and on the high seas, and is scheduled to occur from March 31 to July
20, 2009. Some minor deviation from these dates is possible, depending
on logistics and weather.
Taiwan is one of only a few sites of arc-continent collision
worldwide; and one of the primary tectonic environments for large scale
mountain building. The primary purpose of the TAIGER project is to
investigate the processes of mountain building, a fundamental set of
processes which plays a major role in shaping the face of the Earth.
The vicinity of Taiwan is particularly well-suited for this type of
study, because the collision can be observed at different stages of its
evolution, from incipient, to mature, and finally to post-collision.
As a result of its location in an ongoing tectonic collision zone,
Taiwan experiences a great number of earthquakes, most are small, but
many are large and destructive. This project will provide a great deal
of information about the nature of the earthquakes around Taiwan and
will lead to a better assessment of the earthquake hazards in the area.
The information obtained from this study will help the people and the
earthquake hazards in the area. The information obtained from this
study will help the people and government of Taiwan to better prepare
for future seismic events and may thus mitigate some of the loss of
life and economic disruptions that will inevitably occur.
The action is planned to take place in the territorial seas and
EEZ's of foreign nations, and will be continuous with the activity that
takes place on the high seas. NMFS does not authorize the incidental
take of marine mammals in the territorial seas of foreign nations, as
the MMPA does not apply in those waters. However, NMFS still needs to
calculate the level of incidental take in territorial seas as part of
the analysis supporting issuance of an IHA in order to determine the
biological accuracy of the small numbers and negligible impact
determination.
Description of the Specified Activity
The planned survey will involve one source vessel, the R/V Marcus
G. Langseth (Langseth), which will occur in SE Asia. The Langseth will
deploy an array of 36 airguns (6,600 in\3\) as an energy source at a
tow depth of 6-9 m (20-30 ft). The receiving system will consist of a
hydrophone streamer and approximately 100 ocean bottom seismometers
(OBSs). The Langseth will deploy an 8 km (5 mi) long streamer for most
transects requiring a streamer; however, a shorter streamer (500 m to 2
[[Page 41261]]
km or 1,640 ft to 1.2 mi) will be used during surveys in Taiwan
(Formosa) Strait. As the airgun array is towed along the survey lines,
the hydrophone streamer will receive the returning acoustic signals and
transfer the data to the on-board processing system. The OBSs record
the returning acoustic signals internally for later analysis. The OBSs
to be used for the TAIGER program will be deployed and retrieved
numerous times by a combination of 4 or 5 Taiwanese support vessels, as
well as the Langseth. The Langseth will also retrieve 20 OBSs that were
deployed in the study area during previous years to record earthquake
activity.
Approximately 100 OBSs will be deployed during the survey. OBSs
will likely be deployed and retrieved by the Langseth as well as a
combination of 4 to 5 Taiwanese vessels. The Taiwanese vessels to be
used include two 30 m (98.4 ft) vessels (the R/V Ocean Researcher 2 and
the R/V Ocean Researcher 3) and two vessels greater than 60 m (196.8
ft) in length (R/V Fisheries Research I and the Navy ship Taquan). The
R/V Ocean Research I may also be used if the Langseth is not used to
deploy OBSs. The OBS deployment spacing will vary depending on the
number of instruments available and shiptime. The nominal spacing is 15
km (9.3 mi), but this will vary from as little as 5 km (3.1 mi) to
perhaps as much as 25 km (15.5 mi). The OBSs will be deployed and
recovered several (2 to 4) times. 60 of the 100 OBSs may be deployed
from the Langseth. All OBSs will be retrieved at the end of the study.
Up to 3 different types of OBSs may be used during the 2009
program. The Woods Hole Oceanographic Institution (WHOI) ``D2'' OBS has
a height of approximately 1 m (3.3 ft) and a maximum diameter of 50 cm.
The anchor is made of hot-rolled steel and weighs 23 kg (50.7 lbs). The
anchor dimensions are 2.5 x 30.5 x 38.1 cm. The LC4x4 OBS from the
Scripps Institution of Oceanography (SIO) has a volume of approximately
1 m\3\ (3.3 ft\2\), with an anchor that consists of a large piece of
steel grating (approximately 1 m\2\ or 3.3 ft\2\). Taiwanese OBSs will
also be used; their anchor is in the shape of an `x' with dimensions of
51-76 cm\2\ (1.7-2.5 ft\2\). Once the OBS is ready to be retrieved an
acoustic release transponder interrogates the OBS at a frequency of 9-
11 kHz, and a response is received at a frequency of 9-13 kHz. The burn
wire release assembly is then activated, and the instrument is released
from the anchor to float to the surface.
The seismic survey as described in the Federal Register notice (73
FR 78294, December 22, 2008) for the proposed IHA was 15,902 km (9,881
mi) in length. After public comment, L-DEO revised the tracklines so
that the seismic survey consists of approximately 14,515 km (9,019 mi)
of transect lines within the South and East China Seas as well as the
Philippine Sea, with the majority of the survey effort occurring in the
South China Sea. The total length of the revised tracklines is
approximately 9 percent less than the total length of the original
tracklines. The survey will take place in water depths ranging from
approximately 25 to 6,585 m (82-21,598 ft), but most of the survey
effort (approximately 84.4 percent) will take place in water greater
than 1,000 m (3,280 ft), 11.4 percent will take place in intermediate
depth waters (100-1,000 m or 328-3,280 ft), and 4.2 percent will occur
in shallow depth water (less than 100 m or 328 ft).
All planned geophysical data acquisition activities will be
conducted by L-DEO with onboard assistance by the scientists who have
proposed the study. The scientific team consists of Dr. Francis Wu
(State University of New York at Binghamton) and Dr. Kirk McIntosh
(University of Texas at Austin, Institute of Geophysics). The vessel
will be self-contained, and the crew will live aboard the vessel for
the entire cruise.
In addition to the operations of the airgun array, a 12 kHz Simrad
EM 120 multibeam echosounder (MBES) and a 3.5 kHz sub-bottom profiler
(SBP) will be operated from the Langseth continuously throughout the
TAIGER cruise.
Dates, Duration, and Region of Activity
The survey will encompass the area from approximately
17[deg]30[min]-26[deg]30[min] N, 113[deg]30[min]-126[deg] E within the
EEZs of Taiwan, Japan, and the Philippines. The vessel will approach
mainland Taiwan within 5.2 km (3.2 mi) and mainland China within 116 km
(72 mi). The vessel will approach within 3.7 km (2.3 mi) and 105 km (65
mi) of islands off the coast of Taiwan and China, respectively. The
closest approach to the Ryuku Islands and Okinawa Islands will be 51.5
km (32 mi) and approximately 400 km (249 mi), respectively. Although
the survey will occur at least 32 km (29.9 mi) from Luzon, Philippines,
survey lines will take place approximately 28.6 km (17.8 mi) and 8.8 km
(5.5 mi) from the Babuyan and Batan islands, respectively. Water depths
in the survey area range from approximately 25 to 6,280 m (164-20,603
ft). There are not seismic lines in less than 50 m (164 ft) water
depth. The closest seismic line to land is approximately 3.7 km (2.3
mi) from an island off the east coast of Taiwan. The TAIGER program
consists of 4 legs, each starting and ending in Kao-hsiung, Taiwan. The
first leg is expected to occur from approximately March 31 to April 28,
2009 and will include the survey lines in the South China Sea. The
second leg is scheduled for May 3 to June 3, 2009 and will include
survey lines around Taiwan. The third leg (approximately June 7-14,
2009) will involve OBS recovery by the Langseth only; no seismic
acquisition will occur during this leg. The fourth leg, consisting of
the survey lines in the Luzon Strait and Philippine Sea, is scheduled
to occur from June 18 to July 20, 2009. The program will consist of
approximately 103 days of seismic acquisition. The exact dates of the
activities depend on logistics and weather conditions.
Safety Radii
L-DEO estimated the safety radii around their operations using a
model and by adjusting the model results based on empirical data
gathered in the Gulf of Mexico in 2003. Additional information
regarding safety radii in general, how the safety radii were
calculated, and how the empirical measurements were used to correct the
modeled numbers may be found in NMFS' proposed IHA notice (73 FR 78294,
December 22, 2008) and L-DEO's application. Using the modeled distances
and various correction factors, Table 1 outlines the distances at which
three rms sound levels (190 dB, 180 dB, and 160 dB) are expected to be
received from the various airgun configurations in shallow,
intermediate, and deep water depths.
----------------------------------------------------------------------------------------------------------------
Predicted RMS Distances (m)
Source and volume Tow depth (m) Water depth -----------------------------------------------
190 dB 180 dB 160 dB
----------------------------------------------------------------------------------------------------------------
Single Bolt airgun 40 in\3\... *6-9 Deep............ 12 40 385
.............. Intermediate.... 18 60 578
.............. Shallow......... 150 296 1,050
4 strings 36 airguns 6600 6-7 Deep............ 220 710 4,670
in\3\.
[[Page 41262]]
.............. Intermediate.... 330 1,065 5,189
.............. Shallow......... 1,600 2,761 6,227
8-9 Deep............ 300 950 6,000
.............. Intermediate.... 450 1,425 6,667
.............. Shallow......... 2,182 3,694 8,000
----------------------------------------------------------------------------------------------------------------
Table 1. Predicted distances to which sound levels [gteqt]190, 180, and 160 dB re 1 [mu]Pa might be received in
shallow (<100 m; 328 ft), intermediate (100-1,000 m; 328-3,280 ft), and deep (>1,000 m; 3,280 ft) water from
the 36 airgun array, as well as a single airgun, used during the Central American SubFac and STEEP Gulf of
Alaska survey, and planned during the TAIGER SE Asia survey. *The tow depth has minimal effect on the maximum
near-field output and the shape of the frequency spectrum for the single 40 in\3\ airgun; thus, the predicted
safety radii are essentially the same at each tow depth. The most precautionary distances (i.e., for the
deepest tow depth, 9m) are shown.
Because the predictions in Table 1 are based in part on empirical
correction factors derived from acoustic calibration of airgun
configurations different from those to be used on the Langseth (cf.
Tolstoy et al., 2004a,b), L-DEO conducted an acoustic calibration study
of the Langseth's 36 airgun (approximately 6,600 in\3\) array in late
2007/early 2008 in the Gulf of Mexico (LGL Ltd., 2006). Distances where
sound levels (e.g., 190, 180, and 160 dB re 1 [mu]Pa rms) were received
in deep, intermediate, and shallow water will be determined for various
airgun configurations. Acoustic data analysis is ongoing and a
scientific paper on the Langseth calibration study is currently in
review for future publication (Tolstoy, pers. comm.). After analysis,
the empirical data from the 2007/2008 calibration study will be used to
refine the exclusion zones (EZ) proposed above for use during the
TAIGER cruise, if the data are appropriate and available for use at the
time of the survey.
A more detailed description of the authorized action, including
vessel and acoustic source specifications, was included in the proposed
IHA notice (73 FR 78294, December 22, 2008).
Comments and Responses
A notice of receipt of the L-DEO application and proposed IHA was
published in the Federal Register on December 22, 2008 (73 FR 78294). A
notice extending the public comment period by 15 days, to February 5,
2009, due to several Federal holidays, was published in the Federal
Register on January 16, 2009 (74 FR 2995). During the comment period,
NMFS received comments from the Marine Mammal Commission (Commission).
NMFS also received comments from the Center for Regulatory
Effectiveness (CRE), Natural Resources Defense Council (NRDC) (on
behalf of International Fund for Animal Welfare, Whale and Dolphin
Conservation Society, Cetacean Society International [CSI], Animals
Asia Foundation [AAF], New York Whale and Dolphin Action League, Ocean
Futures Society, and Jean-Michel Cousteau), Wild at Heart Legal Defense
Association (WaH) (on behalf of Changhua County Environmental
Protection Union, Clymene Enterprises, Green Party Taiwan, Taiwan
Friends of the Global Greens, Leviathan Sciences, Environment and
Animal Society of Taiwan, Wild Bird Society of Yunlin, Matsu's Fish
Conservation Union, Blue Dolphin Alliance, Hong Kong Dolphin
Conservation Society [HKDCS], Dr. Ellen Hines, Taiwan Sustainable
Union, Jo Marie V. Acebes, APEX Environmental, Coral Triangle Oceanic
Cetacean Program and IUCN Species Survival Commission--Cetacean
Specialist Group, Kimberly Reihl, Changhua Coast Conservation Action,
Ocean Park Corporation, Dr. Bradley White, Ketos Ecology, CSI, Dr. Wang
Ding, Study Centre for Marine Conservation, AAF, International
Laboratory for Dolphin Behaviour Research, Mary Speer, and American
Cetacean Society), CSI, Linking Individuals for Nature Conservation
(LINC), Humane Society International (HSI), Dr. John Wang, Eastern
Taiwan Strait Sousa Technical Advisory Working Group (ETSSTAWG), AAF,
HKDCS, Dr. Robert Brownell, Dr. Lien-Siang Chou, Dr. Linda Weilgart,
Dr. Kirk McIntosh and Dr. Francis Wu (Dr. McIntosh and Dr. Wu), Dr.
Lemnuel Aragones, Dr. Joseph Minor and Dr. Christine Wilson and James
Minor and Susan Wilson (Minor and Wilson), and a private citizen. The
public comments can be found online at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm.
The following are their comments, and NMFS' responses.
Extension Requests
Comment 1: Numerous parties expressed concern regarding L-DEO's IHA
application under the MMPA to incidentally harass marine mammals during
a proposed marine geophysical survey in SE Asia from March-July, 2009,
as published in the Federal Register (73 FR 78294, December 22, 2008).
Many interested persons and organizations requested an extension of the
30-day public comment period to allow for the adequate review of
lengthy documents associated with the proposed IHA and prepare
responses.
Response: NMFS considered these requests during the 30-day public
comment period and published a notice in the Federal Register (74 FR
2995, January 16, 2009) extending the public comment period for the
proposed IHA from January 21 to February 5, 2009. The 15-day extension
is due to the unique circumstances of the timing of the publication of
the Federal Register notice (74 FR 2995, January 16, 2009) relative to
several Federal holidays. The Federal Register notice (74 FR 2995,
January 16, 2009) published three days before the Christmas holiday,
which fell on Thursday, December 25, 2008. The following day, Friday,
December 26, 2008 was declared a Federal holiday for executive branch
departments and agencies. New Year's Day, a Federal holiday, was the
following Thursday, January 1, 2009. The 15-day extension was given in
recognition of the fact that the timing of these three holidays led
many workers to be away for much of the two-week period and some non-
government organizations closed their offices during that period. NMFS
is also aware that the proposed action was for a new geographical area
rather than a renewal of a prior action, where the associated documents
are lengthy and would likely not be familiar to many interested
parties. NMFS believes that a 30-day comment period with a 15-day
extension (for a total of 45 days) is more than an adequate time period
for the public to address concerns and submit comments.
General Comments
Comment 2: The CRE objects to the statement in the proposed IHA (73
FR 78303, December 22, 2008) on page 78303, column one, paragraph
three, that states: ``However, controlled exposure experiments in the
Gulf of Mexico indicate that foraging behavior
[[Page 41263]]
was altered upon exposure to airgun sound (Jochens et al., 2006).'' CRE
states that this statement is misleading, and does not accurately
reflect the underlying data, and it is not based on the most recent
assessment of those data. NMFS' statement cites a 2006 Sperm Whale
Seismic Study (SWSS) in the Gulf of Mexico Report which discusses data
on foraging behavior and avoidance movements of seven tagged sperm
whales in the Gulf of Mexico during exposure to airguns. The CRE
requests that NMFS cite the final 2008 Synthesis Report on SWSS which
cautions that the ``* * * sample size of seven animals that conducted
foraging dives during exposure was too small to provide definitive
results * * * the power of the test to detect small changes in foraging
success was low, and no conclusions on the biological significance of
these effects for an individual animal or for the populations can be
made from the data sets available.''
Response: As CRE points out in their letter, L-DEO acknowledges in
their application (see Section VI, page 37) that seismic energy alters
sperm whale foraging behavior. NMFS acknowledges the commentor's
interpretation of 2006 SSWS. However, after reviewing the 2008
Synthesis Report, NMFS believes that the following statement: ``* * *
sample size of 7 animals conducted foraging dives during exposure was
too small to provide definitive results * * * the power of the test to
detect small changes in foraging success was low and no conclusions on
the biological significance of these effects for an individual animal
or for the population can be made from the data sets available,''
refers to having the statistical power to detect small changes in
foraging success. Conversely, page 264 of the 2008 Synthesis Report
states the following: ``* * * Our data seem to indicate that airgun
exposure--even at low exposure levels observed in this experiment--can
result in large reductions in foraging rate for some individual sperm
whales.'' Therefore, the proposed IHA notice statement that data
indicated alterations in foraging behavior, is supported by one of the
conclusions discussed in the 2008 Synthesis Report. NSF and L-DEO
presented this study as one of several pieces of information that
relate to this topic. Though the commenter has presented an alternate
interpretation of the data related to foraging behavior, NMFS finds
that the EA provides sufficient analysis of the available data and the
information is not such that NMFS' findings.
Comment 3: The Commission is concerned that most of the issues
raised in its letter have been raised before and, to their knowledge,
little is being done to resolve them. The Commission believes that the
action agency and contractor should bear primary responsibility for
carrying out the studies needed to reduce the existing uncertainty and
that the authorizing and oversight agencies have a degree of
responsibility as well.
Response: NMFS has responded to the best of its ability regarding
all of the Commission's concerns on various issues during the public
comment process.
Comment 4: The Commission is concerned that the opportunity for
scientists, conservationists, and other interested parties from other
countries to comment on research activities to be conducted by U.S.
organizations in foreign waters. Scientists, conservationists, and
others are generally unfamiliar with the procedures for permit review
and authorization in the U.S. but may have a good understanding of the
natural history and vulnerability of potentially affected species. The
Commission believes that they should be provided with opportunities to
contribute to the evaluation of the potential effects of seismic
studies in the context of all other factors that may be affecting these
species. If U.S. scientists and institutions are to engage in research
activities in the waters of other countries, it stands to reason that
our system of review should include sufficient opportunities for
foreign parties to comment on potential effects. This might be
accomplished in any number of ways, such as extending the comment
period to give them additional time to comment and promoting
interaction between the research organization and concerned parties
from other countries. The Commission believes such participation is
appropriate and, in the long run, will facilitate international
cooperation on conservation issues, more informed comments, and more
risk-averse research methods and mitigation procedures.
Response: NMFS agrees with the Commission's comments. NMFS extended
the 30 day public comment for the proposed IHA by an additional 15 days
to accommodate requests from the public. See Extension Request above.
Comment 5: Dr. McIntosh and Dr. Wu have provided some comments
about the nature and significance of our project and also try to allay
some of the expressed concerns. As an introductory statement, the
research Dr. McIntosh and Dr. Wu plan targets fundamental Earth
processes that remain inadequately understood; this includes topics
such as the growth and composition of continents and the fundamental
processes of building mountains. Dr. McIntosh and Dr. Wu choose to do
this research in the Taiwan region because it is the best location, of
only a few places globally, where we can study the collision of an
oceanic island chain with a continent.
Response: NMFS acknowledges Dr. McIntosh and Dr. Wu's comments.
Comment 6: Dr. McIntosh and Dr. Wu state that as for marine mammal
safety, the community of marine mammal biologists can be assured that
their project is not a reckless intrusion into the marine habitat of
endangered species. In fact, detailed studies have been conducted
regarding the possible impacts of this project on marine mammal
populations.
Response: NMFS acknowledges Dr. McIntosh and Dr. Wu's comments.
NMFS expects the principal scientists to abide by the requirements
described in the IHA issued to L-DEO. After issuance of the proposed
IHA, L-DEO negotiated with the project's principal scientists to modify
the cruise plan and adopt more precautionary mitigation measures for
purposes of marine mammal safety in the study area.
Comment 7: Dr. McIntosh and Dr. Wu state that they expect to
produce the most comprehensive subsurface images of the rapidly rising
Taiwan mountains with their data. These images, along with seismicity
recorded by L-DEO's arrays, will form a greatly enhanced basis for
evaluating earthquake and tsunami potentials of Taiwan and can thus be
used to improve the safety and security of the human population at risk
to these phenomena.
Response: NMFS acknowledges Dr. McIntosh and Dr. Wu's comments.
Comment 8: CSI states that the IHA application and EA are similar
in many respects to previous L-DEO EA's. The response, however, is not.
The response to this authorization request will prove to be unique, a
potential watershed in the manner all future seismic surveys should be
critiqued by the scientific community. To be helpful, CSI has attached
some relevant expert reviews to their comments, even if they are
duplicated by others, to ensure that NMFS has the opportunity to
include them in the deliberative process. The expert level of opinion
and proof stimulated by the IHA application and EA challenges previous
assumption and, CSI hopes, will stimulate adequate, directed research
to enable appropriate
[[Page 41264]]
mitigations to satisfy various laws, including the MMPA.
Response: NMFS received numerous comments from interested parties
on L-DEO's proposed IHA for a marine geophysical survey in SE Asia,
March to July 2009. NMFS acknowledges CSI's and other interested
parties' comments on the proposed IHA and EA during the public comment
period. After the issuance of the proposed IHA, L-DEO modified the
cruise plan and adopted more precautionary monitoring and mitigation
measures. NMFS believes that L-DEO's revised survey as well as the
implementation of the monitoring and mitigation measures described in
the IHA will have a negligible impact on the affected species or stocks
of marine mammals in the study area.
L-DEO and NSF have formally consulted with NMFS' Permits,
Conservation, and Education Division under the MMPA regarding the IHA
and NMFS' Endangered Species Division regarding a Biological Opinion
under Section 7 of the ESA for the marine geophysical survey in SE
Asia. NMFS believes L-DEO and NSF have satisfied their responsibilities
under the laws of the MMPA and ESA.
Comment 9: CSI states that the MMPA only authorizes the lethal
taking of marine mammals under extraordinary circumstances that do not
apply to the scientific research proposed by this project. In the
opinion of experts, as expressed in the attachments, mortalities are
likely. How can NMFS believe that all these experts are wrong, or that
associated mortalities would not violate the MMPA? CSI urges NMFS to
apply these experts comments to the EA and IHA application deficiencies
and to require that the L-DEO proposal address them in the only legal
format available to them, an application for a LOA under MMPA Section
101(a)(5)(A-C).
Because the L-DEO's geophysical research will have an incidental
impact on marine mammals that experts predict will include mortalities
and even extirpation it must apply for a letter of authorization under
MMPA section 101(a)(5)(A-C).
Response: While an authorization for taking marine mammals by
mortality cannot be authorized under Section 101(a)(5)(D) of the MMPA,
those paragraphs do authorize taking by Level A harassment. Level A
harassment means any act of pursuit, torment, or annoyance which has
the potential to injure a marine mammal or a marine mammal stock in the
wild. While it is true that an injury can be so severe that it later
may result in mortality, the MMPA does not preclude issuance of an
authorization under Section 101(a)(5)(D) of the MMPA for activities
that have the potential to cause injury. However, as NMFS shows in this
document morality and serious injury are not anticipated to occur
during this seismic survey cruise due to implementation of mitigation
measures (e.g., ramp-up, power-down, shut-down, temporal and spatial
avoidance, procedures for species of particular concern, passive
acoustic and visual monitoring, and quiet acoustic periods). Nor is
take by injury, serious injury, or mortality authorized. Therefore,
issuance of an IHA is appropriate. Monitoring and mitigation measures
are discussed later in this document.
Comment 10: CSI states it is a relief to find so many experts
willing to contribute their knowledge and experience to this process.
They do a far better job than CSI or any NGO could of addressing the
specific flaws found in this L-DEO IHA request. While some of these
same flaws in previous L-DEO requests have been addressed, they may
have been more easily dismissed by NMFS because very few were from
world authorities and scientific experts. This time the experts have
participated directly, and cannot be dismissed.
Response: NMFS acknowledges CSI's comments and considers all
relevant public comments before making a determination on the issuance
of the IHA. After issuance of the proposed IHA, L-DEO modified the
cruise plan and adopted more precautionary monitoring and mitigation
measures in the study area. NMFS believes that L-DEO's revised survey
as well as the implementation of the required monitoring and mitigation
described in the IHA will have a negligible impact on the affected
species or stocks of marine mammals in the study area.
After the issuance of the proposed IHA, L-DEO modified the cruise
plan and adopted more precautionary monitoring and mitigation measures
in the study area. NMFS believes that L-DEO's revised survey as well as
the implementation of the monitoring and mitigation measures described
in the IHA will have a negligible impact on the affected species or
stocks of marine mammals in the study area.
Comment 11: CSI states that the intent of LGL's comment is to
manipulate NMFS into a fast and uncritical decision. By law, the
schedules, as well as the scientific and economic values of this
project, remain irrelevant to the scope of NMFS' deliberations on the
fitness of the proposal.
Response: 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 on any proposed authorizations for the incidental
harassment of small numbers of marine mammals. Within 45 days of the
close of the comment period, NMFS must either issue or deny issuance of
the authorization. NMFS received an IHA application from L-DEO on
October 27, 2008. NMFS published a notice for the proposed IHA in the
Federal Register on December 22, 2008 (73 FR 78294). A notice on the
15-day extension of the comment period for the proposed IHA was
published on January 16, 2009. NMFS issued an IHA to L-DEO on March 31,
2009 and amended the IHA on May 1, 2009.
After issuance of the proposed IHA, L-DEO modified the cruise plan
and adopted more precautionary monitoring and mitigation measures in
the study area. NMFS believes that L-DEO's revised survey as well as
the implementation of the required monitoring and mitigation described
in the IHA will have a negligible impact on the affected species or
stocks of marine mammals in the study area. See L-DEO's Supplemental
EA.
Comment 12: CSI states that it is well aware that the L-DEO, NSF,
and other project supporters represent powerful influences that NMFS
must respect. However, CSI trusts that these rational influences also
recognize the overwhelming need to define and mitigate anthropogenic
affects on the marine environment, with their rapidly accelerating
influences on the planet and eventually human societies. Is it
necessary to do significant, irrevocable damage to marine life in order
to understand geophysical processes?
Response: After issuance of the proposed IHA, L-DEO modified the
cruise plan and adopted more precautionary monitoring and mitigation
measures in the study area. NMFS believes that L-DEO's revised survey
as well as the implementation of the required monitoring and mitigation
described in the IHA will have a negligible impact on the affected
species or stocks of marine mammals in the study area.
On March 31, 2009, NMFS prepared a Finding of No Significant Impact
for L-DEO's marine geophysical survey in SE Asia. NMFS determined that
the issuance of an IHA for the take, by harassment, of small numbers of
marine mammals incidental to L-DEO's March-July, 2009, seismic survey
in SE Asia will not significantly impact the quality of the human
environment.
Comment 13: CSI states that in lieu of such loft concerns economic
efficiency is an excellent rationale for increased support of
appropriate science to
[[Page 41265]]
determine adequate mitigations. Without better science this and future
proposals will face further challenges that will cause delays in the L-
DEO schedule that are likely to have economic consequence. The time and
financial loss is neither the fault of the process or the
responsibility of NMFS. Why not do the job responsibly?
Response: NMFS acknowledges CSI's comments. An authorization for
incidental taking of marine mammals shall be granted if NMFS finds that
the taking will have a negligible impact on the species or stock(s),
will have an unmitigable adverse impact on the availability of the
species or stock(s) for subsistence uses (where relevant), and if the
permissible methods of taking and requirements pertaining to the
mitigation, monitoring, and reporting of such takings are set forth.
After issuance of the proposed IHA, L-DEO modified the cruise plan
and adopted more precautionary monitoring and mitigation measures in
the study area. NMFS believes that L-DEO's revised survey as well as
the implementation of the required monitoring and mitigation described
in the IHA will have a negligible impact on the affected species or
stocks of marine mammals in the study area. NMFS and the applicant (L-
DEO) have fulfilled their responsibilities under the MMPA and ESA for
the issuance of the subject IHA.
Comment 14: CSI states that the fundamental point of CSI's comment
and many others, is that this L-DEO project does not qualify for an
IHA, according to the criteria at www.nmfs.noaa.gov/pr/permits/incidental.htm. The fact that previous L-DEO projects received IHAs
does not provide a precedent under which this proposal also should
receive an IHA, because no matter how NMFS rationalized those past IHAs
this proposal is different, different in scale, scope, and expertise
represented by the formal comments and less public complaints it has
generated from scientific world authorities and regional and species
experts. If these people had been consulted by LGL, the inadequate EA
and request would never have been submitted for an IHA. The original
intent of the IHA process was to expedite some requests, not all
requests. Not this request.
Response: NMFS disagrees with CSI's comments. L-DEO's marine
geophysical survey in SE Asia, March to July 2009, qualifies for an IHA
according to the criteria on the NMFS Office of Protected Resources
Incidental Take Authorizations Web site. Portions of L-DEO's project
occurs on the high seas, which is applicable to the MMPA and ESA.
Section 101(a)(5)(D) of the MMPA established an expedited process by
which citizens of the U.S. can apply for an authorization to
incidentally take small numbers of marine mammals by harassment.
After issuance of the proposed IHA, L-DEO modified the cruise plan
and adopted more precautionary monitoring and mitigation measures in
the study area. NMFS believes that L-DEO's revised survey as well as
the implementation of the required monitoring and mitigation described
in the IHA will have a negligible impact on the affected species or
stocks of marine mammals in the study area.
Comment 15: CSI states that there is little knowledge available for
most of the species that inhabit the waters of SE Asia. Even the most
basic knowledge about the presence/absence of species is incomplete.
Only a small proportion of the large expanse of sea in the region (and
mostly coastal waters) has been surveyed systematically for marine
mammals. Few estimates of abundance or distribution exists for SE Asian
marine mammals an in most cases, this information is for a limited
region, often bounded by political rather than biological borders. What
little is known clearly shows the region to be an area with a high
diversity of marine mammal (and other marine) species.
Response: NMFS agrees that the SE Asia region is likely to have a
high diversity of marine mammal species and that impacts on marine
mammals should be assessed on the population or stock unit level
whenever possible. L-DEO's IHA application provides information on
stock abundance in SE Asia (when available), larger water bodies (such
as the North Pacific Ocean), and the Eastern Tropical Pacific Ocean (if
data was unavailable). NMFS believes that these data are the best
scientific information available for estimating impacts on marine
mammal species and stocks. However, Congress recognized that
information on marine mammal stock abundance may not always be
satisfactory. When information is lacking to define a particular
population or stock of marine mammals then impacts are to be assessed
with respect to the species as a whole (54 FR 40338, September 29,
1989). See relevant discussions throughout this document and L-DEO's
Supplemental EA.
Comment 16: CSI states that the study area is a region where marine
mammals are facing a myriad of serious threats that have made the
continued existence of several marine mammal populations and possibly
some species uncertain (note: some of the same threats and activities
have resulted in the recent `functional extinction' of the baiji
(Turvey et al. 2007), which is endemic to the Yangtze River of China).
Response: L-DEO's EA acknowledges that there are numerous threats
to cetaceans in SE Asia including vessel traffic, habitat loss, oil and
gas industry, pollution, fisheries, and hunting.
After the issuance of the proposed IHA, L-DEO modified the cruise
plan and adopted more precautionary monitoring and mitigation measures.
NMFS believes that L-DEO's revised survey as well as the implementation
of the required monitoring and mitigation measures described in the IHA
will have a negligible impact on the affected species or stocks of
marine mammals in the study area. See L-DEO's EA and Supplemental EA.
Comment 17: CSI states that all small cetaceans in Taiwanese waters
are threatened by fishermen using hand-harpoons, bycatch in fishing
gear, and noise. Those that inhabit coastal waters of western Taiwan
also face habitat degradation, pollution, and possibly prey reduction.
Response: NMFS does not regulate activities (including fishing) in
Taiwanese waters. L-DEO's EA discusses direct and indirect effects on
marine mammals. The numerous threats to cetaceans in SE Asia include
vessel traffic, habitat loss, oil and gas industry, pollution,
fisheries, and hunting.
After the issuance of the proposed IHA, L-DEO modified the cruise
plan and adopted more precautionary monitoring and mitigation measures.
NMFS believes that L-DEO's revised survey as well as the implementation
of the required monitoring and mitigation measures described in the IHA
will have a negligible impact on the affected species or stocks of
marine mammals in the study area.
Comment 18: CSI states that some marine mammals have been reduced
to numbers so low that even minimal `takes' will have a large impact on
the remaining population.
Response: After the issuance of the proposed IHA, L-DEO modified
the cruise plan and adopted more precautionary monitoring and
mitigation measures. NMFS believes that L-DEO's revised survey as well
as the implementation of the required monitoring and mitigation
measures described in the IHA will have a negligible impact on the
affected species or stocks of marine mammals in the study area.
Comment 19: CSI states that a number of marine mammals are
discussed in their comments to NMFS based on what
[[Page 41266]]
is known about their biology, conservation status and threats in the
region. This does not imply other marine mammals that are not
specifically discussed in detail are ``safer'' from the seismic
surveys, in most cases, too little information is available to
understand the impacts, which may be as great as or greater than the
marine mammals discussed in detail in their comments to NMFS.
Response: NSF's and L-DEO's IHA application, EA, and Supplemental
EA sufficiently discusses the marine mammals species and the possible
impacts from seismic surveys in the SE Asia region. After issuance of
the proposed IHA, L-DEO modified the cruise plan and adopted more
precautionary monitoring and mitigation measures. NMFS believes that
the implementation of the required monitoring and mitigation measures
will result in a negligible impact on affected species and stocks of
marine mammals in the study area.
Comment 20: ETSSTAWG states that it should be noted that many
seismic surveys are conducted in the Taiwan region every year without
requesting IHAs. The actions of private oil and gas companies within
the EEZ's of other countries is beyond the jurisdiction of the MMPA,
thus they need no such U.S. authorizations. However, this means that L-
DEO could become a scapegoat for all survey operation in the region,
purely because they have to apply for authorization, as they will
clearly be operating partly on the high seas (and thus fall under MMPA
jurisdiction) and as they have government funding. This is
acknowledged, but until such time as NMFS enforcement confirms the
locations and tracks of every survey undertaken globally this situation
is unlikely to change.
Response: NMFS is aware of seismic surveys and other activities
undertaken worldwide that occur (that may result in incidental takes of
marine mammals) without requesting IHAs or LOAs. NMFS may grant IHAs
upon request by U.S. citizens who engage in a specified activity (other
than commercial fishing) within a specified geographical region. L-DEO
and NSF are considered U.S. citizens under the MMPA. The MMPA applies
to U.S. citizens in U.S. waters, and the high seas, but does not apply
or authorize the incidental take of marine mammals in the territorial
seas of foreign nations. The MMPA does not apply to non-U.S. citizens,
unless they are conducting a specified activity (other than commercial
fishing) that may result in incidental takes of marine mammals in U.S.
waters. NMFS can refer reports of possible violations of the MMPA and
this subject IHA issued to L-DEO to NOAA Enforcement for investigation.
The IHA is valid only for the Langseth's activities associated with
seismic survey operations that are specified in L-DEO's EA,
Supplemental EA, and IHA application. L-DEO is required to comply with
the IHA and the terms and conditions of the Incidental Take Statement
corresponding to NMFS' Biological Opinion. L-DEO and NSF will be
required to reinitiate consultation with NMFS if the identified action
is subsequently modified in a manner that causes an effect that was not
considered during the analysis for making the necessary determinations
for the issuance of the IHA. L-DEO is required to submit a draft report
on all activities and monitoring results to the Office of Protected
Resources, NMFS, within 90 days of the completion of the Langseth's
cruise in SE Asia. The report must contain and summarize information
stated in the IHA issued to L-DEO.
Comment 21: WaH is aware that this L-DEO survey proposal is one of
a very small number of requests for authorization for geophysical
surveys while other user groups, including the oil and gas industry,
are not carrying out such EAs or are not subjected to public scrutiny
in this way. Rather than allowing the focus to be limited to geological
surveys such as L-DEO's, WaH recommends that measures be taken to
ensure that all future marine seismic surveys (whether of an academic
or commercial nature) are made subject to the same level of scrutiny
and transparency, such as by requiring EAs or EISs to be submitted for
professional and public review and with all relevant documents
(including post-survey reports and relevant local permits,
authorizations and licenses) being made publicly available.
Response: All applications submitted to NMFS are subject to public
comment periods. During the public comment period, their NEPA documents
and incidental take authorization applications are available on the
NMFS Web site (https://www.nmfs.noaa.gov/pr/permits/incidental.htm) and
are reviewed by the Commission. NMFS does not force an agency or other
organization to apply for and consult on an incidental take
authorization under the MMPA.
General Opposition
Comment 22: A private citizen questioned why this research was
being conducted in SE Asia. The commenter also believes the U.S. should
not be doing work in the region.
Response: Dr. McIntosh and Dr. Wu, the principal investigators on
the seismic survey, state the primary purpose of the TAIGER project is
to investigate the fundamental processes of mountain building, which
plays a major role in shaping the face of the Earth. Oceanic island
chains, or arcs, along convergent tectonic plate boundaries result from
a process known as subduction where one of Earth's tectonic plates
slides beneath another as they move toward each other. As the lower
plate slides beneath the upper plate, its trajectory usually steepens
with depth and eventually reaches depths of several hundred (to greater
than 700) km. The arc is made up of a chain of volcanoes on the upper
plate, and is typically situated above the point where the lower plate
is at about 100 km (62 mi) depth. As this process of subduction and
volcanism continues through time (millions of years) the crust of the
upper plate becomes thicker, and develops properties more like
continental crust, which is much thicker and less dense than ocean
crust and allows for land surface above sea level. The results of many
studies indicates that much of the crust that forms Earth's continents
was accumulated through time by island arcs colliding with continents
leaving remnants of the arcs attached to the edge of the continents.
Despite this general interpretation, the actual processes of how this
happens, including growth of collisional mountain belts and deformation
of arc and continental crust, is poorly understood and poorly
documented. Ancient collision zones have been studied, but they have
typically undergone many stages of deformation and erosion, leaving
them difficult to interpret. Currently active arc-continent collision
zones include Taiwan, Papua New Guinea, and Timor. Of these active
collisions, Taiwan is currently the most active. Taiwan is also the
most favorable of these to examine the full spectrum of processes as a
plate boundary changes from oceanic subduction to arc-continent
collision. This transition is a major target of the TAIGER project
requiring that L-DEO obtain a series of crustal-scale seismic transects
from south of Taiwan, where subduction is active, to northern Taiwan,
where the collision has reached mature steady state.
One of the by-products of the collision in Taiwan is the generation
of frequent small earthquakes and less frequent, large, destructive
earthquakes. By using the relatively small signals from the Langseth
source array
[[Page 41267]]
(compared to those generated by nature) scientists can topographically
image the mountains and thereby localize the major breaks or faults
underneath the mountains and assess their seismic potential. In
addition to linear arrays of seismographs, the Langseth signals will
also be recorded, as an integrated TAIGER acquisition program, on over
200 land seismographs across the island and 20 OBSs, all of which have
been recording earthquakes. Scientists expect to produce the most
comprehensive subsurface images of the rapidly rising Taiwan mountains
with L-DEO's data. These images, along with seismicity recorded by L-
DEO's arrays, will form a greatly enhanced basis for evaluating
earthquake and tsunami potentials of Taiwan and can thus be used to
improve the safety and security of the human population at risk to
these phenomena.
A previous U.S.-Taiwan project (the 1995 TAICRUST project)
demonstrated the feasibility of the approach to be used in the TAIGER
project, but this project did not include significant seismic data
acquisition in the Taiwan Strait. Subsequent analysis showed that
seismic profiles across the Taiwan, recorded by seismographs in the
strait and on land in Taiwan, are necessary to determine the crustal
structure of the Taiwan collisional mountain belt. Thus, the principal
scientist's plans in the Taiwan Strait are one of the key elements
required for the success of the TAIGER project.
Comment 23: LINC objects to the IHA application and states that
other local NGOs have not had time to respond due to the lack of
sufficient notice. LINC is concerned that NMFS is eager to approve the
L-DEO application and authorize destructive activities in the SE Asia
region without verifying that L-DEO has complied with relevant local
conservation laws and regulations. LINC strongly urges the NMFS to
reject the application of L-DEO until it can be proven that they have
(1) complied with local laws and regulations, and (2) have completed a
comprehensive consultation with local governments, scientists,
researchers, and NGOs based in this region. LINC states that the
approval of the current L-DEO application, as is, would demonstrate a
clear lack of concern for the conservation laws, threats, and
environmental protection efforts in this region.
Response: NMFS believes local NGOs have had sufficient time to
respond to the proposed IHA published in the Federal Register. A 30-day
comment period with a 15-day extension (for a total of 45 days) is more
than an adequate time period for the public to address concerns and
submit comments. The NMFS has received numerous comments from persons
and organizations located nationally and worldwide. Generally, under
the MMPA, NMFS may authorize the harassment of small numbers of marine
mammals incidental to an otherwise lawful activity, provided NMFS finds
that the taking will have a negligible impact on the species or
stock(s), will not have an unmitigable adverse impact on the
availability of the species or stock(s) for subsistence uses (where
relevant), and if the permissible methods of taking and requirements
pertaining to the mitigation, monitoring and reporting of such takings
are set forth to achieve the least practicable adverse impact. L-DEO
and NSF have consulted with the various governments in the action area.
To date, L-DEO and NSF have received foreign clearance notices from the
governments of the Philippines, Taiwan, and Japan. See International
Legal Compliance below.
Comment 24: Given the large volume of evidence for the association
between anthropogenic noise and disturbance in cetaceans and other
marine mammal, a precautionary approach is surely required (as
recommended by Gordon et al., 2004). AAF urges NMFS to consider the
application from L-DEO with information provided, and the findings and
recommendations of the independent reviews of the Eastern Taiwan Strait
Sousa Technical Advisory Working Group (ETSSTAWG) and others, in mind.
Response: NMFS has developed conservative monitoring, mitigation,
and reporting requirements in order to reduce the potential effects of
anthropogenic noise on marine mammals. L-DEO and NSF have considered
the numerous public comments and revised the seismic survey described
in its IHA application. L-DEO's Supplemental EA is in response to the
comments received by NMFS through the public comment period associated
with the IHA process. L-DEO considered the recommendations from several
independent reviewers including ETSSTAWG. NSF received no direct public
comments on the draft EA during (or after) the open comment period
November 14, 2008 through December 15, 2008. Included in L-DEO's
Supplemental EA are a number of changes to the survey design that were
made by L-DEO to address specific comments, some received by a number
of individuals and agencies, and to enhance measures already included
in the original documents to mitigate effects of the proposed survey on
marine mammals. NMFS has made its necessary determinations based on L-
DEO's revised seismic survey and Supplemental EA.
Comment 25: Several commenters requested that NMFS deny issuing the
IHA to L-DEO. They questioned: (1) The adequacy of L-DEO's scientific
research and lack of consultation with local experts; (2) the survey's
potential to expose ETS humpback dolphins to received levels of 180 dB
re 1 [mu]Pa (rms) which they believed could cause permanent
physiological damage, thus constituting at a minimum Level A
harassment; (3) the number of ETS humpback dolphins that L-DEO proposed
to harass, stating that the requested take of ETS humpback dolphins to
be harassed was likely to exceed a sustainable level of take for the
population; (4) the adequacy of the monitoring and mitigation measures
for endangered or cryptic species that may be vulnerable to noise
impacts (e.g., ETS humpback dolphin and finless porpoise); (5) the
timing of the surveys and their impacts on migration routes; (6) biased
and non-precautionary assumptions; and (7) the cumulative effects
analyses in the EA.
Response: NMFS disagrees with the commenters' argument that NMFS
should have denied L-DEO's application for an IHA.
(1) NMFS is charged with issuing IHAs for otherwise lawfully
activity. L-DEO's research is otherwise lawful. NMFS opened the
proposed IHA to public comment. L-DEO plans to conduct the seismic
survey along the Taiwan arc-continental collision in the China and
Philippine Seas. Taiwan is one of only a few sites of arc-continent
collision worldwide--one of the primary tectonic environments for
large-scale mountain building. The primary purpose for the TAIGER
project is to investigate the processes of mountain building, a
fundamental set of processes which plays a major role in shaping the
face of the Earth. The vicinity of Taiwan is particularly well-suited
for this type of study, because the collision can be observed at
different stages of its evolution, from incipient, to mature, and
finally to post-collision. As a result of its location in an ongoing
tectonic collision zone, Taiwan experiences a great number of
earthquakes; most are small, but many are large and destructive. This
project will provide a great deal of information about the nature of
the earthquakes around Taiwan and will lead to a better assessment of
earthquake hazards in the area. The information obtained from this
study will help the people and government of Taiwan to better prepare
[[Page 41268]]
for future seismic events and may thus mitigate some of the loss of
life and economic disruptions that will inevitably occur.
(2) NMFS disagrees with the commenter's characterization of the
potential risk to the ETS sub-population of Indo-Pacific humpback
dolphins. After the issuance of the proposed IHA, L-DEO negotiated with
the project's principal scientists to modify the cruise plan and adopt
more precautionary mitigation measures. L-DEO will limit seismic survey
lines to take place at least 20 km from the west coast of Taiwan,
except for in the passage between the Penghu Islands and the
Waishanding Jhou sandbar, where the survey will pass through the
approximately 17.1 km mid-line distance between the two possibly
sensitive areas, subject to the limitations imposed by other foreign
nations, to minimize the potential for exposing Indo-Pacific humpback
dolphins, finless porpoises, and other coastal species to SPLs greater
than or equal to 160 dB re 1 [mu]Pa (rms). Thus, the precautionary
buffer recommended by ETSSTAWG in their comments to NMFS will be
maintained, ``at least 13 km and perhaps a more precautionary 15 km of
the ETS Sousa population--meaning up to around 20 km from shore.'' L-
DEO will also shut-down the airgun array if an ETS Indo-Pacific
humpback dolphin is visually sighted regardless of the distance of the
animal(s) to the sound source. The array will not resume firing until
15 minutes after the last documented whale visual sighting.
(3) NMFS disagrees with the commenter's assertion that the
requested take of ETS Indo-Pacific humpback dolphins by harassment is
likely to exceed a sustainable level of take for the population. L-
DEO's seismic survey was modified after the issuance of the proposed
IHA to include more precautionary mitigation measures. The
incorporation of precautionary measures reduced the estimated number of
ETS Indo-Pacific humpback dolphins expected to be harassed to zero,
which is clearly a sustainable level of take for the sub-population.
(4) and (5) NMFS believes that the mitigation and monitoring
measures in the IHA are adequate to protect species of concern that may
be vulnerable to noise impacts. After issuance of the proposed IHA, L-
DEO modified the cruise plan and adopted more precautionary mitigation
measures, especially for species that are of particular concern and
have cryptic behaviors that may be vulnerable to noise impacts as well
as to address concerns on the timing of the surveys and their impacts
on migration routes. See Monitoring, Mitigation, Species of Particular
Concern, and Temporal and Spatial Avoidance sections below and L-DEO's
Supplemental EA for more information. NMFS has included requirements to
these effects in the IHA issued to L-DEO.
(6) After issuance of the proposed IHA, L-DEO modified the cruise
plan and adopted more precautionary mitigation measures to address
concerns of potential impacts of the seismic survey on affected species
and stocks of marine mammals in the study area. NMFS believes that L-
DEO's IHA application, EA, and Supplemental EA are not biased as they
adequately consider alternatives, and provides analysis on the affected
environment and environmental consequences of the study area.
(7) The EA adequately addresses the cumulative impacts of a
relatively short-term seismic airgun survey in relation to long-term
noise and events, such as vessel traffic, habitat loss, oil and gas
industry, pollution, fishing, hunting, and other human activities.
These other activities are long-term activities which are unaffected by
NMFS' action here. Nor does this action, when considered in light of
the other activities, become significant.
For more information, see further relevant discussions in this
notice, L-DEO's IHA application, EA, and Supplemental EA.
Comment 26: HSI states that while they appreciate L-DEO's efforts
to comply with the MMPA and the NEPA, HSI is concerned that this
request for an incidental harassment authorization is premature and
that in fact a letter of authorization for incidental take may be
required. HSUS/HSI strongly urges the NMFS to deny this request as
submitted and at a minimum to require L-DEO to resubmit its request
with an updated review of the region's marine mammals, a more complete
review of relevant litera