Incidental Takes of Marine Mammals During Specified Activities; Marine Geophysical Survey in the Northeast Pacific Ocean, August-October, 2009, 42861-42873 [E9-20492]
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Federal Register / Vol. 74, No. 163 / Tuesday, August 25, 2009 / Notices
section 703(a)(2) of the Act. A negative
ITC determination will result in the
investigation being terminated; see
section 703(a)(1) of the Act. Otherwise,
the investigation will proceed according
to statutory and regulatory time limits.
This notice is issued and published
pursuant to section 777(i) of the Act.
Dated: August 18, 2009.
Carole Showers,
Acting Deputy Assistant Secretary for Policy
and Negotiations.
Appendix I
Scope of the Investigation
Imports covered by this petition
consist of certain chemically bonded
(resin or pitch), magnesia carbon bricks
with a magnesia component of at least
70 percent magnesia (‘‘MgO’’) by
weight, regardless of the source of raw
materials for the MgO, with carbon
levels ranging from trace amounts to 30
percent by weight, regardless of
enhancements, (for example, magnesia
carbon bricks can be enhanced with
coating, grinding, tar impregnation or
coking, high temperature heat
treatments, anti–slip treatments or metal
casing) and regardless of whether or not
anti–oxidants are present (for example,
antioxidants can be added to the mix
from trace amounts to 15 percent by
weight as various metals, metal alloys,
and metal carbides). Certain magnesia
carbon bricks that are the subject of this
investigation are currently classifiable
under subheadings 6902.10.10.00,
6902.10.50.00, 6815.91.00.00, and
6815.99 of the Harmonized Tariff
Schedule of the United States (HTSUS).
While HTSUS subheadings are provided
for convenience and customs purposes,
the written description is dispositive.
[FR Doc. E9–20493 Filed 8–24–09; 8:45 am]
BILLING CODE 3510–DS–S
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XR07
pwalker on DSK8KYBLC1PROD with NOTICES
Endangered Species; File No. 14396
AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; receipt of application.
SUMMARY: Notice is hereby given that
the Delaware Department of Natural
Resources and Environmental ControlDivision of Fish and Wildlife, Dover,
Delaware, has applied in due form for
a permit to take shortnose sturgeon
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22:52 Aug 24, 2009
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(Acipenser brevirostrum) for purposes
of scientific research.
DATES: Written, telefaxed, or e-mail
comments must be received on or before
September 24, 2009.
ADDRESSES: The application and related
documents are available for review by
selecting ‘‘Records Open for Public
Comment’’ from the Features box on the
Applications and Permits for Protected
Species (APPS) home page, https://
apps.nmfs.noaa.gov/index.cfm, and
then selecting File No. 14396 from the
list of available applications. These
documents are also available for review
upon written request or by appointment
in the following office(s):
Permits, Conservation and Education
Division, Office of Protected Resources,
NMFS, 1315 East-West Highway, Room
13705, Silver Spring, MD 20910; phone
(301)713–2289; fax (301)713–0376; and
Northeast Region, NMFS, Protected
Resources Division, 55 Great Republic
Drive, Gloucester, MA 01930; phone
(978)281–9300; fax (978)281–9333.
Written comments or requests for a
public hearing on this application
should be mailed to the Chief, Permits,
Conservation and Education Division,
F/PR1, Office of Protected Resources,
NMFS, 1315 East-West Highway, Room
13705, Silver Spring, MD 20910. Those
individuals requesting a hearing should
set forth the specific reasons why a
hearing on this particular request would
be appropriate.
Comments may also be submitted by
facsimile at (301)713–0376, provided
the facsimile is confirmed by hard copy
submitted by mail and postmarked no
later than the closing date of the
comment period.
Comments may also be submitted by
e-mail. The mailbox address for
providing e-mail comments is
NMFS.Pr1Comments@noaa.gov. Include
in the subject line of the e-mail
comment the following document
identifier: File No. 14396.
FOR FURTHER INFORMATION CONTACT:
Malcolm Mohead or Kate Swails,
(301)713–2289.
SUPPLEMENTARY INFORMATION: The
subject permit is requested under the
authority of the Endangered Species Act
of 1973, as amended (ESA; 16 U.S.C.
1531 et seq.), and the regulations
governing the taking, importing, and
exporting of endangered and threatened
species (50 CFR 222–226).
The applicant is seeking a five-year
scientific research permit to conduct a
study of shortnose sturgeon in the
Delaware River. The primary study
objective would be to locate and
document nursery areas, individual
movement patterns, seasonal
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movements, home ranges, and habitats
of juvenile shortnose sturgeon through
the use of telemetry. This focus would
be in association with an ongoing
Atlantic sturgeon (Acipenser oxyrinchus
oxyrhinchus) study with similar
objectives. Up to 200 shortnose sturgeon
would be weighed, measured, examined
for tags, marked with Passive Integrated
Transponder (PIT) tags and Floy tags,
and released. Up to 15 early stage
juvenile shortnose sturgeon would also
be anesthetized and implanted with
acoustic transmitters if they are of
suitable size. A total of one
unintentional mortality is requested
over the five year term of the project
which is scheduled to take place from
March 1 to December 15.
Dated: August 19, 2009.
P. Michael Payne,
Chief, Permits, Conservation and Education
Division, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. E9–20491 Filed 8–24–09; 8:45 am]
BILLING CODE 3510–22–S
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XQ20
Incidental Takes of Marine Mammals
During Specified Activities; Marine
Geophysical Survey in the Northeast
Pacific Ocean, August–October, 2009
AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; issuance of incidental
take authorization.
SUMMARY: In accordance with the
Marine Mammal Protection Act
(MMPA) regulations, notification is
hereby given that NMFS has issued an
Incidental Harassment Authorization
(IHA) to Lamont-Doherty Earth
Observatory (L-DEO), a part of Columbia
University, to take small numbers of
marine mammals, by Level B
harassment only, incidental to
conducting a marine seismic survey in
the northeast Pacific Ocean.
DATES: Effective August 19, 2009
through October 13, 2009.
ADDRESSES: A copy of the IHA and the
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
20910–3225 or by telephoning the
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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 by visiting the
internet at: https://www.nmfs.noaa.gov/
pr/permits/incidental.htm#applications.
Documents cited in this notice may be
viewed, by appointment, during regular
business hours, at the aforementioned
address.
FOR FURTHER INFORMATION CONTACT:
Jeannine Cody, Office of Protected
Resources, NMFS, (301) 713–2289 ext
113.
SUPPLEMENTARY INFORMATION:
Background
Section 101(a)(5)(D) of the MMPA (16
U.S.C. 1371 (a)(5)(D)) directs the
Secretary of Commerce (Secretary) to
allow, upon request, the incidental, but
not intentional, taking of marine
mammals, for periods of not more than
one year, by United States citizens who
engage in a specified activity (other than
commercial fishing) within a specified
geographical region if certain findings
are made and, if the taking is limited to
harassment, a notice of a proposed
authorization is provided to the public
for review.
Authorization for incidental taking of
small numbers of marine mammals shall
be granted if NMFS finds that the taking
will have a negligible impact on the
species or stock(s), and will not have an
unmitigable adverse impact on the
availability of the species or stock(s) for
subsistence uses. The authorization
must set forth the permissible methods
of taking, other means of effecting the
least practicable adverse impact on the
species or stock and its habitat and
monitoring and reporting of such
takings. NMFS has defined ‘‘negligible
impact’’ in 50 CFR 216.103 as ’’...an
impact resulting from the specified
activity that cannot be reasonably
expected to, and is not reasonably likely
to, adversely affect the species or stock
through effects on annual rates of
recruitment or survival.’’
Section 101(a)(5)(D) of the MMPA
established an expedited process by
which citizens of the United States can
apply for an authorization 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
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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’’].
Section 101(a)(5)(D) of the MMPA
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. Not later than 45 days after
the close of the public comment period,
if the Secretary makes the findings set
forth in Section 101(a)(5)(D)(i) of the
MMPA, the Secretary shall issue or
deny issuance of the authorization with
appropriate conditions to meet the
requirements of clause 101(a)(5)(D)(ii) of
the MMPA.
Summary of Request
On February 11, 2009, NMFS received
an application from L-DEO for the
taking by Level B harassment only, of
small numbers of 33 species of marine
mammals incidental to conducting a
marine seismic survey within the
Exclusive Economic Zone (EEZ) of
Canada in the northeast Pacific Ocean
during August through October 2009. LDEO, with research funding from the
NSF, is conducting the geophysical data
acquisition activities. NMFS outlined
the purpose of the research program in
a previous notice for the proposed IHA
(74 FR 21631, May 8, 2009).
Description of the Specified Activity
The planned survey will involve one
source vessel, the R/V Marcus G.
Langseth (Langseth), a seismic research
vessel owned by the NSF and operated
by L-DEO. The proposed project is
scheduled to commence on August 19,
2009, and scheduled to end on October
13, 2009. The vessel will depart Astoria,
Oregon on August 19, 2009 for transit to
the Endeavor MPA, between 47–48° N.
and 128–130° W.
To obtain high-resolution threedimensional (3D) structures of the Lau
Basin’s magmatic systems and thermal
structures, the Langseth will deploy a
towed array of 36 airguns with a total
discharge volume of approximately
6,600 cubic inches (in3). The array
configuration consists of four identical
linear arrays or strings, with 10 airguns
on each string. L-DEO will distribute the
four airgun strings across an
approximate area of 24 x 16 meters (m)
(79 x 52 feet (ft)) behind the Langseth
which will tow the array approximately
50–100 m (164–328 ft) behind the vessel
at a tow-depth of 9–15 m (29.5–49.2 ft).
The airgun array will fire for a brief (0.1
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second (s)) pulse every 180 s. The array
will remain silent at all other times.
The seismic study (e.g., equipment
testing, startup, line changes, repeat
coverage of any areas, and equipment
recovery) will take place in deep
(between 1200 and 3000 m, 3,280 feet
(ft) and 1.8 miles (mi)) water and will
require approximately 10 days to
complete 12 transects of variable lengths
totaling 1800 km of survey lines. Data
acquisition will include approximately
240 hours of airgun operation. Please
see L-DEO’s application for more
detailed information. The exact dates of
the activities will depend on logistics,
weather conditions, and the need to
repeat some lines if data quality is
substandard.
L-DEO will conduct all geophysical
data acquisition activities with on-board
assistance by the scientists who have
proposed the NSF-funded study. The
scientific team consists of NSF, is
conducting the geophysical data
acquisition activities with onboard
assistance by Drs. Toomey and Hooft
from the University of Oregon, and Dr.
Wilcock from the University of
Washington. The vessel will be selfcontained, and the crew will live aboard
the vessel for the entire cruise.
NMFS has provided a more detailed
description of the authorized action,
including vessel and acoustic source
specifications, in a previous notice for
the proposed IHA (74 FR 21631, May 8,
2009).
Safety Radii
The distance from the sound source at
which an animal would be exposed to
these different received sound levels
may be estimated and is typically
referred to as safety radii. These safety
radii are specifically used to help NMFS
estimate the number of marine
mammals likely to be harassed by the
proposed activity and in deciding how
close a marine mammal may approach
an operating sound source before the
applicant will be required to powerdown or shut down the sound source.
L-DEO’s acoustic models predict
received sound levels in relation to
distance and direction from the 36–
airgun array in order to estimate the
safety radii around their operations. LDEO’s model is based on empirical data
gathered during the acoustic calibration
study of the R/V Maurice Ewing’s
(Ewing) array of 20 airguns (total volume
8600 in3) conducted in the northern
Gulf of Mexico in 2003. L-DEO provides
a more detailed description of the
modeling effort and calculations of the
safety radii in the previous notice for
the proposed IHA (74 FR 21631, May 8,
2009), Section I of L-DEO’s IHA
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application, and in Appendix A of the
Environmental Assessment report
prepared by LGL Limited environmental
research associates (LGL) on behalf of
NSF. NMFS has determined that the
foregoing data and studies represent the
best scientific evidence available a the
present time.
Using the modeled distances and
various correction factors, Table 1
outlines the predicted distances at
which three root mean square (rms)
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sound levels (190 decibels (dB), 180 dB,
and 160 dB) are expected to be received
from the 36–airgun array and a single
airgun operating in water greater than
1000 m (3,820 ft) in depth.
Predicted RMS Distances (m)
Source and Volume
Tow Depth (m)
190 dB
Single Bolt airgun 40 in3
4 strings 36 airguns 6600 in3
160 dB
12
220
300
340
380
6–15*
6
9
12
15
180 dB
40
710
950
1120
1220
385
4670
6000
6850
7690
*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.
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Comments and Responses
NMFS published a notice of receipt of
the L-DEO application and proposed
IHA in the Federal Register on May 8,
2009 (74 FR 21631). During the
comment period, NMFS received
comments from the Marine Mammal
Commission (Commission), Cetacean
Society International (CSI); and the
Wild at Heart Legal Defense Association
(WAHLDA). Following are the
comments from the Commission, CSI,
WAHLDA and NMFS’ responses.
Comment 1: The Commission
recommends that NMFS provide
additional justification for its
preliminary determination that the
planned monitoring program will be
sufficient to detect, with a high level of
confidence, all marine mammals within
or entering the identified safety zones;
as such monitoring is essential for
determining whether animals are being
taken in unanticipated ways and
unexpected numbers.
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 radii. 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
visually monitor marine mammals and
conduct passive acoustic monitoring
(PAM).
The Langseth’s high observation
tower is a suitable platform for
conducting marine mammal
observations. When stationed on the
observation platform, the MMO’s eye
level will be approximately 18 m (59 ft)
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above sea level, providing a panoramic
view around the entire vessel. During
the daytime, the MMO(s) will scan the
area around the vessel systematically
using reticle binoculars (e.g., 7 x 50
Fujinon), big-eye binoculars (25 x 150),
and the naked eye. The platform of the
Langseth is high enough that, in good
weather, MMOs can see out to 8.9 nm
(16.5 km, 10.2 mi). All of the 180–dB
safety radii that MMOs will monitor
during ramp-ups and power-downs are
less than 2 km (1.1 nm, 1.2 mi).
MMOs will use night vision devices
(NVDs) (ITT F500 Series Generation 3
binocular-image intensifier or
equivalent), during dusk or nighttime,
when required. Finally, L-DEO will
provide laser rangefinding binoculars
(Leica LRF 1200 laser rangefinder or
equivalent) to MMOs to assist with
distance estimation. MMOs estimate
that visual detection from the ship is
between 150 and 250 m (492 and 820 ft)
using NVDs and about 30 m (98.4 ft)
with the naked eye, which are affected
by ambient lighting conditions, sea
state, and thermal factors.
The Langseth will complement visual
observations of marine mammals with
an acoustical monitoring program. LDEO will use a PAM system to improve
detection, identification, localization,
and tracking of marine mammals. The
acoustic monitoring will alert visual
observers (if on duty) when vocalizing
cetaceans are detected. When an MMO
detects a vocalization while visual
observations are in progress, the
acoustic MMO will contact the visual
MMO immediately, to alert him/her to
the presence of cetaceans (if they have
not already been seen), and to initiate a
power down or shut down, if required.
The theoretical detection distance of
this PAM system is tens of kilometers
and it has reliable detection rates out to
3 km (1.6 nm) and more limited ability
out to tens of kilometers. During the
Ewing’s cruise in the Gulf of Mexico in
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2003, MMOs detected marine mammals
at a distance of approximately 10 km
(5.4 nm) from the vessel and identified
them to species level at approximately
5 km (2.7 nm) from the vessel, though
the bridge of that vessel was only 11 m
(36 ft) above the water (vs. the Langseth,
which is 18 m (59 ft) above sea level).
The likelihood of MMOs visual
detecting a marine mammal at night is
significantly lower than the ability to
detect any species during the day.
However, the PAM operates equally as
effective at night as during the day, and
does not depend on good visibility.
The Langseth will not start up the
airguns unless the MMO can visibly
detect the safety range for the 30
minutes prior (i.e., not at night) to start
up. In all cases at night, the Langseth
will already be operating the airguns.
NMFS believes that operating the
airguns at night will cause many
cetaceans to avoid the vessel; thus
reducing the number of cetaceans likely
to come within the safety radii.
Additionally, all of the safety radii in
deep water depths are smaller than 2 km
(1.1 nm, 1.2 mi) and fall easily within
the reliable detection capabilities of the
PAM.
Comment 2: The Commission
recommends that NMFS clarify the
qualifier ‘‘when feasible’’ with respect
to: (1) using two marine mammal visual
observers to monitor the exclusion zone
for marine mammals during daytime
operations and nighttime start-ups of
the airguns; and (2) using marine
mammal visual observers during
daytime periods to compare sighting
rates and animal behavior during times
when the seismic airguns are operating
and times when they are not.
Response: NMFS considers whether a
particular mitigation is capable of being
effected, done, or executed (i.e.,
feasible). For this IHA, the qualifier
‘‘feasible’’ is only applicable when the
seismic system is not operating. It does
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not apply during seismic operations
(Permit, P.5; Condition 8(a)(i).
NMFS’ consideration of practicability
includes (among other relevant
considerations) economic and
technological feasibility (see 50 CFR
216.104(a)(11)). NMFS believes that the
IHA’s mitigation and monitoring
measures are complete to the fullest
extent practicable, and ensure that the
takings will be limited to harassment
and will result in a negligible impact on
the affected species or stocks of marine
mammals.
The Langseth is utilizing a team of
trained marine mammal observers
(MMO) to both visually monitor from
the high observation tower of the
Langseth and to conduct PAM. L-DEO
will utilize two (except during meal
times), NMFS-qualified, vessel-based
marine mammal visual observers
(MMVO) 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 (7x50 Fujinon), big-eye
binoculars (25x150), and night vision
devices to scan the area around the
vessel. MMVOs 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
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 3: The Commission
recommends that the monitoring period
prior to the initiation of seismic
activities and prior to the resumption of
airgun activities after a power-down be
extended to one hour.
Response: NMFS believes that 30
minutes is an adequate length of time
for monitoring prior to the start-up of
airguns. The IHA requires that the
MMOs monitor the area for at least 30
minutes prior to starting the airgun
array (day or night) to ensure that no
marine mammals are seen within the
safety zone before a seismic survey
commences. The Langseth’s ramp up
protocol begins with the smallest gun in
the array and adds additional airguns in
a sequence such that the source level of
the array will increase in steps not
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exceeding approximately 6 dB per 5–
min period over a total duration of 20–
30 minutes. Thus, the total time of
monitoring prior to start-up of any but
the smallest array is effectively longer
than 30 minutes. In many cases MMOs
are making observations during times
when sonar is not being operated and
will actually be observing the area prior
to the 30–minute observation period.
Comment 4: The Commission
recommends that NMFS require that
observations be made during all rampup procedures to gather the data needed
to analyze and provide a report on the
effectiveness of this method as a
mitigation measure.
Response: The IHA requires L-DEO to
submit a draft and final report on all
activities and monitoring results to the
NMFS, Office of Protected Resources,
within 90 days after the expiration of
the IHA. NMFS will post the report at:
https://www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications.
This report: (1) must include an
estimate of the number (by species) of
marine mammals that are known to
have been exposed to the seismic
activity (visual observation) at received
levels greater than or equal to 160 dB re
1 μPa (rms) and/or 180 dB re 1 μPa (rms)
with a discussion of any specific
behaviors those individuals exhibited;
and (2) must also include an estimate of
the number of marine mammals that
may have been exposed to the seismic
activity at received levels greater than or
equal to 160 dB re 1 μPa (rms) and/or
180 dB re 1 μPa (rms) with a discussion
of the nature of the probable
consequences of that exposure on the
individuals that have been exposed.
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 5: It is expected that
Canada will have consulted and
commented on this proposal, and CSI
respectfully requests a link to those
documents for review.
Response: NMFS received no
comments from the Canadian
government or from any Canadian
organization during the public comment
period. However, the terms and
conditions of the IHA encourage NSF to
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coordinate with the Canadian
government regarding the proposed
seismic activity.
Comment 6: While not relevant to the
MMPA, it should be noted that 12
species found nowhere else in the world
have been identified at the Endeavour
Hydrothermal Vents. Given that the
potential for deleterious acoustic
impacts on invertebrates from the LDEO survey is almost totally unknown,
CSI specifically requests that NMFS
require L-DEO and the NSF to support
a survey of the site sufficient to
document whether or not these
extremely limited species were
impacted by the experiment.
Response: NMFS’ support of a postseismic survey of invertebrates is not
germane to this Federal action under the
MMPA. NMFS acknowledges that at
least 12 species are endemic to the
Endeavour site. However, the area is
dynamic, and the natural variability
within the hydrothermal vents is high.
Although OBS placement will disrupt a
very small area of seafloor habitat and
may disturb benthic invertebrates, the
impacts are expected to be localized and
transitory. NMFS does not expect that
the placement of OBS would have
adverse effects beyond naturally
occurring changes in this environment,
and any effects of the planned activity
on ocean and coastal habitats are
expected to be negligible.
NSF’s EA (and associated report)
analyzed the potential for the seismic
survey activity to affect ecosystem
features and biodiversity components,
including fish, invertebrates, seabirds,
and sea turtles. NMFS’ evaluation
indicates that any direct or indirect
effects of the action would not result in
a substantial impact on biodiversity or
ecosystem function. In particular, the
potential for effects to these resources
are considered here with regard to the
potential effects on diversity or
functions that may serve as essential
components of marine mammal
habitats. Most effects are considered to
be short-term and unlikely to affect
normal ecosystem function or
predatory/prey relationships; therefore,
NMFS believes that there will not be a
substantial impact on marine life
biodiversity associated with the
Endeavor hydrothermal vent, the
Endeavor MPA, or on the normal
function of the nearshore or offshore
environment.
Comment 7: The time between NMFS’
first awareness of an L-DEO application
and the start of the scheduled survey
does not allow for significant changes to
the operation without extraordinary
economic hardship on the applicant,
and that creates pressure on NMFS to
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authorize operations based on cost. CSI
and others question whether this
economic and practical pressure might
influence NMFS’ final decision relating
to an IHA; might a project be authorized
to continue, despite a problem, because
of the cost of fixing it?
Response: Section 101(a)(5)(D) of the
MMPA 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. Not later than 45 days after
the close of the public comment period,
if the Secretary makes the findings set
forth in Section 101(a)(5)(D)(i) of the
MMPA, the Secretary shall issue or
deny issuance of the authorization with
appropriate conditions to meet the
requirements of clause 101(a)(5)(D)(ii) of
the MMPA.
The NMFS, OPR, Permits,
Conservation, and Education Division
has diligently processed L-DEO’s
application within the statutory
timeframe (120 days) for an IHA under
the MMPA. The Division deemed the
application complete on May 1, 2009;
published a notice of receipt and
request for comments in the Federal
Register on May 8, 2009 (74 FR 21631);
and issued the IHA on August 19, 2009.
NMFS received no public comments
requesting L-DEO to significantly alter
the survey’s schedule or institute major
operational changes.
L-DEO’s proposed survey did not
require substantial changes to the cruise
plan or survey tracklines. As stated in
this document, NMFS shall grant an
IHA to L-DEO if NMFS finds that
incidental taking of marine mammals
will have a negligible impact on the
species or stock(s) and will not have an
unmitigable adverse impact on the
availability of the species or stock(s) for
subsistence uses and if the permissible
methods of taking and requirements
pertaining to the mitigation, monitoring
and reporting of such taking are set
forth.
NMFS evaluates each IHA application
independent of the cost of the proposed
action, as this is not relevant to NMFS’
determination of negligible impact or
unmitigable adverse impact on the
availability of the species or stock(s) for
subsistence uses.
For previously authorized IHAs,
NMFS has required applicants to
reschedule cruises; to modify survey
tracklines; incorporate new temporal
and spatial avoidance requirements; and
to institute more precautionary
measures to mitigate against the
potential effects of the action on marine
mammals.
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Comment 8: L-DEO should contract
openly with regional authorities and
experts during the initial planning and
scheduling phase, thereby building the
project around the ‘‘best science’’
available. This amplifies the importance
of the public comment period beyond a
mere statutory requirement.
Response: NMFS acknowledges CSI’s
request and has forwarded your
comment to NSF and L-DEO. If a CSI
representative requests to comment on
the initial planning and scheduling
phases, they should discuss this directly
with a representative from NSF and LDEO.
Comment 9: The Office of Protected
Resources (OPR) has not processed the
application fast enough so that
necessary changes brought to light
through the public comment period
might be applied with less onerous
scheduling and operational changes.
Response: The NMFS, OPR, Permits,
Conservation, and Education Division
has diligently processed L-DEO’s
application within the statutory
timeframe (120 days) for an IHA under
the MMPA. The Division deemed the
application complete on May 1, 2009;
published a notice of receipt and
request for comments in the Federal
Register on May 8, 2009 (74 FR 21631);
and issued the IHA on August 19, 2009.
NMFS received no public comments
requesting L-DEO to significantly alter
the survey’s schedule or institute major
operational changes.
Comment 10: CSI recognizes that OPR
may be required to supplement an
Application with an Endangered
Species Act of 1973 (ESA; 16 U.S.C.
1531 et seq.) section 7 consultation,
Biological Opinion and Environmental
Assessment, all of which take time. This
ETOMO Application was received
February 11, 2009, the Federal Register
Notice was published May 8, 2009, and
we doubt there is time between the June
8, 2009, close of public comments and
the start date of August 19, 2009 for LDEO to adjust to potentially required
changes in an IHA brought to light
within the comment period. From
recent experience the IHA can be
expected to be issued close to the start
date, making changes even more
onerous. In other words, will an IHA be
authorized in spite of issues, because of
the cost to make it right? CSI is not
accusing either OPR or L-DEO, but we
are asking that even the appearance of
the potential be removed.
Response: See NMFS’ response to
Comment 9. NMFS disagrees with the
commenter’s views on the timeliness of
processing of the application. The OPR
received the application on February 11,
2009. However, the Permits,
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Conservation, and Education Division
(PR1) deemed the application
incomplete under the MMPA and
requested additional information from
L-DEO (See 50 CFR 216.104(b)(1) which
states that NMFS must determine the
adequacy and completeness of an
application prior to initiating the public
review process). PR1 deemed the
application complete on May 1, 2009.
Pursuant to the MMPA, NMFS
published a notice of receipt and
request for comments in the Federal
Register on May 8, 2009 (74 FR 21631),
within one week of determining that the
application was complete. Not later than
45 days after the close of the public
comment period, if the Secretary makes
the findings set forth in Section
101(a)(5)(D)(i) of the MMPA, the
Secretary shall issue or deny issuance of
the authorization with appropriate
conditions to meet the requirements of
clause 101(a)(5)(D)(ii). NMFS issued the
IHA on (August19, 2009) within the
required MMPA statutory timeframe of
120 days.
Regarding the ESA section 7
consultation, the Office of Protected
Resources, Endangered Species Division
(PR3) determined that the information
provided by the NSF and L-DEO was
sufficient to initiate formal consultation
under the ESA on April 16, 2009. On
August 18, 2009, NMFS issued a
Biological Opinion (BiOp) and
concluded that the issuance of the IHA
was not likely to jeopardize the
continued existence of the humpback
(Megaptera novaeangliae), sei
(Balaenoptera borealis), fin
(Balaenoptera physalus), blue
(Balaenoptera musculus), and sperm
(Physeter macrocephalus) whales.
NMFS issued the BiOp within the ESA
statutory timeframe of 135 days. NMFS
included the BiOp’s Terms and
Conditions of the Incidental Take
Statement as mitigation measures in the
IHA.
Comment 11: The solution CSI
respectfully asks both OPR and NMFS
for is a longer base time between
application and start date. It is clear that
L-DEO will be at this for a long time,
and schedules must be set for 2010 and
beyond.
Response: See NMFS’ responses to
Comments 9 and 10.
Comment 12: L-DEO’s current process
depends almost entirely upon the
validity of the assumptions and
assessments from L-DEO’s in-house and
contracted analysis, which have been
proven to be inadequate. Perhaps
recognizing this, L-DEO requested
consultations with the South Pacific
Whale Research Consortium (SPWRC)
before the Tonga survey, but demanded
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confidentiality, which SPWRC refused.
L-DEO Tonga went on anyway, without
that expert assistance.
Response: NMFS cannot speak to LDEO’s consultations with the SPWRC
and recommends that CSI should
discuss their concerns with a
representative from L-DEO.
Comment 13: The L-DEO process
failed with the L-DEO TAIGER survey in
Southeast Asia, as public comments
were received from concerned regional
authorities and experts about several
issues. One issue required an amended
IHA, and the project was delayed
accordingly, but the literally last minute
public process should not have been the
impetus. L-DEO would have precluded
the issues by contracting with the wellknown experts that were forced to
express their concerns only during the
public comment period. Taiwan’s
renewed, potentially threatening
interest in the project only came about
because the regional experts were
seeking ways to have their concerns
noted. Why not just hire the local
experts and start earlier?
Response: The Canadian ETOMO
survey is a separate action from the
TAIGER survey. NMFS acknowledges
CSI’s concerns and refers the
commenter to 74 FR 41260, August 14,
2009, for information on the IHA for the
L-DEO TAIGER survey.
Comment 14: The ETOMO
Application should not be ‘‘easy’’
because there are no systematically
collected data on cetacean distribution
and abundance in the proposed survey
region.
Response: NMFS recognizes that
absence of evidence is not the same as
having no effect or impact on the
affected marine mammal species or
stocks. 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 L-DEO’s
application (74 FR 21631, May 8, 2009);
(2) the EA; (3) the BiOp and ITS; and (4)
numerous and salient public comments
received by NMFS during the public
comment period. 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 15: The absence of specific
data elevates the value of Kristin
Kaschner’s Ph.D. thesis, ‘‘Modelling and
mapping resource overlap between
marine mammals and fisheries on a
global scale,’’ (2004) which maps
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suitable habitat for marine mammals
around the world, ranking the Relative
Environmental Suitability (RES) for
each species. Kaschner shows that the
Endeavour MPA offers highly suitable
habitat for several species for which the
daylight visual observation mitigation
measures are inadequate. She predicts
that the habitat is likely to support sei
and sperm whales, which were caught
in the region historically. She predicts
that the habitat is likely to support
poorly studied beaked whales
(especially Cuvier’s [Ziphius
cavirostris]), which are thought to be
susceptible to seismic survey impacts.
And she predicts that the study area
offers good quality habitat for species
known to be recovering from 20th
century commercial whaling, namely
fin, humpback and sperm whales. But
this data is not ‘‘real.’’
Response: NMFS thanks the
commenter for this information and
considers all relevant public comments
before making a determination on the
issuance of the IHA. A detailed
discussion of the potential effects of this
action on marine mammal habitat, was
included in the notice of the proposed
IHA (74 FR 21631, May 8, 2009). Based
on the discussion in the proposed IHA
notice, the authorized operations are not
expected to have any habitat-related
effects that could cause significant or
long-term consequences for individual
marine mammals or their populations or
stocks and 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.
Please note that NMFS’ Biological
Opinion concludes that the issuance of
the IHA was not likely to jeopardize the
continued existence of the humpback),
sei, fin, blue, and sperm (Physeter
macrocephalus) whales.
Comment 16: While science continues
to search for ways to get the necessary
data, L-DEO and NSF will continue to
believe that their seismic surveys have
no significant effect. It is expected that
NMFS will find ‘‘that the taking will
have a negligible impact on the species
or stock(s)’’ despite the lack of real
information. The absence of proof of
harm is not the same as proving that
there is no harm.
Response: See NMFS’ response to
Comment 14.
Comment 17: First, it has not been
adequately explained in the Draft
Environmental Assessment why the ‘‘No
Action’’ alternative might be rejected in
favor of the project, which, according to
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the proponent’s own assessment, has
the potential to harass several thousand
cetaceans, including eight species
described in the notice as being listed as
endangered under the U.S. Endangered
Species Act. That the acquisition of data
concerning one natural phenomenon
(e.g. ‘‘the sub-seafloor structure of
volcanic and hydrothermal features that
form as a result of movements of the
Earth’s plates’’ (DEA, p2)) should
increase the threat to the existence of
another natural phenomenon (e.g. a
species of whale) of equally great (if less
generously funded) academic interest is
an illogical and tragic course of action.
It should be noted that it has not been
proven that knowledge of the subseafloor structure is of greater long-term
importance for the continuation of
human life on Earth than the
biodiversity upon which we are very
much dependent.
Response: The commenter’s
statements on assessing the value of
acquiring information on one natural
phenomena (geophysical) versus
another natural phenomena
(biodiversity) are not germane to NMFS’
federal action the issuance of an MMPA
authorization to L-DEO. Under section
101(a)(5)(D) of the MMPA, NMFS is
required to determine whether the
taking by the applicant’s specified
activity will have a negligible impact on
the affected marine mammal species or
population stocks. Alternatives
assessments are NMFS’ responsibility
under NEPA, not the MMPA. In that
regard, the NSF’s EA and associated EA
report contain adequate information on
the alternatives No Action, Another
Time, and Preferred Action. The
associated EA report provides a step-bystep analysis on how the NSF assessed
the alternatives, starting with (and
citing) the best scientific information
available on marine mammal
distribution and abundance and using
those data to make conservative
estimates on levels of take by
harassment and reasonable assumptions
on why no marine mammals are likely
to be harassed by this survey.
Comment 18: The assessment carried
out by LGL for this L-DEO project must
be treated with caution given the very
recent experience of the L-DEO seismic
survey currently underway in the waters
of southeast Asia, for which LGL
prepared an EA that understated the
numbers of cetaceans of certain species
that might be exposed to airgun noise
and the level of potential harassment,
misquoted the status of at least one
critically endangered population of
cetaceans (the Eastern Taiwan Strait
(ETS) Indo-Pacific humpback dolphins)
and resulted in transect lines running
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directly through the narrow habitat of
the ETS humpback dolphins and the
scheduling of surveys near the
Philippines that coincided ‘‘spatially
and temporally with the northward
migration of mothers with neonatal and
other young calves’’ (Anon, 2009), to
cite a few of the concerns raised by
scientists and NGOs during the
comment period for that project (e.g.
https://www.nmfs.noaa.gov/pr/pdfs/
permits/taiger_comments.pdf).
Response: NMFS acknowledges
WAHLDA’s concerns and refers the
commenter to 74 FR 41260, August 14,
2009, for information on the L-DEO
TAIGER survey.
NMFS closely follows NEPA
regulations and NOAA Administrative
Order 216–6 (Environmental Review
Procedures for Implementing the
National Environmental Policy Act, May
20, 1999) before making a determination
on whether it will adopt another Federal
agency’s NEPA document, or prepare its
own. Critical to this determination is the
quality of another agency’s NEPA
document, whether it fully addresses
the action proposed by NMFS the
issuance of an MMPA authorization to
L-DEO, and whether NMFS’ proposed
action is significant as defined in 40
CFR 1508.27 and NAO 216–6, section
6.01. As noted in the proposed
authorization notice (74 FR 21631, May
8, 2009), the DEA contained a complete
description of the proposed action and
identified alternatives to that action; a
description of the affected environment;
an assessment of impacts, including
unavoidable impacts, indirect impacts
and cumulative impacts; and the
measures proposed to reduce impacts to
the lowest level practicable. In
accordance with NAO 216–6, NMFS has
reviewed the information contained in
NSF’s EA, and associated EA report, and
determined that, while it accurately and
completely describes the alternatives
and the potential impacts, endangered
species and other marine life could be
impacted by the survey activities. As a
result, NMFS has identified additional
mitigation measures (e.g., mandatory
shut-downs for north Pacific right
whales) which are reflected in the final
IHA and the NMFS’ Finding of No
Significant Impact (FONSI).
Comment 19: An additional,
independent scientific review body is
urgently needed in order to improve the
quality of environmental assessment
and recommended actions for this and
all other seismic surveys.
Response: NMFS acknowledges
WAHLDA’s request and has forwarded
your comment to NSF and L-DEO.
Comment 20: The safety radii for this
project are used to decide how close a
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marine mammal may approach an
operating sound source before a powerdown or shut down is required. With
detection of marine mammals being
dependent upon the success of visual
and acoustic monitoring, it is clearly
essential that both forms of monitoring
are carried out in such a way as to
maximize the potential of detection.
However, the description of the
monitoring plans described in the FR
notice suggest once again that
worryingly minimal efforts to detect
cetaceans will be made.
Response: See NMFS’ response to
Comment 1. The Langseth is utilizing a
team of trained (MMVOs) to both
visually monitor from the high
observation tower of the Langseth and to
conduct passive acoustic monitoring.
When stationed on the observation
platform of the Langseth, the MMVO’s
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 8.9 nm (16.5 km) (the largest
safety radii is 7.7 km (4.2 nm)). Big eyes
are most effective at scanning the
horizon (for blows), while 7 x 50 reticle
binoculars are more effective closer in
(MMVOs also scan the area with the
naked eye). Additionally, MMVOs will
have a good view in all directions
around the entire vessel.
Under section 101(a)(5)(D) of the
MMPA, NMFS is required to determine
whether the taking by the applicant’s
specified activity will have a negligible
impact on the affected marine mammal
species or population stocks. The
monitoring and 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.
Comment 21: With a minimum of
only one marine mammal visual
observer (MMVO) being required to be
on duty during all daytime airgun
operations, and only two observers
being required to be on duty for only
thirty minutes before and during rampups (‘‘and when possible at other times’’
(DEA, p.3)) is clearly not a commitment)
the chances of detecting cetaceans in the
area (including the exclusion zone)
within which they may be harassed
(including level A and level B
harassment) will be limited. Neither one
nor two pairs of eyes will be capable of
effectively scanning all areas around the
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Langseth simultaneously for cetaceans
and turtles that is, if the aim of this
measure truly is to attempt to minimize
impacts on cetaceans and turtles. There
should at least be a sufficient number of
qualified, experienced visual observers
to simultaneously cover all areas of
water within the safety radii on duty
during all periods of use of noisegenerating seismic survey equipment
(including before and during ramp-ups
and at all other times of use).
Response: The IHA requires L-DEO to
utilize two (except during meal times),
NMFS-qualified, vessel-based marine
mammal visual observers (MMVO) to
watch for and monitor marine mammals
near the seismic source vessel during all
daytime airgun operations and before
and during start-ups of airguns day or
night. See NMFS’ response to
Comments 1 and 2 for a discussion of
visual and acoustic monitoring of the
safety radii.
Comment 22: The idea that passive
acoustic monitoring (PAM) should be
used during the day and night ‘‘when
practicable’’ (DEA, p. 3) again suggests
a reluctance to commit to applying these
measures to their greatest capability,
and a level of leniency that leaves room
for almost unlimited exceptions. If LDEO is serious about carrying out this
seismic survey at the risk of harassing
more than thirty marine mammal
species and intends to attempt to
mitigate potential impacts to the
(already extremely limited) extent that it
can, it should at least be committed to
use PAM at all times during the survey,
with no exceptions. (The operators’
need for rest, food or other activities can
be dealt with by increasing the number
of (qualified and experienced) staff on
duty and should not be used as a
justification for lower effort to detect
cetaceans using PAM).
Response: The IHA requires that LDEO operates the PAM system both
during the day and at night. The
requirement of PAM for marine
mammal detection is intended to
provide additional monitoring to the
standard visual monitoring by qualified
MMVOs. PAM is not to be solely used
for marine mammal monitoring and
detection for the survey and will not
replace visual monitoring. NMFS
believes that L-DEO will be able to
effectively monitor out to the 180 dB
isopleth.
Comment 23: More worrying still is
the fact that there appears, once again,
to be no restriction against using the
seismic survey equipment in the dark or
‘‘at night’’. The continuation of seismic
survey activity outside of daylight hours
severely reduces the already limited
possibility of detecting cetaceans in the
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vicinity, and effectively reduces
monitoring efforts to the use of PAM,
which will obviously not detect
cetaceans when they are not vocalizing
and will at certain times only be used
‘‘when practicable’’. It is strongly
recommended that no seismic survey
activity be carried out outside of
daylight hours during which the entire
safety radii are visible.
Response: The IHA requires that LDEO operates the PAM system both
during the day and at night. Regarding
cessation of seismic activity at night, LDEO has considered this
recommendation, and has 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 Endeavor cruise.
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.
The IHA prohibits the start of the
seismic source if the MMVOs cannot
view the entire safety radius for any
reason (darkness, fog, or rough seas).
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. MMVOs using night vision
devices (NVD) 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.
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.
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 24: The suggestion in the
DEA that ‘‘additional research studies
planned on the vessel for 2009 and
beyond’’ should be a major deciding
factor in whether the survey can be
rescheduled (which was also used as an
argument to support night-time surveys
for the SE Asia seismic survey) is not
considered a scientifically sound or
otherwise reasonable justification for
reducing already limited impact
mitigation measures. Scheduling should
be based on the necessary impact
mitigation measures, not vice versa.
Response: Under section 101(a)(5)(D)
of the MMPA, NMFS is required to
determine whether the taking by the
applicant’s specified activity will have a
negligible impact on the affected marine
mammal species or population stocks.
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.
As discussed in the EA report, the
scheduling of the Langseth makes the
best use of the vessel to support NSF’s
science mission. In the EA, NSF
concluded that L-DEO rescheduling the
survey to an alternative time would
offer minimal advantages or
disadvantages at the Endeavor location.
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.
Description of Marine Mammals in the
Activity Area
Thirty-three marine mammal species
may occur off the coast of British
Columbia, Canada, including 20
odontocetes (toothed cetaceans), 7
mysticetes (baleen whales), 5 pinnipeds,
and the sea otter (Enhydra sp.). In the
United States, sea otters are managed by
the U.S. Fish and Wildlife Service
(USFWS) and are unlikely to be
encountered in or near the Endeavor
Marine Protected Area where seismic
operations will occur, and are, therefore,
not addressed further in this document.
Eight of these species are listed as
endangered under the U.S. Endangered
Species Act of 1973 (ESA), including
the Steller sea lion (Eumetopias
jubatus), the humpback sei, fin, blue,
North Pacific right (Eubalena japonica),
sperm, and Southern Resident killer
(Orcinus orca) whales.
This IHA will only address requested
take authorizations for cetaceans and
pinnipeds. Table 2 below outlines the
species, their habitat and abundance in
the proposed survey area, and the
estimated exposure levels. Additional
information regarding the status and
distribution of the marine mammals in
the area as well as how L-DEO
calculated the densities were included
in a previous notice for the proposed
IHA (74 FR 21631, May 8, 2009) and in
Sections III and IV of L-DEO’s
application.
Occurrence in the
Survey Area
Estimated Number of Individuals
Exposed to
Sound Levels
≥160 dB
Approx. Percent of Regional Population
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Species
Habitat
Abundance in the NE
Pacific
North Pacific right whale*
Coastal and shelf waters
100–200
Rare and unlikely
0
0
Coastal waters
>6000
Uncommon
6
0.10
Coastal and shelf waters
9000
Uncommon
5
0.06
Pelagic
7260 - 12,620
Uncommon
1
0.01
Humpback whale*
Minke whale
Sei whale*
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Habitat
Abundance in the NE
Pacific
Occurrence in the
Survey Area
Estimated Number of Individuals
Exposed to
Sound Levels
≥160 dB
Approx. Percent of Regional Population
Fin whale*
Pelagic, shelf and coastal
waters
13,620–18,680
Uncommon
8
0.05
Blue whale*
Pelagic, shelf and inshore
waters
1186
Uncommon
2
0.14
Pelagic
24,000
Uncommon
10
0.04
Pygmy sperm whale
Deep waters off the shelf
Not available
Common
9
Not available
Dwarf Sperm whale
Deep waters off the shelf
Not available
Uncommon
0
0.0
Baird’s beaked whale
Deep waters and cont.
slopes
6000
Common
13
0.21
Blainville’s beaked whale
Deep waters and cont.
slopes
603
Uncommon
2
0.28
Cuvier’s beaked whale
Pelagic
20,000
Uncommon
0
0.0
Hubb’s beaked whale
Deep waters and cont.
slopes
421
Uncommon
2
0.40
Stejneger’s beaked
whale
Deep waters
421
Uncommon
2
0.40
Bottlenose dolphin
Coastal and offshore waters
3257
Rare
0
0.0
Pelagic
23,883
Rare
0
0.0
Short-beaked common
dolphin
Coastal and offshore waters
487,622
Common
104
0.02
Pacific white-sided dolphin
Pelagic, shelf and slope
waters
931,000
Common
181
0.02
Northern right-whale dolphin
Pelagic, shelf and slope
waters
15,305
Common
142
0.93
Risso’s dolphin
Pelagic
12,093
Common
95
0.78
False killer whale
Pelagic
Not available
Rare
0
NA
Widely distributed
8500
Uncommon
12
0.15
Pelagic
160,200
Uncommon
0
00.0
Offshore and nearshore
waters
57,549
Common
1081
1.88
Coastal
721,935
Common
73
0.01
Species
Sperm whale*
Striped dolphin
Killer whale
Short-finned pilot whale
Dall’s porpoise
Northern fur seal
Total
1,748
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Table 2. Abundance, preferred habitat, and commonness of the marine mammal species that may be encountered during the proposed survey
within the ETOMO survey area. The far right columns indicate the estimated number and percentage of the population of each species that may
be exposed to sound levels ≥160 dB based on average density estimates. NMFS believes that, when mitigation measures are taken into consideration, the activity is likely to result in take of numbers of animals less than those indicated by the column titled Estimated Number of Individuals
Exposed to Sound Levels ≥160 dB.
* Federally listed endangered species.
Potential Effects of the Proposed
Activity on Marine Mammals
The effects of sounds from airguns
might include one or more of the
following: tolerance, masking of natural
sounds, behavioral disturbance,
temporary or permanent hearing
impairment, or non-auditory physical or
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physiological effects (Richardson et al.,
1995; Gordon et al., 2004; Nowacek et
al., 2007; Southall et al., 2007).
Permanent hearing impairment, in the
unlikely event that it occurred, would
constitute injury, but temporary
threshold shift (TTS) is not an injury
(Southall et al., 2007). Although the
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possibility cannot be entirely excluded,
it is unlikely that the project would
result in any cases of temporary or
permanent hearing impairment, or any
significant non-auditory physical or
physiological effects. Some behavioral
disturbance is expected, but is expected
to be localized and short-term.
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The notice of the proposed IHA (74
FR 21631, May 8, 2009) included a
discussion of the effects of sounds from
airguns on mysticetes (baleen whales),
odontocetes (toothed whales), 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 is discussed in
Appendix B of L-DEO’s application.
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,
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 or pinnipeds to
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 (74
FR 21631, May 8, 2009) included an indepth discussion of the methods used to
calculate the densities of the marine
mammals in the area of the seismic
survey and the take estimates. Based on
numbers of animals encountered during
previous L-DEO seismic surveys, the
likelihood of the successful
implementation of the required
mitigation measures, and the likelihood
that some animals will avoid the area
around the operating airguns, NMFS
believes that L-DEO’s airgun seismic
testing program may result in the Level
B harassment of some lower number of
individual marine mammals (a few
times each) than is indicated by the
column titled, Estimated Number of
Individuals Exposed to Sound Levels
≥160 dB, in Table 2. L-DEO has asked
for authorization for take of their ‘‘best
estimate’’ of numbers for each species.
Though NMFS believes that take of the
requested numbers is unlikely, we still
find these numbers small relative to the
population sizes.
Estimates of the numbers of marine
mammals that might be affected are
based on consideration of the number of
marine mammals that could be
disturbed appreciably by approximately
1800 km of seismic surveys during the
proposed seismic program in the
ETOMO study area. The estimates of
exposures to various sound levels
assume that the surveys will be
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completed; in fact, the planned number
of line-kilometers has been increased by
25 percent to accommodate lines that
may need to be repeated, equipment
testing, etc.
All anticipated ‘‘takes by harassment’’
authorized by this IHA are Level B
harassment only, involving temporary
changes in behavior. Because of the
required implementation of mitigation
measures and the likelihood that some
cetaceans will avoid the area around the
operating airguns of their own accord,
NMFS does not expect any marine
mammal to approach the sound source
close enough to be injured (Level A
harassment). Given these
considerations, the predicted number of
marine mammals that might be exposed
to sounds at or greater than 160 dB may
be somewhat overestimated. Thus, the
following estimates of the numbers of
marine mammals potentially exposed to
sounds equal to or greater than 160 dB
are precautionary, and probably
overestimate the actual numbers of
marine mammals that might be exposed.
Potential Effects on Habitat
A detailed discussion of the potential
effects of this action on marine mammal
habitat, was included in the notice of
the proposed IHA (74 FR 21631, May 8,
2009). Based on the discussion in the
proposed IHA notice, the authorized
operations are not expected to have any
habitat-related effects that could cause
significant or long-term consequences
for individual marine mammals or their
populations or stocks and 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.
The Langseth will deploy and retrieve
approximately 64 OBS. The OBS
anchors will remain upon equipment
recovery. Although OBS placement will
disrupt a very small area of seafloor
habitat and may disturb benthic
invertebrates, the impacts are expected
to be localized and transitory. The
vessel will deploy the OBS in such a
way that creates the least disturbance to
the area. Thus, it is not expected that
the placement of OBS would have
adverse effects beyond naturally
occurring changes in this environment,
and any effects of the planned activity
on marine mammal habitats and food
resources are expected to be negligible.
Monitoring and Mitigation Measures
Mitigation and monitoring measures
required to be implemented for the
proposed seismic survey have been
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developed and refined during previous
L-DEO seismic survey studies and
associated environmental assessments,
IHA applications, and IHAs. The
mitigation and monitoring measures
described herein represent a
combination of the 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 this section.
Required mitigation measures
include: (1) safety radii; (2) speed or
course alteration, provided that doing so
will not compromise operational safety
requirements; (2) power-down
procedures; (3) shutdown procedures;
(4) ramp-up procedures; and (5) special
procedures for nighttime and low-light
hour operations.
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., 9
minutes). When feasible, MMVOs will
also make observations during daytime
periods when the seismic system is not
operating for comparison of animal
abundance and behavior. Based on
MMVO observations, airguns will be
powered down, or if necessary, shut
down completely (see below), when
marine mammals are detected within or
about to enter a designated safety radius
corresponding to 180–dB isopleths. 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 radii are listed
according to the sound source, water
depth, and received isopleth in Table 1.
During seismic operations in the
northeast Pacific Ocean, at least three
visual observers and one bioacoustician
will be based aboard the Langseth.
MMVOs will be appointed by L-DEO
with NMFS’ concurrence. At least two
MMVOs (except during meal times) will
monitor the safety radii for marine
mammals during daytime operations
and nighttime startups of the airguns.
The use of two simultaneous MMVOs
will increase the proportion of the
animals present near the source vessel
that are detected. The MMVO(s) will be
on duty in shifts of duration no longer
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than 4 hours. The vessel crew will also
be instructed to assist in detecting
marine mammals and implementing
mitigation requirements (if practical).
Before the start of the seismic survey the
crew will be given additional
instruction regarding how to do so.
The Langseth’s high observation
tower is a suitable platform for
conducting marine mammal and turtle
observations. When stationed on the
observation platform, the MMOV’s eye
level will be approximately 18 m (59 ft)
above sea level, providing a panoramic
view around the entire vessel. During
the daytime, the MMO(s) will scan the
area around the vessel systematically
using reticle binoculars (e.g., 7 x 50
Fujinon), big-eye binoculars (25 x 150),
and the naked eye. The platform of the
Langseth is high enough that, in good
weather, MMOs can see out to 8.9 nm
(16.5 km, 10.2 mi). All of the 180–dB
safety radii that MMOs will monitor
during ramp-ups and power-downs are
less than 2 km (1.1 nm, 1.2 mi).
MMOs will use night vision devices
(NVDs) (ITT F500 Series Generation 3
binocular-image intensifier or
equivalent), during dusk or nighttime,
when required. Finally, L-DEO will
provide laser rangefinding binoculars
(Leica LRF 1200 laser rangefinder or
equivalent) to MMOs to assist with
distance estimation. MMOs estimate
that visual detection from the ship is
between 150 and 250 m (492 and 820 ft)
using NVDs and about 30 m (98.4 ft)
with the naked eye, which are affected
by ambient lighting conditions, sea
state, and thermal factors.
Passive Acoustic Monitoring
PAM will take place to complement
the visual monitoring program. Acoustic
monitoring can be used in addition to
visual observations to improve
detection, identification, localization,
and tracking of cetaceans. 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. The acoustic monitoring will
serve to alert visual observers when
vocalizing cetaceans are detected. 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.
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A deck cable will connect from the
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 of 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 with the airguns
not operating. One MMO and/or
bioacoustician 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. Of the three
observers required on board, one will
have primarily responsibility for PAM
during the seismic survey. 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 vocalizing marine
mammal(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 includes 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.
Speed or Course Alteration - If a
marine mammal is detected outside the
safety radius and, based on its position
and the relative motion, is likely to
enter the safety radius or exclusion zone
(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
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42871
be closely monitored to determine
whether the animals is approaching the
applicable EZ. If the animal appears
likely to enter the EZ, further mitigation
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
operating airguns in use to minimize the
exclusion zone, so that marine
mammals are no longer in or about to
enter this zone. A power-down of the
airgun array to a reduced number of
operating airguns may 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 at
least 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 safety radii 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
safety radii around that single airgun
(see Table 1 above), all airguns will be
shutdown (see next subsection).
Following a power down, airgun
activity will not resume until the marine
mammal is outside the safety radius for
the full array. The animal will be
considered to have cleared the safety
radius if it:
(1) Is visually observed to have left
the safety radius; or
(2) Has not been seen within the
safety radius for 15 minutes in the case
of small odontocetes or pinnipeds; or
(3) Has not been seen within the
safety radius for 30 minutes in the case
of mysticetes and large odontocetes,
including sperm, pygmy sperm, dwarf
sperm, and beaked whales; or
During airgun operations following a
power-down (or shut-down) and
subsequent animal departure as above,
the airgun array will resume operations
following ramp-up procedures
described below.
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Shutdown Procedures - The operating
airgun(s) will be shut down if a marine
mammal is detected within or
approaching the safety radius for the
then-operating single 40 in3 airgun
while the airgun array is at full volume
or during a power down. Airgun activity
will not resume until the marine
mammal has cleared the safety radius or
until the MMO is confident that the
animal has left the vicinity of the vessel.
Criteria for judging that the animal has
cleared the safety radius will be as
described in the preceding subsection.
Ramp-up Procedures - A ramp-up
procedure will be followed when the
airgun array begins operating after more
than nine minutes without airgun
operations or when a power-down has
exceeded nine minutes. This period is
based on the modeled 180–dB radius for
the 36–airgun array (see Table 1) in
relation to the planned speed of the
Langseth while shooting. Similar
periods (approximately eight to 10
minutes) were used during previous LDEO 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–minute
period over a total duration of
approximately 20 to 25 minutes. During
ramp-up, the MMVOs will monitor the
safety radius, and if marine mammals
are sighted, a course/speed change,
power down, or shutdown will be
implemented as though the full array
were operational.
If the complete safety radius has not
been visible for at least 30 minutes 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 safety radius 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 have the opportunity to
move away. Ramp up of the airguns will
not be initiated if a marine mammal is
sighted within or near the applicable
safety radius during the day or close to
the vessel at night.
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MMVO Data and Documentation
MMVOs will record data to estimate
the numbers of marine mammals
exposed to various received sound
levels and to document any apparent
disturbance reactions or lack thereof.
Data will be used to estimate the
numbers of mammals potentially
‘‘taken’’ by harassment. They will also
provide information needed to order a
power-down or shutdown of airguns
when marine mammals are within or
near the relevant safety radius. When a
sighting is made, the following
information about the sighting will be
recorded:
(1) Species, group size, age/size/sex
categories (if determinable), behavior
when first sighted and after initial
sighting, heading (if consistent), bearing
and distance from seismic vessel,
sighting cue, apparent reaction to the
airguns or vessel (e.g., none, avoidance,
approach, paralleling, etc. and including
responses to ramp-up), and behavioral
pace.
(2) Time, location, heading, speed,
activity of the vessel (including number
of airguns operating and whether in
state or ramp-up, power-down, or full
power), sea state, visibility, cloud cover,
and sun glare.
The data listed under (2) will also be
recorded at the start and end of each
observation watch and during a watch,
whenever there is a change in one or
more of the variables.
All observations, as well as
information regarding airgun power
down and shutdown, will be recorded
in a standardized format. Data will be
entered into a custom electronic
database. The accuracy of data will be
verified by computerized data validity
checks as the data are entered and by
subsequent manual checking of the
database. 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. MMO
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.
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Reporting
A draft report will be submitted to
NMFS within 90 days after expiration of
the IHA. The report will describe the
operations that were conducted and
sightings of marine mammals near the
operations. The report will be submitted
to NMFS, providing full documentation
of methods, results, and interpretation
pertaining to all monitoring and
mitigation. The 90–day draft report will
summarize the dates and locations of
seismic operations (dates, times,
locations, heading, speed, weather, sea
state, activities), and all marine mammal
sightings (dates, times, locations,
species, behavior, number of animals,
associated seismic survey activities).
The report will also include the
estimates of the amount and nature of
potential ‘‘take’’ of marine mammals by
harassment or in other ways, as well as
a description of the implementation and
effectiveness of the monitoring and
mitigation measures of the IHA and
Biological Opinion’s (BiOp) Incidental
Take Statement. L-DEO is then required
to submit a final report within 30 days
after receiving comments from NMFS on
the draft report.
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 Headquarters’ Office of Protected
Resources, Permits, Conservation, and
Education Division 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 August 18, 2009, NMFS
issued a BiOp and concluded that the
issuance of an IHA is not likely to
jeopardize the continued existence of
blue, fin, sei, humpback, and sperm
whales, leatherback sea turtles, as well
as listed salmonids. The BiOp also
concluded that the proposed activities
would have no effect on critical habitat,
as the Canadian government has no
such designation within the action area.
Finally, NMFS has incorporated the
Relevant Terms and Conditions of the
Incidental Take Statement in the BiOp
into the IHA.
National Environmental Policy Act
(NEPA)
On September 22, 2005 (70 FR 55630),
NSF published a notice of intent to
prepare a Programmatic Environmental
Impact Statement/Overseas
Environmental Impact Statement (EIS/
OES) to evaluate the potential
environmental impacts associated with
the use of seismic sources in support of
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NSF-funded research by U.S. academic
scientists. NMFS agreed to be a
cooperating agency in the preparation of
the EIS/OEIS. This EIS/OEIS has not
been completed.
Therefore, in order to meet NSF’s and
NMFS’ NEPA requirements for the
proposed activity and issuance of an
IHA to L-DEO, the NSF has prepared an
EA that is specific to the marine
geophysical survey conducted by the R/
V Marcus G. Langseth in the northeast
Pacific Ocean. NSF’s EA, titled, Marine
Seismic Survey in the Northeast Pacific
Ocean, August/September, 2009 is
based, in part, on an environmental
assessment report (hereinafter, Report),
prepared by LGL Limited environmental
research associates (LGL) on behalf of
NSF, titled, ‘‘Environmental Assessment
of a Marine Geophysical Survey by the
R/V Marcus G. Langseth in the
Northeast Pacific Ocean, August
September, 2009.’’ The EA, and Report,
specifically analyze the fact that L-DEO
intends to obtain an IHA from NMFS in
order to conduct the seismic survey.
The EA evaluates the impacts of
potential incidental Level B harassment
resulting from the specified activity in
the specified geographic region. The
NSF has made a Finding of No
Significant Impact (FONSI)
determination based on information
contained within its EA and Report, that
implementation of the proposed action
is not a major Federal action having
significant effects on the environment
within the meaning of NEPA. NSF
determined, therefore, that an
environmental impact statement would
not be prepared.
On May 8, 2009 (74 FR 2163), NMFS
noted that the NSF had prepared an EA
for the northeast Pacific Ocean surveys
and made this EA, and the Report,
available upon request. NMFS has
independently reviewed the information
contained in NSF’s EA and determined
that the NSF EA describes the proposed
action alternative and evaluates and
discloses the potential impacts on
marine mammals, endangered species,
and other marine life that could be
impacted by the preferred alternative
and the other alternatives. Accordingly,
NMFS has adopted the NSF EA, and
incorporated Report, under 40 CFR
1506.3 and made its own FONSI. The
NMFS FONSI also takes into
consideration additional mitigation
measures required by the IHA that are
not in NSF’s EA or Report. Therefore,
NMFS has determined that it is not
necessary to issue a new EA,
supplemental EA or an EIS for the
issuance of an IHA to L-DEO for this
activity. A copy of the EA and the
VerDate Nov<24>2008
00:58 Aug 25, 2009
Jkt 217001
NMFS FONSI for this activity is
available upon request (see ADDRESSES).
Determinations
NMFS has determined that the impact
of conducting the seismic survey in the
northeast Pacific Ocean may result, at
worst, in a temporary modification in
behavior (Level B harassment) of small
numbers of 33 species of cetaceans.
Though NMFS believes that take of the
requested numbers is unlikely, we still
find these numbers small relative to the
population sizes. Further, this activity is
not expected to adversely affect any
species or stock through affects on
annual recruitment or survival.
Therefore, NMFS has determined that
the activity will have a negligible
impact on the affected species or stocks.
The provision requiring that the
activity not have an unmitigable adverse
impact on the availability of the affected
species or stock for subsistence uses is
not implicated for this proposed action.
There is no subsistence harvest of
marine mammals in the proposed
research area; therefore, there will be no
impact of the activity on the availability
of the species or stocks of marine
mammals for subsistence uses.
The negligible impact determination
is supported by: (1) the likelihood that,
given sufficient warning through
relatively slow ship speed, marine
mammals are expected to move away
from a noise source that is annoying
prior to it becoming potentially
injurious; (2) the fact that marine
mammals would have to be closer than
40 m (131 ft) in deep 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
marine mammals would have to be
closer than 950 m (0.5 nm) in deep
water, when the full array is in use at
a 9–15 m (29.5–49.2 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; (4) the
likelihood that marine mammal
detection ability by trained observers is
good at those distances from the vessel;
(5) 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; (6)
the incorporation of other required
mitigation measures (i.e., ramp-up,
power-down, and shutdown); and (7)
the limited duration of the seismic
survey in the study area (approximately
39 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 00032
Fmt 4703
Sfmt 4703
42873
the required monitoring and mitigation
measures.
While the number of potential
incidental harassment takes will depend
on the distribution and abundance of
marine mammals in the vicinity of the
survey activity, the number of potential
harassment takings is estimated to be
small, relative to the affected species
and stock 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 has issued an IHA to L-DEO for
conducting a marine geophysical survey
in the northeast Pacific Ocean in August
October, 2009, provided the previously
mentioned mitigation, monitoring, and
reporting requirements are incorporated.
Dated: August 19, 2009.
James H. Lecky,
Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. E9–20492 Filed 8–24–09; 8:45 am]
BILLING CODE 3510–22–S
DEPARTMENT OF COMMERCE
International Trade Administration
Initiation of Antidumping and
Countervailing Duty Administrative
Reviews and Request for Revocation
in Part
AGENCY: Import Administration,
International Trade Administration,
Department of Commerce.
SUMMARY: The Department of Commerce
(‘‘the Department’’) has received
requests to conduct administrative
reviews of various antidumping and
countervailing duty orders and findings
with July anniversary dates. In
accordance with the Department’s
regulations, we are initiating those
administrative reviews. The Department
also received a request to revoke one
antidumping duty order in part.
DATES: Effective Date: August 25, 2009.
FOR FURTHER INFORMATION CONTACT:
Sheila E. Forbes, Office of AD/CVD
Operations, Customs Unit, Import
Administration, International Trade
Administration, U.S. Department of
Commerce, 14th Street and Constitution
Avenue, NW, Washington, DC 20230,
telephone: (202) 482–4697.
SUPPLEMENTARY INFORMATION:
Background
The Department has received timely
requests, in accordance with 19 CFR
351.213(b), for administrative reviews of
various antidumping and countervailing
E:\FR\FM\25AUN1.SGM
25AUN1
Agencies
[Federal Register Volume 74, Number 163 (Tuesday, August 25, 2009)]
[Notices]
[Pages 42861-42873]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-20492]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XQ20
Incidental Takes of Marine Mammals During Specified Activities;
Marine Geophysical Survey in the Northeast Pacific Ocean, August-
October, 2009
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; issuance of incidental take authorization.
-----------------------------------------------------------------------
SUMMARY: In accordance with the Marine Mammal Protection Act (MMPA)
regulations, notification is hereby given that NMFS has issued an
Incidental Harassment Authorization (IHA) to Lamont-Doherty Earth
Observatory (L-DEO), a part of Columbia University, to take small
numbers of marine mammals, by Level B harassment only, incidental to
conducting a marine seismic survey in the northeast Pacific Ocean.
DATES: Effective August 19, 2009 through October 13, 2009.
ADDRESSES: A copy of the IHA and the 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 20910-3225 or by
telephoning the
[[Page 42862]]
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 by visiting the internet at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm#applications. Documents
cited in this notice may be viewed, by appointment, during regular
business hours, at the aforementioned address.
FOR FURTHER INFORMATION CONTACT: Jeannine Cody, Office of Protected
Resources, NMFS, (301) 713-2289 ext 113.
SUPPLEMENTARY INFORMATION:
Background
Section 101(a)(5)(D) of the MMPA (16 U.S.C. 1371 (a)(5)(D)) directs
the Secretary of Commerce (Secretary) to allow, upon request, the
incidental, but not intentional, taking of marine mammals, for periods
of not more than one year, by United States citizens who engage in a
specified activity (other than commercial fishing) within a specified
geographical region if certain findings are made and, if the taking is
limited to harassment, a notice of a proposed authorization is provided
to the public for review.
Authorization for incidental taking of small numbers of marine
mammals shall be granted if NMFS finds that the taking will have a
negligible impact on the species or stock(s), and will not have an
unmitigable adverse impact on the availability of the species or
stock(s) for subsistence uses. The authorization must set forth the
permissible methods of taking, other means of effecting the least
practicable adverse impact on the species or stock and its habitat and
monitoring and reporting of such takings. NMFS has defined ``negligible
impact'' in 50 CFR 216.103 as ''...an impact resulting from the
specified activity that cannot be reasonably expected to, and is not
reasonably likely to, adversely affect the species or stock through
effects on annual rates of recruitment or survival.''
Section 101(a)(5)(D) of the MMPA established an expedited process
by which citizens of the United States can apply for an authorization
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''].
Section 101(a)(5)(D) of the MMPA 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. Not later than 45 days
after the close of the public comment period, if the Secretary makes
the findings set forth in Section 101(a)(5)(D)(i) of the MMPA, the
Secretary shall issue or deny issuance of the authorization with
appropriate conditions to meet the requirements of clause
101(a)(5)(D)(ii) of the MMPA.
Summary of Request
On February 11, 2009, NMFS received an application from L-DEO for
the taking by Level B harassment only, of small numbers of 33 species
of marine mammals incidental to conducting a marine seismic survey
within the Exclusive Economic Zone (EEZ) of Canada in the northeast
Pacific Ocean during August through October 2009. L-DEO, with research
funding from the NSF, is conducting the geophysical data acquisition
activities. NMFS outlined the purpose of the research program in a
previous notice for the proposed IHA (74 FR 21631, May 8, 2009).
Description of the Specified Activity
The planned survey will involve one source vessel, the R/V Marcus
G. Langseth (Langseth), a seismic research vessel owned by the NSF and
operated by L-DEO. The proposed project is scheduled to commence on
August 19, 2009, and scheduled to end on October 13, 2009. The vessel
will depart Astoria, Oregon on August 19, 2009 for transit to the
Endeavor MPA, between 47-48[deg] N. and 128-130[deg] W.
To obtain high-resolution three-dimensional (3D) structures of the
Lau Basin's magmatic systems and thermal structures, the Langseth will
deploy a towed array of 36 airguns with a total discharge volume of
approximately 6,600 cubic inches (in\3\). The array configuration
consists of four identical linear arrays or strings, with 10 airguns on
each string. L-DEO will distribute the four airgun strings across an
approximate area of 24 x 16 meters (m) (79 x 52 feet (ft)) behind the
Langseth which will tow the array approximately 50-100 m (164-328 ft)
behind the vessel at a tow-depth of 9-15 m (29.5-49.2 ft). The airgun
array will fire for a brief (0.1 second (s)) pulse every 180 s. The
array will remain silent at all other times.
The seismic study (e.g., equipment testing, startup, line changes,
repeat coverage of any areas, and equipment recovery) will take place
in deep (between 1200 and 3000 m, 3,280 feet (ft) and 1.8 miles (mi))
water and will require approximately 10 days to complete 12 transects
of variable lengths totaling 1800 km of survey lines. Data acquisition
will include approximately 240 hours of airgun operation. Please see L-
DEO's application for more detailed information. The exact dates of the
activities will depend on logistics, weather conditions, and the need
to repeat some lines if data quality is substandard.
L-DEO will conduct all geophysical data acquisition activities with
on-board assistance by the scientists who have proposed the NSF-funded
study. The scientific team consists of NSF, is conducting the
geophysical data acquisition activities with onboard assistance by Drs.
Toomey and Hooft from the University of Oregon, and Dr. Wilcock from
the University of Washington. The vessel will be self-contained, and
the crew will live aboard the vessel for the entire cruise.
NMFS has provided a more detailed description of the authorized
action, including vessel and acoustic source specifications, in a
previous notice for the proposed IHA (74 FR 21631, May 8, 2009).
Safety Radii
The distance from the sound source at which an animal would be
exposed to these different received sound levels may be estimated and
is typically referred to as safety radii. These safety radii are
specifically used to help NMFS estimate the number of marine mammals
likely to be harassed by the proposed activity and in deciding how
close a marine mammal may approach an operating sound source before the
applicant will be required to power-down or shut down the sound source.
L-DEO's acoustic models predict received sound levels in relation
to distance and direction from the 36-airgun array in order to estimate
the safety radii around their operations. L-DEO's model is based on
empirical data gathered during the acoustic calibration study of the R/
V Maurice Ewing's (Ewing) array of 20 airguns (total volume 8600 in\3\)
conducted in the northern Gulf of Mexico in 2003. L-DEO provides a more
detailed description of the modeling effort and calculations of the
safety radii in the previous notice for the proposed IHA (74 FR 21631,
May 8, 2009), Section I of L-DEO's IHA
[[Page 42863]]
application, and in Appendix A of the Environmental Assessment report
prepared by LGL Limited environmental research associates (LGL) on
behalf of NSF. NMFS has determined that the foregoing data and studies
represent the best scientific evidence available a the present time.
Using the modeled distances and various correction factors, Table 1
outlines the predicted distances at which three root mean square (rms)
sound levels (190 decibels (dB), 180 dB, and 160 dB) are expected to be
received from the 36-airgun array and a single airgun operating in
water greater than 1000 m (3,820 ft) in depth.
----------------------------------------------------------------------------------------------------------------
Predicted RMS Distances (m)
Source and Volume Tow Depth (m) --------------------------------------------------------------
190 dB 180 dB 160 dB
----------------------------------------------------------------------------------------------------------------
Single Bolt airgun 40 in\3\ 6-15\*\ 12 40 385
4 strings 36 airguns 6600 6 220 710 4670
in\3\
9 300 950 6000
12 340 1120 6850
15 380 1220 7690
----------------------------------------------------------------------------------------------------------------
\*\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.
Comments and Responses
NMFS published a notice of receipt of the L-DEO application and
proposed IHA in the Federal Register on May 8, 2009 (74 FR 21631).
During the comment period, NMFS received comments from the Marine
Mammal Commission (Commission), Cetacean Society International (CSI);
and the Wild at Heart Legal Defense Association (WAHLDA). Following are
the comments from the Commission, CSI, WAHLDA and NMFS' responses.
Comment 1: The Commission recommends that NMFS provide additional
justification for its preliminary determination that the planned
monitoring program will be sufficient to detect, with a high level of
confidence, all marine mammals within or entering the identified safety
zones; as such monitoring is essential for determining whether animals
are being taken in unanticipated ways and unexpected numbers.
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 radii. 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 visually monitor marine mammals and conduct passive acoustic
monitoring (PAM).
The Langseth's high observation tower is a suitable platform for
conducting marine mammal observations. When stationed on the
observation platform, the MMO's eye level will be approximately 18 m
(59 ft) above sea level, providing a panoramic view around the entire
vessel. During the daytime, the MMO(s) will scan the area around the
vessel systematically using reticle binoculars (e.g., 7 x 50 Fujinon),
big-eye binoculars (25 x 150), and the naked eye. The platform of the
Langseth is high enough that, in good weather, MMOs can see out to 8.9
nm (16.5 km, 10.2 mi). All of the 180-dB safety radii that MMOs will
monitor during ramp-ups and power-downs are less than 2 km (1.1 nm, 1.2
mi).
MMOs will use night vision devices (NVDs) (ITT F500 Series
Generation 3 binocular-image intensifier or equivalent), during dusk or
nighttime, when required. Finally, L-DEO will provide laser
rangefinding binoculars (Leica LRF 1200 laser rangefinder or
equivalent) to MMOs to assist with distance estimation. MMOs estimate
that visual detection from the ship is between 150 and 250 m (492 and
820 ft) using NVDs and about 30 m (98.4 ft) with the naked eye, which
are affected by ambient lighting conditions, sea state, and thermal
factors.
The Langseth will complement visual observations of marine mammals
with an acoustical monitoring program. L-DEO will use a PAM system to
improve detection, identification, localization, and tracking of marine
mammals. The acoustic monitoring will alert visual observers (if on
duty) when vocalizing cetaceans are detected. When an MMO detects a
vocalization while visual observations are in progress, the acoustic
MMO will contact the visual MMO immediately, to alert him/her to the
presence of cetaceans (if they have not already been seen), and to
initiate a power down or shut down, if required.
The theoretical detection distance of this PAM system is tens of
kilometers and it has reliable detection rates out to 3 km (1.6 nm) and
more limited ability out to tens of kilometers. During the Ewing's
cruise in the Gulf of Mexico in 2003, MMOs detected marine mammals at a
distance of approximately 10 km (5.4 nm) from the vessel and identified
them to species level at approximately 5 km (2.7 nm) from the vessel,
though the bridge of that vessel was only 11 m (36 ft) above the water
(vs. the Langseth, which is 18 m (59 ft) above sea level).
The likelihood of MMOs visual detecting a marine mammal at night is
significantly lower than the ability to detect any species during the
day. However, the PAM operates equally as effective at night as during
the day, and does not depend on good visibility.
The Langseth will not start up the airguns unless the MMO can
visibly detect the safety range for the 30 minutes prior (i.e., not at
night) to start up. In all cases at night, the Langseth will already be
operating the airguns. NMFS believes that operating the airguns at
night will cause many cetaceans to avoid the vessel; thus reducing the
number of cetaceans likely to come within the safety radii.
Additionally, all of the safety radii in deep water depths are smaller
than 2 km (1.1 nm, 1.2 mi) and fall easily within the reliable
detection capabilities of the PAM.
Comment 2: The Commission recommends that NMFS clarify the
qualifier ``when feasible'' with respect to: (1) using two marine
mammal visual observers to monitor the exclusion zone for marine
mammals during daytime operations and nighttime start-ups of the
airguns; and (2) using marine mammal visual observers during daytime
periods to compare sighting rates and animal behavior during times when
the seismic airguns are operating and times when they are not.
Response: NMFS considers whether a particular mitigation is capable
of being effected, done, or executed (i.e., feasible). For this IHA,
the qualifier ``feasible'' is only applicable when the seismic system
is not operating. It does
[[Page 42864]]
not apply during seismic operations (Permit, P.5; Condition 8(a)(i).
NMFS' consideration of practicability includes (among other
relevant considerations) economic and technological feasibility (see 50
CFR 216.104(a)(11)). NMFS believes that the IHA's mitigation and
monitoring measures are complete to the fullest extent practicable, and
ensure that the takings will be limited to harassment and will result
in a negligible impact on the affected species or stocks of marine
mammals.
The Langseth is utilizing a team of trained marine mammal observers
(MMO) to both visually monitor from the high observation tower of the
Langseth and to conduct PAM. L-DEO will utilize two (except during meal
times), NMFS-qualified, vessel-based marine mammal visual observers
(MMVO) to watch for and monitor marine mammals near the seismic source
vessel during all daytime airgun operations and before and during
start-ups of airguns day or night.
MMVOs will have access to reticle binoculars (7x50 Fujinon), big-
eye binoculars (25x150), and night vision devices to scan the area
around the vessel. MMVOs 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 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 3: The Commission recommends that the monitoring period
prior to the initiation of seismic activities and prior to the
resumption of airgun activities after a power-down be extended to one
hour.
Response: NMFS believes that 30 minutes is an adequate length of
time for monitoring prior to the start-up of airguns. The IHA requires
that the MMOs monitor the area for at least 30 minutes prior to
starting the airgun array (day or night) to ensure that no marine
mammals are seen within the safety zone before a seismic survey
commences. The Langseth's ramp up protocol begins with the smallest gun
in the array and adds additional airguns in a sequence such that the
source level of the array will increase in steps not exceeding
approximately 6 dB per 5-min period over a total duration of 20-30
minutes. Thus, the total time of monitoring prior to start-up of any
but the smallest array is effectively longer than 30 minutes. In many
cases MMOs are making observations during times when sonar is not being
operated and will actually be observing the area prior to the 30-minute
observation period.
Comment 4: The Commission recommends that NMFS require that
observations be made during all ramp-up procedures to gather the data
needed to analyze and provide a report on the effectiveness of this
method as a mitigation measure.
Response: The IHA requires L-DEO to submit a draft and final report
on all activities and monitoring results to the NMFS, Office of
Protected Resources, within 90 days after the expiration of the IHA.
NMFS will post the report at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm#applications.
This report: (1) must include an estimate of the number (by
species) of marine mammals that are known to have been exposed to the
seismic activity (visual observation) at received levels greater than
or equal to 160 dB re 1 microPa (rms) and/or 180 dB re 1 microPa (rms)
with a discussion of any specific behaviors those individuals
exhibited; and (2) must also include an estimate of the number of
marine mammals that may have been exposed to the seismic activity at
received levels greater than or equal to 160 dB re 1 microPa (rms) and/
or 180 dB re 1 microPa (rms) with a discussion of the nature of the
probable consequences of that exposure on the individuals that have
been exposed.
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 5: It is expected that Canada will have consulted and commented
on this proposal, and CSI respectfully requests a link to those
documents for review.
Response: NMFS received no comments from the Canadian government or
from any Canadian organization during the public comment period.
However, the terms and conditions of the IHA encourage NSF to
coordinate with the Canadian government regarding the proposed seismic
activity.
Comment 6: While not relevant to the MMPA, it should be noted that
12 species found nowhere else in the world have been identified at the
Endeavour Hydrothermal Vents. Given that the potential for deleterious
acoustic impacts on invertebrates from the L-DEO survey is almost
totally unknown, CSI specifically requests that NMFS require L-DEO and
the NSF to support a survey of the site sufficient to document whether
or not these extremely limited species were impacted by the experiment.
Response: NMFS' support of a post-seismic survey of invertebrates
is not germane to this Federal action under the MMPA. NMFS acknowledges
that at least 12 species are endemic to the Endeavour site. However,
the area is dynamic, and the natural variability within the
hydrothermal vents is high. Although OBS placement will disrupt a very
small area of seafloor habitat and may disturb benthic invertebrates,
the impacts are expected to be localized and transitory. NMFS does not
expect that the placement of OBS would have adverse effects beyond
naturally occurring changes in this environment, and any effects of the
planned activity on ocean and coastal habitats are expected to be
negligible.
NSF's EA (and associated report) analyzed the potential for the
seismic survey activity to affect ecosystem features and biodiversity
components, including fish, invertebrates, seabirds, and sea turtles.
NMFS' evaluation indicates that any direct or indirect effects of the
action would not result in a substantial impact on biodiversity or
ecosystem function. In particular, the potential for effects to these
resources are considered here with regard to the potential effects on
diversity or functions that may serve as essential components of marine
mammal habitats. Most effects are considered to be short-term and
unlikely to affect normal ecosystem function or predatory/prey
relationships; therefore, NMFS believes that there will not be a
substantial impact on marine life biodiversity associated with the
Endeavor hydrothermal vent, the Endeavor MPA, or on the normal function
of the nearshore or offshore environment.
Comment 7: The time between NMFS' first awareness of an L-DEO
application and the start of the scheduled survey does not allow for
significant changes to the operation without extraordinary economic
hardship on the applicant, and that creates pressure on NMFS to
[[Page 42865]]
authorize operations based on cost. CSI and others question whether
this economic and practical pressure might influence NMFS' final
decision relating to an IHA; might a project be authorized to continue,
despite a problem, because of the cost of fixing it?
Response: Section 101(a)(5)(D) of the MMPA 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. Not later
than 45 days after the close of the public comment period, if the
Secretary makes the findings set forth in Section 101(a)(5)(D)(i) of
the MMPA, the Secretary shall issue or deny issuance of the
authorization with appropriate conditions to meet the requirements of
clause 101(a)(5)(D)(ii) of the MMPA.
The NMFS, OPR, Permits, Conservation, and Education Division has
diligently processed L-DEO's application within the statutory timeframe
(120 days) for an IHA under the MMPA. The Division deemed the
application complete on May 1, 2009; published a notice of receipt and
request for comments in the Federal Register on May 8, 2009 (74 FR
21631); and issued the IHA on August 19, 2009. NMFS received no public
comments requesting L-DEO to significantly alter the survey's schedule
or institute major operational changes.
L-DEO's proposed survey did not require substantial changes to the
cruise plan or survey tracklines. As stated in this document, NMFS
shall grant an IHA to L-DEO if NMFS finds that incidental taking of
marine mammals will have a negligible impact on the species or stock(s)
and will not have an unmitigable adverse impact on the availability of
the species or stock(s) for subsistence uses and if the permissible
methods of taking and requirements pertaining to the mitigation,
monitoring and reporting of such taking are set forth.
NMFS evaluates each IHA application independent of the cost of the
proposed action, as this is not relevant to NMFS' determination of
negligible impact or unmitigable adverse impact on the availability of
the species or stock(s) for subsistence uses.
For previously authorized IHAs, NMFS has required applicants to
reschedule cruises; to modify survey tracklines; incorporate new
temporal and spatial avoidance requirements; and to institute more
precautionary measures to mitigate against the potential effects of the
action on marine mammals.
Comment 8: L-DEO should contract openly with regional authorities
and experts during the initial planning and scheduling phase, thereby
building the project around the ``best science'' available. This
amplifies the importance of the public comment period beyond a mere
statutory requirement.
Response: NMFS acknowledges CSI's request and has forwarded your
comment to NSF and L-DEO. If a CSI representative requests to comment
on the initial planning and scheduling phases, they should discuss this
directly with a representative from NSF and L-DEO.
Comment 9: The Office of Protected Resources (OPR) has not
processed the application fast enough so that necessary changes brought
to light through the public comment period might be applied with less
onerous scheduling and operational changes.
Response: The NMFS, OPR, Permits, Conservation, and Education
Division has diligently processed L-DEO's application within the
statutory timeframe (120 days) for an IHA under the MMPA. The Division
deemed the application complete on May 1, 2009; published a notice of
receipt and request for comments in the Federal Register on May 8, 2009
(74 FR 21631); and issued the IHA on August 19, 2009. NMFS received no
public comments requesting L-DEO to significantly alter the survey's
schedule or institute major operational changes.
Comment 10: CSI recognizes that OPR may be required to supplement
an Application with an Endangered Species Act of 1973 (ESA; 16 U.S.C.
1531 et seq.) section 7 consultation, Biological Opinion and
Environmental Assessment, all of which take time. This ETOMO
Application was received February 11, 2009, the Federal Register Notice
was published May 8, 2009, and we doubt there is time between the June
8, 2009, close of public comments and the start date of August 19, 2009
for L-DEO to adjust to potentially required changes in an IHA brought
to light within the comment period. From recent experience the IHA can
be expected to be issued close to the start date, making changes even
more onerous. In other words, will an IHA be authorized in spite of
issues, because of the cost to make it right? CSI is not accusing
either OPR or L-DEO, but we are asking that even the appearance of the
potential be removed.
Response: See NMFS' response to Comment 9. NMFS disagrees with the
commenter's views on the timeliness of processing of the application.
The OPR received the application on February 11, 2009. However, the
Permits, Conservation, and Education Division (PR1) deemed the
application incomplete under the MMPA and requested additional
information from L-DEO (See 50 CFR 216.104(b)(1) which states that NMFS
must determine the adequacy and completeness of an application prior to
initiating the public review process). PR1 deemed the application
complete on May 1, 2009. Pursuant to the MMPA, NMFS published a notice
of receipt and request for comments in the Federal Register on May 8,
2009 (74 FR 21631), within one week of determining that the application
was complete. Not later than 45 days after the close of the public
comment period, if the Secretary makes the findings set forth in
Section 101(a)(5)(D)(i) of the MMPA, the Secretary shall issue or deny
issuance of the authorization with appropriate conditions to meet the
requirements of clause 101(a)(5)(D)(ii). NMFS issued the IHA on
(August19, 2009) within the required MMPA statutory timeframe of 120
days.
Regarding the ESA section 7 consultation, the Office of Protected
Resources, Endangered Species Division (PR3) determined that the
information provided by the NSF and L-DEO was sufficient to initiate
formal consultation under the ESA on April 16, 2009. On August 18,
2009, NMFS issued a Biological Opinion (BiOp) and concluded that the
issuance of the IHA was not likely to jeopardize the continued
existence of the humpback (Megaptera novaeangliae), sei (Balaenoptera
borealis), fin (Balaenoptera physalus), blue (Balaenoptera musculus),
and sperm (Physeter macrocephalus) whales. NMFS issued the BiOp within
the ESA statutory timeframe of 135 days. NMFS included the BiOp's Terms
and Conditions of the Incidental Take Statement as mitigation measures
in the IHA.
Comment 11: The solution CSI respectfully asks both OPR and NMFS
for is a longer base time between application and start date. It is
clear that L-DEO will be at this for a long time, and schedules must be
set for 2010 and beyond.
Response: See NMFS' responses to Comments 9 and 10.
Comment 12: L-DEO's current process depends almost entirely upon
the validity of the assumptions and assessments from L-DEO's in-house
and contracted analysis, which have been proven to be inadequate.
Perhaps recognizing this, L-DEO requested consultations with the South
Pacific Whale Research Consortium (SPWRC) before the Tonga survey, but
demanded
[[Page 42866]]
confidentiality, which SPWRC refused. L-DEO Tonga went on anyway,
without that expert assistance.
Response: NMFS cannot speak to L-DEO's consultations with the SPWRC
and recommends that CSI should discuss their concerns with a
representative from L-DEO.
Comment 13: The L-DEO process failed with the L-DEO TAIGER survey
in Southeast Asia, as public comments were received from concerned
regional authorities and experts about several issues. One issue
required an amended IHA, and the project was delayed accordingly, but
the literally last minute public process should not have been the
impetus. L-DEO would have precluded the issues by contracting with the
well-known experts that were forced to express their concerns only
during the public comment period. Taiwan's renewed, potentially
threatening interest in the project only came about because the
regional experts were seeking ways to have their concerns noted. Why
not just hire the local experts and start earlier?
Response: The Canadian ETOMO survey is a separate action from the
TAIGER survey. NMFS acknowledges CSI's concerns and refers the
commenter to 74 FR 41260, August 14, 2009, for information on the IHA
for the L-DEO TAIGER survey.
Comment 14: The ETOMO Application should not be ``easy'' because
there are no systematically collected data on cetacean distribution and
abundance in the proposed survey region.
Response: NMFS recognizes that absence of evidence is not the same
as having no effect or impact on the affected marine mammal species or
stocks. 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 L-DEO's application (74 FR 21631,
May 8, 2009); (2) the EA; (3) the BiOp and ITS; and (4) numerous and
salient public comments received by NMFS during the public comment
period. 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 15: The absence of specific data elevates the value of
Kristin Kaschner's Ph.D. thesis, ``Modelling and mapping resource
overlap between marine mammals and fisheries on a global scale,''
(2004) which maps suitable habitat for marine mammals around the world,
ranking the Relative Environmental Suitability (RES) for each species.
Kaschner shows that the Endeavour MPA offers highly suitable habitat
for several species for which the daylight visual observation
mitigation measures are inadequate. She predicts that the habitat is
likely to support sei and sperm whales, which were caught in the region
historically. She predicts that the habitat is likely to support poorly
studied beaked whales (especially Cuvier's [Ziphius cavirostris]),
which are thought to be susceptible to seismic survey impacts. And she
predicts that the study area offers good quality habitat for species
known to be recovering from 20th century commercial whaling, namely
fin, humpback and sperm whales. But this data is not ``real.''
Response: NMFS thanks the commenter for this information and
considers all relevant public comments before making a determination on
the issuance of the IHA. A detailed discussion of the potential effects
of this action on marine mammal habitat, was included in the notice of
the proposed IHA (74 FR 21631, May 8, 2009). Based on the discussion in
the proposed IHA notice, the authorized operations are not expected to
have any habitat-related effects that could cause significant or long-
term consequences for individual marine mammals or their populations or
stocks and 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.
Please note that NMFS' Biological Opinion concludes that the
issuance of the IHA was not likely to jeopardize the continued
existence of the humpback), sei, fin, blue, and sperm (Physeter
macrocephalus) whales.
Comment 16: While science continues to search for ways to get the
necessary data, L-DEO and NSF will continue to believe that their
seismic surveys have no significant effect. It is expected that NMFS
will find ``that the taking will have a negligible impact on the
species or stock(s)'' despite the lack of real information. The absence
of proof of harm is not the same as proving that there is no harm.
Response: See NMFS' response to Comment 14.
Comment 17: First, it has not been adequately explained in the
Draft Environmental Assessment why the ``No Action'' alternative might
be rejected in favor of the project, which, according to the
proponent's own assessment, has the potential to harass several
thousand cetaceans, including eight species described in the notice as
being listed as endangered under the U.S. Endangered Species Act. That
the acquisition of data concerning one natural phenomenon (e.g. ``the
sub-seafloor structure of volcanic and hydrothermal features that form
as a result of movements of the Earth's plates'' (DEA, p2)) should
increase the threat to the existence of another natural phenomenon
(e.g. a species of whale) of equally great (if less generously funded)
academic interest is an illogical and tragic course of action. It
should be noted that it has not been proven that knowledge of the sub-
seafloor structure is of greater long-term importance for the
continuation of human life on Earth than the biodiversity upon which we
are very much dependent.
Response: The commenter's statements on assessing the value of
acquiring information on one natural phenomena (geophysical) versus
another natural phenomena (biodiversity) are not germane to NMFS'
federal action the issuance of an MMPA authorization to L-DEO. Under
section 101(a)(5)(D) of the MMPA, NMFS is required to determine whether
the taking by the applicant's specified activity will have a negligible
impact on the affected marine mammal species or population stocks.
Alternatives assessments are NMFS' responsibility under NEPA, not the
MMPA. In that regard, the NSF's EA and associated EA report contain
adequate information on the alternatives No Action, Another Time, and
Preferred Action. The associated EA report provides a step-by-step
analysis on how the NSF assessed the alternatives, starting with (and
citing) the best scientific information available on marine mammal
distribution and abundance and using those data to make conservative
estimates on levels of take by harassment and reasonable assumptions on
why no marine mammals are likely to be harassed by this survey.
Comment 18: The assessment carried out by LGL for this L-DEO
project must be treated with caution given the very recent experience
of the L-DEO seismic survey currently underway in the waters of
southeast Asia, for which LGL prepared an EA that understated the
numbers of cetaceans of certain species that might be exposed to airgun
noise and the level of potential harassment, misquoted the status of at
least one critically endangered population of cetaceans (the Eastern
Taiwan Strait (ETS) Indo-Pacific humpback dolphins) and resulted in
transect lines running
[[Page 42867]]
directly through the narrow habitat of the ETS humpback dolphins and
the scheduling of surveys near the Philippines that coincided
``spatially and temporally with the northward migration of mothers with
neonatal and other young calves'' (Anon, 2009), to cite a few of the
concerns raised by scientists and NGOs during the comment period for
that project (e.g. https://www.nmfs.noaa.gov/pr/pdfs/permits/taiger_comments.pdf).
Response: NMFS acknowledges WAHLDA's concerns and refers the
commenter to 74 FR 41260, August 14, 2009, for information on the L-DEO
TAIGER survey.
NMFS closely follows NEPA regulations and NOAA Administrative Order
216-6 (Environmental Review Procedures for Implementing the National
Environmental Policy Act, May 20, 1999) before making a determination
on whether it will adopt another Federal agency's NEPA document, or
prepare its own. Critical to this determination is the quality of
another agency's NEPA document, whether it fully addresses the action
proposed by NMFS the issuance of an MMPA authorization to L-DEO, and
whether NMFS' proposed action is significant as defined in 40 CFR
1508.27 and NAO 216-6, section 6.01. As noted in the proposed
authorization notice (74 FR 21631, May 8, 2009), the DEA contained a
complete description of the proposed action and identified alternatives
to that action; a description of the affected environment; an
assessment of impacts, including unavoidable impacts, indirect impacts
and cumulative impacts; and the measures proposed to reduce impacts to
the lowest level practicable. In accordance with NAO 216-6, NMFS has
reviewed the information contained in NSF's EA, and associated EA
report, and determined that, while it accurately and completely
describes the alternatives and the potential impacts, endangered
species and other marine life could be impacted by the survey
activities. As a result, NMFS has identified additional mitigation
measures (e.g., mandatory shut-downs for north Pacific right whales)
which are reflected in the final IHA and the NMFS' Finding of No
Significant Impact (FONSI).
Comment 19: An additional, independent scientific review body is
urgently needed in order to improve the quality of environmental
assessment and recommended actions for this and all other seismic
surveys.
Response: NMFS acknowledges WAHLDA's request and has forwarded your
comment to NSF and L-DEO.
Comment 20: The safety radii for this project are used to decide
how close a marine mammal may approach an operating sound source before
a power-down or shut down is required. With detection of marine mammals
being dependent upon the success of visual and acoustic monitoring, it
is clearly essential that both forms of monitoring are carried out in
such a way as to maximize the potential of detection. However, the
description of the monitoring plans described in the FR notice suggest
once again that worryingly minimal efforts to detect cetaceans will be
made.
Response: See NMFS' response to Comment 1. The Langseth is
utilizing a team of trained (MMVOs) to both visually monitor from the
high observation tower of the Langseth and to conduct passive acoustic
monitoring. When stationed on the observation platform of the Langseth,
the MMVO's 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 8.9
nm (16.5 km) (the largest safety radii is 7.7 km (4.2 nm)). Big eyes
are most effective at scanning the horizon (for blows), while 7 x 50
reticle binoculars are more effective closer in (MMVOs also scan the
area with the naked eye). Additionally, MMVOs will have a good view in
all directions around the entire vessel.
Under section 101(a)(5)(D) of the MMPA, NMFS is required to
determine whether the taking by the applicant's specified activity will
have a negligible impact on the affected marine mammal species or
population stocks. The monitoring and 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.
Comment 21: With a minimum of only one marine mammal visual
observer (MMVO) being required to be on duty during all daytime airgun
operations, and only two observers being required to be on duty for
only thirty minutes before and during ramp-ups (``and when possible at
other times'' (DEA, p.3)) is clearly not a commitment) the chances of
detecting cetaceans in the area (including the exclusion zone) within
which they may be harassed (including level A and level B harassment)
will be limited. Neither one nor two pairs of eyes will be capable of
effectively scanning all areas around the Langseth simultaneously for
cetaceans and turtles that is, if the aim of this measure truly is to
attempt to minimize impacts on cetaceans and turtles. There should at
least be a sufficient number of qualified, experienced visual observers
to simultaneously cover all areas of water within the safety radii on
duty during all periods of use of noise-generating seismic survey
equipment (including before and during ramp-ups and at all other times
of use).
Response: The IHA requires L-DEO to utilize two (except during meal
times), NMFS-qualified, vessel-based marine mammal visual observers
(MMVO) to watch for and monitor marine mammals near the seismic source
vessel during all daytime airgun operations and before and during
start-ups of airguns day or night. See NMFS' response to Comments 1 and
2 for a discussion of visual and acoustic monitoring of the safety
radii.
Comment 22: The idea that passive acoustic monitoring (PAM) should
be used during the day and night ``when practicable'' (DEA, p. 3) again
suggests a reluctance to commit to applying these measures to their
greatest capability, and a level of leniency that leaves room for
almost unlimited exceptions. If L-DEO is serious about carrying out
this seismic survey at the risk of harassing more than thirty marine
mammal species and intends to attempt to mitigate potential impacts to
the (already extremely limited) extent that it can, it should at least
be committed to use PAM at all times during the survey, with no
exceptions. (The operators' need for rest, food or other activities can
be dealt with by increasing the number of (qualified and experienced)
staff on duty and should not be used as a justification for lower
effort to detect cetaceans using PAM).
Response: The IHA requires that L-DEO operates the PAM system both
during the day and at night. The requirement of PAM for marine mammal
detection is intended to provide additional monitoring to the standard
visual monitoring by qualified MMVOs. PAM is not to be solely used for
marine mammal monitoring and detection for the survey and will not
replace visual monitoring. NMFS believes that L-DEO will be able to
effectively monitor out to the 180 dB isopleth.
Comment 23: More worrying still is the fact that there appears,
once again, to be no restriction against using the seismic survey
equipment in the dark or ``at night''. The continuation of seismic
survey activity outside of daylight hours severely reduces the already
limited possibility of detecting cetaceans in the
[[Page 42868]]
vicinity, and effectively reduces monitoring efforts to the use of PAM,
which will obviously not detect cetaceans when they are not vocalizing
and will at certain times only be used ``when practicable''. It is
strongly recommended that no seismic survey activity be carried out
outside of daylight hours during which the entire safety radii are
visible.
Response: The IHA requires that L-DEO operates the PAM system both
during the day and at night. Regarding cessation of seismic activity at
night, L-DEO has considered this recommendation, and has 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 Endeavor cruise. 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.
The IHA prohibits the start of the seismic source if the MMVOs
cannot view the entire safety radius for any reason (darkness, fog, or
rough seas). 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. MMVOs using
night vision devices (NVD) 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.
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.
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 24: The suggestion in the DEA that ``additional research
studies planned on the vessel for 2009 and beyond'' should be a major
deciding factor in whether the survey can be rescheduled (which was
also used as an argument to support night-time surveys for the SE Asia
seismic survey) is not considered a scientifically sound or otherwise
reasonable justification for reducing already limited impact mitigation
measures. Scheduling should be based on the necessary impact mitigation
measures, not vice versa.
Response: Under section 101(a)(5)(D) of the MMPA, NMFS is required
to determine whether the taking by the applicant's specified activity
will have a negligible impact on the affected marine mammal species or
population stocks. 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.
As discussed in the EA report, the scheduling of the Langseth makes
the best use of the vessel to support NSF's science mission. In the EA,
NSF concluded that L-DEO rescheduling the survey to an alternative time
would offer minimal advantages or disadvantages at the Endeavor
location. 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.
Description of Marine Mammals in the Activity Area
Thirty-three marine mammal species may occur off the coast of
British Columbia, Canada, including 20 odontocetes (toothed cetaceans),
7 mysticetes (baleen whales), 5 pinnipeds, and the sea otter (Enhydra
sp.). In the United States, sea otters are managed by the U.S. Fish and
Wildlife Service (USFWS) and are unlikely to be encountered in or near
the Endeavor Marine Protected Area where seismic operations will occur,
and are, therefore, not addressed further in this document. Eight of
these species are listed as endangered under the U.S. Endangered
Species Act of 1973 (ESA), including the Steller sea lion (Eumetopias
jubatus), the humpback sei, fin, blue, North Pacific right (Eubalena
japonica), sperm, and Southern Resident killer (Orcinus orca) whales.
This IHA will only address requested take authorizations for
cetaceans and pinnipeds. Table 2 below outlines the species, their
habitat and abundance in the proposed survey area, and the estimated
exposure levels. Additional information regarding the status and
distribution of the marine mammals in the area as well as how L-DEO
calculated the densities were included in a previous notice for the
proposed IHA (74 FR 21631, May 8, 2009) and in Sections III and IV of
L-DEO's application.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Estimated Number of
Abundance in the NE Occurrence in the Individuals Exposed Approx. Percent
Species Habitat Pacific Survey Area to Sound Levels of Regional
[gteqt]160 dB Population
--------------------------------------------------------------------------------------------------------------------------------------------------------
North Pacific right whale* Coastal and shelf waters 100-200 Rare and unlikely 0 0
--------------------------------------------------------------------------------------------------------------------------------------------------------
Humpback whale* Coastal waters >6000 Uncommon 6 0.10
--------------------------------------------------------------------------------------------------------------------------------------------------------
Minke whale Coastal and shelf waters 9000 Uncommon 5 0.06
--------------------------------------------------------------------------------------------------------------------------------------------------------
Sei whale* Pelagic 7260 - 12,620 Uncommon 1 0.01
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 42869]]
Fin whale* Pelagic, shelf and coastal 13,620-18,680 Uncommon 8 0.05
waters
--------------------------------------------------------------------------------------------------------------------------------------------------------
Blue whale* Pelagic, shelf and inshore 1186 Uncommon 2 0.14
waters
--------------------------------------------------------------------------------------------------------------------------------------------------------
Sperm whale* Pelagic 24,000 Uncommon 10 0.04
--------------------------------------------------------------------------------------------------------------------------------------------------------
Pygmy sperm whale Deep waters off the shelf Not available Common 9 Not available
--------------------------------------------------------------------------------------------------------------------------------------------------------
Dwarf Sperm whale Deep waters off the shelf Not available Uncommon 0 0.0
--------------------------------------------------------------------------------------------------------------------------------------------------------
Baird's beaked whale Deep waters and cont. 6000 Common 13 0.21
slopes
--------------------------------------------------------------------------------------------------------------------------------------------------------
Blainville's beaked whale Deep waters and cont. 603 Uncommon 2 0.28
slopes
--------------------------------------------------------------------------------------------------------------------------------------------------------
Cuvier's beaked whale Pelagic 20,000 Uncommon 0 0.0
--------------------------------------------------------------------------------------------------------------------------------------------------------
Hubb's beaked whale Deep waters and cont. 421 Uncommon 2 0.40
slopes
--------------------------------------------------------------------------------------------------------------------------------------------------------
Stejneger's beaked whale Deep waters 421 Uncommon 2 0.40
--------------------------------------------------------------------------------------------------------------------------------------------------------
Bottlenose dolphin Coastal and offshore waters 3257 Rare 0 0.0
--------------------------------------------------------------------------------------------------------------------------------------------------------
Striped dolphin Pelagic 23,883 Rare 0 0.0
--------------------------------------------------------------------------------------------------------------------------------------------------------
Short-beaked common dolphin Coastal and offshore waters 487,622 Common 104 0.02
--------------------------------------------------------------------------------------------------------------------------------------------------------
Pacific white-sided dolphin Pelagic, shelf and slope 931,000 Common 181 0.02
waters
--------------------------------------------------------------------------------------------------------------------------------------------------------
Northern right-whale dolphin Pelagic, shelf and slope 15,305 Common 142 0.93
waters
--------------------------------------------------------------------------------------------------------------------------------------------------------
Risso's dolphin Pelagic 12,093 Common 95 0.78
--------------------------------------------------------------------------------------------------------------------------------------------------------
False killer whale Pelagic Not available Rare 0 NA
--------------------------------------------------------------------------------------------------------------------------------------------------------
Killer whale Widely distributed 8500 Uncommon 12 0.15
--------------------------------------------------------------------------------------------------------------------------------------------------------
Short-finned pilot whale Pelagic 160,200 Uncommon 0 00.0
--------------------------------------------------------------------------------------------------------------------------------------------------------
Dall's porpoise Offshore and nearshore 57,549 Common 1081 1.88
waters
--------------------------------------------------------------------------------------------------------------------------------------------------------
Northern fur seal Coastal 721,935 Common 73 0.01
--------------------------------------------------------------------------------------------------------------------------------------------------------
Total ........................... ....................... ...................... 1,748 .................
--------------------------------------------------------------------------------------------------------------------------------------------------------
Table 2. Abundance, preferred habitat, and commonness of the marine mammal species that may be encountered during the proposed survey within the ETOMO
survey area. The far right columns indicate the estimated number and percentage of the population of each species that may be exposed to sound levels
[gteqt]160 dB based on average density estimates. NMFS believes that, when mitigation measures are taken into consideration, the activity is likely to
result in take of numbers of animals less than those indicated by the column titled Estimated Number of Individuals Exposed to Sound Levels [gteqt]160
dB.
* Federally listed endangered species.
Potential Effects of the Proposed Activity on Marine Mammals
The effects of sounds from airguns might include one or more of the
following: tolerance, masking of natural sounds, behavioral
disturbance, temporary or permanent hearing impairment, or non-auditory
physical or physiological effects (Richardson et al., 1995; Gordon et
al., 2004; Nowacek et al., 2007; Southall et al., 2007). Permanent
hearing impairment, in the unlikely event that it occurred, would
constitute injury, but temporary threshold shift (TTS) is not an injury
(Southall et al., 2007). Although the possibility cannot be entirely
excluded, it is unlikely that the project would result in any cases of
temporary or permanent hearing impairment, or any significant non-
auditory physical or physiological effects. Some behavioral disturbance
is expected, but is expected to be localized and short-term.
[[Page 42870]]
The notice of the proposed IHA (74 FR 21631, May 8, 2009) included
a discussion of the effects of sounds from airguns on mysticetes
(baleen whales), odontocetes (toothed whales), 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 is discussed in Appendix B of L-DEO's application.
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, 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 or pinnipeds to 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 (74 FR 21631, May 8, 2009) 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. Based on numbers of animals encountered during previous L-
DEO seismic surveys, the likelihood of the successful implementation of
the required mitigation measures, and the likelihood that some animals
will avoid the area around the operating airguns, NMFS believes that L-
DEO's airgun seismic testing program may result in the Level B
harassment of some lower number of individual marine mammals (a few
times each) than is indicated by the column titled, Estimated Number of
Individuals Exposed to Sound Levels [gteqt]160 dB, in Table 2. L-DEO
has