Taking and Importing Marine Mammals; Taking Marine Mammals Incidental to Operation and Maintenance of the Neptune Liquefied Natural Gas Facility off Massachusetts, 34157-34176 [2011-14614]
Download as PDF
34157
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
TABLE 1—REGULATIONS IMPLEMENTING THE HAZARDOUS AND SOLID WASTE AMENDMENTS OF 1984
Promulgation date
Title of regulation
Federal Register reference
*
*
*
*
*
*
June 13, 2011 ......................... Land Disposal Restrictions: Revision of the Treatment 76 FR [Insert page number] ..
Standards for Carbamate Hazardous Wastes.
*
*
*
*
*
*
*
*
*
*
Effective date
*
8/12/11.
*
*
TABLE 2—SELF-IMPLEMENTING PROVISIONS OF THE HAZARDOUS AND SOLID WASTE AMENDMENTS OF 1984
Effective date
Self-implementing provision
RCRA citation
*
*
*
*
*
*
August 12, 2011 ..................... Land Disposal Restrictions: Revision of the Treatment 3004(m) .................................
Standards for Carbamate Hazardous Wastes.
*
*
*
*
*
*
*
*
[FR Doc. 2011–14594 Filed 6–10–11; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 217
[Docket No. 0808041026–1295–02]
RIN 0648–AX09
Taking and Importing Marine
Mammals; Taking Marine Mammals
Incidental to Operation and
Maintenance of the Neptune Liquefied
Natural Gas Facility off Massachusetts
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
NMFS, upon application from
Neptune LNG LLC (Neptune), is issuing
regulations pursuant to the Marine
Mammal Protection Act (MMPA) to
govern the unintentional taking of
marine mammals, by harassment,
incidental to port commissioning and
operations, including maintenance and
repair activities, at the Neptune
Deepwater Port (the Port) in
Massachusetts Bay for the period of July
2011 through July 2016. These
regulations, which allow for the
issuance of Letters of Authorization
(LOAs) for the incidental take of marine
mammals during the described activities
erowe on DSK5CLS3C1PROD with RULES
SUMMARY:
VerDate Mar<15>2010
17:45 Jun 10, 2011
Jkt 223001
*
*
and specified timeframes, prescribe the
permissible methods of taking and other
means of effecting the least practicable
adverse impact on marine mammal
species or stocks and their habitat, as
well as requirements pertaining to the
monitoring and reporting of such taking.
DATES: Effective from July 11, 2011,
through August 10, 2016.
ADDRESSES: A copy of Neptune’s
application may be obtained by writing
to Michael Payne, Chief, Permits,
Conservation and Education Division,
Office of Protected Resources, NMFS,
1315 East West Highway, Silver Spring,
MD 20910, calling the contact listed
under FOR FURTHER INFORMATION
CONTACT, or visiting the Internet at:
https://www.nmfs.noaa.gov/pr/permits/
incidental.htm. Documents cited in this
final rule may also be viewed, by
appointment, during regular business
hours at the above address.
The Final Environmental Impact
Statement (Final EIS) on the Neptune
Deepwater Port License Application
authored by the Maritime
Administration (MARAD) and U.S.
Coast Guard (USCG) is available for
viewing at https://www.regulations.gov
by entering the search words ‘‘Neptune
LNG.’’
FOR FURTHER INFORMATION CONTACT:
Candace Nachman, Office of Protected
Resources, NMFS, (301) 713–2289, ext
156.
SUPPLEMENTARY INFORMATION:
Background
Sections 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1361 et seq.) direct
the Secretary of Commerce to allow,
PO 00000
Frm 00015
Fmt 4700
Sfmt 4700
*
Federal Register
reference
*
76 FR [Insert
Page Numbers]
*
upon request, the incidental, but not
intentional, taking of small numbers of
marine mammals by U.S. citizens who
engage in a specified activity (other than
commercial fishing) within a specified
geographical region if certain findings
are made and either regulations are
issued or, if the taking is limited to
harassment, a notice of a proposed
authorization is provided to the public
for review.
Authorization for incidental takings
shall be granted if NMFS finds that the
taking will have a negligible impact on
the species or stock(s), will not have an
unmitigable adverse impact on the
availability of the species or stock(s) for
subsistence uses (where relevant), and if
the permissible methods of taking and
requirements pertaining to the
mitigation, monitoring and reporting of
such takings are set forth. NMFS has
defined ‘‘negligible impact’’ in 50 CFR
216.103 as ‘‘* * * an impact resulting
from the specified activity that cannot
be reasonably expected to, and is not
reasonably likely to, adversely affect the
species or stock through effects on
annual rates of recruitment or survival.’’
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’’].
E:\FR\FM\13JNR1.SGM
13JNR1
erowe on DSK5CLS3C1PROD with RULES
34158
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
Summary of Request
On December 14, 2009, NMFS
received an application from Neptune
for the taking, by harassment, of marine
mammals incidental to port
commissioning and operations,
including maintenance and repair
activities, at its Neptune Deepwater Port
(Port) facility in Massachusetts Bay.
NMFS reviewed Neptune’s application
and identified a number of issues
requiring further clarification. After
addressing comments from NMFS,
Neptune modified its application and
submitted a revised application on
March 11, 2010. The March 11, 2010,
application was the one made available
for public comment and considered by
NMFS for these regulations.
Neptune submitted its first complete
application to NMFS on December 27,
2007, for the take of small numbers of
marine mammals, by harassment,
incidental to the construction phase of
the Neptune LNG Port Facility. In June
2008, NMFS issued a 1-year Incidental
Harassment Authorization (IHA) to
Neptune for the construction of the Port
(73 FR 33400, June 12, 2008). This
authorization expired on June 30, 2009.
NMFS issued a second 1-year IHA to
Neptune for the completion of
construction and beginning of Port
operations on June 26, 2009 (74 FR
31926, July 6, 2009), which expired on
June 30, 2010.
On July 12, 2010, NMFS issued a
third IHA to Neptune based on the
request in its March 11, 2010,
application (75 FR 41440, July 16,
2010). This latest IHA is effective
through July 11, 2011. During the period
of this third IHA, Neptune conducted
limited port operations.
During the effective period of this
final rule (July 2011–July 2016),
Neptune intends to continue port
operations (including commissioning of
its second shuttle regasification vessel
[SRV]) and conduct maintenance and
repairs, as needed. The Neptune Port is
located approximately 22 mi (35 km)
northeast of Boston, Massachusetts, in
Federal waters approximately 260 ft (79
m) in depth. The purpose of the Port is
to import liquefied natural gas (LNG)
into the New England region. Take of
marine mammals may occur during port
operations from thruster use during
maneuvering of the SRVs while docking
and undocking, occasional
weathervaning (turning of a vessel at
anchor from one direction to another
under the influence of wind or currents)
at the Port, and during thruster use of
dynamic positioning (DP) maintenance
vessels should a major repair be
necessary. Neptune requested
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
authorization to take 12 marine mammal
species by Level B harassment. The
species are: North Atlantic right whale;
humpback whale; fin whale; sei whale;
minke whale; long-finned pilot whale;
Atlantic white-sided dolphin; harbor
porpoise; common dolphin; Risso’s
dolphin; bottlenose dolphin; and harbor
seal. In the 2009 and 2010 IHAs, NMFS
also authorized take of killer whales and
gray seals. NMFS has determined that it
would be appropriate in this final rule
to authorize take, by Level B harassment
only, incidental to operations and
maintenance activities of these two
species as well. In this final rule, NMFS
has authorized the take, by Level B
harassment, of all 14 marine mammal
species listed here.
Description of the Specified Activity
On March 23, 2007, Neptune received
a license from MARAD to own,
construct, and operate a deepwater port.
The Port, which is located in
Massachusetts Bay, consists of a
submerged buoy system to dock
specifically designed LNG carriers
approximately 22 mi (35 km) northeast
of Boston, Massachusetts, in Federal
waters approximately 260 ft (79 m) in
depth. The two buoys are separated
from one another by a distance of
approximately 2.1 mi (3.4 km). The
locations of the Neptune Port and the
associated pipeline are shown in Figure
2–1 in Neptune’s application (see
ADDRESSES).
All construction of the Neptune Port
was completed in November 2009. The
first SRV was commissioned in
February–March 2010. Between July
2011 and July 2016, (the time period for
these regulations), Neptune plans to
continue Port operations (including
commissioning of its second SRV) and
also plans to conduct any necessary
maintenance and repairs of the Port
facility.
Neptune will be capable of mooring
LNG SRVs with a capacity of
approximately 183,113 cubic yards (yd3;
140,000 cubic meters (m3)) of LNG. Up
to two SRVs will temporarily moor at
the Port by means of a submerged
unloading buoy system. Two separate
buoys will allow natural gas to be
delivered in a continuous flow, without
interruption, by having a brief overlap
between arriving and departing SRVs.
The annual average throughput capacity
will be around 500 million standard
cubic feet per day (mmscfd) with an
initial throughput of 400 mmscfd and a
peak capacity of approximately 750
mmscfd of LNG.
The SRVs will be equipped to store,
transport, and vaporize LNG and to
odorize, meter and send out natural gas
PO 00000
Frm 00016
Fmt 4700
Sfmt 4700
by means of two 16-in (40.6-cm) flexible
risers and one 24-in (61-cm) subsea
flowline. These risers and flowline will
lead to a 24-in (61-cm) gas transmission
pipeline connecting the deepwater port
to the existing 30-in (76.2-cm)
Algonquin HublineSM (HublineSM)
located approximately 9 mi (14.5 km)
west of the Neptune deepwater port
location. The Port will have an expected
operating life of approximately 25 years.
Figure 1–1 of Neptune’s application
shows an isometric view of the Port (see
ADDRESSES). A detailed overview of Port
operations and maintenance and repair
activities, as well as the types of sounds
those activities produce, was provided
in the proposed rule (75 FR 80260,
December 21, 2010). No changes have
been made to the proposed operations
or maintenance and repair activities.
Description of Marine Mammals in the
Area of the Specified Activity
Massachusetts Bay (as well as the
entire Atlantic Ocean) hosts a diverse
assemblage of marine mammals,
including: The North Atlantic right
whale; blue whale; fin whale; sei whale;
minke whale; humpback whale; killer
whale; long-finned pilot whale; sperm
whale; Atlantic white-beaked dolphin;
Atlantic white-sided dolphin; bottlenose
dolphin; common dolphin; harbor
porpoise; Risso’s dolphin; striped
dolphin; gray seal; harbor seal; harp
seal; and hooded seal. Table 3–1 in
Neptune’s application outlines the
marine mammal species that occur in
Massachusetts Bay and the likelihood of
occurrence of each species. Of the
species listed here, the North Atlantic
right, blue, fin, sei, humpback, and
sperm whales are all listed as
endangered under the Endangered
Species Act (ESA) and as depleted
under the MMPA. The northern coastal
stock of bottlenose dolphins is
considered depleted under the MMPA.
Certain stocks or populations of killer
whales are listed as endangered under
the ESA or depleted under the MMPA;
however, none of those stocks or
populations occurs in the activity area.
Of these species, 14 are expected to
occur in the area of Neptune’s
operations. These species include: The
North Atlantic right, humpback, fin, sei,
minke, killer, and long-finned pilot
whales; Atlantic white-sided, common,
Risso’s, and bottlenose dolphins; harbor
porpoise; and harbor and gray seals.
Neptune used information from the
Cetacean and Turtle Assessment
Program (CETAP; 1982) and the U.S.
Navy’s Marine Resource Assessment
(MRA) for the Northeast Operating
Areas (DoN, 2005; available on the
Internet at: https://
E:\FR\FM\13JNR1.SGM
13JNR1
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
erowe on DSK5CLS3C1PROD with RULES
portal.navfac.navy.mil/portal/page/
portal/navfac/navfac_ww_pp/
navfac_hq_pp/navfac_environmental/
mra) to estimate densities of the species
in the area. Nonetheless, NMFS used the
data on cetacean distribution within
Massachusetts Bay, such as those
published by NOAA’s National Centers
for Coastal Ocean Science (NCCOS;
2006), to determine density estimates of
several species of marine mammals in
the vicinity of the project area. The
explanation for those derivations and
the actual density estimates are
described later in this document (see the
‘‘Estimated Take by Incidental
Harassment’’ section).
The proposed rule contains a
discussion of 17 marine mammal
species that are not considered further
in the analysis because of their rarity in
the Massachusetts Bay area (blue whale,
sperm whale, harp seal, hooded seal,
ringed seal, northern bottlenose whale,
Cuvier’s beaked whale, Sowerby’s
beaked whale, Blainville’s beaked
whale, Gervais’ beaked whale, True’s
beaked whale, beluga whale,
pantropical spotted dolphin, false killer
whale, pygmy sperm whale, striped
dolphin, and Atlantic white-beaked
dolphin). The proposed rule also
contains brief summaries on several
commonly sighted marine mammal
species distribution and abundance in
the vicinity of the action area. The
‘‘Description of Marine Mammals in the
Area of the Specified Activity’’ has not
changed from the proposed rule. Please
refer to the proposed rule (75 FR 80260,
December 21, 2010) for the complete
discussion.
Additionally, information on those
species that may be impacted by this
activity is provided in Neptune’s
application and sections 3.2.3 and 3.2.5
in the MARAD/USCG Final EIS on the
Neptune LNG proposal (see ADDRESSES).
Please refer to those documents for more
information on these species. Also,
general information on these marine
mammal species can also be found in
the 2009 NMFS U.S. Atlantic and Gulf
of Mexico Marine Mammal Stock
Assessment Report (SAR; Waring et al.,
2009) and the 2010 Draft NMFS Atlantic
and Gulf of Mexico Marine Mammal
SAR (Waring et al., in prep.), which are
available on the Internet at: https://
www.nefsc.noaa.gov/publications/tm/
tm213/ and https://www.nmfs.noaa.gov/
pr/sars/draft.htm, respectively.
Brief Background on Marine Mammal
Hearing
When considering the influence of
various kinds of sound on the marine
environment, it is necessary to
understand that different kinds of
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
marine life are sensitive to different
frequencies of sound. Based on available
behavioral data, audiograms derived
using auditory evoked potential
techniques, anatomical modeling, and
other data, Southall et al. (2007)
designate ‘‘functional hearing groups’’
for marine mammals and estimate the
lower and upper frequencies of
functional hearing of the groups. The
functional groups and the associated
frequencies are indicated below (though
animals are less sensitive to sounds at
the outer edge of their functional range
and most sensitive to sounds of
frequencies within a smaller range
somewhere in the middle of their
functional hearing range):
• Low frequency cetaceans (13
species of mysticetes): Functional
hearing is estimated to occur between
approximately 7 Hz and 22 kHz
(however, a study by Au et al. (2006) of
humpback whale songs indicate that the
range may extend to at least 24 kHz);
• Mid-frequency cetaceans (32
species of dolphins, six species of larger
toothed whales, and 19 species of
beaked and bottlenose whales):
functional hearing is estimated to occur
between approximately 150 Hz and 160
kHz;
• High frequency cetaceans (eight
species of true porpoises, six species of
river dolphins, Kogia, the franciscana,
and four species of cephalorhynchids):
functional hearing is estimated to occur
between approximately 200 Hz and 180
kHz; and
• Pinnipeds in Water: functional
hearing is estimated to occur between
approximately 75 Hz and 75 kHz, with
the greatest sensitivity between
approximately 700 Hz and 20 kHz.
As mentioned previously in this
document, 14 marine mammal species
(12 cetacean and two pinniped species)
are likely to occur in the Neptune Port
area. Of the 12 cetacean species likely
to occur in Neptune’s project area, five
are classified as low frequency
cetaceans (i.e., North Atlantic right,
humpback, fin, minke, and sei whales),
six are classified as mid-frequency
cetaceans (i.e., killer and pilot whales
and bottlenose, common, Risso’s, and
Atlantic white-sided dolphins), and one
is classified as a high-frequency
cetacean (i.e., harbor porpoise) (Southall
et al., 2007).
Potential Effects of the Specified
Activity on Marine Mammals
With respect to the MMPA, NMFS’
effects assessment serves four primary
purposes: (1) To prescribe the
permissible methods of taking (i.e.,
Level B Harassment, including an
identification of the number and types
PO 00000
Frm 00017
Fmt 4700
Sfmt 4700
34159
of take that could occur by Level B
harassment) and to prescribe other
means of effecting the least practicable
adverse impact on such species or stock
and its habitat (i.e., mitigation); (2) to
determine whether the specified activity
will have a negligible impact on the
affected species or stocks of marine
mammals (based on the likelihood that
the activity will adversely affect the
species or stock through effects on
annual rates of recruitment or survival);
(3) to determine whether the specified
activity will have an unmitigable
adverse impact on the availability of the
species or stock(s) for subsistence uses
(however, there are no subsistence
communities that would be affected in
the Massachusetts Bay area, so this
determination is inapplicable for this
rulemaking); and (4) to prescribe
requirements pertaining to monitoring
and reporting.
Potential effects of Neptune’s
proposed port operations and
maintenance/repair activities would
most likely be acoustic in nature. LNG
port operations and maintenance/repair
activities introduce sound into the
marine environment. Potential acoustic
effects on marine mammals relate to
sound produced by thrusters during
maneuvering of the SRVs while docking
and undocking, occasional
weathervaning at the port, and during
thruster use of DP maintenance vessels
should a major repair be necessary. The
potential effects of sound from the
activities associated with the Neptune
Port might include one or more of the
following: tolerance; masking of natural
sounds; behavioral disturbance; nonauditory physical effects; and, at least in
theory, temporary or permanent hearing
impairment (Richardson et al., 1995).
However, for reasons discussed in the
proposed rule, it is unlikely that there
would be any cases of temporary, or
especially permanent, hearing
impairment resulting from these
activities.
In the ‘‘Potential Effects of Specified
Activities on Marine Mammals’’ section
of the proposed rule, NMFS included a
qualitative discussion of the different
ways that port operations and repair and
maintenance activities may potentially
affect marine mammals. Marine
mammals may experience masking and
behavioral disturbance. The information
contained in the ‘‘Potential Effects of
Specified Activities on Marine
Mammals’’ section from the proposed
rule has not changed. Please refer to the
proposed rule for the full discussion (75
FR 80260, December 21, 2010).
E:\FR\FM\13JNR1.SGM
13JNR1
34160
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
Anticipated Effects on Habitat
The primary potential impacts to
marine mammals and other marine
species are associated with elevated
sound levels produced by the Port
operations and maintenance/repair
activities. However, other potential
impacts from physical disturbance are
also possible. Major repairs to the
Neptune port and pipeline may affect
marine mammal habitat in several ways:
cause disturbance of the seafloor;
increase turbidity slightly; and generate
additional underwater sound in the
area. These underwater sound levels
will cause some species to temporarily
disperse from or avoid repair areas, but
they are expected to return shortly after
the repair is completed. Operation of the
Port will result in long-term, continued
disturbance of the seafloor, regular
withdrawal of seawater, and generation
of underwater sound. The proposed rule
contained a full discussion of the
potential impacts to marine mammal
habitat and prey species in the project
area. No changes have been made to that
discussion. Please refer to the proposed
rule for the full discussion of potential
impacts to marine mammal habitat (75
FR 80260, December 21, 2010). NMFS
has determined that Neptune’s proposed
port operations and maintenance/repair
activities are not expected to have any
habitat-related effects that could cause
significant or long-term consequences
for individual marine mammals or on
the food sources that they utilize.
erowe on DSK5CLS3C1PROD with RULES
Mitigation
In order to issue an incidental take
authorization (ITA) under section
101(a)(5)(A) of the MMPA, NMFS must,
where applicable, set forth the
permissible methods of taking pursuant
to such activity, and other means of
effecting the least practicable adverse
impact on such species or stock and its
habitat, paying particular attention to
rookeries, mating grounds, and areas of
similar significance, and on the
availability of such species or stock for
taking for certain subsistence uses
(where relevant).
Neptune proposed several mitigation
measures in the application (see
ADDRESSES). After a review of these
measures, NMFS determined that some
additional measures should also be
implemented in order to effect the least
practicable adverse impact on the
species or stock and its habitat. Both
sets of measures are discussed next.
Mitigation Measures in Neptune’s
Application
Neptune submitted a ‘‘Marine
Mammal Detection, Monitoring, and
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
Response Plan for the Operations Phase’’
(the Plan) as part of its MMPA
application (Appendix D of the
application; see ADDRESSES). The
measures, which include safety zones
and vessel speed reductions, are fully
described in the Plan and summarized
here. Some slight changes have been
made in this final rule (from what
appears in the Plan) based on public
comments or for clarification purposes.
An explanation of the changes is
contained in the ‘‘Comments and
Responses’’ section found later in this
document.
The 500-yd (457 m) safety zone for
North Atlantic right whales is based on
the approach regulation found at 50 CFR
224.103. The 100 yd (91 m) safety zone
for other marine mammal species was
taken from measures included in the
2007 Biological Opinion completed by
NMFS’ Northeast Regional Office. Any
maintenance and/or repairs needed
shall be scheduled in advance during
the May 1 to November 30 seasonal
window, whenever possible, so that
disturbance to North Atlantic right
whales will be largely avoided. If the
repair cannot be scheduled during this
time frame, additional mitigation
measures are required in these
regulations and described in part (2) of
this section.
(1) Mitigation Measures for Major
Repairs (May 1 to November 30)
(A) During repairs, if a marine
mammal is detected within 0.6 mi (1
km) of the repair vessel (or acoustically),
the vessel superintendent or on-deck
supervisor will be notified immediately.
The vessel’s crew will be put on a
heightened state of alert. The marine
mammal will be monitored constantly
to determine if it is moving toward the
repair area.
(B) Repair vessels will cease any
movement in the area if a marine
mammal other than a right whale is
sighted within or approaching to a
distance of 100 yd (91 m) from the
operating repair vessel. Repair vessels
will cease any movement in the area if
a right whale is sighted within or
approaching to a distance of 500 yd (457
m) from the operating vessel. Vessels
transiting the repair area, such as pipe
haul barge tugs, will also be required to
maintain these separation distances.
(C) Repair vessels will cease all sound
emitting activities if a marine mammal
other than a right whale is sighted
within or approaching to a distance of
100 yd (91 m) or if a right whale is
sighted within or approaching to a
distance of 500 yd (457 m), from the
operating repair vessel. The backcalculated source level, based on the
PO 00000
Frm 00018
Fmt 4700
Sfmt 4700
most conservative cylindrical model of
acoustic energy spreading, is estimated
to be 139 dB re 1 μPa.
(D) Repair activities may resume after
the marine mammal is positively
reconfirmed outside the established
zones (either 500 yd (457 m) or 100 yd
(91 m), depending upon species) or if
the marine mammal has not been resighted in the established zones for 30
minutes.
(E) While under way, all repair
vessels will remain 500 yd (457 m) away
from right whales and 100 yd (91 m)
away from all other marine mammals,
unless constrained by human safety
concerns or navigational constraints.
(F) All repair vessels 300 gross tons or
greater will maintain a speed of 10 knots
(18.5 km/hr) or less. Vessels less than
300 gross tons carrying supplies or crew
between the shore and the repair site
will contact the Mandatory Ship
Reporting System, the USCG, or the
protected species observers (PSOs) at
the repair site before leaving shore for
reports of recent right whale sightings or
active Dynamic Management Areas
(DMAs) and, consistent with navigation
safety, restrict speeds to 10 knots (18.5
km/hr) or less within 5 mi (8 km) of any
recent sighting location and within any
existing DMA.
(G) Vessels transiting through the
Cape Cod Canal and Cape Cod Bay
(CCB) between January 1 and May 15
will reduce speeds to 10 knots (18.5 km/
hr) or less, follow the recommended
routes charted by NOAA to reduce
interactions between right whales and
shipping traffic, and avoid aggregations
of right whales in the eastern portion of
CCB.
(2) Additional Port and Pipeline Major
Repair Measures (December 1 to April
30)
If unplanned/emergency repair
activities cannot be conducted between
May 1 and November 30, Neptune is
required to implement the following
additional mitigation measures:
(A) If on-board PSOs do not have at
least 0.6-mi (1-km) visibility, they shall
call for a shutdown of repair activities.
If dive operations are in progress, then
they shall be halted and divers brought
on board until visibility is adequate to
see a 0.6-mi (1-km) range. At the time
of shutdown, the use of thrusters must
be minimized to the lowest level needed
to maintain personnel safety. If there are
potential safety problems due to the
shutdown, the captain will decide what
operations can safely be shut down and
will document such activities in the
data log.
(B) Prior to leaving the dock to begin
transit, the barge will contact one of the
E:\FR\FM\13JNR1.SGM
13JNR1
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
erowe on DSK5CLS3C1PROD with RULES
PSOs on watch to receive an update of
sightings within the visual observation
area (within 0.6 mi (1 km) of the Port).
If the PSO has observed a North Atlantic
right whale within 30 minutes of the
transit start, the vessel will hold for 30
minutes and again seek clearance to
leave from the PSOs on board. PSOs
will assess whale activity and visual
observation ability at the time of the
transit request to clear the barge for
release and will grant clearance if no
North Atlantic right whales have been
sighted in the last 30 minutes in the
visual observation area. [Similar
requirements from the acoustic
monitoring system is required and
discussed part (4) of this subsection.]
(C) Neptune or its contractor shall
provide a half-day training course to
designated crew members assigned to
the transit barges and other support
vessels who will have responsibilities
for watching for marine mammals. This
course shall cover topics including, but
not limited to, descriptions of the
marine mammals found in the area,
mitigation and monitoring requirements
contained in the LOA, sighting log
requirements, and procedures for
reporting injured or dead marine
mammals. These designated crew
members will be required to keep watch
on the bridge and immediately notify
the navigator of any whale sightings. All
watch crew members will sign into a
bridge log book upon the start and end
of watch. Transit route, destination, sea
conditions, and any protected species
sightings/mitigation actions during
watch will be recorded in the log book.
Any whale sightings within 3,281 ft
(1,000 m) of the vessel will result in a
high alert and slow speed of 4 knots (7.4
km/hr) or less. A sighting within 2,461
ft (750 m) will result in idle speed and/
or ceasing all movement.
(D) The material barges and tugs used
for repair work shall transit from the
operations dock to the work sites during
daylight hours, when possible, provided
the safety of the vessels is not
compromised. Should transit at night be
required, the maximum speed of the tug
will be 5 knots (9.3 km/hr).
(E) Consistent with navigation safety,
all repair vessels must maintain a speed
of 10 knots (18.5 km/hr) or less during
daylight hours. All vessels will operate
at 5 knots (9.3 km/hr) or less at all times
within 3.1 mi (5 km) of the repair area.
(3) Speed Restrictions in Seasonal
Management Areas (SMAs)
Repair vessels and SRVs will transit at
10 knots (18.5 km/hr) or less in the
following seasons and areas, which
either correspond to or are more
restrictive than the times and areas in
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
NMFS’ regulations at 50 CFR 224.105
that implement speed restrictions to
reduce the likelihood and severity of
ship strikes of right whales:
• CCB SMA from January 1 through
May 15, which includes all waters in
CCB, extending to all shorelines of the
Bay, with a northern boundary of 42°
12′ N. latitude;
• Off Race Point SMA year round,
which is bounded by straight lines
connecting the following coordinates in
the order stated: 42°30′ N. 69°45′ W.;
thence to 42°30′ N. 70°30′ W.; thence to
42°12′ N. 70°30′ W.; thence to 42°12′ N.
70°12′ W.; thence to 42°04′56.5″ N.
70°12′ W.; thence along mean high
water line and inshore limits of
COLREGS limit to a latitude of 41°40′
N.; thence due east to 41°41′ N. 69°45′
W.; thence back to starting point; and
• Great South Channel (GSC) SMA
from April 1 through July 31, which is
bounded by straight lines connecting
the following coordinates in the order
stated:
42°30′ N. 69°45′ W.
41°40′ N. 69°45′ W.
41°00′ N. 69°05′ W.
42°09′ N. 67°08′24″ W.
42°30′ N. 67°27′ W.
42°30′ N. 69°45′ W.
(A) When approaching and departing
from the Neptune Port, SRVs shall use
the Boston Traffic Separation Scheme
(TSS) starting and ending at the
entrance to the GSC. Upon entering the
TSS, the SRV shall go into a ‘‘heightened
awareness’’ mode of operation, which is
outlined in great detail in the Plan (see
Neptune’s application).
(B) In the event that a whale is
visually observed within 0.6 mi (1 km)
of the Port or a confirmed acoustic
detection is reported on either of the
two auto-detection buoys (ABs; more
information on the acoustic devices is
contained in the ‘‘Monitoring and
Reporting’’ section later in this
document) closest to the Port, departing
SRVs shall delay their departure from
the Port, unless extraordinary
circumstances, defined in the Plan,
require that the departure is not
delayed. The departure delay shall
continue until either the observed whale
has been visually (during daylight
hours) confirmed as more than 0.6 mi (1
km) from the Port or 30 minutes have
passed without another confirmed
detection either acoustically within the
acoustic detection range of the two ABs
closest to the Port or visually within 0.6
mi (1 km) from Neptune.
(C) SRVs that are approaching or
departing from the Port and are within
Frm 00019
Fmt 4700
Sfmt 4700
the Area to be Avoided (ATBA)
surrounding Neptune shall remain at
least 0.6 mi (1 km) away from any
visually detected right whales and at
least 100 yd (91 m) away from all other
visually detected whales unless
extraordinary circumstances, as defined
in Section 1.2 of the Plan in Neptune’s
application, require that the vessel stay
its course. The ATBA is defined in 33
CFR 150.940. It is the largest area of the
Port marked on nautical charts, and it is
enforceable by the USCG in accordance
with the 33 CFR 150.900 regulations.
The Vessel Master shall designate at
least one lookout to be exclusively and
continuously monitoring for the
presence of marine mammals at all
times while the SRV is approaching or
departing Neptune.
(D) Neptune will ensure that other
vessels providing support to Neptune
operations during regasification
activities that are approaching or
departing from the Port and are within
the ATBA shall be operated so as to
remain at least 0.6 mi (1 km) away from
any visually detected right whales and
at least 100 yd (91 m) from all other
visually detected whales.
Additional Mitigation Measures
Required by NMFS
(4) Additional Mitigation Measures
PO 00000
34161
In addition to the mitigation measures
in Neptune′s application, NMFS has
required the following measures in
these regulations in order to ensure the
least practicable adverse impact on the
affected species or stocks:
(1) Neptune must immediately
suspend any repair and maintenance or
operations activities if a dead or injured
marine mammal is found in the vicinity
of the project area, and the death or
injury of the animal could be
attributable to the LNG facility
activities. Upon finding a dead or
injured marine mammal, Neptune must
contact NMFS, the Northeast Stranding
and Disentanglement Program, and the
USCG. NMFS will review the
documentation submitted by the PSO
and attempt to attribute a cause of
death. Activities will not resume until
review and approval has been given by
NMFS.
(2) PSOs will direct a moving vessel
to slow to idle if a baleen whale is seen
less than 0.6 mi (1 km) from the vessel.
(3) Use of lights during repair or
maintenance activities shall be limited
to areas where work is actually
occurring, and all other lights must be
extinguished. Lights must be
downshielded to illuminate the deck
and shall not intentionally illuminate
surrounding waters, so as not to attract
whales or their prey to the area.
E:\FR\FM\13JNR1.SGM
13JNR1
34162
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
Mitigation Conclusions
NMFS has carefully evaluated the
applicant’s proposed mitigation
measures and considered a range of
other measures in the context of
ensuring that NMFS prescribes the
means of effecting the least practicable
adverse impact on the affected marine
mammal species and stocks and their
habitat. Our evaluation of potential
measures included consideration of the
following factors in relation to one
another:
• The manner in which, and the
degree to which, the successful
implementation of the measure is
expected to minimize adverse impacts
to marine mammals;
• The proven or likely efficacy of the
specific measure to minimize adverse
impacts as planned; and
• The practicability of the measure
for applicant implementation.
Based on our evaluation of the
applicant’s proposed measures, as well
as other measures considered by NMFS
or recommended by the public, NMFS
has determined that the mitigation
measures described above, including the
adaptive management component (see
the ‘‘Adaptive Management’’ section
later in this document), provide the
means of effecting the least practicable
adverse impact on marine mammal
species or stocks and their habitat,
paying particular attention to rookeries,
mating grounds, and areas of similar
significance.
Monitoring and Reporting
erowe on DSK5CLS3C1PROD with RULES
In order to issue an ITA for an
activity, section 101(a)(5)(A) of the
MMPA states that NMFS must, where
applicable, set forth ‘‘requirements
pertaining to the monitoring and
reporting of such taking.’’ The MMPA
implementing regulations at 50 CFR
216.104(a)(13) indicate that requests for
ITAs must include the suggested means
of accomplishing the necessary
monitoring and reporting that will result
in increased knowledge of the species
and of the level of taking or impacts on
populations of marine mammals that are
expected to be present in the action
area.
Neptune proposed both visual and
acoustic monitoring programs in the
Plan contained in the application.
Summaries of those plans, as well as the
proposed reporting, are contained here.
Passive Acoustic Monitoring
Neptune LNG will deploy and
maintain a passive acoustic detection
network along a portion of the TSS and
in the vicinity of Neptune. This network
will consist of autonomous recording
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
units (ARUs) and near-real-time ABs. To
develop, implement, collect, and
analyze the acoustic data obtained from
deployment of the ARUs and ABs, as
well as to prepare reports and maintain
the passive acoustic detection network,
Neptune LNG has engaged the Cornell
University Bioacoustic Research
Program (BRP) in Ithaca, New York, and
the Woods Hole Oceanographic
Institution (WHOI) in Woods Hole,
Massachusetts.
During June 2008, an array of 19
passive seafloor ARUs was deployed by
BRP for Neptune. The layout of the
array centered on the terminal site and
was used to monitor the noise
environment in Massachusetts Bay in
the vicinity of Neptune during
construction of the Port and associated
pipeline lateral. The ARUs were not
designed to provide real-time or nearreal-time information about vocalizing
whales. Rather, archival noise data
collected from the ARU array were used
for the purpose of understanding the
seasonal occurrences and overall
distributions of whales (primarily North
Atlantic right whales) within
approximately 11.5 mi (18.5 km) of the
Neptune Port. Neptune LNG will
maintain these ARUs in the same
configuration for a period of 5 years
during operation of the Neptune Port in
order to monitor the actual acoustic
output of port operations and to alert
NOAA to any unanticipated effects of
port operations, such as large scale
abandonment by marine mammals of
the area. To further assist in evaluations
of Neptune’s acoustic output, source
levels associated with DP of SRVs at the
buoys will be estimated using empirical
measurements collected from the
passive detection network. If it is
determined that this network is
insufficient to collect the data, then
source levels shall be collected from a
platform as close as practicable to
thrusters while in use.
In addition to the ARUs, Neptune
LNG has deployed 10 ABs within the
Separation Zone of the TSS for the
operational life of the Port. The purpose
of the AB array is to detect the presence
of vocalizing North Atlantic right
whales. Each AB has an average
detection range of 5.8 mi (9.3 km) from
the AB, although detection ranges will
vary based on ambient underwater
conditions. The AB system will be the
primary detection mechanism that alerts
the SRV Master to the occurrence of
right whales in the TSS and triggers
heightened SRV awareness. The
configurations of the ARU array and AB
network (see Figure 3 in the Plan in
Neptune’s application) were based upon
PO 00000
Frm 00020
Fmt 4700
Sfmt 4700
configurations developed and
recommended by NOAA personnel.
Each AB deployed in the TSS will
continuously screen the low-frequency
acoustic environment (less than 1,000
Hz) for right whale contact calls
occurring within an approximately 5.8mi (9.3-km) radius from each buoy (the
ABs’ detection range) and rank
detections on a scale from 1 to 10. Each
AB shall transmit up to 10 clips with
ratings 6–10 in near-real-time via
Iridium satellite link to the BRP server
Web site every 20 minutes during
periods of heightened awareness
(otherwise AB detections are
transmitted at a rate of 5 clips per 6
hours). This 20-minute transmission
schedule was determined by
consideration of a combination of
factors including the tendency of right
whale calls to occur in clusters (leading
to a sampling logic of listening for other
calls rather than transmitting
immediately upon detection of a
possible call) and the amount of battery
power required to complete a satellite
transmission. Additional details on the
protocol can be found in Neptune’s
application.
Additional passive acoustic
monitoring shall be required, on a caseby-case basis, during both planned and
emergency repair activities in order to
better detect right whales in the area of
repair work and to collect additional
data on the noise levels produced
during repair and maintenance
activities. Neptune shall work with
NOAA (NMFS and SBNMS) to evaluate
when to install real-time passive
acoustic detection buoys to provide
early warnings for potential occurrence
of right whales in the vicinity of the
repair area. The number of passive
acoustic detection buoys installed
around the activity site, if deemed
necessary, shall be commensurate with
the type and spatial extent of
maintenance/repair work required but
must be sufficient to detect vocalizing
right whales within the 120-dB impact
zone. In addition, Neptune shall provide
NMFS with empirically measured
source level data for all sources of noise
associated with LNG port maintenance
and repair activities. Measurements
shall be carefully planned and
coordinated with noise-producing
activities and shall be collected from the
passive detection network.
Visual Monitoring
(1) Maintenance and Repair Activities
During maintenance- and repairrelated activities, Neptune LNG shall
employ qualified PSOs on each vessel
that has a DP system. All PSOs must
E:\FR\FM\13JNR1.SGM
13JNR1
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
receive training and be approved in
advance by NOAA after a review of their
qualifications. Qualifications for these
PSOs shall include direct field
experience on a marine mammal
observation vessel and/or aerial surveys
in the Atlantic Ocean/Gulf of Mexico.
Two PSOs are on-duty at all times. Each
vessel typically has four PSOs on-board
at all times. The PSOs (one primary and
one secondary) are responsible for
visually locating marine mammals at the
ocean’s surface and, to the extent
possible, identifying the species. The
primary PSO shall act as the
identification specialist, and the
secondary PSO will serve as data
recorder and will assist with
identification. Both PSOs shall have
responsibility for monitoring for the
presence of marine mammals.
The PSOs shall monitor the area
where maintenance and repair work is
conducted using the naked eye, handheld binoculars, and/or power
binoculars (e.g, Big Eyes). Two PSOs are
on-duty 24 hours/day and switch
between primary and secondary duties
(as described in the previous paragraph)
about every 40–60 minutes. During
nighttime watches, PSOs are equipped
with night vision devices. All sightings
must be recorded on marine mammal
field sighting logs.
erowe on DSK5CLS3C1PROD with RULES
(2) Operations
While an SRV is navigating within the
designated TSS, three people have
lookout duties on or near the bridge of
the ship including the SRV Master, the
Officer-of-the-Watch, and the Helmsman
on watch. In addition to standard watch
procedures, while the SRV is within the
ATBA and/or while actively engaging in
the use of thrusters, an additional
lookout shall be designated to
exclusively and continuously monitor
for marine mammals. Once the SRV is
moored and regasification activities
have begun, the vessel is no longer
considered to be in ‘‘heightened
awareness’’ status. However, when
regasification activities conclude and
the SRV prepares to depart from
Neptune, the Master shall once again
ensure that the responsibilities as
defined in the Plan are carried out. All
sightings of marine mammals by the
designated lookout, individuals posted
to navigational lookout duties, and/or
any other crew member while the SRV
is within the TSS, in transit to the
ATBA, within the ATBA, and/or when
actively engaging in the use of thrusters
shall be immediately reported to the
Officer-of-the-Watch who shall then
alert the Master.
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
Reporting Measures
Since the Neptune Port is within the
Mandatory Ship Reporting Area
(MSRA), all SRVs transiting to and from
Neptune shall report their activities to
the mandatory reporting section of the
USCG to remain apprised of North
Atlantic right whale movements within
the area. All vessels entering and exiting
the MSRA shall report their activities to
WHALESNORTH. Vessel operators shall
contact the USCG by standard
procedures promulgated through the
Notice to Mariner system.
For major repair work associated with
the pipeline lateral or other port
components, Neptune LNG shall notify
the appropriate NOAA personnel as
soon as practicable after it is determined
that repair work must be conducted.
During maintenance and repair of the
pipeline lateral or other port
components, weekly status reports must
be provided to NOAA. The weekly
report must include data collected for
each distinct marine mammal species
observed in the project area during the
period of the repair activity. The weekly
reports shall include the following:
• The location, time, and nature of
the pipeline lateral repair activities;
• Whether the DP system was
operated and, if so, the number of
thrusters used and the time and
duration of DP operation;
• Marine mammals observed in the
area (number, species, age group, and
initial behavior);
• The distance of observed marine
mammals from the repair activities;
• Observed marine mammal
behaviors during the sighting;
• Whether any mitigation measures
were implemented;
• Weather conditions (sea state, wind
speed, wind direction, ambient
temperature, precipitation, and percent
cloud cover, etc.);
• Condition of the marine mammal
observation (visibility and glare); and
• Details of passive acoustic
detections and any action taken in
response to those detections.
For minor repairs and maintenance
activities, the following protocols will
be followed:
• All vessel crew members will be
trained in marine mammal
identification and avoidance
procedures;
• Repair vessels will notify
designated NOAA personnel when and
where the repair/maintenance work is to
take place along with a tentative
schedule and description of the work, as
soon as practicable after it is determined
that repair work must be conducted;
PO 00000
Frm 00021
Fmt 4700
Sfmt 4700
34163
• Vessel crews will record/document
any marine mammal sighting(s) during
the work period; and
• At the conclusion of the repair/
maintenance work, a report will be
delivered to designated NOAA
personnel describing any marine
mammal sightings, the type of work
taking place when the sighting occurred,
and any avoidance actions taken during
the repair/maintenance work.
During all phases of project repair/
maintenance activities and operation,
sightings of any injured or dead marine
mammals will be reported immediately
to the USCG, NMFS, and the Northeast
Stranding and Disentanglement
Program, regardless of whether the
injury or death is caused by project
activities. Sightings of injured or dead
marine mammals not associated with
project activities can be reported to the
USCG on VHF Channel 16 or to NMFS
Stranding and Entanglement Hotline. In
addition, if the injury or death was
caused by a project vessel (e.g., SRV,
support vessel, or repair/maintenance
vessel), USCG must be notified
immediately, and a full report must be
provided to NMFS, Northeast Regional
Office, and NMFS, Office of Protected
Resources. The report must include the
following information: (1) The time,
date, and location (latitude/longitude) of
the incident; (2) the name and type of
vessel involved; (3) the vessel’s speed
during the incident; (4) a description of
the incident; (5) water depth; (6)
environmental conditions (e.g., wind
speed and direction, sea state, cloud
cover, and visibility); (7) the species
identification or description of the
animal; (8) the fate of the animal; and
(9) photographs or video footage of the
animal (if equipment is available).
Activities will not resume until review
and approval has been given by NMFS.
An annual report on marine mammal
monitoring and mitigation will be
submitted to NMFS, Office of Protected
Resources, and NMFS, Northeast
Regional Office, on August 1 of each
year. The annual report shall cover the
time period of January 1 through
December 31 of the previous year for
each year of activity. The weekly and
annual reports shall include data
collected for each distinct marine
mammal species observed in the project
area in Massachusetts Bay during the
period of LNG facility operations and
repair/maintenance activities. The
annual report shall also include a
description of marine mammal
behavior, overall numbers of
individuals observed, frequency of
observation, and any behavioral changes
and the context of the changes relative
to operation and repair/maintenance
E:\FR\FM\13JNR1.SGM
13JNR1
34164
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
activities. Additional information that
will be recorded by Neptune or its
contractors during operation and repair/
maintenance activities and contained in
the reports include: results of empirical
source level estimation for thrusters
while in use and activities associated
with maintenance and repair events,
date and time of marine mammal
detections (visually or acoustically),
weather conditions, species
identification, approximate distance
from the source, activity of the vessel or
at the repair site when a marine
mammal is sighted, and whether
thrusters were in use and, if so, how
many at the time of the sighting.
In addition to annual reports,
Neptune must submit a draft
comprehensive final report to NMFS,
Office of Protected Resources, and
NMFS, Northeast Regional Office, 180
days prior to the expiration of these
regulations. This comprehensive
technical report shall provide full
documentation of methods, results, and
interpretation of all monitoring during
the first 4.5 years of the LOA. A revised
final comprehensive technical report,
including all monitoring results during
the entire period of the LOAs will be
due 90 days after the end of the period
of effectiveness of the regulations.
General Conclusions Drawn From
Previous Monitoring Reports
Throughout the construction period
(July 2008–November 2009 with work
stoppages during peak right whale
season), Neptune submitted weekly
reports on marine mammal sightings in
the area. While it is difficult to draw
biological conclusions from these
reports, NMFS can make some general
conclusions. Data gathered by PSOs is
generally useful to indicate the presence
or absence of marine mammals (often to
a species level) within the safety zones
(and sometimes without) and to
document the implementation of
mitigation measures. Though it is by no
means conclusory, it is worth noting
that no instances of obvious behavioral
disturbance as a result of Neptune’s
activities were observed by the PSOs. Of
course, these observations only cover
the animals that were at the surface and
within the distance that the PSOs could
see. Neptune has not yet conducted any
repair or maintenance activities at the
Port.
As described previously in this
document, Neptune was required to
maintain an acoustic array to monitor
calling North Atlantic right whales
(humpback and fin whale calls were
also able to be detected). The ARUs log
continuous acoustic data for up to 110
days per each deployment. At the end
of each ARU recording cycle, the 19
units are recovered by BRP personnel.
The data are analyzed based on seven
objectives, which are as follows: (1)
Determine daily presence of fin whale
sounds; (2) determine daily presence of
humpback whale sounds; (3) determine
hourly presence of right whale sounds;
(4) estimate locations and numbers of
vocalizing right whales in the
monitoring area each day; (5) estimate
sound exposure for each locatable
vocalizing whale; (6) assess noise
conditions; and (7) improve analysis
software applications.
Cornell BRP analyzed the data and
submitted a report covering the initial
construction phase of the project, which
occurred in 2008. While acoustic data
can only be collected if the animals are
actively calling, the report indicates that
humpback and fin whales were heard
calling on at least some of the ARUs on
all construction days, and right whale
calls were heard only 28 percent of the
time during active construction days.
Background noise analysis revealed
definite increases in acoustic noise in
association with the different types of
construction activities with increases
highest in the right whale band and next
highest in the humpback band. The
report asserted that the influence of
construction activities on the acoustic
habitat that was monitored could not be
adequately evaluated by simply
counting the number of detected whales
exposed to a received noise level above
120 dB.
The September 2010 ARU quarterly
passive acoustic monitoring status
report indicates that only a small
portion of the 2010 data have been
analyzed to date. The final Marine
Mammal Acoustic Monitoring and
Analysis for the Operation of the
Neptune Liquefied Natural Gas
Terminal: 1 January–31 December 2010
will be submitted to NOAA, USGC, and
MARAD by July 31, 2011.
The AB network has been deployed
and operational in the Boston TSS since
January 2010. Acoustic data from these
buoys are sent to the BRP Cornell lab in
near-real-time for analysis for the
presence of North Atlantic right whales
in the monitoring area. Positive North
Atlantic right whale detections are
relayed to SRVs during transit through
the shipping lanes. The cycle of data
analysis and information submission is
a 24 hrs/day, 7 days/week operation
when SRVs are in the monitoring area.
To date, Cornell has prepared and
submitted two reports for the AB system
for 2010: January–June time period and
July–September time period.
There are two monitoring conditions
that dictate the tasks performed by
analysts at BRP: ‘‘normal’’ monitoring
conditions and ‘‘heightened watch’’
monitoring conditions. During ‘‘normal’’
monitoring conditions (i.e., no SRVs are
present in the monitoring area), analysts
at BRP monitor and report on North
Atlantic right whale activity twice a
day. During ‘‘heightened watch’’
monitoring conditions (i.e., when a SRV
is 24 hours from the TSS AB coverage
area, traveling through the Boston
Shipping Lanes or transiting to the
Neptune Port from the Boston Shipping
Lanes) analysts at BRP monitor and
report on North Atlantic right whale
acoustic activity in near-real-time. Table
1 in this document outlines the
detections and data that were recorded
on the ABs from January–September
2010. The highest number of detections
was recorded in March and the lowest
number recorded in June. During the
period January–September 2010, there
were two SRV visits to the Port. This
resulted in ‘‘heightened watch’’
monitoring conditions of the AB array
for 2 days in February, 2 days in March,
7 days in April, 1 day in May, 1 day in
July, and 7 days in August. The passive
acoustic arrays will remain deployed
during the effective period of these
regulations in order to obtain
information during the operational
phase of the Port facility.
erowe on DSK5CLS3C1PROD with RULES
TABLE 1—INFORMATION ON NORTH ATLANTIC RIGHT WHALE CALL DATA COLLECTED FROM THE AB ARRAY DEPLOYED
NEAR THE NEPTUNE PORT FROM JANUARY THROUGH SEPTEMBER 2010
January
Number of ABs with a detection ...................................
Total number of detections for all ABs .........................
Highest number of detections on a single day .............
Number of days with no recorded detections ...............
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
February
March
April
May
June
July
August
September
8
328
58
(Jan. 14)
5
10
573
103
(Feb. 25)
2
10
3,874
1,059
(Mar. 25)
0
10
2,786
255
(Apr. 24)
0
10
1,538
186
(May 1)
1
5
34
8
(Jun. 15)
14
8
64
26
(Jul. 3)
16
8
112
35
(Aug. 14)
9
8
189
43
(Sep. 18)
11
PO 00000
Frm 00022
Fmt 4700
Sfmt 4700
E:\FR\FM\13JNR1.SGM
13JNR1
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
Adaptive Management
erowe on DSK5CLS3C1PROD with RULES
NMFS has included an adaptive
management component in the
regulations governing the take of marine
mammals incidental to operation and
repair/maintenance activities at the
Neptune Port. In accordance with 50
CFR 216.105(c), regulations for the
proposed activity must be based on the
best available information. As new
information is developed, through
monitoring, reporting, or research, the
regulations may be modified, in whole
or in part, after notice and opportunity
for public review and comment. The use
of adaptive management will allow
NMFS to consider new information
from different sources to determine if
mitigation or monitoring measures
should be modified (including additions
or deletions) if new data suggest that
such modifications are appropriate for
subsequent LOAs.
The following are some of the
possible sources of applicable data:
• Results from Neptune’s monitoring
from the previous year;
• Results from general marine
mammal and sound research; or
• Any information which reveals that
marine mammals may have been taken
in a manner, extent or number not
authorized by these regulations or
subsequent LOAs.
If, during the effective period of the
regulations, new information is
presented from monitoring, reporting, or
research, these regulations may be
modified, in whole, or in part after
notice and opportunity for public
review and comment, as allowed for in
50 CFR 216.105(c). In addition, LOAs
shall be withdrawn or suspended if,
after notice and opportunity for public
comment, the Assistant Administrator
finds, among other things, that the
regulations are not being substantially
complied with or the taking allowed is
having more than a negligible impact on
the species or stock, as allowed for in 50
CFR 216.106(e). That is, should
substantial changes in marine mammal
populations in the project area occur or
monitoring and reporting show that the
Port operations are having more than a
negligible impact on marine mammals,
then NMFS reserves the right to modify
the regulations and/or withdraw or
suspend LOAs after public review and
comment.
Comments and Responses
On December 21, 2010 (75 FR 80260),
NMFS published a proposed rule in
response to Neptune’s request to take
marine mammals incidental to port
commissioning and operations,
including maintenance and repair
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
activities, at its Deepwater Port in
Massachusetts Bay and requested
comments, information, and suggestions
concerning the request. During the 45day public comment period, NMFS
received comments from two private
individuals and the Marine Mammal
Commission (MMC). NMFS has
responded to these comments here.
Comment 1: One of the private citizen
letters noted the continual harassment
and stress sustained by marine
mammals from human activities, and,
therefore, urged that the regulations be
denied.
Response: NMFS considered the
potential for harassment from these
activities in its impacts analysis in the
proposed rule (75 FR 80260, December
21, 2010). Authorization for incidental
takings shall be granted if NMFS finds
that the taking will have a negligible
impact on the species or stock(s), will
not have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (where
relevant), and if the permissible
methods of taking and requirements
pertaining to the mitigation, monitoring
and reporting of such takings are set
forth. Based on the assessment in the
proposed rule and contained later in
this document, NMFS determined that
the level of harassment from these
activities would take only small
numbers of marine mammals and would
not have more than a negligible impact
on the affected species or stocks. There
are no relevant subsistence uses of
marine mammals implicated by this
action. Therefore, NMFS has
determined that the total taking of
affected species or stocks would not
have an unmitigable adverse impact on
the availability of such species or stocks
for taking for subsistence purposes. The
permissible methods of taking and the
required mitigation, monitoring, and
reporting measures are laid out in this
final rule.
Comment 2: The second private
citizen letter expressed contradicting
points of view. It stated on the one hand
that NMFS should not stop LNG
operations, as it would force increased
prices for the public. However, the letter
also stated that NMFS should take
positive steps to protect marine
mammals.
Response: NMFS is not the agency
with regulatory authority over offshore
deepwater LNG ports. That authority
falls to the USCG and MARAD.
Therefore, those are the agencies that
either allow or deny LNG port
construction and operation. NMFS
authorizes the take of marine mammals
incidental to a specified activity if
certain findings are made. Those
PO 00000
Frm 00023
Fmt 4700
Sfmt 4700
34165
findings are described in the
‘‘Background’’ section found earlier in
this document. The final rule and
associated LOA contain mitigation and
monitoring measures to ensure the least
practicable adverse impact on marine
mammal species and stocks in the Port
area.
Comment 3: The MMC expressed
three concerns with the information in
the proposed rule as to the derivation of
take estimates. First, the MMC
expressed concern about the 120-dB
zones that were used as they were
smaller than those derived from in-situ
measurements and incorporated into
models in appendices in Neptune’s
application. This resulted in an
underestimation of the zones of
exposure. Second, the hypothetical strip
width that was used by NMFS was
much smaller than the strip width used
during the surveys, thus producing
overestimates of marine mammal
densities in the area. Lastly, NMFS only
estimated take from repair and
maintenance activities and DP but not
weathervaning.
The MMC is concerned that the
presence of these errors and omissions
in the proposed rule may have
compromised the public’s opportunity
to comment meaningfully on the
proposed authorization. Without seeing
the new analyses, it is difficult to know
whether the final rule will differ
significantly enough from the proposed
rule that an additional opportunity for
public review and comment should be
provided. Therefore, the MMC
recommends that NMFS allow for an
additional opportunity for public review
and comment before publication of a
final rule if the recalculated takes or
zones in which takes might occur are
significantly greater than those
described in the proposed rule. If NMFS
determines that additional notice and
opportunity to comment are not needed,
the MMC recommends that NMFS
ensure that the revised estimates of the
zones of exposure and anticipated takes
for each of the three proposed activities
are provided in the final rule, together
with the rationale for not providing an
additional opportunity for public review
and comment.
Response: NMFS has revised the take
estimates in this final rule from those
contained in the proposed rule. A
summary of the revisions is provided
here, and more details can be found in
the ‘‘Estimated Take by Incidental
Harassment’’ section found later in this
document.
As noted by the MMC, NMFS
inadvertently did not estimate takes
from weathervaning in the proposed
rule. Takes from this activity (in
E:\FR\FM\13JNR1.SGM
13JNR1
erowe on DSK5CLS3C1PROD with RULES
34166
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
addition to DP use and repair/
maintenance activities) have now been
calculated and added to the total annual
take estimate for each species. NMFS
estimated that Neptune would require
up to 8 days/year to conduct
weathervaning to maintain position at
the Port. This is based on information
contained in their application and
associated appendices. Including this
activity only added a very small number
of individuals of each species to the
overall take totals for each species.
In December 2009, LGL Limited
completed a Second Supplementary
Biological Effects Report titled
Assessment of the Effects of Underwater
Noise from Thrusters to be Used on the
Neptune LNG Project (LGL, 2009). This
report incorporated measurements of
the SRVs conducted by Samsung and
new transmission loss modeling by
JASCO Applied Sciences. This report
presents zones of influence (ZOIs; e.g.,
the area ensonified by the 120-dB
contour) for DP during thruster use for
docking and undocking, weathervaning
(to maintain position on the mooring),
and repair and maintenance activities.
For each of these three activities that
have the potential to result in take of
marine mammals, LGL presented a
range for the radius of the 120-dB
isopleth. NMFS took the average (or
mean) value for each of these three radii
to determine the ZOIs for each activity
and the amount of take for each species.
NMFS used the following radii (and
ZOIs) in its take calculations:
• DP during thruster use for docking
and undocking: Radius of 2.33 mi (3.75
km) and an area of 17.06 mi2 (44.18
km2);
• Weathervaning: Radius of 3.2 mi
(5.15 km) and an area of 32.17 mi2
(83.32 km2); and
• Repair and maintenance activities:
Radius of 4.38 mi (7.05 km) and an area
of 60.29 mi2 (156.14 km2).
The radius for DP increased only
slightly between the proposed and final
rules from 1.9 mi (3 km) to 2.33 mi (3.75
km). The increase in radius (and
therefore ZOI) from repair and
maintenance activities had a more
dramatic increase between the proposed
and final rules: 2.4 mi (3.9 km) to 4.38
mi (7.05 km). However, the radius for
repair and maintenance activities
assumes that all such activities would
be similar to construction activities.
Activities during construction were
noisier and required more vessels on
site at the same time than what would
be expected for most repair or
maintenance type activities. Therefore,
this radius and associated ZOI are likely
overestimates, as many of the activities
would not occur on this large of a scale.
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
As noted by the MMC, NMFS used an
extremely conservative hypothetical
strip width in the proposed rule to
derive density estimates. By doing so,
the density estimates were severely
inflated. NMFS has reviewed the 2006
NCCOS report from which data were
used to determine species densities.
Some of the data used a strip-transect
survey method. The value for this was
2.3 mi (3.7 km). In order to convert a
strip-transect value to a line transect for
the strip width, one must divide the
strip transect width by 2. Therefore, in
this final rule, NMFS has used a strip
width of 1.15 mi (1.85 km) to derive
density estimates for the seven species
discussed in the NCCOS (2006) report.
This value is more realistic of actual
field conditions than the original value
used in the proposed rule. By using this
larger strip width, the take estimates
dropped dramatically (especially for DP
thruster use), even with the larger ZOIs.
The take estimates for DP thruster use
with the lower density estimates and
larger ensonified areas decreased by
nearly three times the values in the
proposed rule.
NMFS has determined that there does
not need to be another opportunity for
public comment on this rule based
merely on the fact that the take
estimates have been revised. When all of
the recommended modifications to the
take estimates were made (i.e., inclusion
of weathervaning, increasing ZOIs, and
increasing strip width), the end result
was that in all cases, the take estimates
decreased slightly for the species
described in the 2006 NCCOS report.
Additionally, the public’s opportunity
to comment meaningfully was not
compromised. Besides the MMC, only
two other people submitted comment
letters. Neither of these letters discussed
the issue of take estimates or how the
values were calculated in the proposed
rule. NMFS has provided ample
explanation for how the estimates were
derived in this final rule and where
changes in derivation were made from
the proposed rule.
Comment 4: The MMC recommends
that NMFS adopt a consistent
requirement that mitigation zones be
clear of all species of marine mammals
for 30 minutes before initiation or
resumption of activities.
Response: NMFS has changed the
requirement that repair and
maintenance activities not resume until
the marine mammal has been positively
confirmed to have left the mitigation
zone to also state that if the animal has
not been re-sighted for 30 minutes in the
appropriate mitigation zone that
activities may resume. This change is
consistent with requirements and
PO 00000
Frm 00024
Fmt 4700
Sfmt 4700
conditions contained in other MMPA
ITAs.
Comment 5: The MMC notes that the
proposed rule uses a 0.6-mi (1-km)
radius of the area that must be visible
for certain activities and a 0.5-mi (0.8km) radius for repair and maintenance
activities. The basis for allowing lower
visibility for certain activities is not
clear. The MMC recommends that
NMFS require that visibility also be at
least 0.6 mi (1 km) before maintenance
and repair activities can proceed or
provide a reasoned basis for allowing
these activities under poorer visibility.
Response: NMFS has changed the
visibility requirement for repair and
maintenance activities in the final rule
to be consistent with that of other
activities for which mitigation is
required in the rule. NMFS agrees with
the MMC that there is no reason for the
discrepancy in the visibility distances
and therefore has made the requested
change. The mitigation requirements for
such activities now state that a zone of
0.6 mi (1 km) must be visible.
Comment 6: The MMC also questions
whether the planned visual monitoring
is adequate for mitigation purposes. The
proposed rule specifies that PSOs would
conduct visual monitoring for 40
minutes each hour, beginning at
daybreak. With that 20-minute break
each hour, if the Port operates 24 hours/
day, then in a season with 12 hours of
daily sunlight, observers would be on
watch for a total of 8 hours only—that
is, during one-third of operations. In
essence, NMFS’ approach implies that
visual monitoring is necessary for
mitigation purposes only at certain
times, and the MMC does not see the
basis for that conclusion. To address
that concern, the MMC recommends
that NMFS (1) require that PSOs
monitor continuously for the presence
of marine mammals when activities
occur during daylight hours and (2)
either prohibit nighttime operations or
adopt measures that it can demonstrate
to be reliable for detecting all marine
mammals within the specified
mitigation zones under nighttime
conditions.
Response: The information contained
in the proposed rule about the
procedures used by PSOs during repair
and maintenance activities at the
Neptune Port was not described clearly.
Additional information has been added
to the ‘‘Monitoring and Reporting’’
section of this document to add clarity.
PSOs are on-duty continuously to
monitor for the presence of marine
mammals. This includes work done
during nighttime hours. Two PSOs are
on-watch at all times and take turns
during the shift between being the
E:\FR\FM\13JNR1.SGM
13JNR1
erowe on DSK5CLS3C1PROD with RULES
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
primary observer watching for marine
mammals and the secondary observer
who records sightings in the log book
and watches for marine mammals when
not entering data. Should repair and
maintenance activities occur during
nighttime hours, PSOs are equipped
with night vision devices. These devices
have proven to be useful within the
small distances that are encompassed by
the mitigation zones for this project.
Comment 7: The MMC believes that
NMFS’ determination under the MMPA
that these activities will have a
negligible impact on marine mammal
species or stocks needs to take into
account possible cumulative effects,
even if cumulative effects analyses have
been conducted under the National
Environmental Policy Act (NEPA).
Unless such an analysis is done, NMFS
could continue indefinitely to grant
ITAs for individual activities that, by
themselves, have a negligible impact
even though the combined total of all
impacts might significantly impede a
species’ recovery or contribute to its
further decline. With that concern in
mind, the MMC recommends that
NMFS include in its final rule an
analysis evaluating the impact of the
proposed operations together with the
cumulative impacts of all the other
pertinent risk factors affecting right
whales and other marine mammals that
occur in the Port area and explain why
it believes that the combined impacts
would be negligible.
Response: NMFS considered the
cumulative effects analysis contained in
the USCG’s and MARAD’s 2006 Final
EIS and other relevant data to inform its
MMPA determination here. NMFS was
a cooperating agency in the
development of both the Draft and Final
EISs for this project. Pursuant to NEPA,
those documents contained a
cumulative impacts assessment, as well
as an assessment of the impacts of the
proposed Neptune Port construction,
operation, and abandonment on marine
mammals and other protected resources.
Section 101(a)(5)(A) of the MMPA and
its implementing regulations require
NMFS to consider a request for the
taking of marine mammals incidental to
a specified activity within a specified
geographical region and, assuming
certain findings can be made, to
authorize the taking of small numbers of
marine mammals while engaged in that
activity. NMFS has defined ‘‘specified
activity’’ in 50 CFR 216.103 as ‘‘any
activity, other than commercial fishing,
that takes place in a specified
geographical region and potentially
involves the taking of small numbers of
marine mammals.’’ When making a
negligible impact determination, NMFS
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
considers the total impact during each
5-year period resulting from the
specified activity only and supports its
determination by relying on factors such
as: (1) The number of anticipated
mortalities from the activity; (2) the
number and nature of anticipated
injuries from the activity; (3) the
number, nature, intensity, and duration
of Level B harassment resulting from the
activity; and (4) the context in which
the takes occur.
NMFS considered the impacts
analyses (i.e., direct, indirect, and
cumulative) contained in the 2006 EIS
in reaching its conclusion that any
marine mammals exposed to the low
level sounds produced by operations or
repair/maintenance activities at the
Neptune Port would be disturbed for
only a short period of time and would
not be harmed or killed. Furthermore,
the required mitigation and monitoring
measures are expected to reduce the
likelihood or severity of any impacts to
marine mammals over the course of
these activities.
Moreover, NMFS gave careful
consideration to a number of other
issues and sources of information. In
particular, NMFS relied upon a number
of scientific reports, including the 2009
and 2010 U.S. Atlantic and Gulf of
Mexico Marine Mammal SARs to
support its findings. The SARs contain
a description of each marine mammal
stock, its geographic range, a minimum
population estimate, current population
trends, current and maximum net
productivity rates, optimum sustainable
population levels and allowable
removal levels, and estimates of annual
human-caused mortality and serious
injury through interactions with
commercial fisheries. NMFS also used
data from the 2006 NCCOS report to
determine density levels of several of
the marine mammal species in the
proposed activity area.
After careful consideration of the
proposed activities, the context in
which Neptune’s proposed activities
would occur, the best available
scientific information, and all effects
analyses (including cumulative effects),
NMFS has determined that the taking
from the specified activities: (1) Would
not result in more than the behavioral
harassment (i.e., Level B harassment) of
small numbers of marine mammal
species or stocks; (2) would not result in
more than a negligible impact on
affected species or stocks; and (3) would
not have an unmitigable adverse impact
on the availability of such species or
stocks for taking for subsistence uses.
Therefore NMFS has decided to issue
regulations and associated LOA(s) to
Neptune to take, by no more than Level
PO 00000
Frm 00025
Fmt 4700
Sfmt 4700
34167
B harassment, small numbers of marine
mammals incidental to operation and
repair/maintenance activities at the
Neptune Port off Massachusetts.
Estimated Take by Incidental
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].’’ Only take by Level B
harassment is anticipated as a result of
Neptune’s operational and repair/
maintenance activities. Anticipated take
of marine mammals is associated with
thruster sound during maneuvering of
the SRVs while docking and undocking,
occasional weathervaning at the Port,
and during thruster use of DP
maintenance vessels should a major
repair be necessary. The regasification
process itself is an activity that does not
rise to the level of taking, as the
modeled source level for this activity is
110 dB (rms). Certain species may have
a behavioral reaction to the sound
emitted during the activities; however,
hearing impairment as a result of these
activities is not anticipated.
Additionally, vessel strikes are not
anticipated, especially because of the
required speed restriction measures that
were described earlier in this document.
For continuous sounds, such as those
produced by Neptune’s activities, NMFS
uses a received level of 120-dB (rms) to
indicate the onset of Level B
harassment. The basis for Neptune’s
‘‘take’’ estimate is the number of marine
mammals that potentially could be
exposed to sound levels in excess of 120
dB. This has been determined by
applying the modeled ZOI to the
seasonal use (density) of the area by
marine mammals and correcting for
seasonal duration of sound-generating
activities and estimated duration of
individual activities when the
maximum sound-generating activities
are intermittent to occasional. Nearly all
of the required information is readily
available in the MARAD/USCG Final
EIS, with the exception of marine
mammal density estimates for the
project area. In the case of data gaps, a
conservative approach was used to
ensure that the potential number of
takes is not underestimated, as
described next.
E:\FR\FM\13JNR1.SGM
13JNR1
erowe on DSK5CLS3C1PROD with RULES
34168
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
Based on comments received from the
MMC, NMFS has reevaluated the take
estimates. The following factors for
developing the take estimates have been
taken into account in this final rule,
which were not considered in the
proposed rule:
• Takes from weathervaning were
also estimated (in addition to takes from
thruster use during DP and repair and
maintenance activities, which were
estimated in the proposed rule);
• The ZOIs for each of the three
activities listed here are taken from
Appendix C3 in Neptune’s application,
which are taken from in-situ
measurements and incorporated into
models in Neptune’s application instead
of the ZOIs from earlier reports, which
were used in the proposed rule; and
• Density estimates were derived
using a strip width of 1.15 mi (1.85 km)
instead of the overly conservative strip
width of 0.25 mi (0.4 km) used in the
proposed rule.
In December 2009, LGL Limited
completed a Second Supplementary
Biological Effects Report titled
Assessment of the Effects of Underwater
Noise from Thrusters to be Used on the
Neptune LNG Project (LGL, 2009). This
report incorporated measurements of
the SRVs conducted by Samsung and
new transmission loss modeling by
JASCO Applied Sciences. This report
presents ZOIs for DP during thruster use
for docking and undocking,
weathervaning (to maintain position on
the mooring), and repair and
maintenance activities. For each of these
three activities that have the potential to
result in take of marine mammals, LGL
presented a range for the radius of the
120-dB isopleth and also for the 120-dB
ensonified area. NMFS took the average
(or mean) value for each of these three
radii to determine the ZOIs for each
activity and the amount of take for each
species from the three activities.
Therefore, NMFS used the following
radii (and ZOIs) in its take calculations:
• DP during thruster use for docking
and undocking: Radius of 2.33 mi (3.75
km) and an area of 17.06 mi2 (44.18
km2);
• Weathervaning: Radius of 3.2 mi
(5.15 km) and an area of 32.17 mi2
(83.32 km2); and
• Repair and maintenance activities:
Radius of 4.38 mi (7.05 km) and an area
of 60.29 mi2 (156.14 km2).
Additionally, in the calculation of
take from repair and maintenance
activities, the proposed rule determined
that such activities may only need to
occur for 14 days each year. However,
after a reevaluation, NMFS has
determined that it would be more
appropriate to assume 28 days per year
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
for repair and maintenance activities.
While some repairs may take 3–4 weeks
in any given year, there is also the
possibility that some years may not have
any repair or maintenance activities
occur.
NMFS recognizes that baleen whale
species other than North Atlantic right
whales have been sighted in the project
area from May to November. However,
the occurrence and abundance of fin,
humpback, and minke whales is not
well documented within the project
area. Nonetheless, NMFS used the data
on cetacean distribution within
Massachusetts Bay, such as those
published by the NCCOS (2006), to
determine potential takes of marine
mammals in the vicinity of the project
area. Neptune presented density
estimates using the CETAP (1982) and
U.S. Navy MRA (2005) data. The
NCCOS (2006) report uses information
from these sources; however, it also
includes information from some other
studies. Therefore, NMFS used density
information for the species that are
included in the NCCOS (2006) report.
These species include: North Atlantic
right, fin, humpback, minke, pilot, and
sei whales and Atlantic white-sided
dolphins.
The NCCOS study used cetacean
sightings from two sources: (1) The
North Atlantic Right Whale Consortium
(NARWC) sightings database held at the
University of Rhode Island (Kenney,
2001); and (2) the Manomet Bird
Observatory (MBO) database, held at
NMFS’ Northeast Fisheries Science
Center (NEFSC). The NARWC data
contained survey efforts and sightings
data from ship and aerial surveys and
opportunistic sources between 1970 and
2005. The main data contributors
included: The CETAP, the Canadian
Department of Fisheries and Oceans, the
Provincetown Center for Coastal
Studies, International Fund for Animal
Welfare, NEFSC, New England
Aquarium, WHOI, and the University of
Rhode Island. A total of 406,293 mi
(653,725 km) of survey track and 34,589
cetacean observations were
provisionally selected for the NCCOS
study in order to minimize bias from
uneven allocation of survey effort in
both time and space. The sightings-perunit-effort (SPUE) was calculated for all
cetacean species by month covering the
southern Gulf of Maine study area,
which also includes the project area
(NCCOS, 2006).
The MBO’s Cetacean and Seabird
Assessment Program (CSAP) was
contracted from 1980 to 1988 by NEFSC
to provide an assessment of the relative
abundance and distribution of
cetaceans, seabirds, and marine turtles
PO 00000
Frm 00026
Fmt 4700
Sfmt 4700
in the shelf waters of the northeastern
U.S. (MBO, 1987). The CSAP program
was designed to be completely
compatible with NEFSC databases so
that marine mammal data could be
compared directly with fisheries data
throughout the time series during which
both types of information were gathered.
A total of 8,383 mi (5,210 km) of survey
distance and 636 cetacean observations
from the MBO data were included in the
NCCOS analysis. Combined valid
survey effort for the NCCOS studies
included 913,840 mi (567,955 km) of
survey track for small cetaceans
(dolphins and porpoises) and 1,060,226
mi (658,935 km) for large cetaceans
(whales) in the southern Gulf of Maine.
The NCCOS study then combined these
two data sets by extracting cetacean
sighting records, updating database field
names to match the NARWC database,
creating geometry to represent survey
tracklines and applying a set of data
selection criteria designed to minimize
uncertainty and bias in the data used.
Based on the comprehensiveness and
total coverage of the NCCOS cetacean
distribution and abundance study,
NMFS calculated the estimated take
number of marine mammals based on
the most recent NCCOS report
published in December, 2006. A
summary of seasonal cetacean
distribution and abundance in the
project area was provided in the
proposed rule, in the ‘‘Description of
Marine Mammals in the Area of the
Specified Activity’’ section (75 FR
80260, December 21, 2010). For a
detailed description and calculation of
the cetacean abundance data and SPUE,
refer to the NCCOS study (NCCOS,
2006). SPUE for all four seasons were
analyzed, and the highest value SPUE
for the season with the highest
abundance of each species was used to
determine relative abundance. Based on
the data, the relative abundance of
North Atlantic right, fin, humpback,
minke, sei, and pilot whales and
Atlantic white-sided dolphins, as
calculated by SPUE in number of
animals per square kilometer, is 0.0082,
0.0097, 0.0265, 0.0059, 0.0084, 0.0407,
and 0.1314 n/km, respectively. Table 2
in this document outlines the density,
abundance, take estimates, and percent
of population for the 14 species for
which NMFS is authorizing Level B
harassment.
In calculating the area density of these
species from these linear density data,
NMFS used 1.15 mi (1.85 km) as the
strip width (W). This is larger than the
extremely conservative hypothetical
strip width of 0.25 mi (0.4 km) that was
used in the proposed rule. This revised
strip width is based on the distance of
E:\FR\FM\13JNR1.SGM
13JNR1
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
erowe on DSK5CLS3C1PROD with RULES
visibility used in the NARWC data that
was part of the NCCOS (2006) study.
However, those surveys used a strip
transect instead of a line transect
methodology. Therefore, in order to
obtain a strip width, one must divide
the visibility or transect value in half.
Since the visibility value used in the
NARWC data was 2.3 mi (3.7 km), it
thus gives a strip width of 1.15 mi (1.85
km). Based on this information, the area
density (D) of these species in the
project area can be obtained by the
following formula:
D = SPUE/2W.
Based on the calculation, the
estimated take numbers by Level B
harassment on an annual basis for North
Atlantic right, fin, humpback, minke,
sei, and pilot whales and Atlantic
white-sided dolphins, within the 120dB ensonified area during DP of
thrusters for docking and undocking of
approximately 17.06 mi2 (44.18 km2)
maximum ZOI, corrected for 50 percent
underwater, are 7, 9, 24, 5, 2, 36, and
118, respectively. This estimate is based
on an estimated 50 SRV trips annually
(for all of these species except for sei
whales) that will produce sounds of 120
dB or greater. This estimate is based on
an estimated 12.5 SRV trips annually
that will produce sounds of 120 dB or
greater for sei whales. Sei whales only
occur in the area in the spring.
Therefore, shipments during the other
three seasons will not result in the take
of sei whales. For this reason, take from
shipment operations has only been
calculated at a quarter of the rate of the
other species for sei whales. With the
revised strip width and ZOI, the take
estimates for these seven species from
DP during thruster use is about onethird the estimates in the proposed rule
(75 FR 80260, December 21, 2010).
Based on the same calculation method
described above for DP thruster use (but
using the 120-dB ZOI of approximately
60.29 mi2 (156.14 km2)), the estimated
take numbers by Level B harassment on
an annual basis for North Atlantic right,
fin, humpback, minke, sei, and pilot
whales and Atlantic white-sided
dolphins incidental to Port maintenance
and repair activities, corrected for 50
percent underwater, are 15, 17, 47, 11,
7, 72, and 233, respectively. These
numbers are based on 28 days of repair
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
and maintenance activities occurring
annually (for all of these species except
for sei whales). As mentioned
previously, sei whales only occur in the
area in spring. Since most repair work
is to be scheduled for the spring and
summer seasons, the take estimate for
sei whales was calculated based on 14
days or repair and maintenance
activities annually. It is unlikely that
this much repair and maintenance work
would be required each year. With the
revised strip width and ZOI, the take
estimates for these seven species from
maintenance and repair activities
increased only slightly (i.e., no more
than 9 individuals for any endangered
whale species) from the proposed rule
(75 FR 80260, December 21, 2010).
The third activity that has the
potential to take marine mammals is
weathervaning in order to maintain
position at the Port. This activity is not
anticipated to occur for more than 8
days in any given year. Therefore, the
take estimates are based on the
possibility of weathervaning occurring
for up to 8 days for all species except
sei whales. Again, since sei whales only
occur in the area in spring, the estimate
for this species was calculated at onequarter the rate (i.e., 2 days of
weathervaning per year). Using a ZOI of
32.17 mi2 (83.32 km2), the estimated
take numbers by Level B harassment on
an annual basis for North Atlantic right,
fin, humpback, minke, sei, and pilot
whales and Atlantic white-sided
dolphins incidental to weathervaning,
corrected for 50 percent underwater, are
2, 3, 7, 2, 1, 11, 36, respectively.
The total estimated annual take of
each of these species as a result of all
three activities with the potential to
incidentally take marine mammals (i.e.,
DP thruster use, repair and maintenance
activities, and weathervaning) at the
Neptune Port facility is: 24 North
Atlantic right whales; 29 fin whales; 78
humpback whales; 18 minke whales; 12
sei whales; 119 long-finned pilot
whales; and 387 Atlantic white-sided
dolphins. These numbers represent a
maximum of 7, 1.3, 9.2, 0.5, 3.1, 0.9, and
0.6 percent of the populations for these
species or stocks in the western North
Atlantic, respectively. The revised take
estimates for these seven species are
lower than the take estimates presented
in the proposed rule (75 FR 80260,
PO 00000
Frm 00027
Fmt 4700
Sfmt 4700
34169
December 21, 2010). It is likely that
individual animals will be ‘‘taken’’ by
harassment multiple times (because
certain individuals may occur in the
area more than once while other
individuals of the population or stock
may not enter the project area).
Additionally, the highest value SPUE
for the season with the highest
abundance of each species was used to
determine relative abundance.
Moreover, it is not expected that
Neptune will have 50 SRV transits and
LNG deliveries in the first year or two
of operations. Therefore, these
percentages represent the upper
boundary of the animal population that
could be affected. Thus, the actual
number of individual animals being
exposed or taken is expected to be far
less, especially in the first couple of
years of operation.
In addition, bottlenose dolphins,
common dolphins, Risso’s dolphins,
killer whales, harbor porpoises, harbor
seals, and gray seals could also be taken
by Level B harassment as a result of the
deepwater LNG port project. Because
these species are less likely to occur in
the area, and there are no density
estimates specific to this particular area,
NMFS based the take estimates on one
or two encounters with typical group
size. Therefore, NMFS estimates that up
to approximately 10 bottlenose
dolphins, 20 common dolphins, 20
Risso’s dolphins, 20 killer whales, 5
harbor porpoises, 15 harbor seals, and
15 gray seals could be exposed to
continuous noise at or above 120 dB re
1 μPa rms incidental to operations (i.e.,
DP thruster use and weathervaning) and
repair and maintenance activities
annually, respectively. The take
estimates for these seven species have
not changed from the proposed rule.
Because Massachusetts Bay represents
only a small fraction of the western
North Atlantic basin where these
animals occur, NMFS has determined
that only small numbers of the marine
mammal species or stocks in the area
would be potentially affected by the
Neptune LNG deepwater project. The
take estimates presented in this section
of the document do not take into
consideration the mitigation and
monitoring measures required in the
regulations.
E:\FR\FM\13JNR1.SGM
13JNR1
34170
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
TABLE 2—DENSITY ESTIMATES, POPULATION ABUNDANCE ESTIMATES, TOTAL ANNUAL AUTHORIZED TAKE (WHEN COMBINE TAKES FROM DP THRUSTER USE, MAINTENANCE/REPAIR ACTIVITIES, AND WEATHERVANING), AND PERCENTAGE
OF POPULATION THAT MAY BE TAKEN FOR THE POTENTIALLY AFFECTED SPECIES
Species
North Atlantic right whale .....................................................
Fin whale ..............................................................................
Humpback whale .................................................................
Minke whale .........................................................................
Sei whale .............................................................................
Long-finned pilot whale ........................................................
Atlantic white-sided dolphin .................................................
Bottlenose dolphin ...............................................................
Common dolphin ..................................................................
Risso’s dolphin .....................................................................
Killer whale ...........................................................................
Harbor porpoise ...................................................................
Harbor seal ..........................................................................
Gray seal ..............................................................................
1 Abundance
erowe on DSK5CLS3C1PROD with RULES
2 Abundance
0.0022
0.0026
0.0072
0.0016
0.0023
0.011
0.0355
NA
NA
NA
NA
NA
NA
NA
Abundance 2
345
2,269
847
3,312
386
31,139
63,368
7,489
120,743
20,479
NA
89,054
99,340
125,541–
169,064
361
3,985
847
8,987
386
12,619
63,368
9,604
120,743
20,479
NA
89,054
NA
125,541–
169,064
Total annual
authorized
take
24
29
78
18
12
119
387
10
20
20
20
5
15
15
Percentage of
stock or population
6.6–7
0.7–1.3
9.2
0.2–0.5
3.1
0.4–0.9
0.6
0.1
0.02
0.1
NA
0.01
0.02
0.01
estimates in 2009 NMFS Atlantic and Gulf of Mexico SAR;
estimates in 2010 Draft NMFS Atlantic and Gulf of Mexico SAR; NA=Not Available.
Negligible Impact and Small Numbers
Analysis and Determination
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.’’
In making a negligible impact
determination, NMFS considers a
variety of factors, including but not
limited to: (1) The number of
anticipated mortalities; (2) the number
and nature of anticipated injuries; (3)
the number, nature, intensity, and
duration of Level B harassment; and (4)
the context in which the takes occur.
No injuries or mortalities are
anticipated to occur as a result of
Neptune’s port operation and
maintenance and repair activities, and
none are authorized by NMFS.
Additionally, animals in the area are not
anticipated to incur any hearing
impairment (i.e., TTS, a Level B
harassment, or PTS, a Level A [injury]
harassment), as the modeling results for
the SRV indicate a source level of 180
dB (rms), which is below the threshold
used by NMFS for acoustic injury to
marine mammals. All takes are
anticipated to be by Level B behavioral
harassment only. Certain species may
have a behavioral reaction (e.g.,
increased swim speed, avoidance of the
area, etc.) to the sound emitted during
the operations and maintenance
activities. Table 2 in this document
outlines the number of Level B
harassment takes that are anticipated as
a result of the activities. These takes are
anticipated to be of low intensity due to
VerDate Mar<15>2010
Abundance 1
Density
14:06 Jun 10, 2011
Jkt 223001
the low level of sound emitted by the
activities themselves. The activities
could occur year-round. However,
operations are not anticipated to occur
on successive days. Should repair or
maintenance work be required, this
could occur on successive days but
likely only for 1–2 weeks but no more
than 3–4 weeks. The activities do not
occur in any critical habitat for the
affected species, although there is some
nearby for North Atlantic right whales.
Maintenance and repair activities will
be conducted to avoid times of year
when that species is most likely to be in
the area.
While some of the species occur in
the project area year-round, some
species only occur in the area during
certain seasons. For example, sei whales
are only anticipated in the area during
the spring. Therefore, if shipments and/
or maintenance/repair activities occur
in other seasons, the likelihood of sei
whales being affected is quite low.
Additionally, any repairs that can be
scheduled in advance will be scheduled
to avoid the peak time that North
Atlantic right whales occur in the area,
which usually is during the early spring.
North Atlantic right, humpback, and
minke whales are not expected in the
project area in the winter. During the
winter, a large portion of the North
Atlantic right whale population occurs
in the southeastern U.S. calving grounds
(i.e., South Carolina, Georgia, and
northern Florida). The fact that certain
activities will occur during times when
certain species are not commonly found
in the area will help reduce the amount
of Level B harassment for these species.
PO 00000
Frm 00028
Fmt 4700
Sfmt 4700
Many animals perform vital functions,
such as feeding, resting, traveling, and
socializing, on a diel cycle (24-hr cycle).
Behavioral reactions to noise exposure
(such as disruption of critical life
functions, displacement, or avoidance of
important habitat) are more likely to be
significant if they last more than one
diel cycle or recur on subsequent days
(Southall et al., 2007). Consequently, a
behavioral response lasting less than
one day and not recurring on
subsequent days is not considered
particularly severe unless it could
directly affect reproduction or survival
(Southall et al., 2007). Operational
activities (i.e., DP and weathervaning)
are not anticipated to occur at the Port
on consecutive days. Once Neptune is at
full operations, SRV shipments would
occur every 4–8 days, with thruster use
needed for a couple of hours during
each shipment. Weathervaning is
anticipated to be needed during only a
small portion of the shipments.
Therefore, Neptune will not be creating
increased sound levels in the marine
environment for several days at a time.
Of the 14 marine mammal species
likely to occur in the area, four are listed
as endangered under the ESA: North
Atlantic right, humpback, fin, and sei
whales. These four species, as well as
the northern coastal stock of bottlenose
dolphin, are also considered depleted
under the MMPA. The affected
humpback and North Atlantic right
whale populations have been increasing
in recent years. However, there is
insufficient data to determine
population trends for the other depleted
species in the project area. There are
several well known North Atlantic right
E:\FR\FM\13JNR1.SGM
13JNR1
erowe on DSK5CLS3C1PROD with RULES
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
whale feeding grounds in the CCB and
GSC. However, they are outside of the
area of the Port. As mentioned
previously, to the greatest extent
practicable, all maintenance/repair work
will be scheduled during the May 1 to
November 30 time frame to avoid peak
right whale feeding in these areas,
which occur close to the Neptune Port.
Additionally, to protect North Atlantic
right whales (and other marine
mammals in the project area), Neptune
must cease sound emitting activities
and/or reduce vessel speed if animals
enter into the designated zones. No
mortality or injury is expected to occur
and due to the nature, degree, and
context of the Level B harassment
anticipated, the activity is not expected
to impact rates of recruitment or
survival.
The population estimates for the
species that may be taken by harassment
from the most recent U.S. Atlantic SARs
were provided in Table 2 in this
document. From the most conservative
estimates of both marine mammal
densities in the project area and the size
of the 120-dB ZOI, the maximum
calculated number of individual marine
mammals for each species that could
potentially be harassed annually is
small relative to the overall population
sizes (9.2 percent for humpback whales,
6.6–7 percent for North Atlantic right
whales, and no more than 3.1 percent of
any other species).
As stated previously, NMFS’ practice
has been to apply the 120 dB re 1 μPa
(rms) received level threshold for
underwater continuous sound levels to
determine whether take by Level B
harassment occurs. However, not all
animals react to sounds at this low
level, and many will not show strong
reactions (and in some cases any
reaction) until sounds are much
stronger. Southall et al. (2007) provide
a severity scale for ranking observed
behavioral responses of both freeranging marine mammals and laboratory
subjects to various types of
anthropogenic sound (see Table 4 in
Southall et al. (2007)). Tables 15, 17, 19,
and 21 in Southall et al. (2007) outline
the numbers of low-frequency, midfrequency, and high-frequency
cetaceans and pinnipeds in water,
respectively, reported as having
behavioral responses to non-pulses in
10-dB received level increments. These
tables illustrate, especially for
cetaceans, that more intense observed
behavioral responses did not occur until
sounds were higher than 120 dB (rms).
Many of the animals had no observable
response at all when exposed to
anthropogenic sound at levels of 120 dB
(rms) or even higher.
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
The take estimates presented in this
document are likely an overestimate of
the actual number of animals that may
be taken by Level B harassment in any
given year. First, NMFS used the highest
value SPUE for the season with the
highest abundance of each species to
determine relative abundance from the
NCCOS (2006) report. However, the
SPUE quantiles used in that report had
very large ranges. For example, for
humpback whales, NMFS used the
SPUE quantile with a value of 0.1–11.8
but used 11.8 as the SPUE to determine
density. In most cases, the highest value
SPUE in any given quantile is many
magnitudes larger than the minimum
value in that particular quantile.
Second, the estimates assume that
repairs will be required every year,
which may not be the case. For the
reasons discussed in this section of the
document (and elsewhere), the take
estimates presented by NMFS are likely
an overestimate.
Based on the analysis contained
herein of the likely effects of the
specified activity on marine mammals
and their habitat, and taking into
consideration the implementation of the
mitigation and monitoring measures,
NMFS finds that operation, including
repair and maintenance activities, of the
Neptune Port will result in the
incidental take of small numbers of
marine mammals, by Level B
harassment only, and that the total
taking from Neptune’s activities will
have a negligible impact on the affected
species or stocks.
Impact on Availability of Affected
Species or Stock for Taking for
Subsistence Uses
There are no relevant subsistence uses
of marine mammals implicated by this
action. Therefore, NMFS has
determined that the total taking of
affected species or stocks would not
have an unmitigable adverse impact on
the availability of such species or stocks
for taking for subsistence purposes.
Endangered Species Act (ESA)
On January 12, 2007, NMFS
concluded consultation with MARAD
and USCG under section 7 of the ESA
on the proposed construction and
operation of the Neptune LNG facility
and issued a Biological Opinion. The
finding of that consultation was that the
construction and operation of the
Neptune LNG terminal may adversely
affect, but is not likely to jeopardize, the
continued existence of northern right,
humpback, and fin whales, and is not
likely to adversely affect sperm, sei, or
blue whales and Kemp’s ridley,
PO 00000
Frm 00029
Fmt 4700
Sfmt 4700
34171
loggerhead, green, or leatherback sea
turtles.
On March 2, 2010, MARAD and
USCG sent a letter to NMFS requesting
reinitiation of the ESA section 7
consultation. MARAD and USCG
determined that certain routine planned
operations and maintenance activities,
inspections, surveys, and unplanned
repair work on the Neptune Deepwater
Port pipelines and flowlines, as well as
any other Neptune Deepwater Port
component (including buoys, risers/
umbilicals, mooring systems, and subsea manifolds), may constitute a
modification not previously considered
in the 2007 Biological Opinion.
Construction of the Port facility has
been completed, and, therefore, is no
longer part of the proposed action. On
July 12, 2010, NMFS’ Northeast
Regional Office issued a Biological
Opinion, which concludes that the
operation of the Neptune LNG
deepwater port, including required
maintenance and repair work, is likely
to adversely affect, but is not likely to
jeopardize the continued existence of
the North Atlantic right, humpback, fin,
and sei whales. NMFS reached this
conclusion after reviewing the best
available information on the status of
endangered and threatened species
under NMFS jurisdiction, the
environmental baseline for the action
area, the effects of the action, and the
cumulative effects in the action area.
Although MARAD served as the lead
Federal agency for the section 7
consultation, the Biological Opinion
also considered the effects of permits
issued by the Army Corps of Engineers,
the Federal Energy Regulatory
Commission, and the Environmental
Protection Agency for various portions
of the maintenance and operation of the
Port and associated pipeline, as well as
NMFS’ issuance of authorizations to
Neptune under the MMPA for the take
of marine mammals incidental to Port
operations and maintenance/repairs.
NMFS has determined that issuance of
these regulations and subsequent LOAs
will not have any impacts beyond those
analyzed in the 2010 Biological
Opinion. NMFS’ Northeast Regional
Office will issue an Incidental Take
Statement upon issuance of the LOA.
National Environmental Policy Act
(NEPA)
MARAD and the USCG released a
Final EIS/Environmental Impact Report
(EIR) for the proposed Neptune LNG
Deepwater Port (see ADDRESSES). A
notice of availability of the Final EIS/
EIR was published by MARAD on
November 2, 2006 (71 FR 64606). The
Final EIS/EIR provides detailed
E:\FR\FM\13JNR1.SGM
13JNR1
34172
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
erowe on DSK5CLS3C1PROD with RULES
information on the proposed project
facilities, construction methods, and
analysis of potential impacts on marine
mammals.
NMFS was a cooperating agency in
the preparation of the Draft and Final
EISs based on a Memorandum of
Understanding related to the Licensing
of Deepwater Ports entered into by the
U.S. Department of Commerce along
with 10 other government agencies. On
June 3, 2008, NMFS adopted the USCG
and MARAD FEIS and issued a separate
Record of Decision for issuance of
authorizations pursuant to sections
101(a)(5)(A) and (D) of the MMPA for
the construction and operation of the
Neptune LNG Port facility. NMFS
reviewed the FEIS to ensure that the
analysis contained in that document
accurately describes and analyzes the
impacts to the human environment of
NMFS’ action of issuing an MMPA
authorization for the operation and
repair and maintenance of the Neptune
Port. NMFS has determined that the
FEIS sufficiently covers the activities
considered in this final rule.
Classification
The Office of Management and Budget
(OMB) has determined that this final
rule is not significant for purposes of
Executive Order 12866.
At the proposed rule stage, the Chief
Counsel for Regulation of the
Department of Commerce certified to
the Chief Counsel for Advocacy of the
Small Business Administration that this
rule, if adopted, would not have a
significant economic impact on a
substantial number of small entities.
Neptune LNG LLC is the only entity that
would be subject to the requirements in
these regulations. Neptune is one of
several companies at GDF SUEZ Energy
North America (GSENA), which itself is
a business division of GDF SUEZ Energy
Europe & International. GSENA has
more than 2,000 employees in North
America alone. Therefore, it is not a
small governmental jurisdiction, small
organization, or small business, as
defined by the Regulatory Flexibility
Act. Because of this certification, a
regulatory flexibility analysis is not
required and none has been prepared.
Notwithstanding any other provision
of law, no person is required to respond
to nor shall a person be subject to a
penalty for failure to comply with a
collection of information subject to the
requirements of the Paperwork
Reduction Act (PRA) unless that
collection of information displays a
currently valid OMB control number.
This final rule contains collection-ofinformation requirements subject to the
provisions of the PRA. These
VerDate Mar<15>2010
17:45 Jun 10, 2011
Jkt 223001
requirements have been approved by
OMB under control number 0648–0151
and include applications for regulations,
subsequent LOAs, and reports.
List of Subjects in 50 CFR Part 217
Neptune Deepwater Port within Outer
Continental Shelf blocks NK 19–04 6525
and NK 19–04 6575, which are located
at approximately 42°28′09″ N. lat and
70°36′22″ W. long.
Exports, Fish, Imports, Indians,
Labeling, Marine mammals, Penalties,
Reporting and recordkeeping
requirements, Seafood, Transportation.
§ 217.171
Dated: June 7, 2011.
Samuel D. Rauch III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
§ 217.172
For reasons set forth in the preamble,
50 CFR part 217 is amended as follows:
PART 217—REGULATIONS
GOVERNING THE TAKE OF MARINE
MAMMALS INCIDENTAL TO
SPECIFIED ACTIVITIES
1. The authority citation for part 217
continues to read as follows:
■
Authority: 16 U.S.C. 1361 et seq.
2. Subpart R is added to part 217 to
read as follows:
■
Subpart R—Taking of Marine Mammals
Incidental to Operation and Maintenance of
the Neptune Liquefied Natural Gas Facility
Off Massachusetts
Sec.
217.170 Specified activity and specified
geographical region.
217.171 Effective dates.
217.172 Permissible methods of taking.
217.173 Prohibitions.
217.174 Mitigation.
217.175 Requirements for monitoring and
reporting.
217.176 Applications for Letters of
Authorization.
217.177 Letters of Authorization.
217.178 Renewal of Letters of Authorization
and adaptive management.
217.179 Modifications of Letters of
Authorization.
Subpart R—Taking of Marine Mammals
Incidental to Operation and
Maintenance of a Liquefied Natural
Gas Facility Off Massachusetts
§ 217.170 Specified activity and specified
geographical region.
(a) Regulations in this subpart apply
only to Neptune LNG LLC (Neptune)
and those persons it authorizes to
conduct activities on its behalf for the
taking of marine mammals that occurs
in the area outlined in paragraph (b) of
this section and that occur incidental to
commissioning and operation, including
maintenance and repair activities, at the
Neptune Deepwater Port (Port).
(b) The taking of marine mammals by
Neptune may be authorized in a Letter
of Authorization only if it occurs at the
PO 00000
Frm 00030
Fmt 4700
Sfmt 4700
Effective dates.
Regulations in this subpart are
effective from July 11, 2011, through
August 10, 2016.
Permissible methods of taking.
(a) Under Letters of Authorization
issued pursuant to §§ 216.106 and
217.177 of this chapter, the Holder of
the Letter of Authorization (hereinafter
‘‘Neptune’’) may incidentally, but not
intentionally, take marine mammals
within the area described in
§ 217.170(b), provided the activity is in
compliance with all terms, conditions,
and requirements of the regulations in
this subpart and the appropriate Letter
of Authorization.
(b) The incidental take of marine
mammals under the activities identified
in § 217.170(a) is limited to the
following species and is limited to Level
B Harassment:
(1) Mysticetes:
(i) North Atlantic right whale
(Eubalaena glacialis)—120 (an average
of 24 annually).
(ii) Fin whale (Balaenoptera
physalus)—145 (an average of 29
annually).
(iii) Humpback whale (Megaptera
novaeangliae)—390 (an average of 78
annually).
(iv) Minke whale (Balaenoptera
acutorostrata)—90 (an average of 18
annually).
(v) Sei whale (Balaenoptera
borealis)—60 (an average of 12
annually).
(2) Odontocetes:
(i) Long-finned pilot whale
(Globicephala melas)—595 (an average
of 119 annually).
(ii) Atlantic white-sided dolphin
(Lagenorhynchus acutus)—1,935 (an
average of 387 annually).
(iii) Bottlenose dolphin (Tursiops
truncatus)—50 (an average of 10
annually).
(iv) Common dolphin (Delphinus
delphis)—100 (an average of 20
annually).
(v) Risso’s dolphin (Grampus
griseus)—100 (an average of 20
annually).
(vi) Killer whale (Orcinus orca)—100
(an average of 20 annually).
(vii) Harbor porpoise (Phocoena
phocoena)—25 (an average of 5
annually).
(3) Pinnipeds:
(i) Harbor seal (Phoca vitulina)—75
(an average of 15 annually).
E:\FR\FM\13JNR1.SGM
13JNR1
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
(ii) Gray seal (Halichoerus grypus)—
75 (an average of 15 annually).
§ 217.173
Prohibitions.
Notwithstanding takings
contemplated in § 217.170 and
authorized by a Letter of Authorization
issued under §§ 216.106 and 217.177 of
this chapter, no person in connection
with the activities described in
§ 217.170 may:
(a) Take any marine mammal not
specified in § 217.172(b);
(b) Take any marine mammal
specified in § 217.172(b) other than by
incidental, unintentional Level B
Harassment;
(c) Take a marine mammal specified
in § 217.172(b) if such taking results in
more than a negligible impact on the
species or stocks of such marine
mammal; or
(d) Violate, or fail to comply with, the
terms, conditions, and requirements of
this subpart or a Letter of Authorization
issued under §§ 216.106 and 217.177 of
this chapter.
erowe on DSK5CLS3C1PROD with RULES
§ 217.174
Mitigation.
(a) When conducting the activities
identified in § 217.170(a), the mitigation
measures contained in the Letter of
Authorization issued under §§ 216.106
and 217.177 must be implemented.
These mitigation measures include but
are not limited to:
(1) Major Repairs (May 1–November
30):
(i) During repairs, if a marine mammal
is detected within 0.6 mi (1 km) of the
repair vessel (or acoustically), the vessel
superintendent or on-deck supervisor
shall be notified immediately. The
vessel’s crew will be put on a
heightened state of alert. The marine
mammal will be monitored constantly
to determine if it is moving toward the
repair area.
(ii) Repair vessels shall cease any
movement in the area if a marine
mammal other than a right whale is
sighted within or approaching to a
distance of 100 yd (91 m) from the
operating repair vessel. Repair vessels
shall cease any movement in the
construction area if a right whale is
sighted within or approaching to a
distance of 500 yd (457 m) from the
operating vessel. Vessels transiting the
repair area, such as pipe haul barge tugs,
shall also be required to maintain these
separation distances.
(iii) Repair vessels shall cease all
sound emitting activities if a marine
mammal other than a right whale is
sighted within or approaching to a
distance of 100 yd (91 m) or if a right
whale is sighted within or approaching
to a distance of 500 yd (457 m), from the
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
operating repair vessel. The backcalculated source level, based on the
most conservative cylindrical model of
acoustic energy spreading, is estimated
to be 139 dB re 1 μPa.
(iv) Repair activities may resume after
the marine mammal is positively
reconfirmed outside the established
zones (either 500 yd (457 m) or 100 yd
(91 m), depending upon species) or if
the marine mammal has not been resighted in the established zones for 30
minutes.
(v) While under way, all repair vessels
shall remain 500 yd (457 m) away from
right whales and 100 yd (91 m) away
from all other marine mammals, unless
constrained by human safety concerns
or navigational constraints.
(vi) All repair vessels 300 gross tons
or greater must maintain a speed of 10
knots (18.5 km/hr) or less. Vessels less
than 300 gross tons carrying supplies or
crew between the shore and the repair
site must contact the Mandatory Ship
Reporting System, the U.S. Coast Guard
(USCG), or the protected species
observers (PSOs) at the repair site before
leaving shore for reports of recent right
whale sightings or active Dynamic
Management Areas (DMAs) and,
consistent with navigation safety,
restrict speeds to 10 knots (18.5 km/hr)
or less within 5 mi (8 km) of any recent
sighting location and within any
existing DMA.
(vii) Vessels transiting through the
Cape Cod Canal and Cape Cod Bay
(CCB) between January 1 and May 15
must reduce speeds to 10 knots (18.5
km/hr) or less, follow the recommended
routes charted by NOAA to reduce
interactions between right whales and
shipping traffic, and avoid aggregations
of right whales in the eastern portion of
CCB.
(2) Major Repairs (December 1–April
30): If unplanned/emergency repair
activities cannot be conducted between
May 1 and November 30, then Neptune
shall implement the following
mitigation measures in addition to those
listed in § 217.174(a)(1)(i) through (vii):
(i) If on-board PSOs do not have at
least 0.6-mi (1-km) visibility, they shall
call for a shutdown of repair activities.
If dive operations are in progress, then
they shall be halted and divers brought
on board until visibility is adequate to
see a 0.6-mi (1-km) range. At the time
of shutdown, the use of thrusters must
be minimized to the lowest level needed
to maintain personnel safety. If there are
potential safety problems due to the
shutdown, the captain must decide
what operations can safely be shut
down and shall document such
activities in the data log.
PO 00000
Frm 00031
Fmt 4700
Sfmt 4700
34173
(ii) Prior to leaving the dock to begin
transit, the barge must contact one of the
PSOs on watch to receive an update of
sightings within the visual observation
area. If the PSO has observed a North
Atlantic right whale within 30 minutes
of the transit start, the vessel shall hold
for 30 minutes and again seek clearance
to leave from the PSOs on board. PSOs
will assess whale activity and visual
observation ability at the time of the
transit request to clear the barge for
release and will grant clearance if no
North Atlantic right whales have been
sighted in the last 30 minutes in the
visual observation area.
(iii) Neptune or its contractor shall
provide a half-day training course to
designated crew members assigned to
the transit barges and other support
vessels who will have responsibilities
for watching for marine mammals. This
course shall cover topics including, but
not limited to, descriptions of the
marine mammals found in the area,
mitigation and monitoring requirements
contained in the Letter of Authorization,
sighting log requirements, and
procedures for reporting injured or dead
marine mammals. These designated
crew members shall be required to keep
watch on the bridge and immediately
notify the navigator of any whale
sightings. All watch crew members shall
sign into a bridge log book upon start
and end of watch. Transit route,
destination, sea conditions, and any
protected species sightings/mitigation
actions during watch shall be recorded
in the log book. Any whale sightings
within 3,281 ft (1,000 m) of the vessel
shall result in a high alert and slow
speed of 4 knots (7.4 km/hr) or less. A
sighting within 2,461 ft (750 m) shall
result in idle speed and/or ceasing all
movement.
(iv) The material barges and tugs used
for repair work shall transit from the
operations dock to the work sites during
daylight hours, when possible, provided
the safety of the vessels is not
compromised. Should transit at night be
required, the maximum speed of the tug
shall be 5 knots (9.3 km/hr).
(v) Consistent with navigation safety,
all repair vessels must maintain a speed
of 10 knots (18.5 km/hr) or less during
daylight hours. All vessels shall operate
at 5 knots (9.3 km/hr) or less at all times
within 3.1 mi (5 km) of the repair area.
(3) Speed Restrictions in Seasonal
Management Areas (SMAs): Repair
vessels and shuttle regasification vessels
(SRVs) shall transit at 10 knots (18.5
km/hr) or less in the following seasons
and areas, which either correspond to or
are more restrictive than the times and
areas in NMFS’ regulations at 50 CFR
224.105 that implement speed
E:\FR\FM\13JNR1.SGM
13JNR1
erowe on DSK5CLS3C1PROD with RULES
34174
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
restrictions to reduce the likelihood and
severity of ship strikes of right whales:
(i) CCB SMA from January 1 through
May 15, which includes all waters in
CCB, extending to all shorelines of the
Bay, with a northern boundary of 42°
12′ N. latitude;
(ii) Off Race Point SMA year round,
which is bounded by straight lines
connecting the following coordinates in
the order stated: 42°30′ N. 69°45′ W.;
thence to 42°30′ N. 70°30′ W.; thence to
42°12′ N. 70°30′ W.; thence to 42°12′ N.
70°12′ W.; thence to 42°04′ 56.5″ N.
70°12′ W.; thence along mean high
water line and inshore limits of
COLREGS limit to a latitude of 41°40′
N.; thence due east to 41°41′ N. 69°45′
W.; thence back to starting point; and
(iii) Great South Channel (GSC) SMA
from April 1 through July 31, which is
bounded by straight lines connecting
the following coordinates in the order
stated:
(A) 42°30′ N. 69°45′ W.
(B) 41°40′ N. 69°45′ W.
(C) 41°00′ N. 69°05′ W.
(D) 42°09′ N. 67°08′ 24″ W.
(E) 42°30′ N. 67°27′ W.
(F) 42°30′ N. 69°45′ W.
(4) Additional Mitigation Measures:
(i) When approaching and departing
from the Neptune Port, SRVs shall use
the Boston Traffic Separation Scheme
(TSS) starting and ending at the
entrance to the GSC. Upon entering the
TSS, the SRV shall go into a ‘‘heightened
awareness’’ mode of operation.
(ii) In the event that a whale is
visually observed within 0.6 mi (1 km)
of the Port or a confirmed acoustic
detection is reported on either of the
two auto-detection buoys (ABs) closest
to the Port, departing SRVs shall delay
their departure from the Port, unless
extraordinary circumstances, defined in
the Marine Mammal Detection,
Monitoring, and Response Plan (the
Plan), require that the departure is not
delayed. The departure delay shall
continue until either the observed whale
has been visually (during daylight
hours) confirmed as more than 0.6 mi (1
km) from the Port or 30 minutes have
passed without another confirmed
detection either acoustically within the
acoustic detection range of the two ABs
closest to the Port or visually within 0.6
mi (1 km) from Neptune.
(iii) SRVs that are approaching or
departing from the Port and are within
the Area to be Avoided (ATBA)
surrounding Neptune shall remain at
least 0.6 mi (1 km) away from any
visually detected right whales and at
least 100 yd (91 m) away from all other
visually detected whales unless
extraordinary circumstances, as defined
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
in Section 1.2 of the Plan, require that
the vessel stay its course. The ATBA is
defined in 33 CFR 150.940. It is the
largest area of the Port marked on
nautical charts, and it is enforceable by
the USCG in accordance with the 33
CFR 150.900 regulations. The Vessel
Master shall designate at least one
lookout to be exclusively and
continuously monitoring for the
presence of marine mammals at all
times while the SRV is approaching or
departing Neptune.
(iv) Neptune shall ensure that other
vessels providing support to Port
operations during regasification
activities that are approaching or
departing from the Port and are within
the ATBA shall be operated so as to
remain at least 0.6 mi (1 km) away from
any visually detected right whales and
at least 100 yd (91 m) from all other
visually detected whales.
(v) PSOs shall direct a moving vessel
to slow to idle if a baleen whale is seen
less than 0.6 mi (1 km) from the vessel.
(vi) Use of lights during repair or
maintenance activities shall be limited
to areas where work is actually
occurring, and all other lights must be
extinguished. Lights must be
downshielded to illuminate the deck
and shall not intentionally illuminate
surrounding waters, so as not to attract
whales or their prey to the area.
(vii) Neptune must immediately
suspend any repair and maintenance or
operations activities if a dead or injured
marine mammal is found in the vicinity
of the project area, and the death or
injury of the animal could be
attributable to the Port facility activities.
Upon finding a dead or injured marine
mammal, Neptune must contact NMFS,
the Northeast Stranding and
Disentanglement Program, and the
USCG. NMFS will review the
documentation submitted by the PSO
and attempt to attribute a cause of
death. Activities shall not resume until
review and approval has been given by
NMFS.
(5) Additional mitigation measures as
contained in a Letter of Authorization
issued under §§ 216.106 and 217.177 of
this chapter.
(b) [Reserved]
§ 217.175 Requirements for monitoring
and reporting.
(a) Visual Monitoring Program:
(1) Neptune shall employ PSOs
during maintenance- and repair-related
activities on each vessel that has a
dynamic positioning system. Two (2)
PSOs shall be on-duty at all times. All
PSOs must receive NMFS-approved
PSO training and be approved in
PO 00000
Frm 00032
Fmt 4700
Sfmt 4700
advance by NMFS after a review of their
qualifications.
(2) Qualifications for these PSOs shall
include direct field experience on a
marine mammal observation vessel and/
or aerial surveys in the Atlantic Ocean/
Gulf of Mexico.
(3) The PSOs (one primary and one
secondary) are responsible for visually
locating marine mammals at the ocean’s
surface and, to the extent possible,
identifying the species. The primary
PSO shall act as the identification
specialist, and the secondary PSO shall
serve as data recorder and also assist
with identification. Both PSOs shall
have responsibility for monitoring for
the presence of marine mammals.
(4) The PSOs shall monitor the
maintenance/repair area using the
naked eye, hand-held binoculars, and/or
power binoculars.
(5) The PSOs shall scan the ocean
surface during maintenance- and repairrelated activities and record all sightings
in marine mammal field sighting logs.
Observations of marine mammals shall
be identified to the species or the lowest
taxonomic level possible, and their
relative position in relation to the vessel
shall be recorded.
(6) While a SRV is navigating within
the designated TSS, three people have
lookout duties on or near the bridge of
the ship including the SRV Master, the
Officer-of-the-Watch, and the Helmsman
on watch.
(7) In addition to standard watch
procedures, while the SRV is within the
ATBA and/or while actively engaging in
the use of thrusters, an additional
lookout shall be designated to
exclusively and continuously monitor
for marine mammals. Once the SRV is
moored and regasification activities
have begun, the vessel is no longer
considered in ‘‘heightened awareness’’
status.
(8) At the conclusion of regasification
activities, when the SRV is prepared to
depart from the Port, the Master shall
once again ensure that the
responsibilities as defined in the Plan
are carried out. All sightings of marine
mammals by the designated lookout,
individuals posted to navigational
lookout duties, and/or any other crew
member while the SRV is within the
TSS, in transit to the ATBA, within the
ATBA, and/or when actively engaging
in the use of thrusters shall be
immediately reported to the Officer-ofthe-Watch who shall then alert the
Master.
(b) Passive Acoustic Monitoring
(PAM) Program:
(1) Neptune shall work with NMFS,
Stellwagen Bank National Marine
Sanctuary (SBNMS), and other scientists
E:\FR\FM\13JNR1.SGM
13JNR1
erowe on DSK5CLS3C1PROD with RULES
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
to install and monitor an array of
passive acoustic detection buoys in the
Boston TSS that meets the criteria
specified in the recommendations
developed by NOAA through
consultation with the USCG under the
National Marine Sanctuary Act (NMSA).
The system shall provide near real-time
information on the presence of
vocalizing whales in the shipping lanes.
(2) Neptune shall work with NMFS,
SBNMS, and other scientists to monitor
the archival array of acoustic recording
units (ARUs), or ‘‘pop-ups,’’ around the
Port that meets the criteria specified in
the program developed by NOAA in
consultation with the USCG under the
NMSA. The ARUs shall remain in place
for 5 years following initiation of
operations to monitor the actual
acoustic output of port operations and
alert NOAA to any unanticipated
adverse effects of port operations, such
as large-scale abandonment of the area
or greater acoustic impacts than
predicted through modeling.
(3) Passive acoustic devices shall be
actively monitored for detections by a
NMFS-approved bioacoustic technician.
(4) Repair Activity PAM Measures:
PAM, in addition to that required in this
section of these regulations, shall be
required, on a case-by-case basis, during
both planned and emergency repair
activities in order to better detect right
whales in the area of repair work and to
collect additional data on the noise
levels produced during repair and
maintenance activities.
(i) Neptune shall work with NOAA
(NMFS and SBNMS) to evaluate when
to install and maintain an array of realtime passive acoustic detection buoys to
provide early warnings for potential
occurrence of right whales in the
vicinity of the repair area. The number
of passive acoustic detection buoys
installed around the activity site, if
deemed necessary, shall be
commensurate with the type and spatial
extent of maintenance/repair work
required, but must be sufficient to detect
vocalizing right whales within the 120dB impact zone.
(ii) Neptune shall provide NMFS with
empirically measured source level data
for all sources of noise associated with
Port maintenance and repair activities.
Measurements shall be carefully
planned and coordinated with noiseproducing activities and shall be
collected from the passive detection
network.
(5) SRV Regasification PAM
Measures: Source levels associated with
dynamic positioning of SRVs at the
buoys shall be estimated using
empirical measurements collected from
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
a platform positioned as close as
practicable to thrusters while in use.
(c) Neptune must implement the
following reporting requirements:
(1) Because the Port is within the
Mandatory Ship Reporting Area
(MSRA), all SRVs transiting to and from
the Port must report their activities to
the mandatory reporting section of the
USCG to remain apprised of North
Atlantic right whale movements within
the area. All vessels entering and exiting
the MSRA must report their activities to
WHALESNORTH. Any North Atlantic
right whale sightings must be reported
to the NMFS Sighting Advisory System.
(2) Repair Work Reports. (i) For major
repair work associated with the pipeline
lateral or other port components,
Neptune shall notify the appropriate
NOAA personnel as soon as practicable
after it is determined that repair work
must be conducted.
(ii) During maintenance and repair of
the pipeline lateral or other port
components, weekly status reports must
be provided to NOAA. The weekly
report must include data collected for
each distinct marine mammal species
observed in the project area during the
period of the repair activity. The weekly
reports shall include the following:
(A) The location, time, and nature of
the pipeline lateral activities;
(B) Whether the dynamic position
(DP) system was operated and, if so, the
number of thrusters used and the time
and duration of DP operation;
(C) Marine mammals observed in the
area (number, species, age group, and
initial behavior);
(D) The distance of observed marine
mammals from the repair activities;
(E) Observed marine mammal
behaviors during the sighting;
(F) Whether any mitigation measures
were implemented;
(G) Weather conditions (sea state,
wind speed, wind direction, ambient
temperature, precipitation, and percent
cloud cover, etc.);
(H) Condition of the marine mammal
observation (visibility and glare); and
(I) Details of passive acoustic
detections and any action taken in
response to those detections.
(iii) For all minor repair work,
Neptune must notify NOAA regarding
when and where the repair/maintenance
work is to take place along with a
tentative schedule and description of
the work, as soon as practicable after it
is determined that repair work must be
conducted. Vessel crews shall record/
document any marine mammal
sightings during the work period.
(iv) At the conclusion of all minor
repair work, Neptune shall provide
NOAA with a report describing any
PO 00000
Frm 00033
Fmt 4700
Sfmt 4700
34175
marine mammal sightings, the type of
work taking place when the sighting
occurred, and any avoidance actions
taken during the repair/maintenance
work.
(3) Incident Reports. During all phases
of project repair/maintenance activities
and operation, sightings of any injured
or dead marine mammals must be
reported immediately to the Chief,
Permits, Conservation and Education
Division or staff member and the
Northeast Stranding and
Disentanglement Program, regardless of
whether the injury or death is caused by
project activities. If the injury or death
was caused by a project vessel (e.g.,
SRV, support vessel, or construction
vessel), the USCG must be notified
immediately, and a full report must be
provided to NMFS. Activities will not
resume until review and approval has
been given by NMFS. The report must
include the following information:
(i) Time, date, and location (latitude/
longitude) of the incident;
(ii) The name and type of vessel
involved;
(iii) The vessel’s speed during the
incident;
(iv) Description of the incident;
(v) Water depth;
(vi) Environmental conditions (e.g.,
wind speed and direction, sea state,
cloud cover, and visibility);
(vii) Species identification or
description of the animal;
(viii) The fate of the animal; and
(ix) Photographs or video footage of
the animal (if equipment is available).
(4) Annual Reports. (i) An annual
report on marine mammal monitoring
and mitigation shall be submitted to
NMFS, Office of Protected Resources,
and NMFS, Northeast Regional Office
(specific contact information to be
provided in Letter of Authorization), on
August 1 of each year. The annual
report shall cover the time period of
January 1 through December 31 of each
year of activity.
(ii) The annual report shall include
data collected for each distinct marine
mammal species observed in the project
area in the Massachusetts Bay during
the period of Port operations and repair/
maintenance activities. The annual
report shall also include a description of
marine mammal behavior, overall
numbers of individuals observed,
frequency of observation, and any
behavioral changes and the context of
the changes relative to operation and
repair/maintenance activities.
Additional information that shall be
recorded by Neptune or its contractor
during operations and repair/
maintenance activities and contained in
the reports include: results of empirical
E:\FR\FM\13JNR1.SGM
13JNR1
34176
Federal Register / Vol. 76, No. 113 / Monday, June 13, 2011 / Rules and Regulations
source level estimation for thrusters
while in use and activities associated
with maintenance and repair events,
date and time of marine mammal
detections (visually or acoustically),
weather conditions, species
identification, approximate distance
from the source, activity of the vessel
when a marine mammal is sighted, and
whether thrusters were in use and, if so,
how many at the time of the sighting.
(5) Five-year Comprehensive Report.
(i) Neptune shall submit a draft
comprehensive final report to NMFS,
Office of Protected Resources, and
NMFS, Northeast Regional Office
(specific contact information to be
provided in Letter of Authorization),
180 days prior to the expiration of the
regulations. This comprehensive
technical report shall provide full
documentation of methods, results, and
interpretation of all monitoring during
the first four and a half years of the
LOA.
(ii) Neptune shall submit a revised
final comprehensive technical report,
including all monitoring results during
the entire period of the LOAs, 90 days
after the end of the period of
effectiveness of the regulations to
NMFS, Office of Protected Resources,
and NMFS, Northeast Regional Office
(specific contact information to be
provided in Letter of Authorization).
§ 217.176 Applications for Letters of
Authorization.
(a) To incidentally take marine
mammals pursuant to these regulations,
the U.S. Citizen (as defined by
§ 216.103) conducting the activity
identified in § 217.170(a) (i.e., Neptune)
must apply for and obtain either an
initial Letter of Authorization in
accordance with § 217.177 or a renewal
under § 217.178.
(b) [Reserved]
erowe on DSK5CLS3C1PROD with RULES
§ 217.177
Letters of Authorization.
(a) A Letter of Authorization, unless
suspended or revoked, shall be valid for
a period of time not to exceed the period
of validity of this subpart.
(b) The Letter of Authorization shall
set forth:
(1) Permissible methods of incidental
taking;
(2) Means of effecting the least
practicable adverse impact on the
species, its habitat, and on the
availability of the species for
subsistence uses (i.e., mitigation); and
VerDate Mar<15>2010
14:06 Jun 10, 2011
Jkt 223001
(3) Requirements for mitigation,
monitoring and reporting.
(c) Issuance and renewal of the Letter
of Authorization shall be based on a
determination that the total number of
marine mammals taken by the activity
as a whole will have no more than a
negligible impact on the affected species
or stock of marine mammal(s).
§ 217.178 Renewal of Letters of
Authorization and adaptive management.
(a) A Letter of Authorization issued
under § 216.106 and § 217.177 of this
chapter for the activity identified in
§ 217.170(a) shall be renewed upon
request by the applicant or
determination by NMFS and the
applicant that modifications are
appropriate pursuant to the adaptive
management component of these
regulations, provided that:
(1) NMFS is notified that the activity
described in the application submitted
under § 217.176 will be undertaken and
that there will not be a substantial
modification to the described work,
mitigation or monitoring undertaken
during the upcoming 12 months;
(2) NMFS recieves the monitoring
reports required under § 217.175(c)(1)–
(4); and
(3) NMFS determines that the
mitigation, monitoring and reporting
measures required under §§ 217.174 and
217.175 and the Letter of Authorization
issued under §§ 216.106 and 217.177 of
this chapter were undertaken and will
be undertaken during the upcoming
annual period of validity of a renewed
Letter of Authorization.
(b) If either a request for a renewal of
a Letter of Authorization issued under
§§ 216.106 and 217.178 or a
determination by NMFS and the
applicant that modifications are
appropriate pursuant to the adaptive
management component of these
regulations indicates that a substantial
modification, as determined by NMFS,
to the described work, mitigation or
monitoring undertaken during the
upcoming season will occur, NMFS will
provide the public a period of 30 days
for review and comment on the request.
Review and comment on renewals of
Letters of Authorization are restricted
to:
(1) New cited information and data
indicating that the determinations made
in this document are in need of
reconsideration, and
(2) Proposed substantive changes to
the mitigation and monitoring
PO 00000
Frm 00034
Fmt 4700
Sfmt 9990
requirements contained in these
regulations or in the current Letter of
Authorization.
(c) A notice of issuance or denial of
a renewal of a Letter of Authorization
will be published in the Federal
Register.
(d) Adaptive Management—NMFS
may modify or augment the existing
mitigation or monitoring measures (after
consulting with Neptune regarding the
practicability of the modifications) if
doing so creates a reasonable likelihood
of more effectively accomplishing the
goals of mitigation and monitoring set
forth in the preamble of these
regulations. Below are some of the
possible sources of new data that could
contribute to the decision to modify the
mitigation or monitoring measures:
(1) Results from Neptune’s monitoring
from the previous year;
(2) Results from general marine
mammal and sound research; or
(3) Any information which reveals
that marine mammals may have been
taken in a manner, extent or number not
authorized by these regulations or
subsequent LOAs.
§ 217.179 Modifications of Letters of
Authorization.
(a) Except as provided in paragraph
(b) of this section, no substantive
modification (including withdrawal or
suspension) to the Letter of
Authorization issued by NMFS,
pursuant to §§ 216.106 and 217.177 of
this chapter and subject to the
provisions of this subpart shall be made
until after notification and an
opportunity for public comment has
been provided. For purposes of this
paragraph, a renewal of a Letter of
Authorization under § 217.178, without
modification (except for the period of
validity), is not considered a substantive
modification.
(b) If the Assistant Administrator
determines that an emergency exists
that poses a significant risk to the wellbeing of the species or stocks of marine
mammals specified in § 217.172(b), a
Letter of Authorization issued pursuant
to §§ 216.106 and 217.177 of this
chapter may be substantively modified
without prior notification and an
opportunity for public comment.
Notification will be published in the
Federal Register within 30 days
subsequent to the action.
[FR Doc. 2011–14614 Filed 6–10–11; 8:45 am]
BILLING CODE 3510–22–P
E:\FR\FM\13JNR1.SGM
13JNR1
Agencies
[Federal Register Volume 76, Number 113 (Monday, June 13, 2011)]
[Rules and Regulations]
[Pages 34157-34176]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-14614]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 217
[Docket No. 0808041026-1295-02]
RIN 0648-AX09
Taking and Importing Marine Mammals; Taking Marine Mammals
Incidental to Operation and Maintenance of the Neptune Liquefied
Natural Gas Facility off Massachusetts
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS, upon application from Neptune LNG LLC (Neptune), is
issuing regulations pursuant to the Marine Mammal Protection Act (MMPA)
to govern the unintentional taking of marine mammals, by harassment,
incidental to port commissioning and operations, including maintenance
and repair activities, at the Neptune Deepwater Port (the Port) in
Massachusetts Bay for the period of July 2011 through July 2016. These
regulations, which allow for the issuance of Letters of Authorization
(LOAs) for the incidental take of marine mammals during the described
activities and specified timeframes, prescribe the permissible methods
of taking and other means of effecting the least practicable adverse
impact on marine mammal species or stocks and their habitat, as well as
requirements pertaining to the monitoring and reporting of such taking.
DATES: Effective from July 11, 2011, through August 10, 2016.
ADDRESSES: A copy of Neptune's application may be obtained by writing
to Michael Payne, Chief, Permits, Conservation and Education Division,
Office of Protected Resources, NMFS, 1315 East West Highway, Silver
Spring, MD 20910, calling the contact listed under FOR FURTHER
INFORMATION CONTACT, or visiting the Internet at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm. Documents cited in this
final rule may also be viewed, by appointment, during regular business
hours at the above address.
The Final Environmental Impact Statement (Final EIS) on the Neptune
Deepwater Port License Application authored by the Maritime
Administration (MARAD) and U.S. Coast Guard (USCG) is available for
viewing at https://www.regulations.gov by entering the search words
``Neptune LNG.''
FOR FURTHER INFORMATION CONTACT: Candace Nachman, Office of Protected
Resources, NMFS, (301) 713-2289, ext 156.
SUPPLEMENTARY INFORMATION:
Background
Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.)
direct the Secretary of Commerce to allow, upon request, the
incidental, but not intentional, taking of small numbers of marine
mammals by U.S. citizens who engage in a specified activity (other than
commercial fishing) within a specified geographical region if certain
findings are made and either regulations are issued or, if the taking
is limited to harassment, a notice of a proposed authorization is
provided to the public for review.
Authorization for incidental takings shall be granted if NMFS finds
that the taking will have a negligible impact on the species or
stock(s), will not have an unmitigable adverse impact on the
availability of the species or stock(s) for subsistence uses (where
relevant), and if the permissible methods of taking and requirements
pertaining to the mitigation, monitoring and reporting of such takings
are set forth. NMFS has defined ``negligible impact'' in 50 CFR 216.103
as ``* * * an impact resulting from the specified activity that cannot
be reasonably expected to, and is not reasonably likely to, adversely
affect the species or stock through effects on annual rates of
recruitment or survival.''
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''].
[[Page 34158]]
Summary of Request
On December 14, 2009, NMFS received an application from Neptune for
the taking, by harassment, of marine mammals incidental to port
commissioning and operations, including maintenance and repair
activities, at its Neptune Deepwater Port (Port) facility in
Massachusetts Bay. NMFS reviewed Neptune's application and identified a
number of issues requiring further clarification. After addressing
comments from NMFS, Neptune modified its application and submitted a
revised application on March 11, 2010. The March 11, 2010, application
was the one made available for public comment and considered by NMFS
for these regulations.
Neptune submitted its first complete application to NMFS on
December 27, 2007, for the take of small numbers of marine mammals, by
harassment, incidental to the construction phase of the Neptune LNG
Port Facility. In June 2008, NMFS issued a 1-year Incidental Harassment
Authorization (IHA) to Neptune for the construction of the Port (73 FR
33400, June 12, 2008). This authorization expired on June 30, 2009.
NMFS issued a second 1-year IHA to Neptune for the completion of
construction and beginning of Port operations on June 26, 2009 (74 FR
31926, July 6, 2009), which expired on June 30, 2010.
On July 12, 2010, NMFS issued a third IHA to Neptune based on the
request in its March 11, 2010, application (75 FR 41440, July 16,
2010). This latest IHA is effective through July 11, 2011. During the
period of this third IHA, Neptune conducted limited port operations.
During the effective period of this final rule (July 2011-July
2016), Neptune intends to continue port operations (including
commissioning of its second shuttle regasification vessel [SRV]) and
conduct maintenance and repairs, as needed. The Neptune Port is located
approximately 22 mi (35 km) northeast of Boston, Massachusetts, in
Federal waters approximately 260 ft (79 m) in depth. The purpose of the
Port is to import liquefied natural gas (LNG) into the New England
region. Take of marine mammals may occur during port operations from
thruster use during maneuvering of the SRVs while docking and
undocking, occasional weathervaning (turning of a vessel at anchor from
one direction to another under the influence of wind or currents) at
the Port, and during thruster use of dynamic positioning (DP)
maintenance vessels should a major repair be necessary. Neptune
requested authorization to take 12 marine mammal species by Level B
harassment. The species are: North Atlantic right whale; humpback
whale; fin whale; sei whale; minke whale; long-finned pilot whale;
Atlantic white-sided dolphin; harbor porpoise; common dolphin; Risso's
dolphin; bottlenose dolphin; and harbor seal. In the 2009 and 2010
IHAs, NMFS also authorized take of killer whales and gray seals. NMFS
has determined that it would be appropriate in this final rule to
authorize take, by Level B harassment only, incidental to operations
and maintenance activities of these two species as well. In this final
rule, NMFS has authorized the take, by Level B harassment, of all 14
marine mammal species listed here.
Description of the Specified Activity
On March 23, 2007, Neptune received a license from MARAD to own,
construct, and operate a deepwater port. The Port, which is located in
Massachusetts Bay, consists of a submerged buoy system to dock
specifically designed LNG carriers approximately 22 mi (35 km)
northeast of Boston, Massachusetts, in Federal waters approximately 260
ft (79 m) in depth. The two buoys are separated from one another by a
distance of approximately 2.1 mi (3.4 km). The locations of the Neptune
Port and the associated pipeline are shown in Figure 2-1 in Neptune's
application (see ADDRESSES).
All construction of the Neptune Port was completed in November
2009. The first SRV was commissioned in February-March 2010. Between
July 2011 and July 2016, (the time period for these regulations),
Neptune plans to continue Port operations (including commissioning of
its second SRV) and also plans to conduct any necessary maintenance and
repairs of the Port facility.
Neptune will be capable of mooring LNG SRVs with a capacity of
approximately 183,113 cubic yards (yd\3\; 140,000 cubic meters (m\3\))
of LNG. Up to two SRVs will temporarily moor at the Port by means of a
submerged unloading buoy system. Two separate buoys will allow natural
gas to be delivered in a continuous flow, without interruption, by
having a brief overlap between arriving and departing SRVs. The annual
average throughput capacity will be around 500 million standard cubic
feet per day (mmscfd) with an initial throughput of 400 mmscfd and a
peak capacity of approximately 750 mmscfd of LNG.
The SRVs will be equipped to store, transport, and vaporize LNG and
to odorize, meter and send out natural gas by means of two 16-in (40.6-
cm) flexible risers and one 24-in (61-cm) subsea flowline. These risers
and flowline will lead to a 24-in (61-cm) gas transmission pipeline
connecting the deepwater port to the existing 30-in (76.2-cm) Algonquin
Hubline\SM\ (Hubline\SM\) located approximately 9 mi (14.5 km) west of
the Neptune deepwater port location. The Port will have an expected
operating life of approximately 25 years. Figure 1-1 of Neptune's
application shows an isometric view of the Port (see ADDRESSES). A
detailed overview of Port operations and maintenance and repair
activities, as well as the types of sounds those activities produce,
was provided in the proposed rule (75 FR 80260, December 21, 2010). No
changes have been made to the proposed operations or maintenance and
repair activities.
Description of Marine Mammals in the Area of the Specified Activity
Massachusetts Bay (as well as the entire Atlantic Ocean) hosts a
diverse assemblage of marine mammals, including: The North Atlantic
right whale; blue whale; fin whale; sei whale; minke whale; humpback
whale; killer whale; long-finned pilot whale; sperm whale; Atlantic
white-beaked dolphin; Atlantic white-sided dolphin; bottlenose dolphin;
common dolphin; harbor porpoise; Risso's dolphin; striped dolphin; gray
seal; harbor seal; harp seal; and hooded seal. Table 3-1 in Neptune's
application outlines the marine mammal species that occur in
Massachusetts Bay and the likelihood of occurrence of each species. Of
the species listed here, the North Atlantic right, blue, fin, sei,
humpback, and sperm whales are all listed as endangered under the
Endangered Species Act (ESA) and as depleted under the MMPA. The
northern coastal stock of bottlenose dolphins is considered depleted
under the MMPA. Certain stocks or populations of killer whales are
listed as endangered under the ESA or depleted under the MMPA; however,
none of those stocks or populations occurs in the activity area.
Of these species, 14 are expected to occur in the area of Neptune's
operations. These species include: The North Atlantic right, humpback,
fin, sei, minke, killer, and long-finned pilot whales; Atlantic white-
sided, common, Risso's, and bottlenose dolphins; harbor porpoise; and
harbor and gray seals. Neptune used information from the Cetacean and
Turtle Assessment Program (CETAP; 1982) and the U.S. Navy's Marine
Resource Assessment (MRA) for the Northeast Operating Areas (DoN, 2005;
available on the Internet at: https://
[[Page 34159]]
portal.navfac.navy.mil/portal/page/portal/navfac/navfac--ww--pp/
navfac--hq--pp/navfac--environmental/mra) to estimate densities of the
species in the area. Nonetheless, NMFS used the data on cetacean
distribution within Massachusetts Bay, such as those published by
NOAA's National Centers for Coastal Ocean Science (NCCOS; 2006), to
determine density estimates of several species of marine mammals in the
vicinity of the project area. The explanation for those derivations and
the actual density estimates are described later in this document (see
the ``Estimated Take by Incidental Harassment'' section).
The proposed rule contains a discussion of 17 marine mammal species
that are not considered further in the analysis because of their rarity
in the Massachusetts Bay area (blue whale, sperm whale, harp seal,
hooded seal, ringed seal, northern bottlenose whale, Cuvier's beaked
whale, Sowerby's beaked whale, Blainville's beaked whale, Gervais'
beaked whale, True's beaked whale, beluga whale, pantropical spotted
dolphin, false killer whale, pygmy sperm whale, striped dolphin, and
Atlantic white-beaked dolphin). The proposed rule also contains brief
summaries on several commonly sighted marine mammal species
distribution and abundance in the vicinity of the action area. The
``Description of Marine Mammals in the Area of the Specified Activity''
has not changed from the proposed rule. Please refer to the proposed
rule (75 FR 80260, December 21, 2010) for the complete discussion.
Additionally, information on those species that may be impacted by
this activity is provided in Neptune's application and sections 3.2.3
and 3.2.5 in the MARAD/USCG Final EIS on the Neptune LNG proposal (see
ADDRESSES). Please refer to those documents for more information on
these species. Also, general information on these marine mammal species
can also be found in the 2009 NMFS U.S. Atlantic and Gulf of Mexico
Marine Mammal Stock Assessment Report (SAR; Waring et al., 2009) and
the 2010 Draft NMFS Atlantic and Gulf of Mexico Marine Mammal SAR
(Waring et al., in prep.), which are available on the Internet at:
https://www.nefsc.noaa.gov/publications/tm/tm213/ and https://www.nmfs.noaa.gov/pr/sars/draft.htm, respectively.
Brief Background on Marine Mammal Hearing
When considering the influence of various kinds of sound on the
marine environment, it is necessary to understand that different kinds
of marine life are sensitive to different frequencies of sound. Based
on available behavioral data, audiograms derived using auditory evoked
potential techniques, anatomical modeling, and other data, Southall et
al. (2007) designate ``functional hearing groups'' for marine mammals
and estimate the lower and upper frequencies of functional hearing of
the groups. The functional groups and the associated frequencies are
indicated below (though animals are less sensitive to sounds at the
outer edge of their functional range and most sensitive to sounds of
frequencies within a smaller range somewhere in the middle of their
functional hearing range):
Low frequency cetaceans (13 species of mysticetes):
Functional hearing is estimated to occur between approximately 7 Hz and
22 kHz (however, a study by Au et al. (2006) of humpback whale songs
indicate that the range may extend to at least 24 kHz);
Mid-frequency cetaceans (32 species of dolphins, six
species of larger toothed whales, and 19 species of beaked and
bottlenose whales): functional hearing is estimated to occur between
approximately 150 Hz and 160 kHz;
High frequency cetaceans (eight species of true porpoises,
six species of river dolphins, Kogia, the franciscana, and four species
of cephalorhynchids): functional hearing is estimated to occur between
approximately 200 Hz and 180 kHz; and
Pinnipeds in Water: functional hearing is estimated to
occur between approximately 75 Hz and 75 kHz, with the greatest
sensitivity between approximately 700 Hz and 20 kHz.
As mentioned previously in this document, 14 marine mammal species
(12 cetacean and two pinniped species) are likely to occur in the
Neptune Port area. Of the 12 cetacean species likely to occur in
Neptune's project area, five are classified as low frequency cetaceans
(i.e., North Atlantic right, humpback, fin, minke, and sei whales), six
are classified as mid-frequency cetaceans (i.e., killer and pilot
whales and bottlenose, common, Risso's, and Atlantic white-sided
dolphins), and one is classified as a high-frequency cetacean (i.e.,
harbor porpoise) (Southall et al., 2007).
Potential Effects of the Specified Activity on Marine Mammals
With respect to the MMPA, NMFS' effects assessment serves four
primary purposes: (1) To prescribe the permissible methods of taking
(i.e., Level B Harassment, including an identification of the number
and types of take that could occur by Level B harassment) and to
prescribe other means of effecting the least practicable adverse impact
on such species or stock and its habitat (i.e., mitigation); (2) to
determine whether the specified activity will have a negligible impact
on the affected species or stocks of marine mammals (based on the
likelihood that the activity will adversely affect the species or stock
through effects on annual rates of recruitment or survival); (3) to
determine whether the specified activity will have an unmitigable
adverse impact on the availability of the species or stock(s) for
subsistence uses (however, there are no subsistence communities that
would be affected in the Massachusetts Bay area, so this determination
is inapplicable for this rulemaking); and (4) to prescribe requirements
pertaining to monitoring and reporting.
Potential effects of Neptune's proposed port operations and
maintenance/repair activities would most likely be acoustic in nature.
LNG port operations and maintenance/repair activities introduce sound
into the marine environment. Potential acoustic effects on marine
mammals relate to sound produced by thrusters during maneuvering of the
SRVs while docking and undocking, occasional weathervaning at the port,
and during thruster use of DP maintenance vessels should a major repair
be necessary. The potential effects of sound from the activities
associated with the Neptune Port might include one or more of the
following: tolerance; masking of natural sounds; behavioral
disturbance; non-auditory physical effects; and, at least in theory,
temporary or permanent hearing impairment (Richardson et al., 1995).
However, for reasons discussed in the proposed rule, it is unlikely
that there would be any cases of temporary, or especially permanent,
hearing impairment resulting from these activities.
In the ``Potential Effects of Specified Activities on Marine
Mammals'' section of the proposed rule, NMFS included a qualitative
discussion of the different ways that port operations and repair and
maintenance activities may potentially affect marine mammals. Marine
mammals may experience masking and behavioral disturbance. The
information contained in the ``Potential Effects of Specified
Activities on Marine Mammals'' section from the proposed rule has not
changed. Please refer to the proposed rule for the full discussion (75
FR 80260, December 21, 2010).
[[Page 34160]]
Anticipated Effects on Habitat
The primary potential impacts to marine mammals and other marine
species are associated with elevated sound levels produced by the Port
operations and maintenance/repair activities. However, other potential
impacts from physical disturbance are also possible. Major repairs to
the Neptune port and pipeline may affect marine mammal habitat in
several ways: cause disturbance of the seafloor; increase turbidity
slightly; and generate additional underwater sound in the area. These
underwater sound levels will cause some species to temporarily disperse
from or avoid repair areas, but they are expected to return shortly
after the repair is completed. Operation of the Port will result in
long-term, continued disturbance of the seafloor, regular withdrawal of
seawater, and generation of underwater sound. The proposed rule
contained a full discussion of the potential impacts to marine mammal
habitat and prey species in the project area. No changes have been made
to that discussion. Please refer to the proposed rule for the full
discussion of potential impacts to marine mammal habitat (75 FR 80260,
December 21, 2010). NMFS has determined that Neptune's proposed port
operations and maintenance/repair activities are not expected to have
any habitat-related effects that could cause significant or long-term
consequences for individual marine mammals or on the food sources that
they utilize.
Mitigation
In order to issue an incidental take authorization (ITA) under
section 101(a)(5)(A) of the MMPA, NMFS must, where applicable, set
forth the permissible methods of taking pursuant to such activity, and
other means of effecting the least practicable adverse impact on such
species or stock and its habitat, paying particular attention to
rookeries, mating grounds, and areas of similar significance, and on
the availability of such species or stock for taking for certain
subsistence uses (where relevant).
Neptune proposed several mitigation measures in the application
(see ADDRESSES). After a review of these measures, NMFS determined that
some additional measures should also be implemented in order to effect
the least practicable adverse impact on the species or stock and its
habitat. Both sets of measures are discussed next.
Mitigation Measures in Neptune's Application
Neptune submitted a ``Marine Mammal Detection, Monitoring, and
Response Plan for the Operations Phase'' (the Plan) as part of its MMPA
application (Appendix D of the application; see ADDRESSES). The
measures, which include safety zones and vessel speed reductions, are
fully described in the Plan and summarized here. Some slight changes
have been made in this final rule (from what appears in the Plan) based
on public comments or for clarification purposes. An explanation of the
changes is contained in the ``Comments and Responses'' section found
later in this document.
The 500-yd (457 m) safety zone for North Atlantic right whales is
based on the approach regulation found at 50 CFR 224.103. The 100 yd
(91 m) safety zone for other marine mammal species was taken from
measures included in the 2007 Biological Opinion completed by NMFS'
Northeast Regional Office. Any maintenance and/or repairs needed shall
be scheduled in advance during the May 1 to November 30 seasonal
window, whenever possible, so that disturbance to North Atlantic right
whales will be largely avoided. If the repair cannot be scheduled
during this time frame, additional mitigation measures are required in
these regulations and described in part (2) of this section.
(1) Mitigation Measures for Major Repairs (May 1 to November 30)
(A) During repairs, if a marine mammal is detected within 0.6 mi (1
km) of the repair vessel (or acoustically), the vessel superintendent
or on-deck supervisor will be notified immediately. The vessel's crew
will be put on a heightened state of alert. The marine mammal will be
monitored constantly to determine if it is moving toward the repair
area.
(B) Repair vessels will cease any movement in the area if a marine
mammal other than a right whale is sighted within or approaching to a
distance of 100 yd (91 m) from the operating repair vessel. Repair
vessels will cease any movement in the area if a right whale is sighted
within or approaching to a distance of 500 yd (457 m) from the
operating vessel. Vessels transiting the repair area, such as pipe haul
barge tugs, will also be required to maintain these separation
distances.
(C) Repair vessels will cease all sound emitting activities if a
marine mammal other than a right whale is sighted within or approaching
to a distance of 100 yd (91 m) or if a right whale is sighted within or
approaching to a distance of 500 yd (457 m), from the operating repair
vessel. The back-calculated source level, based on the most
conservative cylindrical model of acoustic energy spreading, is
estimated to be 139 dB re 1 [mu]Pa.
(D) Repair activities may resume after the marine mammal is
positively reconfirmed outside the established zones (either 500 yd
(457 m) or 100 yd (91 m), depending upon species) or if the marine
mammal has not been re-sighted in the established zones for 30 minutes.
(E) While under way, all repair vessels will remain 500 yd (457 m)
away from right whales and 100 yd (91 m) away from all other marine
mammals, unless constrained by human safety concerns or navigational
constraints.
(F) All repair vessels 300 gross tons or greater will maintain a
speed of 10 knots (18.5 km/hr) or less. Vessels less than 300 gross
tons carrying supplies or crew between the shore and the repair site
will contact the Mandatory Ship Reporting System, the USCG, or the
protected species observers (PSOs) at the repair site before leaving
shore for reports of recent right whale sightings or active Dynamic
Management Areas (DMAs) and, consistent with navigation safety,
restrict speeds to 10 knots (18.5 km/hr) or less within 5 mi (8 km) of
any recent sighting location and within any existing DMA.
(G) Vessels transiting through the Cape Cod Canal and Cape Cod Bay
(CCB) between January 1 and May 15 will reduce speeds to 10 knots (18.5
km/hr) or less, follow the recommended routes charted by NOAA to reduce
interactions between right whales and shipping traffic, and avoid
aggregations of right whales in the eastern portion of CCB.
(2) Additional Port and Pipeline Major Repair Measures (December 1 to
April 30)
If unplanned/emergency repair activities cannot be conducted
between May 1 and November 30, Neptune is required to implement the
following additional mitigation measures:
(A) If on-board PSOs do not have at least 0.6-mi (1-km) visibility,
they shall call for a shutdown of repair activities. If dive operations
are in progress, then they shall be halted and divers brought on board
until visibility is adequate to see a 0.6-mi (1-km) range. At the time
of shutdown, the use of thrusters must be minimized to the lowest level
needed to maintain personnel safety. If there are potential safety
problems due to the shutdown, the captain will decide what operations
can safely be shut down and will document such activities in the data
log.
(B) Prior to leaving the dock to begin transit, the barge will
contact one of the
[[Page 34161]]
PSOs on watch to receive an update of sightings within the visual
observation area (within 0.6 mi (1 km) of the Port). If the PSO has
observed a North Atlantic right whale within 30 minutes of the transit
start, the vessel will hold for 30 minutes and again seek clearance to
leave from the PSOs on board. PSOs will assess whale activity and
visual observation ability at the time of the transit request to clear
the barge for release and will grant clearance if no North Atlantic
right whales have been sighted in the last 30 minutes in the visual
observation area. [Similar requirements from the acoustic monitoring
system is required and discussed part (4) of this subsection.]
(C) Neptune or its contractor shall provide a half-day training
course to designated crew members assigned to the transit barges and
other support vessels who will have responsibilities for watching for
marine mammals. This course shall cover topics including, but not
limited to, descriptions of the marine mammals found in the area,
mitigation and monitoring requirements contained in the LOA, sighting
log requirements, and procedures for reporting injured or dead marine
mammals. These designated crew members will be required to keep watch
on the bridge and immediately notify the navigator of any whale
sightings. All watch crew members will sign into a bridge log book upon
the start and end of watch. Transit route, destination, sea conditions,
and any protected species sightings/mitigation actions during watch
will be recorded in the log book. Any whale sightings within 3,281 ft
(1,000 m) of the vessel will result in a high alert and slow speed of 4
knots (7.4 km/hr) or less. A sighting within 2,461 ft (750 m) will
result in idle speed and/or ceasing all movement.
(D) The material barges and tugs used for repair work shall transit
from the operations dock to the work sites during daylight hours, when
possible, provided the safety of the vessels is not compromised. Should
transit at night be required, the maximum speed of the tug will be 5
knots (9.3 km/hr).
(E) Consistent with navigation safety, all repair vessels must
maintain a speed of 10 knots (18.5 km/hr) or less during daylight
hours. All vessels will operate at 5 knots (9.3 km/hr) or less at all
times within 3.1 mi (5 km) of the repair area.
(3) Speed Restrictions in Seasonal Management Areas (SMAs)
Repair vessels and SRVs will transit at 10 knots (18.5 km/hr) or
less in the following seasons and areas, which either correspond to or
are more restrictive than the times and areas in NMFS' regulations at
50 CFR 224.105 that implement speed restrictions to reduce the
likelihood and severity of ship strikes of right whales:
CCB SMA from January 1 through May 15, which includes all
waters in CCB, extending to all shorelines of the Bay, with a northern
boundary of 42[deg] 12' N. latitude;
Off Race Point SMA year round, which is bounded by
straight lines connecting the following coordinates in the order
stated: 42[deg]30' N. 69[deg]45' W.; thence to 42[deg]30' N. 70[deg]30'
W.; thence to 42[deg]12' N. 70[deg]30' W.; thence to 42[deg]12' N.
70[deg]12' W.; thence to 42[deg]04'56.5'' N. 70[deg]12' W.; thence
along mean high water line and inshore limits of COLREGS limit to a
latitude of 41[deg]40' N.; thence due east to 41[deg]41' N. 69[deg]45'
W.; thence back to starting point; and
Great South Channel (GSC) SMA from April 1 through July
31, which is bounded by straight lines connecting the following
coordinates in the order stated:
42[deg]30' N. 69[deg]45' W.
41[deg]40' N. 69[deg]45' W.
41[deg]00' N. 69[deg]05' W.
42[deg]09' N. 67[deg]08'24'' W.
42[deg]30' N. 67[deg]27' W.
42[deg]30' N. 69[deg]45' W.
(4) Additional Mitigation Measures
(A) When approaching and departing from the Neptune Port, SRVs
shall use the Boston Traffic Separation Scheme (TSS) starting and
ending at the entrance to the GSC. Upon entering the TSS, the SRV shall
go into a ``heightened awareness'' mode of operation, which is outlined
in great detail in the Plan (see Neptune's application).
(B) In the event that a whale is visually observed within 0.6 mi (1
km) of the Port or a confirmed acoustic detection is reported on either
of the two auto-detection buoys (ABs; more information on the acoustic
devices is contained in the ``Monitoring and Reporting'' section later
in this document) closest to the Port, departing SRVs shall delay their
departure from the Port, unless extraordinary circumstances, defined in
the Plan, require that the departure is not delayed. The departure
delay shall continue until either the observed whale has been visually
(during daylight hours) confirmed as more than 0.6 mi (1 km) from the
Port or 30 minutes have passed without another confirmed detection
either acoustically within the acoustic detection range of the two ABs
closest to the Port or visually within 0.6 mi (1 km) from Neptune.
(C) SRVs that are approaching or departing from the Port and are
within the Area to be Avoided (ATBA) surrounding Neptune shall remain
at least 0.6 mi (1 km) away from any visually detected right whales and
at least 100 yd (91 m) away from all other visually detected whales
unless extraordinary circumstances, as defined in Section 1.2 of the
Plan in Neptune's application, require that the vessel stay its course.
The ATBA is defined in 33 CFR 150.940. It is the largest area of the
Port marked on nautical charts, and it is enforceable by the USCG in
accordance with the 33 CFR 150.900 regulations. The Vessel Master shall
designate at least one lookout to be exclusively and continuously
monitoring for the presence of marine mammals at all times while the
SRV is approaching or departing Neptune.
(D) Neptune will ensure that other vessels providing support to
Neptune operations during regasification activities that are
approaching or departing from the Port and are within the ATBA shall be
operated so as to remain at least 0.6 mi (1 km) away from any visually
detected right whales and at least 100 yd (91 m) from all other
visually detected whales.
Additional Mitigation Measures Required by NMFS
In addition to the mitigation measures in Neptune's application,
NMFS has required the following measures in these regulations in order
to ensure the least practicable adverse impact on the affected species
or stocks:
(1) Neptune must immediately suspend any repair and maintenance or
operations activities if a dead or injured marine mammal is found in
the vicinity of the project area, and the death or injury of the animal
could be attributable to the LNG facility activities. Upon finding a
dead or injured marine mammal, Neptune must contact NMFS, the Northeast
Stranding and Disentanglement Program, and the USCG. NMFS will review
the documentation submitted by the PSO and attempt to attribute a cause
of death. Activities will not resume until review and approval has been
given by NMFS.
(2) PSOs will direct a moving vessel to slow to idle if a baleen
whale is seen less than 0.6 mi (1 km) from the vessel.
(3) Use of lights during repair or maintenance activities shall be
limited to areas where work is actually occurring, and all other lights
must be extinguished. Lights must be downshielded to illuminate the
deck and shall not intentionally illuminate surrounding waters, so as
not to attract whales or their prey to the area.
[[Page 34162]]
Mitigation Conclusions
NMFS has carefully evaluated the applicant's proposed mitigation
measures and considered a range of other measures in the context of
ensuring that NMFS prescribes the means of effecting the least
practicable adverse impact on the affected marine mammal species and
stocks and their habitat. Our evaluation of potential measures included
consideration of the following factors in relation to one another:
The manner in which, and the degree to which, the
successful implementation of the measure is expected to minimize
adverse impacts to marine mammals;
The proven or likely efficacy of the specific measure to
minimize adverse impacts as planned; and
The practicability of the measure for applicant
implementation.
Based on our evaluation of the applicant's proposed measures, as
well as other measures considered by NMFS or recommended by the public,
NMFS has determined that the mitigation measures described above,
including the adaptive management component (see the ``Adaptive
Management'' section later in this document), provide the means of
effecting the least practicable adverse impact on marine mammal species
or stocks and their habitat, paying particular attention to rookeries,
mating grounds, and areas of similar significance.
Monitoring and Reporting
In order to issue an ITA for an activity, section 101(a)(5)(A) of
the MMPA states that NMFS must, where applicable, set forth
``requirements pertaining to the monitoring and reporting of such
taking.'' The MMPA implementing regulations at 50 CFR 216.104(a)(13)
indicate that requests for ITAs must include the suggested means of
accomplishing the necessary monitoring and reporting that will result
in increased knowledge of the species and of the level of taking or
impacts on populations of marine mammals that are expected to be
present in the action area.
Neptune proposed both visual and acoustic monitoring programs in
the Plan contained in the application. Summaries of those plans, as
well as the proposed reporting, are contained here.
Passive Acoustic Monitoring
Neptune LNG will deploy and maintain a passive acoustic detection
network along a portion of the TSS and in the vicinity of Neptune. This
network will consist of autonomous recording units (ARUs) and near-
real-time ABs. To develop, implement, collect, and analyze the acoustic
data obtained from deployment of the ARUs and ABs, as well as to
prepare reports and maintain the passive acoustic detection network,
Neptune LNG has engaged the Cornell University Bioacoustic Research
Program (BRP) in Ithaca, New York, and the Woods Hole Oceanographic
Institution (WHOI) in Woods Hole, Massachusetts.
During June 2008, an array of 19 passive seafloor ARUs was deployed
by BRP for Neptune. The layout of the array centered on the terminal
site and was used to monitor the noise environment in Massachusetts Bay
in the vicinity of Neptune during construction of the Port and
associated pipeline lateral. The ARUs were not designed to provide
real-time or near-real-time information about vocalizing whales.
Rather, archival noise data collected from the ARU array were used for
the purpose of understanding the seasonal occurrences and overall
distributions of whales (primarily North Atlantic right whales) within
approximately 11.5 mi (18.5 km) of the Neptune Port. Neptune LNG will
maintain these ARUs in the same configuration for a period of 5 years
during operation of the Neptune Port in order to monitor the actual
acoustic output of port operations and to alert NOAA to any
unanticipated effects of port operations, such as large scale
abandonment by marine mammals of the area. To further assist in
evaluations of Neptune's acoustic output, source levels associated with
DP of SRVs at the buoys will be estimated using empirical measurements
collected from the passive detection network. If it is determined that
this network is insufficient to collect the data, then source levels
shall be collected from a platform as close as practicable to thrusters
while in use.
In addition to the ARUs, Neptune LNG has deployed 10 ABs within the
Separation Zone of the TSS for the operational life of the Port. The
purpose of the AB array is to detect the presence of vocalizing North
Atlantic right whales. Each AB has an average detection range of 5.8 mi
(9.3 km) from the AB, although detection ranges will vary based on
ambient underwater conditions. The AB system will be the primary
detection mechanism that alerts the SRV Master to the occurrence of
right whales in the TSS and triggers heightened SRV awareness. The
configurations of the ARU array and AB network (see Figure 3 in the
Plan in Neptune's application) were based upon configurations developed
and recommended by NOAA personnel.
Each AB deployed in the TSS will continuously screen the low-
frequency acoustic environment (less than 1,000 Hz) for right whale
contact calls occurring within an approximately 5.8-mi (9.3-km) radius
from each buoy (the ABs' detection range) and rank detections on a
scale from 1 to 10. Each AB shall transmit up to 10 clips with ratings
6-10 in near-real-time via Iridium satellite link to the BRP server Web
site every 20 minutes during periods of heightened awareness (otherwise
AB detections are transmitted at a rate of 5 clips per 6 hours). This
20-minute transmission schedule was determined by consideration of a
combination of factors including the tendency of right whale calls to
occur in clusters (leading to a sampling logic of listening for other
calls rather than transmitting immediately upon detection of a possible
call) and the amount of battery power required to complete a satellite
transmission. Additional details on the protocol can be found in
Neptune's application.
Additional passive acoustic monitoring shall be required, on a
case-by-case basis, during both planned and emergency repair activities
in order to better detect right whales in the area of repair work and
to collect additional data on the noise levels produced during repair
and maintenance activities. Neptune shall work with NOAA (NMFS and
SBNMS) to evaluate when to install real-time passive acoustic detection
buoys to provide early warnings for potential occurrence of right
whales in the vicinity of the repair area. The number of passive
acoustic detection buoys installed around the activity site, if deemed
necessary, shall be commensurate with the type and spatial extent of
maintenance/repair work required but must be sufficient to detect
vocalizing right whales within the 120-dB impact zone. In addition,
Neptune shall provide NMFS with empirically measured source level data
for all sources of noise associated with LNG port maintenance and
repair activities. Measurements shall be carefully planned and
coordinated with noise-producing activities and shall be collected from
the passive detection network.
Visual Monitoring
(1) Maintenance and Repair Activities
During maintenance- and repair-related activities, Neptune LNG
shall employ qualified PSOs on each vessel that has a DP system. All
PSOs must
[[Page 34163]]
receive training and be approved in advance by NOAA after a review of
their qualifications. Qualifications for these PSOs shall include
direct field experience on a marine mammal observation vessel and/or
aerial surveys in the Atlantic Ocean/Gulf of Mexico. Two PSOs are on-
duty at all times. Each vessel typically has four PSOs on-board at all
times. The PSOs (one primary and one secondary) are responsible for
visually locating marine mammals at the ocean's surface and, to the
extent possible, identifying the species. The primary PSO shall act as
the identification specialist, and the secondary PSO will serve as data
recorder and will assist with identification. Both PSOs shall have
responsibility for monitoring for the presence of marine mammals.
The PSOs shall monitor the area where maintenance and repair work
is conducted using the naked eye, hand-held binoculars, and/or power
binoculars (e.g, Big Eyes). Two PSOs are on-duty 24 hours/day and
switch between primary and secondary duties (as described in the
previous paragraph) about every 40-60 minutes. During nighttime
watches, PSOs are equipped with night vision devices. All sightings
must be recorded on marine mammal field sighting logs.
(2) Operations
While an SRV is navigating within the designated TSS, three people
have lookout duties on or near the bridge of the ship including the SRV
Master, the Officer-of-the-Watch, and the Helmsman on watch. In
addition to standard watch procedures, while the SRV is within the ATBA
and/or while actively engaging in the use of thrusters, an additional
lookout shall be designated to exclusively and continuously monitor for
marine mammals. Once the SRV is moored and regasification activities
have begun, the vessel is no longer considered to be in ``heightened
awareness'' status. However, when regasification activities conclude
and the SRV prepares to depart from Neptune, the Master shall once
again ensure that the responsibilities as defined in the Plan are
carried out. All sightings of marine mammals by the designated lookout,
individuals posted to navigational lookout duties, and/or any other
crew member while the SRV is within the TSS, in transit to the ATBA,
within the ATBA, and/or when actively engaging in the use of thrusters
shall be immediately reported to the Officer-of-the-Watch who shall
then alert the Master.
Reporting Measures
Since the Neptune Port is within the Mandatory Ship Reporting Area
(MSRA), all SRVs transiting to and from Neptune shall report their
activities to the mandatory reporting section of the USCG to remain
apprised of North Atlantic right whale movements within the area. All
vessels entering and exiting the MSRA shall report their activities to
WHALESNORTH. Vessel operators shall contact the USCG by standard
procedures promulgated through the Notice to Mariner system.
For major repair work associated with the pipeline lateral or other
port components, Neptune LNG shall notify the appropriate NOAA
personnel as soon as practicable after it is determined that repair
work must be conducted. During maintenance and repair of the pipeline
lateral or other port components, weekly status reports must be
provided to NOAA. The weekly report must include data collected for
each distinct marine mammal species observed in the project area during
the period of the repair activity. The weekly reports shall include the
following:
The location, time, and nature of the pipeline lateral
repair activities;
Whether the DP system was operated and, if so, the number
of thrusters used and the time and duration of DP operation;
Marine mammals observed in the area (number, species, age
group, and initial behavior);
The distance of observed marine mammals from the repair
activities;
Observed marine mammal behaviors during the sighting;
Whether any mitigation measures were implemented;
Weather conditions (sea state, wind speed, wind direction,
ambient temperature, precipitation, and percent cloud cover, etc.);
Condition of the marine mammal observation (visibility and
glare); and
Details of passive acoustic detections and any action
taken in response to those detections.
For minor repairs and maintenance activities, the following
protocols will be followed:
All vessel crew members will be trained in marine mammal
identification and avoidance procedures;
Repair vessels will notify designated NOAA personnel when
and where the repair/maintenance work is to take place along with a
tentative schedule and description of the work, as soon as practicable
after it is determined that repair work must be conducted;
Vessel crews will record/document any marine mammal
sighting(s) during the work period; and
At the conclusion of the repair/maintenance work, a report
will be delivered to designated NOAA personnel describing any marine
mammal sightings, the type of work taking place when the sighting
occurred, and any avoidance actions taken during the repair/maintenance
work.
During all phases of project repair/maintenance activities and
operation, sightings of any injured or dead marine mammals will be
reported immediately to the USCG, NMFS, and the Northeast Stranding and
Disentanglement Program, regardless of whether the injury or death is
caused by project activities. Sightings of injured or dead marine
mammals not associated with project activities can be reported to the
USCG on VHF Channel 16 or to NMFS Stranding and Entanglement Hotline.
In addition, if the injury or death was caused by a project vessel
(e.g., SRV, support vessel, or repair/maintenance vessel), USCG must be
notified immediately, and a full report must be provided to NMFS,
Northeast Regional Office, and NMFS, Office of Protected Resources. The
report must include the following information: (1) The time, date, and
location (latitude/longitude) of the incident; (2) the name and type of
vessel involved; (3) the vessel's speed during the incident; (4) a
description of the incident; (5) water depth; (6) environmental
conditions (e.g., wind speed and direction, sea state, cloud cover, and
visibility); (7) the species identification or description of the
animal; (8) the fate of the animal; and (9) photographs or video
footage of the animal (if equipment is available). Activities will not
resume until review and approval has been given by NMFS.
An annual report on marine mammal monitoring and mitigation will be
submitted to NMFS, Office of Protected Resources, and NMFS, Northeast
Regional Office, on August 1 of each year. The annual report shall
cover the time period of January 1 through December 31 of the previous
year for each year of activity. The weekly and annual reports shall
include data collected for each distinct marine mammal species observed
in the project area in Massachusetts Bay during the period of LNG
facility operations and repair/maintenance activities. The annual
report shall also include a description of marine mammal behavior,
overall numbers of individuals observed, frequency of observation, and
any behavioral changes and the context of the changes relative to
operation and repair/maintenance
[[Page 34164]]
activities. Additional information that will be recorded by Neptune or
its contractors during operation and repair/maintenance activities and
contained in the reports include: results of empirical source level
estimation for thrusters while in use and activities associated with
maintenance and repair events, date and time of marine mammal
detections (visually or acoustically), weather conditions, species
identification, approximate distance from the source, activity of the
vessel or at the repair site when a marine mammal is sighted, and
whether thrusters were in use and, if so, how many at the time of the
sighting.
In addition to annual reports, Neptune must submit a draft
comprehensive final report to NMFS, Office of Protected Resources, and
NMFS, Northeast Regional Office, 180 days prior to the expiration of
these regulations. This comprehensive technical report shall provide
full documentation of methods, results, and interpretation of all
monitoring during the first 4.5 years of the LOA. A revised final
comprehensive technical report, including all monitoring results during
the entire period of the LOAs will be due 90 days after the end of the
period of effectiveness of the regulations.
General Conclusions Drawn From Previous Monitoring Reports
Throughout the construction period (July 2008-November 2009 with
work stoppages during peak right whale season), Neptune submitted
weekly reports on marine mammal sightings in the area. While it is
difficult to draw biological conclusions from these reports, NMFS can
make some general conclusions. Data gathered by PSOs is generally
useful to indicate the presence or absence of marine mammals (often to
a species level) within the safety zones (and sometimes without) and to
document the implementation of mitigation measures. Though it is by no
means conclusory, it is worth noting that no instances of obvious
behavioral disturbance as a result of Neptune's activities were
observed by the PSOs. Of course, these observations only cover the
animals that were at the surface and within the distance that the PSOs
could see. Neptune has not yet conducted any repair or maintenance
activities at the Port.
As described previously in this document, Neptune was required to
maintain an acoustic array to monitor calling North Atlantic right
whales (humpback and fin whale calls were also able to be detected).
The ARUs log continuous acoustic data for up to 110 days per each
deployment. At the end of each ARU recording cycle, the 19 units are
recovered by BRP personnel. The data are analyzed based on seven
objectives, which are as follows: (1) Determine daily presence of fin
whale sounds; (2) determine daily presence of humpback whale sounds;
(3) determine hourly presence of right whale sounds; (4) estimate
locations and numbers of vocalizing right whales in the monitoring area
each day; (5) estimate sound exposure for each locatable vocalizing
whale; (6) assess noise conditions; and (7) improve analysis software
applications.
Cornell BRP analyzed the data and submitted a report covering the
initial construction phase of the project, which occurred in 2008.
While acoustic data can only be collected if the animals are actively
calling, the report indicates that humpback and fin whales were heard
calling on at least some of the ARUs on all construction days, and
right whale calls were heard only 28 percent of the time during active
construction days. Background noise analysis revealed definite
increases in acoustic noise in association with the different types of
construction activities with increases highest in the right whale band
and next highest in the humpback band. The report asserted that the
influence of construction activities on the acoustic habitat that was
monitored could not be adequately evaluated by simply counting the
number of detected whales exposed to a received noise level above 120
dB.
The September 2010 ARU quarterly passive acoustic monitoring status
report indicates that only a small portion of the 2010 data have been
analyzed to date. The final Marine Mammal Acoustic Monitoring and
Analysis for the Operation of the Neptune Liquefied Natural Gas
Terminal: 1 January-31 December 2010 will be submitted to NOAA, USGC,
and MARAD by July 31, 2011.
The AB network has been deployed and operational in the Boston TSS
since January 2010. Acoustic data from these buoys are sent to the BRP
Cornell lab in near-real-time for analysis for the presence of North
Atlantic right whales in the monitoring area. Positive North Atlantic
right whale detections are relayed to SRVs during transit through the
shipping lanes. The cycle of data analysis and information submission
is a 24 hrs/day, 7 days/week operation when SRVs are in the monitoring
area. To date, Cornell has prepared and submitted two reports for the
AB system for 2010: January-June time period and July-September time
period.
There are two monitoring conditions that dictate the tasks
performed by analysts at BRP: ``normal'' monitoring conditions and
``heightened watch'' monitoring conditions. During ``normal''
monitoring conditions (i.e., no SRVs are present in the monitoring
area), analysts at BRP monitor and report on North Atlantic right whale
activity twice a day. During ``heightened watch'' monitoring conditions
(i.e., when a SRV is 24 hours from the TSS AB coverage area, traveling
through the Boston Shipping Lanes or transiting to the Neptune Port
from the Boston Shipping Lanes) analysts at BRP monitor and report on
North Atlantic right whale acoustic activity in near-real-time. Table 1
in this document outlines the detections and data that were recorded on
the ABs from January-September 2010. The highest number of detections
was recorded in March and the lowest number recorded in June. During
the period January-September 2010, there were two SRV visits to the
Port. This resulted in ``heightened watch'' monitoring conditions of
the AB array for 2 days in February, 2 days in March, 7 days in April,
1 day in May, 1 day in July, and 7 days in August. The passive acoustic
arrays will remain deployed during the effective period of these
regulations in order to obtain information during the operational phase
of the Port facility.
Table 1--Information on North Atlantic Right Whale Call Data Collected From the AB Array Deployed Near the Neptune Port From January Through September
2010
--------------------------------------------------------------------------------------------------------------------------------------------------------
January February March April May June July August September
--------------------------------------------------------------------------------------------------------------------------------------------------------
Number of ABs with a detection.............. 8 10 10 10 10 5 8 8 8
Total number of detections for all ABs...... 328 573 3,874 2,786 1,538 34 64 112 189
Highest number of detections on a single day 58 103 1,059 255 186 8 26 35 43
(Jan. 14) (Feb. 25) (Mar. 25) (Apr. 24) (May 1) (Jun. 15) (Jul. 3) (Aug. 14) (Sep. 18)
Number of days with no recorded detections.. 5 2 0 0 1 14 16 9 11
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 34165]]
Adaptive Management
NMFS has included an adaptive management component in the
regulations governing the take of marine mammals incidental to
operation and repair/maintenance activities at the Neptune Port. In
accordance with 50 CFR 216.105(c), regulations for the proposed
activity must be based on the best available information. As new
information is developed, through monitoring, reporting, or research,
the regulations may be modified, in whole or in part, after notice and
opportunity for public review and comment. The use of adaptive
management will allow NMFS to consider new information from different
sources to determine if mitigation or monitoring measures should be
modified (including additions or deletions) if new data suggest that
such modifications are appropriate for subsequent LOAs.
The following are some of the possible sources of applicable data:
Results from Neptune's monitoring from the previous year;
Results from general marine mammal and sound research; or
Any information which reveals that marine mammals may have
been taken in a manner, extent or number not authorized by these
regulations or subsequent LOAs.
If, during the effective period of the regulations, new information
is presented from monitoring, reporting, or research, these regulations
may be modified, in whole, or in part after notice and opportunity for
public review and comment, as allowed for in 50 CFR 216.105(c). In
addition, LOAs shall be withdrawn or suspended if, after notice and
opportunity for public comment, the Assistant Administrator finds,
among other things, that the regulations are not being substantially
complied with or the taking allowed is having more than a negligible
impact on the species or stock, as allowed for in 50 CFR 216.106(e).
That is, should substantial changes in marine mammal populations in the
project area occur or monitoring and reporting show that the Port
operations are having more than a negligible impact on marine mammals,
then NMFS reserves the right to modify the regulations and/or withdraw
or suspend LOAs after public review and comment.
Comments and Responses
On December 21, 2010 (75 FR 80260), NMFS published a proposed rule
in response to Neptune's request to take marine mammals incidental to
port commissioning and operations, including maintenance and repair
activities, at its Deepwater Port in Massachusetts Bay and requested
comments, information, and suggestions concerning the request. During
the 45-day public comment period, NMFS received comments from two
private individuals and the Marine Mammal Commission (MMC). NMFS has
responded to these comments here.
Comment 1: One of the private citizen letters noted the continual
harassment and stress sustained by marine mammals from human
activities, and, therefore, urged that the regulations be denied.
Response: NMFS considered the potential for harassment from these
activities in its impacts analysis in the proposed rule (75 FR 80260,
December 21, 2010). Authorization for incidental takings shall be
granted if NMFS finds that the taking will have a negligible impact on
the species or stock(s), will not have an unmitigable adverse impact on
the availability of the species or stock(s) for subsistence uses (where
relevant), and if the permissible methods of taking and requirements
pertaining to the mitigation, monitoring and reporting of such takings
are set forth. Based on the assessment in the proposed rule and
contained later in this document, NMFS determined that the level of
harassment from these activities would take only small numbers of
marine mammals and would not have more than a negligible impact on the
affected species or stocks. There are no relevant subsistence uses of
marine mammals implicated by this action. Therefore, NMFS has
determined that the total taking of affected species or stocks would
not have an unmitigable adverse impact on the availability of such
species or stocks for taking for subsistence purposes. The permissible
methods of taking and the required mitigation, monitoring, and
reporting measures are laid out in this final rule.
Comment 2: The second private citizen letter expressed
contradicting points of view. It stated on the one hand that NMFS
should not stop LNG operations, as it would force increased prices for
the public. However, the letter also stated that NMFS should take
positive steps to protect marine mammals.
Response: NMFS is not the agency with regulatory authority over
offshore deepwater LNG ports. That authority falls to the USCG and
MARAD. Therefore, those are the agencies that either allow or deny LNG
port construction and operation. NMFS authorizes the take of marine
mammals incidental to a specified activity if certain findings are
made. Those findings are described in the ``Background'' section found
earlier in this document. The final rule and associated LOA contain
mitigation and monitoring measures to ensure the least practicable
adverse impact on marine mammal species and stocks in the Port area.
Comment 3: The MMC expressed three concerns with the information in
the proposed rule as to the derivation of take estimates. First, the
MMC expressed concern about the 120-dB zones that were used as they
were smaller than those derived from in-situ measurements and
incorporated into models in appendices in Neptune's application. This
resulted in an underestimation of the zones of exposure. Second, the
hypothetical strip width that was used by NMFS was much smaller than
the strip width used during the surveys, thus producing overestimates
of marine mammal densities in the area. Lastly, NMFS only estimated
take from repair and maintenance activities and DP but not
weathervaning.
The MMC is concerned that the presence of these errors and
omissions in the proposed rule may have compromised the public's
opportunity to comment meaningfully on the proposed authorization.
Without seeing the new analyses, it is difficult to know whether the
final rule will differ significantly enough from the proposed rule that
an additional opportunity for public review and comment should be
provided. Therefore, the MMC recommends that NMFS allow for an
additional opportunity for public review and comment before publication
of a final rule if the recalculated takes or zones in which takes might
occur are significantly greater than those described in the proposed
rule. If NMFS determines that additional notice and opportunity to
comment are not needed, the MMC recommends that NMFS ensure that the
revised estimates of the zones of exposure and anticipated takes for
each of the three proposed activities are provided in the final rule,
together with the rationale for not providing an additional opportunity
for public review and comment.
Response: NMFS has revised the take estimates in this final rule
from those contained in the proposed rule. A summary of the revisions
is provided here, and more details can be found in the ``Estimated Take
by Incidental Harassment'' section found later in this document.
As noted by the MMC, NMFS inadvertently did not estimate takes from
weathervaning in the proposed rule. Takes from this activity (in
[[Page 34166]]
addition to DP use and repair/maintenance activities) have now been
calculated and added to the total annual take estimate for each
species. NMFS estimated that Neptune would require up to 8 days/year to
conduct weathervaning to maintain position at the Port. This is based
on information contained in their application and associated
appendices. Including this activity only added a very small number of
individuals of each species to the overall take totals for each
species.
In December 2009, LGL Limited completed a Second Supplementary
Biological Effects Report titled Assessment of the Effects of
Underwater Noise from Thrusters to be Used on the Neptune LNG Project
(LGL, 2009). This report incorporated measurements of the SRVs
conducted by Samsung and new transmission loss modeling by JASCO
Applied Sciences. This report pres