Draft 2018 Marine Mammal Stock Assessment Reports, 47131-47135 [2018-20185]
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Federal Register / Vol. 83, No. 181 / Tuesday, September 18, 2018 / Notices
For further information, contact Diane
Finver at Diane.Finver@trade.gov or
(202) 482–1367.
DEPARTMENT OF COMMERCE
Foreign-Trade Zones Board
Dated: September 12, 2018.
Andrew McGilvray,
Executive Secretary.
[B–57–2018]
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Foreign-Trade Zone (FTZ) 149—
Freeport, Texas; Notification of
Proposed Production Activity; DSM
Nutritional Products, LLC; (Vinylol)
Freeport, Texas
[FR Doc. 2018–20256 Filed 9–17–18; 8:45 am]
BILLING CODE 3510–DS–P
The Port of Freeport, grantee of FTZ
149, submitted a notification of
proposed production activity to the FTZ
Board on behalf of DSM Nutritional
Products, LLC (DSM) (formerly
Hoffmann-La Roche Inc.), located in
Freeport, Texas. The notification
conforming to the requirements of the
regulations of the FTZ Board (15 CFR
400.22) was received on September 11,
2018.
DSM already has authority to produce
beta carotene crystalline, C–25 aldehyde
and vinyl salt within Subzone 149B.
The current request would add a
finished product (vinylol-pure and
crude) to the scope of authority.
Pursuant to 15 CFR 400.14(b),
additional FTZ authority would be
limited to the specific finished product
described in the submitted notification
and subsequently authorized by the FTZ
Board.
Production under FTZ procedures
could exempt DSM from customs duty
payments on the foreign-status
materials/components in the existing
scope of authority used in export
production of vinylol-pure and crude.
On its domestic sales, for the foreignstatus materials/components in the
existing scope of authority (duty rates,
3.7% or 5.5%), DSM would be able to
choose the duty rate during customs
entry procedures that applies to vinylolpure and crude (duty rate 5.5%). DSM
would be able to avoid duty on foreignstatus components which become scrap/
waste. Customs duties also could
possibly be deferred or reduced on
foreign-status production equipment.
Public comment is invited from
interested parties. Submissions shall be
addressed to the Board’s Executive
Secretary at the address below. The
closing period for their receipt is
October 29, 2018.
A copy of the notification will be
available for public inspection at the
Office of the Executive Secretary,
Foreign-Trade Zones Board, Room
21013, U.S. Department of Commerce,
1401 Constitution Avenue NW,
Washington, DC 20230–0002, and in the
‘‘Reading Room’’ section of the Board’s
website, which is accessible via
www.trade.gov/ftz.
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XG300
Draft 2018 Marine Mammal Stock
Assessment Reports
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; request for comments
and correction.
AGENCY:
NMFS reviewed the Alaska,
Atlantic, and Pacific regional marine
mammal stock assessment reports
(SARs) in accordance with the Marine
Mammal Protection Act. SARs for
marine mammals in the Alaska,
Atlantic, and Pacific regions were
revised according to new information.
NMFS solicits public comments on the
draft 2018 SARs. NMFS also announces
the availability of revised Atlantic
Regional 2016 and 2017 SARs that
include technical corrections.
DATES: Comments must be received by
December 17, 2018.
ADDRESSES: The 2018 draft SARs are
available in electronic form via the
internet at https://www.fisheries.noaa.
gov/national/marine-mammalprotection/draft-marine-mammal-stockassessment-reports. The revised final
Atlantic Regional SAR for 2016 is
available at https://www.nefsc.noaa.gov/
publications/tm/tm241/and the revised
2017 SAR is available at https://
www.nefsc.noaa.gov/publications/tm/
tm245/.
Copies of the Alaska Regional SARs
may be requested from Marcia Muto,
Alaska Fisheries Science Center, NMFS,
7600 Sand Point Way NE, Seattle, WA
98115–6349.
Copies of the Atlantic, Gulf of Mexico,
and Caribbean Regional SARs may be
requested from Elizabeth Josephson,
Northeast Fisheries Science Center, 166
Water St., Woods Hole, MA 02543.
Copies of the Pacific Regional SARs
may be requested from Jim Carretta,
Southwest Fisheries Science Center,
8604 La Jolla Shores Drive, La Jolla, CA
92037–1508.
SUMMARY:
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You may submit comments, identified
by NOAA–NMFS–2018–0086, by either
of the following methods:
Federal e-Rulemaking Portal: Go to
www.regulations.gov/#!docketDetail;
D=NOAA-NMFS-2018-0086, click the
‘‘Comment Now!’’ icon, complete the
required fields, and enter or attach your
comments.
Mail: Send comments or requests for
copies of reports to: Chief, Marine
Mammal and Sea Turtle Conservation
Division, Office of Protected Resources,
National Marine Fisheries Service, 1315
East-West Highway, Silver Spring, MD
20910–3226, Attn: Stock Assessments.
Instructions: NMFS may not consider
comments if they are sent by any other
method, to any other address or
individual, or received after the end of
the comment period. All comments
received are a part of the public record
and will generally be posted for public
viewing on www.regulations.gov
without change. All personal identifying
information (e.g., name, address, etc.),
confidential business information, or
otherwise sensitive information
submitted voluntarily by the sender will
be publicly accessible. NMFS will
accept anonymous comments (enter
‘‘N/A’’ in the required fields if you wish
to remain anonymous).
FOR FURTHER INFORMATION CONTACT: Lisa
Lierheimer, Office of Protected
Resources, 301–427–8402,
Lisa.Lierheimer@noaa.gov; Marcia
Muto, 206–526–4026, Marcia.Muto@
noaa.gov, regarding Alaska regional
stock assessments; Elizabeth Josephson,
508–495–2362, Elizabeth.Josephson@
noaa.gov, regarding Atlantic, Gulf of
Mexico, and Caribbean regional stock
assessments; or Jim Carretta, 858–546–
7171, Jim.Carretta@noaa.gov, regarding
Pacific regional stock assessments.
SUPPLEMENTARY INFORMATION:
Background
Section 117 of the Marine Mammal
Protection Act (MMPA) (16 U.S.C. 1361
et seq.) requires NMFS and the U.S. Fish
and Wildlife Service (FWS) to prepare
stock assessments for each stock of
marine mammals occurring in waters
under the jurisdiction of the United
States, including the Exclusive
Economic Zone. These reports must
contain information regarding the
distribution and abundance of the stock,
population growth rates and trends,
estimates of annual human-caused
mortality and serious injury (M/SI) from
all sources, descriptions of the fisheries
with which the stock interacts, and the
status of the stock. Initial reports were
completed in 1995.
The MMPA requires NMFS and FWS
to review the SARs at least annually for
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strategic stocks and stocks for which
significant new information is available,
and at least once every three years for
non-strategic stocks. The term ‘‘strategic
stock’’ means a marine mammal stock:
(A) For which the level of direct humancaused mortality exceeds the potential
biological removal level or PBR (defined
by the MMPA as the maximum number
of animals, not including natural
mortalities, that may be removed from a
marine mammal stock while allowing
that stock to reach or maintain its
optimum sustainable population); (B)
which, based on the best available
scientific information, is declining and
is likely to be listed as a threatened
species under the Endangered Species
Act (ESA) within the foreseeable future;
or (C) which is listed as a threatened
species or endangered species under the
ESA. NMFS and the FWS are required
to revise a SAR if the status of the stock
has changed or can be more accurately
determined.
Prior to public review, the updated
SARs under NMFS’ jurisdiction are
peer-reviewed within NMFS Fisheries
Science Centers and by members of
three regional independent Scientific
Review Groups, which were established
under the MMPA to independently
advise NMFS on information and
uncertainties related to the status of
marine mammals.
The period covered by the 2018 draft
SARs is 2012–2016. NMFS reviewed the
status of marine mammal stocks as
required and revised a total of 47 reports
representing 76 stocks in the Alaska,
Atlantic, and Pacific regions to
incorporate new information. The 2018
revisions consist primarily of updated
or revised M/SI estimates and updated
abundance estimates. One stock (Alaska
bearded seal) changed in status from
non-strategic to strategic, and three
stocks (Gulf of Maine humpback whale,
and Western North Atlantic short-finned
and long-finned pilot whales) changed
in status from strategic to non-strategic.
Substantive revisions to the SARs are
discussed below. NMFS solicits public
comments on the draft 2018 SARs.
Alaska Reports
In 2018, NMFS reviewed all 45 stocks
in the Alaska region, and revised SARs
under NMFS jurisdiction for 18 stocks
(14 strategic and 4 non-strategic). The
Alaska bearded seal stock changed from
‘‘non-strategic’’ to ‘‘strategic’’ status
because the stock is now considered
depleted under the MMPA (see below).
A list of the 18 reports revised in 2018
for stocks in the Alaska region is
presented in Table 1. Information on the
remaining Alaska region stocks can be
found in the final 2017 reports (Muto et
al., 2018).
TABLE 1—LIST OF MARINE MAMMAL STOCKS IN THE ALASKA REGION REVISED IN 2018
Strategic stocks
•
•
•
•
•
•
•
•
•
•
•
•
•
•
Non-strategic stocks
Revisions to the Alaska SARs
included updates of abundance and/or
M/SI estimates, including revised
abundance estimates for Western U.S.
Steller sea lion; Eastern Pacific northern
fur seal; and Cook Inlet beluga whale.
Alaska Bearded Seal
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•
•
•
•
Steller sea lion, Western U.S.
northern fur seal, Eastern Pacific.
bearded seal, Alaska.
beluga whale, Cook Inlet.
killer whale, AT1 Transient.
harbor porpoise, Southeast Alaska.
harbor porpoise, Gulf of Alaska.
harbor porpoise, Bering Sea.
sperm whale, North Pacific.
humpback whale, Western North Pacific.
humpback whale, Central North Pacific.
fin whale, Northeast Pacific.
North Pacific right whale, Eastern North Pacific.
bowhead whale, Western Arctic.
In 2012, NMFS listed the Beringia
distinct population segment of bearded
seal, and thus the Alaska stock of
bearded seal, as threatened under the
ESA (77 FR 76740, December 28, 2012).
The primary concern for this population
is the ongoing and projected loss of seaice cover stemming from climate
change, which is expected to pose a
significant threat to the persistence of
these seals in the foreseeable future. In
2014, the U.S. District Court for the
District of Alaska issued a decision
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ribbon seal, Alaska.
Pacific white-sided dolphin, North Pacific.
Dall’s porpoise, Alaska.
Minke whale, Alaska.
vacating NMFS’ listing in a lawsuit that
challenged listing bearded seals under
the ESA (Alaska Oil and Gas
Association v. Pritzker, Case No. 4:13–
cv–00018–RPB). Consequently, it was
also no longer designated as ‘‘depleted’’
or classified as a strategic stock. In 2016,
the 9th Circuit Court of Appeals
overturned the decision and approved
the agency’s protection of the seals; and
in 2018, the U.S. Supreme Court
declined a challenge to NMFS’ listing
decision. Thus, because of its threatened
status under the ESA, this bearded seal
stock is considered depleted under the
Marine Mammal Protection Act andis
now classified as a ‘‘strategic’’ stock.
Atlantic Reports
In 2018, NMFS reviewed all 117
stocks in the Atlantic region (including
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the Atlantic Ocean, Gulf of Mexico, and
U.S. territories in the Caribbean) under
NMFS jurisdiction. This year, NMFS
revised 16 reports and created 2 new
common bottlenose dolphin reports
(West Bay and Terrebonne Bay/
Timbalier Bay). These updated reports
represent 42 stocks (26 strategic and 16
non-strategic). The Gulf of Maine
humpback whale stock and Western
North Atlantic (WNA) long-finned and
short-finned pilot whale stocks changed
from ‘‘strategic’’ to ‘‘non-strategic’’
status because the mean annual humancaused M/SI is below PBR (see below).
A list of the 42 stocks in the Atlantic
region (contained in 18 reports), is
presented in Table 2. Information on the
remaining Atlantic region stocks can be
found in the final 2017 reports (Hayes
et al., 2018).
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47133
TABLE 2—LIST OF MARINE MAMMAL STOCKS IN THE ATLANTIC REGION REVISED IN 2018
Strategic stocks
Non-strategic stocks
• North Atlantic right whale, Western Atlantic.
• fin whale, WNA.
• common bottlenose dolphin (24 stocks).*
Æ Laguna Madre.
Æ Neuces Bay/Corpus Christi Bay.
Æ Copano Bay/Aransas Bay/San Antonio Bay/Redfish Bay/Espiritu
Santo Bay.
Æ Matagorda Bay/Tres Palacios Bay/Lavaca Bay.
Æ Galveson Bay/East Bay/Trinity Bay.
Æ Sabine Lake.
Æ Calcasieu Lake.
Æ Vermilion Bay/West Cote Blanche Bay/Atchafalaya Bay.
Æ Mississippi River Delta.
Æ Mobile Bay/Bonsecour Bay.
Æ Perdido Bay.
Æ Pensacola Bay/East Bay.
Æ St. Andrew Bay.
Æ St. Vincent Sound/Apalachicola Bay/St. George Sound.
Æ Apalachee Bay.
Æ Waccassa Bay/Withlacoochee Bay/Crystal Bay.
Æ St. Joseph Sound/Clearwater Harbor.
Æ Tampa Bay.
Æ Pine Island Sound/Charlotte Harbor/Gasparilla Sound/Lemon
Bay.
Æ Caloosahatchee River.
Æ Estero Bay.
Æ Chokoloskee Bay/Ten Thousand Islands/Gullivan Bay.
Æ Whitewater Bay.
Æ Florida Keys (Bahia Honda to Key West).
•
•
•
•
•
•
humpback whale, Gulf of Maine.
minke whale, Canadian East Coast.
Risso’s dolphin, WNA.
pilot whale, long-finned, WNA.
pilot whale, short-finned, WNA.
Atlantic white-sided dolphin, WNA.
•
•
•
•
•
•
•
•
common dolphin, WNA offshore.
rough-toothed dolphin, WNA.
harbor porpoise, Gulf of Maine/Bay of Fundy.
harbor seal, WNA.
gray seal, WNA.
harp seal, WNA.
hooded seal, WNA.
common bottlenose dolphin (3 stocks).
Æ West Bay.
Æ Terrebonne Bay/Timbalier Bay.
Æ Sarasota Bay/Little Sarasota Bay.*
* Details for these 25 stocks are included in the report: Common bottlenose dolphin, Northern Gulf of Mexico Bay, Sound, and Estuary Stocks.
Revisions to the Atlantic SARs
included updates of abundance and/or
M/SI estimates. New abundance
estimates are available for the North
Atlantic right whale, Gulf of Maine
humpback whale, WNA short-finned
pilot whale, WNA rough-toothed
dolphin, and the West Bay and
Terrebonne Bay/Timbalier Bay common
bottlenose dolphin stocks.
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North Atlantic Right Whale, Western
Atlantic
Although PBR analyses in this 2018
SAR reflect data collected through 2016,
it should be noted that an additional 17
North Atlantic right whale mortalities
were observed in 2017 (Daoust et al.
2017). This number exceeds the largest
estimated mortality rate during the past
25 years. Further, despite the usual
extensive survey effort, only 5 and 0
new calves were detected in 2017 and
2018, respectively. Therefore, the
decline in the right whale population is
expected to continue for at least an
additional 2 years. The minimum
population size for the Western Atlantic
stock of the North Atlantic right whale
is 445 and PBR is 0.9.
Humpback Whale, Gulf of Maine
The updated abundance estimate for
the Gulf of Maine humpback whale
stock is 896, based on a recent count of
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the minimum number alive (MNA). The
2015 humpback whale MNA was
produced by counting the number of
unique individuals seen in 2015 in the
Gulf of Maine stock area as well as seen
both before and after 2015. The 2015
humpback whale MNA includes not
only cataloged whales but some calves
born in 2015 but not yet identifiable.
MNA is a rigorous accounting of
individuals and has no associated
coefficient of variation (CV). It is both
more recent and larger than the previous
2011 line transect estimate of 335 and
has zero probability of overestimating
abundance. Although the abundance
appears to increase from 2017 to 2018,
these estimates should not be compared
as they were derived using different
methodologies and data sets. As a result
of the higher abundance estimate, the
PBR for the Gulf of Maine humpback
whale stock increased from 3.7 to 14.6
whales. Based on a recovery factor of
0.5, the estimate of human-caused M/SI
is now below PBR; thus, the stock has
changed from ‘‘strategic’’ to ‘‘nonstrategic.’’
Long-Finned Pilot Whale, Western North
Atlantic
The PBR for the western North
Atlantic long-finned pilot whale is 35
and the estimate of total annual
observed average fishery-related of
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human-caused M/SI is 27. In bottom
trawls and mid-water trawls and in the
gillnet fisheries, mortalities were more
generally observed north of 40° N
latitude and in areas expected to have
only long-finned pilot whales. Takes in
these fisheries were therefore attributed
to the long-finned pilot whales. Takes in
the pelagic longline fishery were
partitioned according to a logistic
regression model (Garrison and Rosel
2017). Because the M/SI does not
exceed PBR, the stock has changed from
‘‘strategic’’ to ‘‘non-strategic.’’
Short-Finned Pilot Whale, Western
North Atlantic
The best available abundance estimate
for short-finned pilot whales, based on
shipboard surveys conducted during the
summer of 2016 in the western North
Atlantic, is 28,924. These most recent
surveys covered the full range of shortfinned pilot whales in U.S. Atlantic
waters. Because long-finned and shortfinned pilot whales are difficult to
distinguish at sea, sightings data are
reported as Globicephala sp. These
survey data have been combined with
an analysis of the spatial distribution of
the two pilot whale species based on
genetic analyses of biopsy samples to
derive separate abundance estimates for
each species. Due to changes in survey
methodology, previous abundance
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estimates should not be used to make
comparisons with more current
estimates. As a result of the higher
abundance estimate, the PBR for the
western North Atlantic short-finned
pilot whale increased from 159 to 236
and the estimate of total annual
observed average fishery-related of
human-caused M/SI is 27. The estimate
of human-caused M/SI is now below
PBR; thus, the stock has changed from
‘‘strategic’’ to ‘‘non-strategic.’’
Common Bottlenose Dolphins
NMFS is in the process of writing
individual stock assessment reports for
each of the 31 bay, sound, and estuary
stocks of common bottlenose dolphins
in the northern Gulf of Mexico. Two
new individual reports, for the West Bay
and Terrebonne-Timbalier Bay
Estuarine System stocks, were
completed for the draft 2018 SARs.
Therefore, the reader will not see
tracked changes in the draft 2018
reports for these stocks. To date, six
bottlenose dolphin stocks have
individual reports completed (West Bay,
Terrebonne-Timbalier Bay Estuarine
System, Barataria Bay Estuarine System,
Mississippi Sound/Lake Borgne/Bay
Boudreau, Choctawhatchee Bay, and St.
Joseph Bay), and the remaining 25
stocks are included in the Northern Gulf
of Mexico Bay, Sound, and Estuary
Stocks report.
Pacific Reports
In 2018, NMFS reviewed all 87 stocks
in the Pacific region (waters along the
west coast of the United States, within
waters surrounding the main and
Northwestern Hawaiian Islands, and
within waters surrounding U.S.
territories in the Western Pacific), and
revised SARs for 16 stocks (7 strategic
and 9 non-strategic). A list of the reports
revised in 2018, representing 16 stocks
in the Pacific region, is presented in
Table 3. Information on the remaining
Pacific region stocks can be found in the
final 2017 reports (Carretta et al., 2018).
TABLE 3—LIST OF MARINE MAMMAL STOCKS IN THE PACIFIC REGION REVISED IN 2018
Strategic stocks
•
•
•
•
•
•
Non-strategic stocks
New abundance estimates are
available for 8 stocks: California sea
lions, Hawaiian monk seals, Eastern
North Pacific Offshore killer whales,
Southern Resident killer whales, Eastern
North Pacific gray whales, Western
North Pacific gray whales, California/
Oregon/Washington humpback whales,
and Hawaii Island spinner dolphins.
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•
•
•
•
•
Hawaiian monk seal
killer whale, Eastern N Pacific Southern Resident
humpback whale, CA/OR/WA
blue whale, Eastern N Pacific
fin whale, CA/OR/WA
sei whale, Eastern N Pacific
New Methodology To Estimate Level of
Vessel Strike Mortality: CA/OR/WA
Humpback Whale, CA/OR/WA Fin
Whale, and the Eastern North Pacific
Blue Whales
New information on serious injury
and mortality resulting from estimated
vessel strikes based on an analysis by
Rockwood et al. (2017) is included for
the following stocks of large whales:
CA/OR/WA humpback whale, CA/OR/
WA fin whale, and the Eastern North
Pacific blue whales. Using the moderate
level of vessel avoidance, this model
estimated the following annual
mortality of these stocks of large whales
due to ship strikes as follows: 22
humpback whales (representing
approximately 0.7 percent of the
estimated population size of the stock);
43 fin whales (representing
approximately <0.5 percent of the
estimated population size of the stock);
and 18 blue whales (representing
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California sea lion.
killer whale, Eastern N Pacific Offshore.
gray whale, Eastern N Pacific.
gray whale, Western N Pacific.
spinner dolphin:
Æ Hawaii pelagic.
Æ Hawaii Island.
Æ O’ahu/4 Islands.
Æ Kaua’i/Ni’ihau.
Æ Kure/Midway.
Æ Pearl and Hermes Reef.
approximately 1 percent of the
estimated population size of the stock.
Based on this new methodology,
estimated levels of vessel strike
mortality exceed PBR for both Eastern
North Pacific blue and CA/OR/WA
humpback whale stocks, although
estimated vessel strike levels represent
a small fraction of the overall estimated
population sizes. Estimated vessel
strikes are also compared with recent
detected levels of vessel strikes, which
indicate that detection rates for vessel
strike events are quite low, ranging from
approximately 1 percent (for blue
whales) to 12 percent (for humpback
whales). There is uncertainty regarding
the estimated number of ship strike
deaths as carcass recovery rates are
quite low.
New Methodology To Assign Cases of
Entangled but Unidentified Whales to
Stock: CA/OR/WA Humpback Whale,
CA/OR/WA Fin Whale, Eastern North
Pacific Gray Whale, and Eastern North
Pacific Blue Whales
Unidentified whales represent
approximately 15 percent of
entanglement cases along the U.S. West
Coast. In previous stock assessments,
unidentified entanglements were not
assigned to stock. For large whale
stocks, including gray, humpback, blue,
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and fin whales, a new methodology
based on an assignment model
generated from historic known-species
entanglements in the region was used to
assign previous cases of unidentified
whale entanglements to species
(Carretta 2018). This has eliminated a
negative bias in assessments that occurs
when unidentified whale entanglements
are not assigned to any species/stock. In
the case of CA/OR/WA humpback
whales, observed levels of
entanglements and vessel strikes
combined exceed PBR.
New Methodology To Calculate the
Minimum Population Estimate (Nmin)
for California Sea Lion
The 2018 SAR for California sea lions
uses a different methodology for
estimating Nmin. The updated
minimum population size of the U.S.
stock is 233,515 (153,337 in 2014 SAR).
This resulted in an increase in PBR from
9,200 (in 2014) to 14,011. The updated
best abundance estimate available for
California sea lions, based on a 1975–
2014 time series of pup counts,
combined with mark-recapture
estimates of survival rates, is 257,606
sea lions (Laake et al., 2018) (down from
296,750 in 2014 SAR).
The previous approach to calculate
Nmin used two times the annual pup
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count, which resulted in negativelybiased Nmin values because not all age
classes are represented. The Guidelines
for preparing Stock Assessment Reports
(NMFS 2016) recommends defining
Nmin as the 20th percentile of a lognormal distribution based on an
estimate of the number of animals in a
stock (which is equivalent to the lower
limit of a 60% 2-tailed confidence
interval). The Guidelines allow for other
approaches to be used to estimate Nmin
if they provide an adequate level of
assurance that the stock size is equal to
or greater than that estimate. Laake et al.
(2018) did not provide a CV for the
estimated population size, so the
updated Nmin is based on the lower 95
percent confidence limit. The stock is
estimated to be approximately 40
percent above its maximum net
productivity level (MNPL = 183,481
animals), and it is therefore considered
within the range of its optimum
sustainable population. The carrying
capacity of the population was
estimated at 275,298 animals in 2014
(Laake et al. 2018). The total human
caused mortality is less than the PBR of
14,011.
Corrections to the 2016 and 2017 SARs
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Subsequent to announcing the
availability of the final 2016 (82 FR
29039, June 27, 2017) and 2017 (83 FR
32093, July 11, 2018) SARs, we were
made aware that the SARs contained
some technical errors. In the 2016 North
Atlantic right whale SAR, the PBR was
listed incorrectly as 1. The correct PBR
value for 2016 is 0.9. Similarly, in the
2017 North Atlantic right whale SAR,
PBR was listed as 1.4, but the correct
value is 0.9. In addition, the 2017 SAR
for the WNA Central Florida Coastal
Stock of common bottlenose dolphins
contained a technical error. In the
‘‘Population Size’’ section, the name of
the stock was incorrectly listed as the
‘‘Northern’’ Florida Coastal Stock
instead of the ‘‘Central’’ Florida Coastal
Stock. We have corrected the errors and
posted revised versions of the 2016 and
2017 North Atlantic right whale SARs
and 2017 WNA Central Florida Coastal
Stock common bottlenose dolphin SAR
on the NMFS website (see ADDRESSES).
With this Federal Register notice, we
are notifying the public about the
revised versions.
References
Carretta, J.V., K.A. Forney, E.M. Oleson, D.W.
Weller, A.R. Lang, J. Baker, M.M. Muto,
B. Hanson, A.J. Orr, H. Huber, M.S.
Lowry, J. Barlow, J.E. Moore, D. Lynch,
L. Carswell, and R.L. Brownell Jr. 2018.
U.S. Pacific Marine Mammal Stock
Assessments: 2017. U.S. Department of
VerDate Sep<11>2014
19:14 Sep 17, 2018
Jkt 244001
Commerce. NOAA Technical
Memorandum NMFS–SWFSC–602.
155 pp.
Daoust, P.-Y., E.L. Couture, T. Wimmer and
L. Bourque. 2017. Incident Report: North
Atlantic right whale mortality event in
the Gulf of St. Lawrence, 2017.
Collaborative report produced by:
Canadian Wildlife Health Cooperative,
Marine Animal Response Society, and
Fisheries and Oceans Canada. 256 pp.
Garrison, L.P. and P.E. Rosel. 2017.
Partitioning short-finned and long-finned
pilot whale bycatch estimates using
habitat and genetic information.
Southeast Fisheries Science Center,
Protected Resources and Biodiversity
Division, 75 Virginia Beach Dr., Miami,
FL 33140. PRBD Contribution # PRBD–
2016–17, 24 pp.
Hayes, S.A., E. Josephson, K. Maze-Foley,
P.E. Rosel, B. Byrd, S. Chavez-Rosales,
T.V.N. Col, L. Engleby, L.P. Garrison, J.
Hatch, A. Henry, S.C. Horstman, J. Litz,
M.C. Lyssikatos, K.D. Mullin, C.
Orphanides, R.M. Pace, D.L. Palka, M.
Soldevilla, and F.W. Wenzel. 2018. U.S.
Atlantic and Gulf of Mexico Marine
Mammal Stock Assessments—2017.
NOAA Tech Memo NMFS NE–245;
371 p.
Laake, J.L., M.S. Lowry, R.L. DeLong, S.R.
Melin, and J.V. Carretta. 2018.
Population growth and status of
California sea lions. The Journal of
Wildlife Management, DOI: 10.1002/
jwmg.21405.
NMFS (National Marine Fisheries Service).
2016. Guidelines for preparing Stock
Assessment Reports pursuant to the 1994
Amendments to the MMPA, NMFS
Instruction 02–204–01, February 22,
2016. 24 pp.
Rockwood, R.C., J. Calambokidis, and J.
Jahncke. 2017. High mortality of blue,
humpback and fin whales from modeling
of vessel collisions on the U.S. West
Coast suggests population impacts and
insufficient protection. PLoS ONE
12(8):e0183052.
Dated: September 12, 2018.
Catherine E. Tortorici,
Acting Deputy Director, Office of Protected
Resources, National Marine Fisheries Service.
[FR Doc. 2018–20185 Filed 9–17–18; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XG451
Taking and Importing Marine
Mammals; Taking Marine Mammals
Incidental to Northwest Fisheries
Science Center Fisheries Research
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
AGENCY:
PO 00000
Frm 00012
Fmt 4703
Sfmt 4703
47135
Notice of issuance of Letter of
Authorization.
ACTION:
In accordance with the
Marine Mammal Protection Act
(MMPA), as amended, and
implementing regulations, notification
is hereby given that a Letter of
Authorization (LOA) has been issued to
the NMFS Northwest Fisheries Science
Center (NWFSC) for the take of marine
mammals incidental to fisheries
research conducted in the Pacific
Ocean, including Puget Sound and the
Columbia River.
DATES: The authorization is effective
from August 27, 2018, through August
28, 2023.
ADDRESSES: The LOA and supporting
documentation is available online:
www.fisheries.noaa.gov/action/
incidental-take-authorization-noaafisheries-nwfsc-fisheries-and-ecosystemresearch. In case of problems accessing
these documents, please call the contact
listed below.
FOR FURTHER INFORMATION CONTACT: Ben
Laws, Office of Protected Resources,
NMFS, (301) 427–8401.
SUPPLEMENTARY INFORMATION:
SUMMARY:
Background
Paragraphs 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1371(a)(5)(A) and (D))
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.
An 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)
E:\FR\FM\18SEN1.SGM
18SEN1
Agencies
[Federal Register Volume 83, Number 181 (Tuesday, September 18, 2018)]
[Notices]
[Pages 47131-47135]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-20185]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XG300
Draft 2018 Marine Mammal Stock Assessment Reports
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; request for comments and correction.
-----------------------------------------------------------------------
SUMMARY: NMFS reviewed the Alaska, Atlantic, and Pacific regional
marine mammal stock assessment reports (SARs) in accordance with the
Marine Mammal Protection Act. SARs for marine mammals in the Alaska,
Atlantic, and Pacific regions were revised according to new
information. NMFS solicits public comments on the draft 2018 SARs. NMFS
also announces the availability of revised Atlantic Regional 2016 and
2017 SARs that include technical corrections.
DATES: Comments must be received by December 17, 2018.
ADDRESSES: The 2018 draft SARs are available in electronic form via the
internet at https://www.fisheries.noaa.gov/national/marine-mammal-protection/draft-marine-mammal-stock-assessment-reports. The revised
final Atlantic Regional SAR for 2016 is available at https://www.nefsc.noaa.gov/publications/tm/tm241/and the revised 2017 SAR is
available at https://www.nefsc.noaa.gov/publications/tm/tm245/.
Copies of the Alaska Regional SARs may be requested from Marcia
Muto, Alaska Fisheries Science Center, NMFS, 7600 Sand Point Way NE,
Seattle, WA 98115-6349.
Copies of the Atlantic, Gulf of Mexico, and Caribbean Regional SARs
may be requested from Elizabeth Josephson, Northeast Fisheries Science
Center, 166 Water St., Woods Hole, MA 02543.
Copies of the Pacific Regional SARs may be requested from Jim
Carretta, Southwest Fisheries Science Center, 8604 La Jolla Shores
Drive, La Jolla, CA 92037-1508.
You may submit comments, identified by NOAA-NMFS-2018-0086, by
either of the following methods:
Federal e-Rulemaking Portal: Go to www.regulations.gov/#!docketDetail;D=NOAA-NMFS-2018-0086, click the ``Comment Now!'' icon,
complete the required fields, and enter or attach your comments.
Mail: Send comments or requests for copies of reports to: Chief,
Marine Mammal and Sea Turtle Conservation Division, Office of Protected
Resources, National Marine Fisheries Service, 1315 East-West Highway,
Silver Spring, MD 20910-3226, Attn: Stock Assessments.
Instructions: NMFS may not consider comments if they are sent by
any other method, to any other address or individual, or received after
the end of the comment period. All comments received are a part of the
public record and will generally be posted for public viewing on
www.regulations.gov without change. All personal identifying
information (e.g., name, address, etc.), confidential business
information, or otherwise sensitive information submitted voluntarily
by the sender will be publicly accessible. NMFS will accept anonymous
comments (enter ``N/A'' in the required fields if you wish to remain
anonymous).
FOR FURTHER INFORMATION CONTACT: Lisa Lierheimer, Office of Protected
Resources, 301-427-8402, [email protected]; Marcia Muto, 206-
526-4026, [email protected], regarding Alaska regional stock
assessments; Elizabeth Josephson, 508-495-2362,
[email protected], regarding Atlantic, Gulf of Mexico, and
Caribbean regional stock assessments; or Jim Carretta, 858-546-7171,
[email protected], regarding Pacific regional stock assessments.
SUPPLEMENTARY INFORMATION:
Background
Section 117 of the Marine Mammal Protection Act (MMPA) (16 U.S.C.
1361 et seq.) requires NMFS and the U.S. Fish and Wildlife Service
(FWS) to prepare stock assessments for each stock of marine mammals
occurring in waters under the jurisdiction of the United States,
including the Exclusive Economic Zone. These reports must contain
information regarding the distribution and abundance of the stock,
population growth rates and trends, estimates of annual human-caused
mortality and serious injury (M/SI) from all sources, descriptions of
the fisheries with which the stock interacts, and the status of the
stock. Initial reports were completed in 1995.
The MMPA requires NMFS and FWS to review the SARs at least annually
for
[[Page 47132]]
strategic stocks and stocks for which significant new information is
available, and at least once every three years for non-strategic
stocks. The term ``strategic stock'' means a marine mammal stock: (A)
For which the level of direct human-caused mortality exceeds the
potential biological removal level or PBR (defined by the MMPA as the
maximum number of animals, not including natural mortalities, that may
be removed from a marine mammal stock while allowing that stock to
reach or maintain its optimum sustainable population); (B) which, based
on the best available scientific information, is declining and is
likely to be listed as a threatened species under the Endangered
Species Act (ESA) within the foreseeable future; or (C) which is listed
as a threatened species or endangered species under the ESA. NMFS and
the FWS are required to revise a SAR if the status of the stock has
changed or can be more accurately determined.
Prior to public review, the updated SARs under NMFS' jurisdiction
are peer-reviewed within NMFS Fisheries Science Centers and by members
of three regional independent Scientific Review Groups, which were
established under the MMPA to independently advise NMFS on information
and uncertainties related to the status of marine mammals.
The period covered by the 2018 draft SARs is 2012-2016. NMFS
reviewed the status of marine mammal stocks as required and revised a
total of 47 reports representing 76 stocks in the Alaska, Atlantic, and
Pacific regions to incorporate new information. The 2018 revisions
consist primarily of updated or revised M/SI estimates and updated
abundance estimates. One stock (Alaska bearded seal) changed in status
from non-strategic to strategic, and three stocks (Gulf of Maine
humpback whale, and Western North Atlantic short-finned and long-finned
pilot whales) changed in status from strategic to non-strategic.
Substantive revisions to the SARs are discussed below. NMFS solicits
public comments on the draft 2018 SARs.
Alaska Reports
In 2018, NMFS reviewed all 45 stocks in the Alaska region, and
revised SARs under NMFS jurisdiction for 18 stocks (14 strategic and 4
non-strategic). The Alaska bearded seal stock changed from ``non-
strategic'' to ``strategic'' status because the stock is now considered
depleted under the MMPA (see below). A list of the 18 reports revised
in 2018 for stocks in the Alaska region is presented in Table 1.
Information on the remaining Alaska region stocks can be found in the
final 2017 reports (Muto et al., 2018).
Table 1--List of Marine Mammal Stocks in the Alaska Region Revised in
2018
------------------------------------------------------------------------
Strategic stocks Non-strategic stocks
------------------------------------------------------------------------
Steller sea lion, Western U.S. ribbon seal,
Alaska.
northern fur seal, Eastern Pacific white-sided
Pacific. dolphin, North Pacific.
bearded seal, Alaska. Dall's porpoise,
Alaska.
beluga whale, Cook Inlet. Minke whale,
Alaska.
killer whale, AT1 Transient. ............................
harbor porpoise, Southeast ............................
Alaska.
harbor porpoise, Gulf of Alaska. ............................
harbor porpoise, Bering Sea. ............................
sperm whale, North Pacific. ............................
humpback whale, Western North ............................
Pacific.
humpback whale, Central North ............................
Pacific.
fin whale, Northeast Pacific. ............................
North Pacific right whale, ............................
Eastern North Pacific.
bowhead whale, Western Arctic.
------------------------------------------------------------------------
Revisions to the Alaska SARs included updates of abundance and/or
M/SI estimates, including revised abundance estimates for Western U.S.
Steller sea lion; Eastern Pacific northern fur seal; and Cook Inlet
beluga whale.
Alaska Bearded Seal
In 2012, NMFS listed the Beringia distinct population segment of
bearded seal, and thus the Alaska stock of bearded seal, as threatened
under the ESA (77 FR 76740, December 28, 2012). The primary concern for
this population is the ongoing and projected loss of sea-ice cover
stemming from climate change, which is expected to pose a significant
threat to the persistence of these seals in the foreseeable future. In
2014, the U.S. District Court for the District of Alaska issued a
decision vacating NMFS' listing in a lawsuit that challenged listing
bearded seals under the ESA (Alaska Oil and Gas Association v.
Pritzker, Case No. 4:13-cv-00018-RPB). Consequently, it was also no
longer designated as ``depleted'' or classified as a strategic stock.
In 2016, the 9th Circuit Court of Appeals overturned the decision and
approved the agency's protection of the seals; and in 2018, the U.S.
Supreme Court declined a challenge to NMFS' listing decision. Thus,
because of its threatened status under the ESA, this bearded seal stock
is considered depleted under the Marine Mammal Protection Act andis now
classified as a ``strategic'' stock.
Atlantic Reports
In 2018, NMFS reviewed all 117 stocks in the Atlantic region
(including the Atlantic Ocean, Gulf of Mexico, and U.S. territories in
the Caribbean) under NMFS jurisdiction. This year, NMFS revised 16
reports and created 2 new common bottlenose dolphin reports (West Bay
and Terrebonne Bay/Timbalier Bay). These updated reports represent 42
stocks (26 strategic and 16 non-strategic). The Gulf of Maine humpback
whale stock and Western North Atlantic (WNA) long-finned and short-
finned pilot whale stocks changed from ``strategic'' to ``non-
strategic'' status because the mean annual human-caused M/SI is below
PBR (see below). A list of the 42 stocks in the Atlantic region
(contained in 18 reports), is presented in Table 2. Information on the
remaining Atlantic region stocks can be found in the final 2017 reports
(Hayes et al., 2018).
[[Page 47133]]
Table 2--List of Marine Mammal Stocks in the Atlantic Region Revised in
2018
------------------------------------------------------------------------
Strategic stocks Non-strategic stocks
------------------------------------------------------------------------
North Atlantic right whale, humpback whale,
Western Atlantic. Gulf of Maine.
fin whale, WNA. minke whale,
Canadian East Coast.
common bottlenose dolphin (24 Risso's dolphin,
stocks).* WNA.
[cir] Laguna Madre. pilot whale, long-
finned, WNA.
[cir] Neuces Bay/Corpus Christi Bay. pilot whale, short-
finned, WNA.
[cir] Copano Bay/Aransas Bay/San Atlantic white-
Antonio Bay/Redfish Bay/Espiritu sided dolphin, WNA.
Santo Bay.
[cir] Matagorda Bay/Tres Palacios Bay/ common dolphin, WNA
Lavaca Bay. offshore.
[cir] Galveson Bay/East Bay/Trinity rough-toothed
Bay. dolphin, WNA.
[cir] Sabine Lake. harbor porpoise,
Gulf of Maine/Bay of Fundy.
[cir] Calcasieu Lake. harbor seal, WNA.
[cir] Vermilion Bay/West Cote Blanche gray seal, WNA.
Bay/Atchafalaya Bay.
[cir] Mississippi River Delta. harp seal, WNA.
[cir] Mobile Bay/Bonsecour Bay. hooded seal, WNA.
[cir] Perdido Bay. common bottlenose
dolphin (3 stocks).
[cir] Pensacola Bay/East Bay. [cir] West Bay.
[cir] St. Andrew Bay. [cir] Terrebonne Bay/
Timbalier Bay.
[cir] St. Vincent Sound/Apalachicola [cir] Sarasota Bay/Little
Bay/St. George Sound. Sarasota Bay.*
[cir] Apalachee Bay.
[cir] Waccassa Bay/Withlacoochee Bay/
Crystal Bay.
[cir] St. Joseph Sound/Clearwater
Harbor.
[cir] Tampa Bay.
[cir] Pine Island Sound/Charlotte
Harbor/Gasparilla Sound/Lemon Bay.
[cir] Caloosahatchee River.
[cir] Estero Bay.
[cir] Chokoloskee Bay/Ten Thousand
Islands/Gullivan Bay.
[cir] Whitewater Bay.
[cir] Florida Keys (Bahia Honda to Key
West).
------------------------------------------------------------------------
* Details for these 25 stocks are included in the report: Common
bottlenose dolphin, Northern Gulf of Mexico Bay, Sound, and Estuary
Stocks.
Revisions to the Atlantic SARs included updates of abundance and/or
M/SI estimates. New abundance estimates are available for the North
Atlantic right whale, Gulf of Maine humpback whale, WNA short-finned
pilot whale, WNA rough-toothed dolphin, and the West Bay and Terrebonne
Bay/Timbalier Bay common bottlenose dolphin stocks.
North Atlantic Right Whale, Western Atlantic
Although PBR analyses in this 2018 SAR reflect data collected
through 2016, it should be noted that an additional 17 North Atlantic
right whale mortalities were observed in 2017 (Daoust et al. 2017).
This number exceeds the largest estimated mortality rate during the
past 25 years. Further, despite the usual extensive survey effort, only
5 and 0 new calves were detected in 2017 and 2018, respectively.
Therefore, the decline in the right whale population is expected to
continue for at least an additional 2 years. The minimum population
size for the Western Atlantic stock of the North Atlantic right whale
is 445 and PBR is 0.9.
Humpback Whale, Gulf of Maine
The updated abundance estimate for the Gulf of Maine humpback whale
stock is 896, based on a recent count of the minimum number alive
(MNA). The 2015 humpback whale MNA was produced by counting the number
of unique individuals seen in 2015 in the Gulf of Maine stock area as
well as seen both before and after 2015. The 2015 humpback whale MNA
includes not only cataloged whales but some calves born in 2015 but not
yet identifiable. MNA is a rigorous accounting of individuals and has
no associated coefficient of variation (CV). It is both more recent and
larger than the previous 2011 line transect estimate of 335 and has
zero probability of overestimating abundance. Although the abundance
appears to increase from 2017 to 2018, these estimates should not be
compared as they were derived using different methodologies and data
sets. As a result of the higher abundance estimate, the PBR for the
Gulf of Maine humpback whale stock increased from 3.7 to 14.6 whales.
Based on a recovery factor of 0.5, the estimate of human-caused M/SI is
now below PBR; thus, the stock has changed from ``strategic'' to ``non-
strategic.''
Long-Finned Pilot Whale, Western North Atlantic
The PBR for the western North Atlantic long-finned pilot whale is
35 and the estimate of total annual observed average fishery-related of
human-caused M/SI is 27. In bottom trawls and mid-water trawls and in
the gillnet fisheries, mortalities were more generally observed north
of 40[deg] N latitude and in areas expected to have only long-finned
pilot whales. Takes in these fisheries were therefore attributed to the
long-finned pilot whales. Takes in the pelagic longline fishery were
partitioned according to a logistic regression model (Garrison and
Rosel 2017). Because the M/SI does not exceed PBR, the stock has
changed from ``strategic'' to ``non-strategic.''
Short-Finned Pilot Whale, Western North Atlantic
The best available abundance estimate for short-finned pilot
whales, based on shipboard surveys conducted during the summer of 2016
in the western North Atlantic, is 28,924. These most recent surveys
covered the full range of short-finned pilot whales in U.S. Atlantic
waters. Because long-finned and short-finned pilot whales are difficult
to distinguish at sea, sightings data are reported as Globicephala sp.
These survey data have been combined with an analysis of the spatial
distribution of the two pilot whale species based on genetic analyses
of biopsy samples to derive separate abundance estimates for each
species. Due to changes in survey methodology, previous abundance
[[Page 47134]]
estimates should not be used to make comparisons with more current
estimates. As a result of the higher abundance estimate, the PBR for
the western North Atlantic short-finned pilot whale increased from 159
to 236 and the estimate of total annual observed average fishery-
related of human-caused M/SI is 27. The estimate of human-caused M/SI
is now below PBR; thus, the stock has changed from ``strategic'' to
``non-strategic.''
Common Bottlenose Dolphins
NMFS is in the process of writing individual stock assessment
reports for each of the 31 bay, sound, and estuary stocks of common
bottlenose dolphins in the northern Gulf of Mexico. Two new individual
reports, for the West Bay and Terrebonne-Timbalier Bay Estuarine System
stocks, were completed for the draft 2018 SARs. Therefore, the reader
will not see tracked changes in the draft 2018 reports for these
stocks. To date, six bottlenose dolphin stocks have individual reports
completed (West Bay, Terrebonne-Timbalier Bay Estuarine System,
Barataria Bay Estuarine System, Mississippi Sound/Lake Borgne/Bay
Boudreau, Choctawhatchee Bay, and St. Joseph Bay), and the remaining 25
stocks are included in the Northern Gulf of Mexico Bay, Sound, and
Estuary Stocks report.
Pacific Reports
In 2018, NMFS reviewed all 87 stocks in the Pacific region (waters
along the west coast of the United States, within waters surrounding
the main and Northwestern Hawaiian Islands, and within waters
surrounding U.S. territories in the Western Pacific), and revised SARs
for 16 stocks (7 strategic and 9 non-strategic). A list of the reports
revised in 2018, representing 16 stocks in the Pacific region, is
presented in Table 3. Information on the remaining Pacific region
stocks can be found in the final 2017 reports (Carretta et al., 2018).
Table 3--List of Marine Mammal Stocks in the Pacific Region Revised in
2018
------------------------------------------------------------------------
Strategic stocks Non-strategic stocks
------------------------------------------------------------------------
Hawaiian monk seal California sea
lion.
killer whale, Eastern N Pacific killer whale,
Southern Resident Eastern N Pacific Offshore.
humpback whale, CA/OR/WA gray whale, Eastern
blue whale, Eastern N Pacific N Pacific.
fin whale, CA/OR/WA gray whale, Western
sei whale, Eastern N Pacific N Pacific.
spinner dolphin:
[cir] Hawaii pelagic.
[cir] Hawaii Island.
[cir] O'ahu/4 Islands.
[cir] Kaua'i/Ni'ihau.
[cir] Kure/Midway.
[cir] Pearl and Hermes Reef.
------------------------------------------------------------------------
New abundance estimates are available for 8 stocks: California sea
lions, Hawaiian monk seals, Eastern North Pacific Offshore killer
whales, Southern Resident killer whales, Eastern North Pacific gray
whales, Western North Pacific gray whales, California/Oregon/Washington
humpback whales, and Hawaii Island spinner dolphins.
New Methodology To Estimate Level of Vessel Strike Mortality: CA/OR/WA
Humpback Whale, CA/OR/WA Fin Whale, and the Eastern North Pacific Blue
Whales
New information on serious injury and mortality resulting from
estimated vessel strikes based on an analysis by Rockwood et al. (2017)
is included for the following stocks of large whales: CA/OR/WA humpback
whale, CA/OR/WA fin whale, and the Eastern North Pacific blue whales.
Using the moderate level of vessel avoidance, this model estimated the
following annual mortality of these stocks of large whales due to ship
strikes as follows: 22 humpback whales (representing approximately 0.7
percent of the estimated population size of the stock); 43 fin whales
(representing approximately <0.5 percent of the estimated population
size of the stock); and 18 blue whales (representing approximately 1
percent of the estimated population size of the stock. Based on this
new methodology, estimated levels of vessel strike mortality exceed PBR
for both Eastern North Pacific blue and CA/OR/WA humpback whale stocks,
although estimated vessel strike levels represent a small fraction of
the overall estimated population sizes. Estimated vessel strikes are
also compared with recent detected levels of vessel strikes, which
indicate that detection rates for vessel strike events are quite low,
ranging from approximately 1 percent (for blue whales) to 12 percent
(for humpback whales). There is uncertainty regarding the estimated
number of ship strike deaths as carcass recovery rates are quite low.
New Methodology To Assign Cases of Entangled but Unidentified Whales to
Stock: CA/OR/WA Humpback Whale, CA/OR/WA Fin Whale, Eastern North
Pacific Gray Whale, and Eastern North Pacific Blue Whales
Unidentified whales represent approximately 15 percent of
entanglement cases along the U.S. West Coast. In previous stock
assessments, unidentified entanglements were not assigned to stock. For
large whale stocks, including gray, humpback, blue, and fin whales, a
new methodology based on an assignment model generated from historic
known-species entanglements in the region was used to assign previous
cases of unidentified whale entanglements to species (Carretta 2018).
This has eliminated a negative bias in assessments that occurs when
unidentified whale entanglements are not assigned to any species/stock.
In the case of CA/OR/WA humpback whales, observed levels of
entanglements and vessel strikes combined exceed PBR.
New Methodology To Calculate the Minimum Population Estimate (Nmin) for
California Sea Lion
The 2018 SAR for California sea lions uses a different methodology
for estimating Nmin. The updated minimum population size of the U.S.
stock is 233,515 (153,337 in 2014 SAR). This resulted in an increase in
PBR from 9,200 (in 2014) to 14,011. The updated best abundance estimate
available for California sea lions, based on a 1975-2014 time series of
pup counts, combined with mark-recapture estimates of survival rates,
is 257,606 sea lions (Laake et al., 2018) (down from 296,750 in 2014
SAR).
The previous approach to calculate Nmin used two times the annual
pup
[[Page 47135]]
count, which resulted in negatively-biased Nmin values because not all
age classes are represented. The Guidelines for preparing Stock
Assessment Reports (NMFS 2016) recommends defining Nmin as the 20th
percentile of a log-normal distribution based on an estimate of the
number of animals in a stock (which is equivalent to the lower limit of
a 60% 2-tailed confidence interval). The Guidelines allow for other
approaches to be used to estimate Nmin if they provide an adequate
level of assurance that the stock size is equal to or greater than that
estimate. Laake et al. (2018) did not provide a CV for the estimated
population size, so the updated Nmin is based on the lower 95 percent
confidence limit. The stock is estimated to be approximately 40 percent
above its maximum net productivity level (MNPL = 183,481 animals), and
it is therefore considered within the range of its optimum sustainable
population. The carrying capacity of the population was estimated at
275,298 animals in 2014 (Laake et al. 2018). The total human caused
mortality is less than the PBR of 14,011.
Corrections to the 2016 and 2017 SARs
Subsequent to announcing the availability of the final 2016 (82 FR
29039, June 27, 2017) and 2017 (83 FR 32093, July 11, 2018) SARs, we
were made aware that the SARs contained some technical errors. In the
2016 North Atlantic right whale SAR, the PBR was listed incorrectly as
1. The correct PBR value for 2016 is 0.9. Similarly, in the 2017 North
Atlantic right whale SAR, PBR was listed as 1.4, but the correct value
is 0.9. In addition, the 2017 SAR for the WNA Central Florida Coastal
Stock of common bottlenose dolphins contained a technical error. In the
``Population Size'' section, the name of the stock was incorrectly
listed as the ``Northern'' Florida Coastal Stock instead of the
``Central'' Florida Coastal Stock. We have corrected the errors and
posted revised versions of the 2016 and 2017 North Atlantic right whale
SARs and 2017 WNA Central Florida Coastal Stock common bottlenose
dolphin SAR on the NMFS website (see Addresses). With this Federal
Register notice, we are notifying the public about the revised
versions.
References
Carretta, J.V., K.A. Forney, E.M. Oleson, D.W. Weller, A.R. Lang, J.
Baker, M.M. Muto, B. Hanson, A.J. Orr, H. Huber, M.S. Lowry, J.
Barlow, J.E. Moore, D. Lynch, L. Carswell, and R.L. Brownell Jr.
2018. U.S. Pacific Marine Mammal Stock Assessments: 2017. U.S.
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Dated: September 12, 2018.
Catherine E. Tortorici,
Acting Deputy Director, Office of Protected Resources, National Marine
Fisheries Service.
[FR Doc. 2018-20185 Filed 9-17-18; 8:45 am]
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