List of Fisheries for 2012, 73912-73953 [2011-30607]
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Federal Register / Vol. 76, No. 229 / Tuesday, November 29, 2011 / Rules and Regulations
SUPPLEMENTARY INFORMATION:
National Oceanic and Atmospheric
Administration
50 CFR Part 229
[Docket No. 110207104–1536–02]
RIN 0648–BA76
List of Fisheries for 2012
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
The National Marine
Fisheries Service (NMFS) publishes its
final List of Fisheries (LOF) for 2012, as
required by the Marine Mammal
Protection Act (MMPA). The final LOF
for 2012 reflects new information on
interactions between commercial
fisheries and marine mammals. NMFS
must classify each commercial fishery
on the LOF into one of three categories
under the MMPA based upon the level
of serious injury and mortality of marine
mammals that occurs incidental to each
fishery. The classification of a fishery in
the LOF determines whether
participants in that fishery are subject to
certain provisions of the MMPA, such as
registration, observer coverage, and take
reduction plan (TRP) requirements.
DATES: This final rule is effective
January 1, 2012.
ADDRESSES: Comments regarding the
burden-hour estimates, or any other
aspect of the collection of information
requirements contained in this final
rule, should be submitted in writing to
Chief, Marine Mammal and Sea Turtle
Conservation Division, Office of
Protected Resources, NMFS, 1315 EastWest Highway, Silver Spring, MD
20910, or to Nathan Frey, OMB, by fax
to (202) 395–7285 or by email to
Nathan_Frey@omb.eop.gov.
FOR FURTHER INFORMATION CONTACT:
Melissa Andersen, Office of Protected
Resources, (301) 713–2322; David
Gouveia, Northeast Region, (978) 281–
9280; Laura Engleby, Southeast Region,
(727) 551–5791; Elizabeth Petras,
Southwest Region, (562) 980–3238;
Brent Norberg, Northwest Region, (206)
526–6733; Bridget Mansfield, Alaska
Region, (907) 586–7642; Lisa Van Atta,
Pacific Islands Region, (808) 944–2257.
Individuals who use a
telecommunications device for the
hearing impaired may call the Federal
Information Relay Service at 1–(800)
877–8339 between 8 a.m. and 4 p.m.
Eastern time, Monday through Friday,
excluding Federal holidays.
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SUMMARY:
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Fishery Classification Criteria
Availability of Published Materials
DEPARTMENT OF COMMERCE
The fishery classification criteria
consist of a two-tiered, stock-specific
approach that first addresses the total
impact of all fisheries on each marine
mammal stock, and then addresses the
impact of individual fisheries on each
stock. This approach is based on
consideration of the rate, in numbers of
animals per year, of incidental
mortalities and serious injuries of
marine mammals due to commercial
fishing operations relative to the
potential biological removal (PBR) level
for each marine mammal stock. The
MMPA (16 U.S.C. 1362(20)) defines the
PBR level 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. This
definition can also be found in the
implementing regulations for section
118 of the MMPA (50 CFR 229.2).
Tier 1: If the total annual mortality
and serious injury of a marine mammal
stock, across all fisheries, is less than or
equal to 10 percent of the PBR level of
the stock, all fisheries interacting with
the stock would be placed in Category
III (unless those fisheries interact with
other stock(s) in which total annual
mortality and serious injury is greater
than 10 percent of PBR). Otherwise,
these fisheries are subject to the next
tier (Tier 2) of analysis to determine
their classification.
Tier 2, Category I: Annual mortality
and serious injury of a stock in a given
fishery is greater than or equal to 50
percent of the PBR level (i.e., frequent
incidental mortality and serious injuries
of marine mammals).
Tier 2, Category II: Annual mortality
and serious injury of a stock in a given
fishery is greater than 1 percent and less
than 50 percent of the PBR level (i.e.,
occasional incidental mortality and
serious injuries of marine mammals).
Tier 2, Category III: Annual mortality
and serious injury of a stock in a given
fishery is less than or equal to 1 percent
of the PBR level (i.e., a remote
likelihood or no known incidental
mortality and serious injuries of marine
mammals).
While Tier 1 considers the cumulative
fishery mortality and serious injury for
a particular stock, Tier 2 considers
fishery-specific mortality and serious
injury for a particular stock. Additional
details regarding how the categories
were determined are provided in the
preamble to the final rule implementing
section 118 of the MMPA (60 FR 45086,
August 30, 1995).
Information regarding the LOF and
the Marine Mammal Authorization
Program, including registration
procedures and forms, current and past
LOFs, information on each Category I
and II fishery, observer requirements,
and marine mammal injury/mortality
reporting forms and submittal
procedures, may be obtained at:
https://www.nmfs.noaa.gov/pr/
interactions/lof/, or from any NMFS
Regional Office at the addresses listed
below:
NMFS, Northeast Region, 55 Great
Republic Drive, Gloucester, MA 01930–
2298, Attn: Allison Rosner;
NMFS, Southeast Region, 263 13th
Avenue South, St. Petersburg, FL 33701,
Attn: Laura Engleby;
NMFS, Southwest Region, 501 W.
Ocean Blvd., Suite 4200, Long Beach,
CA 90802–4213, Attn: Charles Villafana;
NMFS, Northwest Region, 7600 Sand
Point Way NE., Seattle, WA 98115, Attn:
Protected Resources Division;
NMFS, Alaska Region, Protected
Resources, P.O. Box 22668, 709 West
9th Street, Juneau, AK 99802, Attn:
Bridget Mansfield; or
NMFS, Pacific Islands Region,
Protected Resources, 1601 Kapiolani
Boulevard, Suite 1110, Honolulu, HI
96814–4700, Attn: Lisa Van Atta.
What is the list of fisheries?
Section 118 of the MMPA requires
NMFS to place all U.S. commercial
fisheries into one of three categories
based on the level of incidental serious
injury and mortality of marine mammals
occurring in each fishery (16 U.S.C.
1387(c)(1)). The classification of a
fishery on the LOF determines whether
participants in that fishery may be
required to comply with certain
provisions of the MMPA, such as
registration, observer coverage, and TRP
requirements. NMFS must reexamine
the LOF annually, considering new
information in the Marine Mammal
Stock Assessment Reports (SAR) and
other relevant sources, and publish in
the Federal Register any necessary
changes to the LOF after notice and
opportunity for public comment (16
U.S.C. 1387(c)(1)(C)).
How does NMFS determine in which
category a fishery is placed?
The definitions for the fishery
classification criteria can be found in
the implementing regulations for section
118 of the MMPA (50 CFR 229.2). The
criteria are also summarized here.
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Because fisheries are classified on a
per-stock basis, a fishery may qualify as
one Category for one marine mammal
stock and another Category for a
different marine mammal stock. A
fishery is typically classified on the LOF
at its highest level of classification (e.g.,
a fishery qualifying for Category III for
one marine mammal stock and for
Category II for another marine mammal
stock will be listed under Category II).
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Other Criteria That May Be Considered
There are several fisheries on the LOF
classified as Category II that have no
recent documented injuries or
mortalities of marine mammals, or
fisheries that did not result in a serious
injury or mortality rate greater than 1
percent of a stock’s PBR level based on
known interactions. NMFS has
classified these fisheries as Category II
by analogy to other Category I or II
fisheries (NMFS does not classify
fisheries as Category I based on analogy)
that are sufficiently analogous to the
fishery in question (e.g., use similar
fishing techniques or gear that are
known to cause mortality or serious
injury of marine mammals), or
according to factors discussed in the
final LOF for 1996 (60 FR 67063,
December 28, 1995) and listed in the
regulatory definition of a Category II
fishery. The regulations at 50 CFR 229.2
state that in the absence of reliable
information indicating the frequency of
incidental mortality and serious injury
of marine mammals by a commercial
fishery, NMFS will determine whether
the incidental serious injury or
mortality is ‘‘occasional’’ or ‘‘remote’’ by
‘‘* * * evaluating other factors such as
fishing techniques, gear used, methods
used to deter marine mammals, target
species, seasons and areas fished,
qualitative data from logbooks or fisher
reports, stranding data, and the species
and distribution of marine mammals in
the area, or at the discretion of the
Assistant Administrator for Fisheries.’’
Further, eligible commercial fisheries
not specifically identified on the LOF
are deemed to be Category II fisheries
until the next LOF is published (50 CFR
229.2).
Information That May Be Considered
When Classifying Fisheries
Under regulations pursuant to section
118 of the MMPA, observer data,
logbook data, stranding data, fishers’
reports, anecdotal reports, and
information on incidental serious injury
or mortality to marine mammals
reported in SARs are used to classify
fisheries (60 FR 45086, August 30, 1995;
60 FR 67063, December 28, 1995).
Further, the factors for consideration
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laid out in 50 CFR 229.2 (fishing
techniques, gear used, methods used to
deter marine mammals, target species,
seasons and areas fished, qualitative
data from logbooks or fisher reports,
stranding data, and the species and
distribution of marine mammals in the
area, or at the discretion of the Assistant
Administrator for Fisheries), generally
termed ‘‘analogy’’ in the LOF, are used
to classify fisheries in the absence of
reliable data on the frequency of
interactions.
How does NMFS determine which
species or stocks are included as
incidentally killed or injured in a
fishery?
The LOF includes a list of marine
mammal species or stocks incidentally
killed or injured in each commercial
fishery. To determine which species or
stocks are included as incidentally
killed or injured in a fishery, NMFS
annually reviews the information
presented in the current SARs. The
SARs are based upon the best available
scientific information and provide the
most current and inclusive information
on each stock’s PBR level and level of
interaction with commercial fishing
operations. NMFS also reviews other
sources of new information, including
observer data, stranding data, fisher selfreports, and anecdotal reports.
In the absence of reliable information
on the level of mortality or injury of a
marine mammal stock, or insufficient
observer data, NMFS will determine
whether a species or stock should be
added to, or deleted from, the list by
considering other factors such as:
changes in gear used, increases or
decreases in fishing effort, increases or
decreases in the level of observer
coverage, and/or changes in fishery
management that are expected to lead to
decreases in interactions with a given
marine mammal stock (such as a TRP or
a fishery management plan (FMP)).
NMFS will provide case-specific
justification in the LOF for changes to
the list of species or stocks incidentally
killed or injured.
How does NMFS determine the levels of
observer coverage in a fishery on the
LOF?
Data obtained from the observer
program and the observer coverage
levels in a particular fishery are
important tools in estimating the level
of annual marine mammal mortality and
serious injury in commercial fishing
operations. The best available
information on the level of observer
coverage, and the spatial and temporal
distribution of observed marine
mammal interactions, is presented in
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the SARs. Starting with the 2005 SARs,
each SAR includes an appendix with
detailed descriptions of each Category I
and II fishery on the LOF, including
observer coverage in those fisheries. The
SARs generally do not provide detailed
information on observer coverage in
Category III fisheries because, under the
MMPA, Category III fisheries are not
required to accommodate observers
aboard vessels due to the remote
likelihood of mortality and serious
injury of marine mammals. Fishery
information presented in the SARs’
appendices includes: level of observer
coverage, target species, levels of fishing
effort, spatial and temporal distribution
of fishing effort, characteristics of
fishing gear and operations,
management and regulations, and
interactions with marine mammals.
Copies of the SARs are available on the
NMFS Office of Protected Resources’
Web site at: https://www.nmfs.noaa.gov/
pr/sars/. Information on observer
coverage levels in Category I and II
fisheries can also be found in the
Category I and II fishery fact sheets on
the NMFS Office of Protected Resources
Web site: https://www.nmfs.noaa.gov/pr/
interactions/lof/. Additional
information on observer programs in
commercial fisheries can be found on
the NMFS National Observer Program’s
Web site: https://www.st.nmfs.gov/st4/
nop/.
How do I find out if a specific fishery
is in category I, II, or III?
This final rule includes three tables
that list all U.S. commercial fisheries by
LOF Category. Table 1 lists all of the
commercial fisheries in the Pacific
Ocean (including Alaska); Table 2 lists
all of the commercial fisheries in the
Atlantic Ocean, Gulf of Mexico, and
Caribbean; and Table 3 lists all U.S.authorized commercial fisheries on the
high seas. A fourth table, Table 4, lists
all commercial fisheries managed under
applicable TRPs or take reduction teams
(TRT).
Are high seas fisheries included on the
LOF?
NMFS includes high seas fisheries in
Table 3 of the LOF, along with the
number of valid High Seas Fishing
Compliance Act (HSFCA) permits in
each fishery. As of 2004, NMFS issues
HSFCA permits only for high seas
fisheries analyzed in accordance with
the National Environmental Policy Act
(NEPA) and the Endangered Species Act
(ESA). The authorized high seas
fisheries are broad in scope and
encompass multiple specific fisheries
identified by gear type. For the purposes
of the LOF, the high seas fisheries are
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subdivided based on gear type (e.g.,
trawl, longline, purse seine, gillnet,
troll, etc.) to provide more detail on
composition of effort within these
fisheries. Many fisheries operate in both
U.S. waters and on the high seas,
creating some overlap between the
fisheries listed in Tables 1 and 2 and
those in Table 3. In these cases, the high
seas component of the fishery is not
considered a separate fishery, but an
extension of a fishery operating within
U.S. waters (listed in Table 1 or 2).
NMFS designates those fisheries in
Tables 1, 2, and 3 by a ‘‘*’’ after the
fishery’s name. The number of HSFCA
permits listed in Table 3 for the high
seas components of these fisheries
operating in U.S. waters does not
necessarily represent additional effort
that is not accounted for in Tables 1 and
2. Many vessels/participants holding
HSFCA permits also fish within U.S.
waters and are included in the number
of vessels and participants operating
within those fisheries in Tables 1 and 2.
HSFCA permits are valid for five
years, during which time FMPs can
change. Therefore, some vessels/
participants may possess valid HSFCA
permits without the ability to fish under
the permit because it was issued for a
gear type that is no longer authorized
under the most current FMP. For this
reason, the number of HSFCA permits
displayed in Table 3 is likely higher
than the actual U.S. fishing effort on the
high seas. For more information on how
NMFS classifies high seas fisheries on
the LOF, see the preamble text in the
final 2009 LOF (73 FR 73032; December
1, 2008).
Where can I find specific information
on fisheries listed on the LOF?
NMFS maintains summary
documents, or fishery fact sheets, for
each Category I and II fishery on the
LOF. These fishery fact sheets provide
the full history of each Category I and
II fishery, including: when the fishery
was added to the LOF, the basis for the
fishery’s initial classification,
classification changes to the fishery,
changes to the list of species or stocks
incidentally killed or injured in the
fishery, fishery gear and methods used,
observer coverage levels, fishery
management and regulation, and
applicable TRPs or TRTs, if any. These
fishery fact sheets are updated after each
final LOF and can be found under ‘‘How
Do I Find Out if a Specific Fishery is in
Category I, II, or III?’’ on the NMFS
Office of Protected Resources’ Web site:
https://www.nmfs.noaa.gov/pr/
interactions/lof/, linked to the ‘‘List of
Fisheries by Year’’ table. NMFS is
developing similar fishery fact sheets for
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each Category III fishery on the LOF.
However, due to the large number of
Category III fisheries on the LOF and the
lack of accessible and detailed
information on many of these fisheries,
the development of these fishery fact
sheets will take significant time to
complete. NMFS anticipates posting the
Category III fishery fact sheets along
with the final 2013 LOF, although this
timeline may be revised as this exercise
progresses.
Am I required to register under the
MMPA?
Owners of vessels or gear engaging in
a Category I or II fishery are required
under the MMPA (16 U.S.C. 1387(c)(2)),
as described in 50 CFR 229.4, to register
with NMFS and obtain a marine
mammal authorization to lawfully take
non-endangered and non-threatened
marine mammals incidental to
commercial fishing operations. Owners
of vessels or gear engaged in a Category
III fishery are not required to register
with NMFS or obtain a marine mammal
authorization.
How do I register and receive my
authorization certificate and injury/
mortality reporting forms?
NMFS has integrated the MMPA
registration process, implemented
through the Marine Mammal
Authorization Program (MMAP), with
existing state and Federal fishery
license, registration, or permit systems
for Category I and II fisheries on the
LOF. Participants in these fisheries are
automatically registered under the
MMAP and are not required to submit
registration or renewal materials
directly under the MMAP.
In the Southwest, Northwest, and
Alaska regions, NMFS will issue vessel
or gear owners an authorization
certificate and/or injury/mortality
reporting forms via U.S. mail or with
their state or Federal license at the time
of renewal.
In the Pacific Islands region, NMFS
will issue vessel or gear owners who
hold a Federal permit an authorization
certificate and/or injury/mortality
reporting forms via U.S. mail or with
their Federal permit at the time of
renewal; for vessel or gear owners
holding state licenses only, NMFS will
issue an authorization certificate via
U.S. mail automatically at the beginning
of each calendar year. Individuals
participating in Category I or II fisheries
who obtain state commercial marine
licenses after the beginning of the
calendar year may request an
authorization certificate and/or injury/
mortality reporting forms by contacting
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the NMFS Pacific Islands Regional
Office at (808) 944–2200.
In the Northeast region, NMFS will
issue vessel or gear owners an
authorization certificate via U.S. mail
automatically at the beginning of each
calendar year; but vessel or gear owners
must request or print injury/mortality
reporting forms by contacting the NMFS
Northeast Regional Office at (978) 281–
9328 or by visiting the Northeast
Regional Office Web site (https://
www.nero.noaa.gov/).
In the Southeast region, NMFS will
issue vessel or gear owners notification
of registry and vessel or gear owners
may receive their authorization
certificate and/or injury/mortality
reporting form by contacting the
Southeast Regional Office at (727) 209–
5952 or by visiting the Southeast
Regional Office Web site (https://
sero.nmfs.noaa.gov/pr/mm/mmap.htm)
and following the instructions for
printing the necessary documents.
The authorization certificate, or a
copy, must be on board the vessel while
it is operating in a Category I or II
fishery, or for non-vessel fisheries, in
the possession of the person in charge
of the fishing operation (50 CFR
229.4(e)). Although efforts are made to
limit the issuance of authorization
certificates to only those vessel or gear
owners that participate in Category I or
II fisheries, not all state and Federal
permit systems distinguish between
fisheries as classified by the LOF.
Therefore, some vessel or gear owners in
Category III fisheries may receive
authorization certificates even though
they are not required for Category III
fisheries. Individuals fishing in Category
I and II fisheries for which no state or
Federal permit is required must register
with NMFS by contacting their
appropriate Regional Office (see
ADDRESSES).
How do I renew my registration under
the MMPA?
In Pacific Islands, Southwest, Alaska
or Northeast regional fisheries,
registrations of vessel or gear owners are
automatically renewed and participants
should receive an authorization
certificate by January 1 of each new
year. In Northwest regional fisheries,
vessel or gear owners receive
authorization with each renewed state
fishing license, the timing of which
varies based on target species. Vessel or
gear owners who participate in these
regions and have not received
authorization certificates by January 1 or
with renewed fishing licenses must
contact the appropriate NMFS Regional
Office (see ADDRESSES).
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In Southeast regional fisheries, vessel
or gear owners may receive an
authorization certificate by contacting
the Southeast Regional Office or visiting
the Southeast Regional Office Web site
(https://sero.nmfs.noaa.gov/pr/mm/
mmap.htm) and following the
instructions for printing the necessary
documents.
Am I required to submit reports when
I injure or kill a marine mammal
during the course of commercial fishing
operations?
In accordance with the MMPA (16
U.S.C. 1387(e)) and 50 CFR 229.6, any
vessel owner or operator, or gear owner
or operator (in the case of non-vessel
fisheries), participating in a fishery
listed on the LOF must report to NMFS
all incidental injuries and mortalities of
marine mammals that occur during
commercial fishing operations,
regardless of the category in which the
fishery is placed (I, II or III) within 48
hours of the end of the fishing trip. 50
CFR 229.2 defines an injury as ‘‘a
wound or other physical harm,’’ and
includes examples of signs of injury. In
addition, any animal that ingests fishing
gear or any animal that is released with
fishing gear entangling, trailing, or
perforating any part of the body is
considered injured, regardless of the
presence of any wound or other
evidence of injury, and must be
reported. Injury/mortality reporting
forms and instructions for submitting
forms to NMFS can be downloaded
from: https://www.nmfs.noaa.gov/pr/
pdfs/interactions/
mmap_reporting_form.pdf or by
contacting the appropriate Regional
office (see ADDRESSES). Reporting
requirements and procedures can be
found in 50 CFR 229.6.
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Am I required to take an observer
aboard my vessel?
Individuals participating in a
Category I or II fishery are required to
accommodate an observer aboard their
vessel(s) upon request from NMFS.
MMPA section 118 (16 U.S.C. 1387)
states that an observer will not be
placed on a vessel if the facilities for
quartering an observer or performing
observer functions are inadequate or
unsafe; thereby, exempting vessels too
small to accommodate an observer from
this requirement. However, observer
requirements will not be exempted,
regardless of vessel size, for U.S.
Atlantic Ocean, Caribbean, Gulf of
Mexico large pelagics longline vessels
operating in special areas designated by
the Pelagic Longline Take Reduction
Plan implementing regulations (50 CFR
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229.36(d)). Observer requirements can
be found in 50 CFR 229.7.
Am I required to comply with any
marine mammal take reduction plan
regulations?
Table 4 in this final rule provides a
list of fisheries affected by TRPs and
TRTs. TRP regulations can be found at
50 CFR 229.30 through 229.36. A
description of each TRT and copies of
each TRP can be found at: https://
www.nmfs.noaa.gov/pr/interactions/trt/.
Sources of Information Reviewed for
the Final 2012 LOF
NMFS reviewed the marine mammal
incidental injury, serious injury and
mortality information presented in the
SARs for all fisheries. The SARs are
based on the best scientific information
available at the time of preparation,
including the level of serious injury and
mortality of marine mammals that
occurs incidental to commercial fishery
operations and the PBR levels of marine
mammal stocks. The information
contained in the SARs is reviewed by
regional Scientific Review Groups
(SRGs) representing Alaska, the Pacific
(including Hawaii), and the U.S.
Atlantic, Gulf of Mexico, and Caribbean.
The SRGs were created by the MMPA to
review the science that informs the
SARs, and to advise NMFS on marine
mammal population status, trends, and
stock structure, uncertainties in the
science, research needs, and other
issues.
NMFS also reviewed other sources of
new information, including marine
mammal stranding data, observer
program data, fisher self-reports, reports
to the SRGs, conference papers,
anecdotal reports, FMPs, and ESA
documents.
The final LOF for 2012 was based on
information provided in the NEPA and
ESA documents analyzing authorized
high seas fisheries; stranding data;
fishermen self-reports through the
MMAP; observer program reports;
anecdotal reports; and the final SARs for
1996 (63 FR 60, January 2, 1998), 2001
(67 FR 10671, March 8, 2002), 2002 (68
FR 17920, April 14, 2003), 2003 (69 FR
54262, September 8, 2004), 2004 (70 FR
35397, June 20, 2005), 2005 (71 FR
26340, May 4, 2006), 2006 (72 FR 12774,
March 19, 2007), 2007 (73 FR 21111,
April 18, 2008), 2008 (74 FR 19530,
April 29, 2009), 2009 (75 FR 12498,
March 16, 2010), and 2010 (76 FR
34054, June 10, 2011). The SARs are
available at: https://www.nmfs.noaa.gov/
pr/sars/.
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Fishery Descriptions
Beginning with the final 2008 LOF (72
FR 66048, November 27, 2007), NMFS
describes each Category I and II fishery
on the LOF. Below, NMFS describes the
fisheries classified as Category I or II on
the 2012 LOF that were not classified as
such on a previous LOF (and therefore
have not yet been defined on the LOF).
Additional details for Category I and II
fisheries operating in U.S. waters are
included in the SARs, FMPs, and TRPs,
through state agencies, or through the
fishery fact sheets available on the
NMFS Office of Protected Resources
Web site (https://www.nmfs.noaa.gov/pr/
interactions/lof/). Additional details for
Category I and II fisheries operating on
the high seas are included in various
FMPs, NEPA, or ESA documents.
State and regional abbreviations used
in the following text include: AK
(Alaska), BSAI (Bering Sea, Aleutian
Islands), CA (California), DE (Delaware),
FL (Florida), GMX (Gulf of Mexico), HI
(Hawaii), MA (Massachusetts), ME
(Maine), MHI (Main Hawaiian Islands),
NC (North Carolina), NY (New York),
OR (Oregon), RI (Rhode Island), SC
(South Carolina), VA (Virginia), WA
(Washington), and WNA (Western North
Atlantic).
Southeastern U.S. Atlantic, Gulf of
Mexico Stone Crab Trap/Pot Fishery
The ‘‘Southeastern U.S. Atlantic, Gulf
of Mexico stone crab trap/pot’’ fishery
operates primarily nearshore in the
State of FL. Stone crab fishing outside
of this area is likely very minimal. In
2010, the State of FL issued 1,282
commercial stone crab licenses and
1,190,285 stone crab trap tags. FL state
regulations limit recreational stone crab
trap/pot numbers to five per person (FL
Administrative Code (F.A.C.) Chapter
68B–13). The season for commercial and
recreational stone crab harvest is from
October 15 to May 15. Traps are the
most typical gear type used for the
commercial and recreational stone crab
fishery. Commercial traps must be
designed to conform to the
specifications established under U.S. 50
CFR 654.22, as well as F.A.C. Chapter
68B–13. Baited traps are frequently set
in waters of 65 ft (19.8 m) depth or less
in a double line formation, generally
100–300 ft (30.5–91.4 m) apart, running
parallel to a bottom contour. The
margins of seagrass flats and bottoms
with low rocky relief are also favored
areas for trap placement. Buoys are
attached to the trap/pot via float line. In
FL, commercial trap/pot buoys are
required to be marked with the letter
‘‘X,’’ the trap owner’s stone crab
endorsement number (in characters at
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least 2 inches high), and a tag that
corresponds to a valid FWC-issued trap
certificate. Recreational trap/pot buoys,
except those fished from a dock, must
have a permanently affixed and legible
‘‘R’’ at least 2 inches high and the
harvester’s name and address (Ch. 68B–
13.009(3), F.A.C).
Comments and Responses
NMFS received 19 comment letters on
the proposed 2012 LOF (76 FR 37716,
June 28, 2011). Comments were received
from the Blue Water Fishermen’s
Association, Center for Biological
Diversity, Florida Fish and Wildlife
Conservation Commission, Florida Keys
Commercial Fishermen’s Association,
Freezer Longline Coalition, Garden State
Seafood Association, Hawaii Longline
Association, Humane Society of the
United States, Marine Mammal
Commission, Natural Resources Defense
Council, State of Hawaii, U.S. Fish and
Wildlife Service, Western Pacific
Regional Fishery Management Council,
and 6 individuals. Comments on issues
outside the scope of the LOF were
noted, but are generally not responded
to in this final rule.
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General Comments
Comment 1: An individual
commenter recommends NMFS inform
the U.S. Department of Defense (DOD)
of the LOF, NMFS, and MMPA. The
commenter further wondered whether
the Navy is also a contributor of injury
or death of animals listed on the LOF,
if the process is complying with
Advisory Council on Historic
Preservation Section 106, and, if so,
which Native Hawaiian Organizations
are involved.
Response: Certain military readiness
activities are subject to sections
101(a)(5)(A) and (D) of the MMPA,
which authorizes the Secretary of
Commerce to allow, upon request, the
incidental, but not intentional taking of
marine mammals subject to required
notifications and determinations.
However, the Navy is not subject to
section 118 of the MMPA, which
applies to commercial fisheries.
National Historic Preservation Act
(NHPA) section 106 generally requires
federal agencies to consult the
appropriate State Historic Preservation
Office (SHPO) and/or Tribal or Native
Hawaiian groups on undertakings,
including projects, activities, and
programs that may affect qualifying
historic properties. The LOF only
involves classification determinations
for commercial fisheries based upon
marine mammal interactions, and is not
a federal undertaking under the NHPA.
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Comment 2: The Marine Mammal
Commission (Commission)
acknowledges NMFS’ efforts for
summarizing and providing information
about observer coverage and other
characteristics of listed fisheries, and
commends NMFS for its efforts to
centralize information used to classify
Category III fisheries and looks forward
to seeing this effort come to fruition.
The Commission appreciates that NMFS
has considered their concerns and is
exploring ways to fully and effectively
convey the reasons for listing fisheries,
which must be based on the best
available information and may or may
not include observer-derived data.
Response: NMFS agrees that
summarizing the information used as
the basis to classify each fishery on the
LOF in one location could be useful for
interested readers. NMFS has posted
information on each Category I and II
fishery on the LOF on the NMFS Office
of Protected Resources Web site, where
it can be considered at the readers’
discretion, and is pleased the
Commission finds the information
useful while reviewing the LOF. NMFS
is developing similar fishery fact sheets
for each Category III fishery and
anticipates posting those fishery fact
sheets along with the final 2013 LOF.
However, due to the large number of
Category III fisheries on the LOF and the
lack of accessible and detailed
information on many of these fisheries,
this timeline may be revised as this
exercise progresses.
Comment 3: The Center for Biological
Diversity (CBD) notes that the proposed
2012 LOF once again includes
aquaculture operations as Category III
fisheries and reiterates comments on
past LOFs that aquaculture facilities are
not ‘‘commercial fishing operations’’
eligible for the take authorization
contained in Section 118 of the MMPA.
The CBD states that these operations
consistently compete with marine
mammals for habitat and resources due
to their stationary nature; therefore,
aquaculture facilities and activities are
more appropriately subject to the take
prohibitions and permitting regimes
contained in Section 101 of the MMPA.
Response: NMFS received similar
comments on the 2009 and 2010 LOFs.
Section 118 of the MMPA governs the
‘‘taking of marine mammals incidental
to commercial fishing operations.’’ The
MMPA does not provide a definition of
a commercial fishing operation;
therefore, NMFS defined ‘‘commercial
fishing operation’’ in regulations at 50
CFR 229.2. The definition was
presented in the proposed and final
rules implementing the regulations for
section 118 of the MMPA (60 FR 31666,
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June 16, 1995; 60 FR 65086, August 30,
1995). As noted in those proposed and
final rules, and in the responses to
comments on the 2009 and 2010 LOFs
(73 FR 73032, December 1, 2008,
comment/response 5; 74 FR 58859,
November 16, 2009, comment/response
11), the definition of a ‘‘commercial
fishing operation’’ includes aquaculture.
The regulations in 50 CFR 229.2 define
a ‘‘commercial fishing operation’’ as
‘‘the catching, taking, or harvesting of
fish from the marine environment
* * *. The term includes * * *
aquaculture activities.’’ Further,
‘‘fishing or to fish’’ is defined as ‘‘any
commercial fishing operation.’’
Therefore, aquaculture fisheries are
considered commercial fisheries that are
managed under section 118 of the
MMPA and are therefore included on
the annual LOF.
Comment 4: The CBD urges NMFS not
to reclassify fisheries to a less serious
category when information on the
fishery and its interactions with marine
mammals is scant. In these cases, the
CBD urges NMFS to instead rely more
heavily upon the known impacts of the
fishery’s gear and the marine mammals
known to inhabit the area being fished,
rather than relying, for example, on the
lack of reported interactions in fisheries
with little or no observer coverage. The
CBD states that every Federal FMP by
law must include ‘‘a standardized
reporting methodology to assess the
amount and type of bycatch,’’ and that
the ESA and MMPA make no exceptions
to protection on the basis of state versus
Federal fisheries. The CBD asserts that
failure to assess marine mammal
bycatch is an unacceptable justification
for denying marine mammals protection
via the LOF.
Response: NMFS considers a broad
range of information when proposing or
making fishery classification decisions
on the LOF, and does not classify
fisheries based solely on the presence or
absence of serious injuries or mortalities
obtained through observer programs.
Under regulations pursuant to section
118, NMFS uses observer data, logbook
data, stranding data, fishers’ reports,
anecdotal reports, qualitative factors
outlined in 50 CFR 229.2 (i.e., fishing
techniques, gear used, methods used to
deter marine mammals, target species,
seasons and areas fished, qualitative
data from logbooks or fisher reports,
stranding data, and the species and
distribution of marine mammals in the
area), information on incidental serious
injury or mortality to marine mammals
reported in SARs (50 CFR 229.2; 60 FR
45086, August 30, 1995; 60 FR 67063,
December 28, 1995), and input received
during the public comment periods.
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NMFS considers all of the information
to determine whether the fishery can be
classified on the LOF based on
quantitative information analyzed
through the Tier 1 and 2 analyses; or
whether the fishery can be classified on
the LOF based on the qualitative
information outlined in NMFS
regulations at 50 CFR 229.2 (and
presented above).
Comments on Commercial Fisheries in
the Pacific Ocean
Comment 5: The Freezer Longline
Coalition (FLC) recommends the ‘‘BSAI
Pacific cod longline’’ fishery be
reclassified as Category III because the
annual serious injury and mortality for
all stocks listed as killed or injured in
this fishery is less than 1 percent of PBR
for the most recent five-year period
(2004–2008). The FLC states that the
2010 SAR shows that there are no
serious injuries or mortalities of killer
whales (AK resident stock) or ribbon
seals from 2004–2008, and the mean
annual serious injury and mortality of
Steller sea lions (Western distinct
population segment) is 0.488 percent of
PBR; however, the fishery continues to
be classified as Category II based on
serious injury and mortality of resident
killers whales from 2002–2006. The FLC
asserts that the fishery should not
continue to be classified based on
outdated data simply because NMFS has
been unable to ‘‘finalize’’ data for 2007
and 2008, which is inconsistent with
the MMPA’s best available science
mandate, the Information Quality Act,
and NMFS’ associated guidelines.
Response: The classification of
fisheries for the proposed 2012 LOF was
based on the best available scientific
information at the time the fishery
classifications were made. In this case,
the most current available information
on serious injury and mortality of
marine mammals was presented in the
final 2010 SAR, which included an
analysis data from 2002–2006. More
recent data from a new analysis for the
2007–2010 period will be available for
use in classifying fisheries on the 2013
LOF. At that time, NMFS will consider
the information available from the new
analysis and consider a reclassification
for the BSAI Pacific cod longline
fishery, if appropriate.
Comment 6: The FLC asserts that the
estimated mortality reported in the
SARs for AK longline fisheries uses
incorrect observer coverage percentages,
resulting in significant overestimation of
mortality. The FLC further asserts that
the default recovery factors used for
multiple AK marine mammal stocks
need to be re-evaluated for populations
that are increasing, have a large
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population, or whose population status
is known.
Response: NMFS does not calculate
observer percentages or recovery factors
in the annual LOF, instead this
information is provided in the SARs
after NMFS and the Alaska SRG have
evaluated the information during their
annual review. Therefore, NMFS
suggests the FLC submit this comment
during the public comment period for
the draft 2011 SARs. Further, NMFS
responded to similar comments on the
2009 SARs and therefore refers the FLC
to that Federal Register notice for
additional information (75 FR 12498,
March 16, 2010; comment/response 13
and 16).
Comment 7: The Commission concurs
that the ‘‘CA thresher shark/swordfish
drift gillnet’’ fishery meets the criteria
for Category II and concurs with the
designation of the CA/OR/WA stock of
humpback whales as the basis for that
classification.
Response: NMFS acknowledges this
comment. The ‘‘CA thresher shark/
swordfish drift gillnet’’ fishery is
classified as Category II in this final
rule.
Comment 8: The Humane Society of
the United States (HSUS) supports the
elevation of the ‘‘CA thresher shark/
swordfish drift gillnet’’ fishery to
Category II. The HSUS notes that there
is a long-standing record of interactions
between drift gillnet fisheries and
protected species worldwide and feels it
is appropriate for NMFS to develop a
better understanding of this driftnet
fishery and the extent to which it
interacts with marine mammals through
use of observer coverage, which is more
likely for a fishery placed in Category II.
Response: NMFS acknowledges this
comment and notes that this fishery is
subject to requirements under the
Pacific Offshore Cetacean Take
Reduction Plan and is regulated under
the Fishery Management Plan for U.S.
West Coast Fisheries for Highly
Migratory Species, which authorizes
NOAA to place observers on fishing
vessels in west coast highly migratory
species fisheries (such as drift gillnet),
regardless of the LOF category.
Comment 9: The U.S. Fish and
Wildlife Service (USFWS) reiterated a
recommendation made on the 2011 LOF
to include southern sea otters on the list
of species/stocks killed or injured in the
Category III ‘‘CA spiny lobster trap’’ or
the ‘‘CA coonstripe shrimp, rock crab,
tanner crab pot or trap’’ fisheries
because experiments have shown that
sea otters can enter these traps and
drown. The USFWS provided a
publication by Hatfield et al. (2011) to
support this recommendation.
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Response: NMFS responded to a
similar comment on the 2011 LOF (75
FR 68475, November 8, 2010, comment/
response 13) and provided detailed
information on an extensive review of
marine mammal interactions with West
Coast trap and pot gear in the proposed
2009 LOF (73 FR 33760, June 13, 2008).
In 2008, NMFS Southwest Regional
Office (SWRO) consulted with experts
on marine mammals and pot/trap
fisheries including the NMFS Southwest
Fisheries Science Center, NMFS
Northwest Fisheries Science Center,
NMFS Northwest Regional Office, and
CA Department of Fish and Game
(CDFG) to evaluate which fisheries may
be affecting marine mammals. The
primary intent of the analysis was to
review interactions between trap/pot
gear and humpback whales, but all
marine mammals were addressed in the
review. During the 2008 review, the
only information available on southern
sea otter interactions with trap/pot gear
were stranding records of from 1987 and
1991 (2008 SAR; pers. comm. with staff
from CDFG). At that time, NMFS
determined that sea otters should be
removed from the list of species killed
or injured in the ‘‘CA spiny lobster trap’’
and the ‘‘CA coonstripe shrimp, rock
crab, tanner crab pot or trap’’ fisheries
because the information was
approximately 20 years old and there
had been no indications of interactions
since that time. NMFS SWRO continues
to consult with NMFS and CDFG
specialists regarding marine mammal
interactions with trap/pot gear. NMFS
has not received additional information
since 2008 to suggest that southern sea
otters are currently being incidentally
killed or injured in pot and trap gear.
As part of their public comment, the
USFWS submitted a paper by Hatfield et
al. (2011), detailing experiments that
indicate sea otters can enter and become
entrapped in traps with openings of
certain sizes. However, this paper
presented no evidence of such takes
occurring during commercial fishing
activities off CA. The possibility of an
interaction is insufficient justification to
include southern sea otters on the list of
species incidentally injured or killed in
the ‘‘CA spiny lobster trap’’ or the ‘‘CA
coonstripe shrimp, rock crab, tanner
crab pot or trap’’ fisheries. Instead,
NMFS needs some indication that takes
are occurring or have occurred in these
fisheries in recent years (e.g., fisher self
reports, observer data, stranding data). If
additional information becomes
available to indicate that southern sea
otters have been injured or killed in CA
trap/pot fisheries in recent years, NMFS
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will consider including this species on
the LOF at that time.
Comment 10: The Hawaii Longline
Association (HLA) believes that the
abundance estimate for the false killer
whale (pelagic stock) is not
scientifically sound and, because the
survey data used for that abundance
estimate was collected in 2002, that
NMFS is using data it knows to be stale
to make LOF determinations for the
2012 LOF (as defined by NMFS
guidelines). The HLA views these errors
to be particularly acute because NMFS
completed a new marine mammal
survey in the Hawaiian EEZ in 2010;
however, this current, available data are
not the data upon which the proposed
2012 LOF is based. Therefore, the HLA
asserts that if the 2012 LOF is issued as
proposed (i.e., not based on the 2010
data), it would violate the MMPA’s
‘‘best available science’’ mandate.
Response: NMFS used the best
available science in preparing the 2012
LOF. Proposed changes to the 2012 LOF
were developed in spring and summer
2011, and were largely based on the
draft and final 2010 SARs, which were
the most recent SARs available. NMFS
conducted a new cetacean assessment
survey in the U.S. EEZ around the
Hawaiian Islands (HICEAS II) in
August–December 2010, with the goal of
updating abundance estimates for all
Hawaiian cetaceans. The survey data are
currently being analyzed, and
abundance estimates and PBR
calculations based on the data are not
yet available. Preliminary estimates of
abundance based on the visual sightings
data will be included in the draft 2012
SAR, which is expected to be published
and available for public review and
comment in spring 2013. The acoustic
and other data collected during the
survey will take longer to analyze, and
abundance estimates will likely be
revised in future SARs to incorporate
the new analysis. The currently
available data and estimates still
constitute the best available information
within existing NMFS parameters and
therefore are appropriately included in
the final 2010 SARs, draft 2011 SARs,
and the 2012 LOF.
Comment 11: The Western Pacific
Fishery Management Council (Council)
and the HLA both recommend that the
‘‘HI shallow-set (swordfish target)
longline/set line’’ fishery be classified as
a Category III. The Council and the HLA
note that this fishery is classified as
Category II based on one serious injury
of a bottlenose dolphin (HI stock) within
the HI EEZ. The commenters note that
the only other fishery to have incidental
serious injury or mortality of this stock
is the ‘‘HI deep-set (tuna target)
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longline/set line’’ fishery, and the
combined serious injury and mortality
rate for these two fisheries is less than
10 percent of PBR. The Council and
HLA further note that the analysis for
fishery classification places all fisheries
interacting with a stock in Category III
if the total interaction rate is equal to or
less than 10 percent of the PBR unless
a fishery qualifies for another Category
for a different stock; however, no other
marine mammal stock qualifies the HI
shallow-set fishery for Category I or II.
Response: NMFS concurs that, based
on the marine mammal interactions
within the U.S. EEZ reported in the final
2010 SAR, the shallow-set longline
fishery would meet the definition of a
Category III fishery. There are no marine
mammal stocks within the EEZ that
have mortality and serious injury that
exceed 10 percent of PBR across all
fisheries and that individually exceed 1
percent of PBR in the shallow-set
fishery. However, there are documented
injuries and mortalities of numerous
species and stocks of marine mammals
by the shallow-set longline fishery on
the high seas, which are listed in Table
3 for the high seas component of the
shallow-set longline fishery (‘‘Western
Pacific Pelagic (HI Shallow-set
component)’’). Because there currently
are no abundance estimates or PBRs
available for most of these marine
mammal stocks on the high seas,
quantitative comparison of mortality
and serious injury against PBR is
currently not possible.
MMPA regulations (50 CFR 229.2)
provide that in the absence of reliable
information indicating the frequency of
incidental mortality and serious injury
of marine mammals by a commercial
fishery, NMFS will determine whether
the incidental serious injury or
mortality is ‘‘occasional’’ by evaluating
other factors such as fishing techniques,
gear used, methods used to deter marine
mammals, target species, seasons and
areas fished, qualitative data from
logbooks or fisher reports, stranding
data, and the species and distribution of
marine mammals in the area, or at the
discretion of the Assistant
Administrator. HI-based shallow-set
fishing vessels operating within the U.S.
EEZ and on the high seas employ the
same vessels, the same fishing methods
and gear, target the same fish stocks,
and employ the same marine mammal
mitigation and deterrence measures. A
review of NMFS observer data indicates
that approximately 7 percent of shallowset trips from 2004–2008 had marine
mammal interactions, including
interactions with Bryde’s whale, Risso’s
dolphin, humpback whale, striped
dolphin, bottlenose dolphin, and Kogia
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sp. whale (pygmy or dwarf sperm
whale). The number and rate of marine
mammal interactions increased each
year in that 5-year timeframe. Of the 22
total marine mammal interactions
observed on 325 shallow-set trips from
2004–2008, 19 were taken on the high
seas. Seventeen of the total 22 observed
interactions resulted in mortality or
serious injury, 16 of which occurred on
the high seas (Forney, 2010; NMFS
Pacific Islands Regional Observer
Program, 2004–2008). Although NMFS
is currently unable to quantitatively
establish the impact of these
interactions on high seas marine
mammal stocks because of the lack of
population information, these
interactions do provide qualitative
evidence that the shallow-set fishery
continues to have ‘‘occasional’’
interactions with marine mammals and
should remain a Category II commercial
fishery.
As noted in the preamble of the
proposed 2012 LOF and the response to
a comment in the final 2010 LOF (74 FR
58859, November 16, 2009; comment/
response 17) regarding high seas
fisheries classification, the high seas
portion of the shallow-set longline
fishery is an extension of the fishery
operating within U.S. waters, and is not
a separate fishery. A fishery is classified
on the LOF as its highest level of
classification (e.g., a fishery qualifying
for Category II for one marine mammal
stock and Category III for another
marine mammal stock will be listed as
Category II). Because the ‘‘Western
Pacific Pelagic (HI Shallow-set
component)’’ and ‘‘HI shallow-set
(swordfish target) longline/set line’’ are
two components of the same fishery,
both components are classified as
Category II.
The Category II classification is
further supported by data in the draft
2011 SAR, which was not available
when the proposed 2012 LOF was
drafted. The draft 2011 SAR reports an
observed serious injury to a false killer
whale in the shallow-set fishery within
the U.S. EEZ in 2009. Based on one
observed non-serious injury in 2008 and
one observed serious injury in 2009, the
shallow-set fishery has an average
annual mortality and serious injury rate
of 0.2 HI pelagic false killer whales per
year within the EEZ. This represents
approximately 8 percent of the stock’s
PBR level, which also qualifies it as a
Category II fishery.
Comment 12: The HLA disagrees with
the addition of the insular stock of false
killer whales to the list of stocks
incidentally injured or killed in the ‘‘HI
deep-set (tuna target) longline/set line’’
fishery because the inclusion is based
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on NMFS’ proration of an isolated nonserious interaction between this
fishery’s insular stock and pelagic stock
interaction rate, which is not based on
the best available science. The HLA
asserts that this fishery has never been
observed to interact with the insular
stock and that the interaction in
question occurred in an area where no
member of the insular stock has ever
been observed in or near, and that
NMFS has no genetic evidence showing
that the deep-set fishery has ever
interacted with a member of the insular
stock. The HLA also disagrees with
NMFS’ extension of the 140 km insular
stock ‘‘range’’ uniformly around the
MHI based on a single tagged animal
over 100 km to the south of the MHI.
Response: NMFS determines which
species or stocks are included as
incidentally killed or injured in a
fishery by annually reviewing the
information presented in the current
SARs, among other relevant sources.
The SARs are based on the best
available scientific information and
provide the most current and inclusive
information on each stock, including
range, abundance, PBR level, and level
of interaction with commercial fishing
operations. The LOF does not analyze or
evaluate the SARs. The commenter
questions the validity of the data and
calculations contained within the SAR
for false killer whales; and, thus, NMFS
encourages the commenter to submit
this comment during the public
comment period for the draft SAR.
The draft 2011 SAR for false killer
whales indicates an average of 0.6
mortalities or serious injuries of HI
insular false killer whales per year
incidental to the HI-based deep-set
longline fishery. One non-serious injury
to a false killer whale was observed
within the overlap zone between the HI
insular and HI pelagic stocks of false
killer whales. In the SAR, all estimated
takes, and observed takes for which an
injury severity determination could not
be made, were prorated based on the
proportions of observed interactions
that resulted in death or serious injury,
or non-serious injury between 2000–
2009. Further, takes of false killer
whales of unknown stock origin within
the insular/pelagic stock overlap zone
were prorated assuming that the density
of the insular stock declines and the
density of the pelagic stock increases
with increasing distance from shore. No
genetic samples are available to
establish stock identity for these takes,
but both stocks are considered at risk of
interacting with longline gear within
this region.
Additionally, the draft 2011 SAR
reports that from 2005–2009, eight
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unidentified cetaceans, known to be
either false killer whales or short-finned
pilot whales (together termed
‘‘blackfish’’) were seriously injured in
the deep-set longline fishery within U.S.
EEZ waters, two of which were taken
within the insular stock range. The draft
2011 SAR prorates blackfish to each
species and stock based on their
distance from shore (see McCracken,
2010 for details on the distance-fromshore model).
For these reasons, NMFS is not
changing its proposal to add the HI
insular stock of false killer whales on
the list of marine mammal stocks
incidentally killed or injured in the HI
deep-set longline fishery. For a more
complete analysis of the methodology
for determining mortality and serious
injury of insular and pelagic false killer
whales, the commenter is referred to the
draft 2011 SAR.
Comment 13: The CBD recommends
NMFS classify ‘‘American Samoa
longline’’ fishery as Category I based on
analogy to the ‘‘HI deep-set (tuna target)
longline/set line’’ fishery, interactions
with false killer whales, and
interactions with rough-toothed
dolphins, citing three arguments. First,
CBD notes that NMFS has proposed to
require longline hooks in this fishery are
set at depths of 100 meters or deeper to
reduce interactions with Pacific green
sea turtles (76 FR 32929, June 7, 2011),
which will make the gear and methods
like the Category I Hawaii deep-set
longline fishery. Second, CBD asserts
that even though abundance estimates
are unavailable for the American Samoa
false killer whale stocks, the humancaused mortality falls within the range
of likely PBRs for both of these marine
mammal stocks and the 2010 SAR
concludes that the false killer whales in
American Samoa would probably be
strategic if abundance estimates were
available. Lastly, CBD notes that this
fishery also interacts with the American
Samoa stock of rough-toothed dolphins,
for which the 2010 SAR indicates the
estimated rate of fisheries-related
mortality or serious injury (3.6 dolphins
per year) is within the range of likely
PBRs (3.4–22).
Response: Abundance estimates for
the American Samoa stocks of false
killer whales and rough-toothed
dolphins are unknown, and PBRs
cannot be calculated. The final 2010
SARs present a plausible range of
abundance estimates for each stock
based on density estimates of the
species in other areas of the Pacific, and
calculate a range of likely PBRs using
those ranges of abundance. The SARs
further note that estimated mortality
and serious injury of false killer whales
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exceeds the range of the stock’s likely
PBRs, and mortality and serious injury
of rough-toothed dolphin falls within
the range of the stock’s likely PBRs.
These estimates provide an indication
that cetacean bycatch in the fishery is
not insignificant. However, without an
actual calculation of PBR, NMFS cannot
accurately evaluate the effect of
mortality and serious injury on the
stocks to determine whether the fishery
meets the definition of a Category I
fishery. Under NMFS regulations, a
Category I is one that cause frequent
mortality or serious injury of marine
mammals, which is defined as ‘‘one that
is by itself responsible for the annual
removal of 50 percent or more of any
stock’s potential biological removal
level’’ (50 CFR 229.2). Only in the
absence of reliable information
indicating the frequency of incidental
mortality and serious injury of marine
mammals does NMFS consider other
factors that may be used to classify the
fishery as either Category II or III,
including evaluation of fishing
techniques, gear used, methods used to
deter marine mammals, target species,
seasons and areas fished, qualitative
data from logbooks or fisher reports,
stranding data, and the species and
distribution of marine mammals in the
area, or at the discretion of the Assistant
Administrator (50 CFR 229.2). Until
quantitative information is available to
allow a calculation of PBR, NMFS will
retain the American Samoa longline
fishery as Category II, by analogy to
other longline fisheries.
Comment 14: The CBD recommended
NMFS classify the ‘‘HI vertical longline’’
and ‘‘HI kaka line’’ fisheries as Category
I based on serious injury and mortality
of false killer whales (HI insular stock),
which is proposed to be listed as
endangered under the ESA (75 FR
70169, November 17, 2010). The CBD
notes that the ESA scientific Biological
Review Team (BRT) for this stock found
a high level of current and future risk
from interactions with troll, handline,
shortline, and kaka line fisheries (Id. at
70180), and the BRT stated that
although ‘‘each of these fisheries is
required by law under the MMPA to
report interactions with marine
mammals, the low number of reports
strongly suggests that interactions are
occurring and are not being reported’’
(Id. at 70179). Lastly, the CBD asserts
that a high level of anecdotal evidence,
including fishermen that have reported
shooting at false killer whales and a
high rate of dorsal fin disfigurements
consistent with injuries from
unidentified fishing line, and the fact
that the State of HI does not monitor
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bycatch of marine mammals in any of its
state fisheries, also suggest that the
fisheries are having a greater impact
than is reported. Therefore, the CBD
asserts that the scientific information
and opinion show that fisheries
interactions present a high risk of
extinction to the insular false killer
whale, compelling NMFS to list these
fisheries as Category I, especially in
light of what appears to be deliberate
efforts to obscure fishery mortality in
order to prevent further protection for
an endangered marine mammal.
Response: At this time, there is no
quantitative information to support a
Category I classification for either of
these fisheries. As stated in the response
to comment 13, a Category I fishery is
one that NMFS determines has frequent
incidental mortality and serious injury
of marine mammals, defined as one that
is, by itself, responsible for the annual
removal of 50 percent or more of any
stock’s PBR level (50 CFR 229.2). NMFS
considers other factors when
determining whether a fishery meets the
definition of a Category II or III fishery,
including evaluation of fishing
techniques, gear used, methods used to
deter marine mammals, target species,
seasons and areas fished, qualitative
data from logbooks or fisher reports,
stranding data, and the species and
distribution of marine mammals in the
area, or at the discretion of the Assistant
Administrator (50 CFR 229.2).
Currently, NMFS does not have reliable
information that either of these fisheries
causes frequent incidental mortality and
serious injury of marine mammals, such
that would support classification of a
Category I fishery, as that term is
defined. Based on the currently
available information, NMFS continues
to believe that these two fisheries
present a remote likelihood of
interactions with marine mammals.
NMFS is retaining these fisheries on the
LOF as Category III fisheries but will
consider any information that supports
a reevaluation of the fisheries’
classification in the future.
Comment 15: The CBD comments that
the various fisheries that are known or
suspected of interacting with Hawaiian
monk seals should be classified as
Category I because, given the critically
endangered status of the monk seal, any
interaction is significant. The CBD notes
that fishery interactions are becoming
more common (Baker et al., 2011), yet
all Hawaiian fisheries known or
suspected of interactions with monk
seals, such as the Hawaii lobster trap
and the Hawaii tuna handline, are listed
as Category III. Further, the CBD asserts
that, while a PBR is not calculated for
this stock (final 2010 SAR), any
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mortality from fisheries would qualify
the fishery for Category I if a PBR was
calculated.
Response: The LOF lists the Hawaiian
monk seal on the list of species and
stocks incidentally killed or injured in
the Category III ‘‘HI lobster trap’’ and
‘‘HI Main Hawaiian Islands (MHI) deep
sea bottomfish handline’’ fisheries. In
the 2009 LOF, NMFS removed the
Hawaiian monk seal from the list of
species/stocks killed/injured in the ‘‘HI
tuna handline fishery,’’ under which the
stock had been listed since the 1996
LOF, because NMFS has never received
a report of interactions between monk
seals and tuna handline gear. The
available information on Hawaiian
monk seal interactions with the other
two fisheries is:
(1) ‘‘HI lobster trap’’ fishery: There
have not been any reported interactions
since the mid-1980s, when one seal died
in a trap; and
(2) ‘‘HI Main Hawaiian Islands deep
sea bottomfish handline fishery:’’ A
Federal observer program of the
Northwestern Hawaiian Islands (NWHI)
bottomfish handline fishery was
conducted from the fourth quarter of
2003 through 2005, and no monk seal
interactions were observed. The fishery
has since been phased out as required
under the Proclamation establishing the
Papahanaumokuakea Marine National
Monument. While fishing in the NWHI
has been phased out, in previous years
when commercial bottomfish boats were
fishing in this area, NMFS received one
self-reported incident (a hooking in
1994), and bottomfish hooks were
observed in two seals at the French
Frigate Shoals (one in 1982 and one in
1993). NMFS also had reports from the
mid-1990s of seals stealing catch, seals
being fed bait or non-target species by
fishermen to discourage seals from
taking catch, and some seals becoming
hooked and cut free. The final 2010 SAR
notes that no mortality or serious
injuries have been attributed to the MHI
deep sea bottomfish handline fishery.
While there have been no observed or
reported interactions between monk
seals and the ‘‘HI lobster trap’’ and ‘‘HI
Main Hawaiian Islands deep sea
bottomfish handline’’ fisheries in recent
years, NMFS has retained Hawaiian
monk seals as a species or stock
incidentally killed or injured in these
fisheries because monk seals in the
MHIs are hooked and entangled but at
a rate that has not been reliably assessed
(final 2010 SAR). NMFS cannot confirm
whether seals have been hooked on
commercial or recreational gear, or a
combination of both. However, NMFS
consultations completed under the ESA
section 7 found the MHI federal
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bottomfish fishery and the MHI federal
lobster trap fishery were not likely to
adversely affect Hawaiian monk seals
(NMFS 2008a, 2008b). Finally, the PBR
level for monk seals is currently
‘‘undetermined,’’ and NMFS is unable
to make a quantitative evaluation of
incidental mortality and serious injury
compared to PBR. Due to the fact that
the PBR level for monk seals is
undetermined and the hooking and
entanglement rate with commercial gear
cannot be reliably assessed, NMFS will
retain the ‘‘HI lobster trap’’ and ‘‘HI
Main Hawaiian Islands deep sea
bottomfish handline’’ fisheries as
Category III fisheries on the LOF until
more information becomes available to
determine whether reclassification is
warranted.
Comments on the Hawaii Troll and
Charter Vessel Fisheries
NMFS received 10 comment letters
addressing the proposed reclassification
of the Hawaii trolling and charter vessel
fisheries, four of which supported the
proposal and six of which did not
support the proposal. Generally, the
comments focused on the following
issues: (1) Concern regarding the use
and quality of anecdotal reports of
marine mammal interactions in the
fisheries; (2) NMFS’ use of quantitative
versus qualitative information; (3)
NMFS’ estimation of commercial fishing
effort ‘‘fishing on’’ dolphins; (4) the
frequency of marine mammal
interactions in the fisheries; (5) the
severity of injuries sustained by marine
mammals; (6) the PBR level for
Pantropical spotted dolphins; (7) bait
depredation by other dolphin species in
these fisheries; (8) support for better
understanding fishery interactions in HI
and prioritization of a fishery observer
program to better inform management;
(9) the burden to the State of HI for
mailing marine mammal Authorization
Certificates to Category II fishery
participants; and (10) the potential for
the fisheries’ elevation to lead to
increased illegal fishing. Below, NMFS
summarizes each comment received on
the 2012 proposed LOF related to the HI
troll and charter vessel fisheries and
issues one response following the
collective comments.
Comment 16: Three individual
commenters, the Council, and the State
of HI assert that NMFS should not use
anecdotal reports of hookings as
evidence or support for management
decisions, given their lack of
verification and details, nor should they
be used to extrapolate mortality and
serious injury to the entire fleet. An
individual commenter notes that the use
of such anecdotal reports does not
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constitute objective and thorough
science, and the Council suggests that
NMFS develop a standard in using
anecdotal reports in rulemaking to
require verification and ensure
decisions are based on the best available
science. Further, the author of the
newspaper article NMFS considered
(Rizutto, 2007) commented that NMFS
should not rely on his newspaper article
for purposes of elevating the fisheries,
that the instance described in the article
was based on a third-hand account, and
that he reported on this one instance
because he believed it to be a rare event.
Comment 17: Four commenters
address NMFS’ use of quantitative
versus qualitative data in drawing
conclusions regarding the frequency of
fishery interactions with spotted
dolphins. The Council states that NMFS
did not provide an upper limit of
estimated mortality and serious injury,
so there was not sufficient information
to establish that collective fishery
impacts exceeds 10 percent of PBR (Tier
1 analysis). Three commenters note the
lack of quantitative data on the
frequency of marine mammal
interactions in the fisheries, and pointed
to MMPA implementing regulations that
instruct NMFS to evaluate other factors
to determine the level of interactions
when quantitative information is not
available. The NRDC notes that the
regulations also allow NMFS to consider
other evidence at its own discretion.
These three commenters concluded that
the available qualitative data indicate a
strong likelihood of occasional
interactions, and the Commission stated
that, until quantitative data are available
on marine mammal takes from observer
or other programs, the fisheries should
be Category II.
Comment 18: Six commenters provide
information on patterns of fishing effort
in these fisheries. The Council, the State
of HI, and two individual commenters
suggest that NMFS overestimated the
level of commercial fishing effort
‘‘fishing on’’ dolphins; i.e., where
vessels congregate on and deploy lines
in close proximity to dolphins. The
Council and two individual commenters
assert that the majority of participants in
these fisheries do not target tunas
associated with, or fish within spotted
dolphin pods, and an individual
commenter noted that those who do,
fish ‘‘in front of’’ not ‘‘on’’ dolphins,
and that fishing around dolphins is only
known to occur in two locations off the
Big Island and Oahu. The State of HI
noted that many commercial vessels fish
part-time, and much of the effort is
seasonal when there is a run of tuna.
The State of HI also commented that
many of those vessels observed trolling
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around dolphins may be noncommercial. The Council expresses
concern that NMFS’ account of Dr.
Robin Baird’s sightings rate of vessels
‘‘fishing on’’ spotted dolphins is skewed
to produce a high result.
Dr. Baird asserts that his estimate of
the percentage of spotted dolphin
groups that had fishing vessels present
is negatively biased (i.e., is likely more
than the percentage NMFS cites in
proposed rule). He states that beginning
in 2008, his research group began
avoiding clusters of fishing vessels in
their surveys to reduce the likelihood of
encountering spotted dolphin groups at
rates higher than would be expected
given their presence in the area. As
such, he states that in the last three
years, he has been more likely to
encounter groups that do not have
fishing vessels present. Dr. Baird
commented that observations of troll
fishing vessels included up to eight
vessels actively targeting dolphin pods,
with multiples lines trailing hooks being
trolled through the dolphins repeatedly.
The Natural Resources Defense Council
(NRDC) notes that this often occurred
for several hours, at speeds up to 10
knots. The NRDC states that the degree
of targeted fishing effort alone suggests
the likelihood of incidental mortality or
serious injury is not ‘‘remote.’’
Comment 19: The Council, the State
of HI, the NRDC, and two individual
commenters address the frequency of
incidental interactions with Pantropical
spotted dolphins in the HI troll and
charter vessel fisheries. The Council, the
State of HI and two individuals suggest
that fishery interactions with
Pantropical spotted dolphins are a rare
event, the frequency is lower than
NMFS estimated, and these fishery
interactions are therefore not a
conservation concern. One individual
commenter cites experience fishing with
these methods and never having hooked
a dolphin, that they are not drawn to the
lures or bait, and having only heard of
one hooked dolphin that was hooked in
the tail and released alive. The State of
HI provides license and trip report data
that indicate infrequent (0.25 percent of
trips annually) reporting of catch lost to
dolphin predation, and suggested the
frequency at which dolphins are
seriously injured fall below these
percentages. The State of HI also states
that NMFS applied assumptions that
likely resulted in an overestimate of
projected take levels.
The NRDC and an individual
commenter suggest that interactions or
the risk of interactions are likely higher
than NMFS estimated, or at least do not
qualify as ‘‘remote.’’ Dr. Baird describes
his conversations with four HI
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fishermen, two of whom reported they
had hooked spotted dolphins, and noted
that spotted dolphins feed on flying fish
near the surface during the day,
increasing the potential for interactions
with fishers. Finally, the NRDC states
that the degree of targeted fishing effort
alone suggests that the likelihood of
incidental mortality and serious injury
is not ‘‘remote,’’ which is required for a
Category III fishery.
Comment 20: The Council and one
individual commenter disagree with
NMFS’ determination that dolphins
interacting with the troll and charter
fisheries likely suffer serious injuries.
One individual commenter notes that
the reported dolphin was hooked in the
mouth, was treated gently and cut loose
without suffering the stress of being
brought close to the boat. The Council
asserts that NMFS ignored anecdotal
information about dolphins surviving
and recovering from these interactions,
and that not all hookings result in the
removal of the animal from the
population. The Council also notes that
the dolphins’ injuries described in the
proposed rule cannot be attributed to
fishing vessels, and scarring shows that
animals can survive and recover from
such incidents.
Comment 21: The NRDC, the HSUS,
and two individual commenters address
the Pantropical spotted dolphin’s PBR
level. One individual commenter states
that the PBR for the affected Pantropical
spotted dolphin stock is
underestimated. One individual
commenter asserts that the abundance
survey, the basis for the abundance
estimate, was not designed to assess the
dolphin population being impacted,
evidenced by the low number of spotted
dolphin sightings and the high CV.
However, Dr. Baird says that the CV for
the abundance estimate (upon which
PBR is based) is the fifth lowest of all
18 species for which abundance was
estimated from the 2002 survey,
reflecting low density in Hawaiian
waters. Dr. Baird, the NRDC, and the
HSUS state that NMFS’ SAR indicates
the stock may be split into multiple
island-associated stocks in the future
pursuant to new genetic studies, so PBR,
especially for the population around the
Big Island where the largest share of
charter fishing occurs, is likely to be
smaller than the current PBR for the
single defined stock.
Comment 22: The Council comments
that NMFS ignored the information in a
newspaper article (Rizzuto, 2007)
regarding other dolphin species (roughtoothed and bottlenose) depredating on
bait in these fisheries. The Council
claims that NMFS has made selective
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and arbitrary use of anecdotal
information.
Comment 23: The HSUS comments
that they were pleased to see a proposal
for better understanding fishery
interactions in Hawaii where marine
mammal stock structure, abundance,
and fishery interactions have long been
ignored or accorded a lower priority
than appropriate, and notes that the
reclassification allows for a targeted
observer program, which will provide
data to better inform management.
Comment 24: The State of HI is
concerned that since NMFS does not
possess a database of commercial
fishermen in HI, the proposed elevation
of the ‘‘HI charter vessel’’ and ‘‘HI
trolling, rod and reel’’ fisheries would
place a significant administrative
burden on the State for mailings of the
MMAP authorization certificate to the
more than 2,000 state-registered fishers.
Further, the State of HI notes that it
continually receives new applications
for licenses during the year; however,
NMFS only issues MMAP certificates at
the beginning of the calendar year.
Comment 25: The State of HI states
that NMFS must consider the potential
for fishermen who are now licensed in
the ‘‘HI charter vessel’’ and ‘‘HI trolling,
rod and reel’’ fisheries to refuse to
renew their Commercial Marine
Licenses because of the requirements
associated with participating in a
Category II fishery, and if they continue
to fish, may market their catch illegally.
The State of HI asserts that this would
reduce reportings to the State’s licensing
and reporting system, which NMFS
relies on to manage fisheries.
Comment 26: The Council is
concerned that NMFS apparently
applies an arbitrary standard in
determining fishery classifications and
requests NMFS standardize any
inconsistent analysis and
determinations across regions. The
Council observes that the proposed 2012
LOF includes seven Category III troll
fisheries in the Pacific and several other
Category III fisheries in the Atlantic that
presumably include troll fisheries;
however, the only proposed elevation to
Category II is for the HI troll fishery. The
Council argues that if gear type, fishing
techniques, and anecdotal reports are
sufficient to elevate one fishery to
Category II, then all other troll fisheries
in the Pacific and Atlantic, by the
method of analogy, should also be
analyzed for similar elevation. Further,
the Council argues that where data and
anecdotal reports of interactions (e.g.,
depredation) are available for other
fisheries, those fisheries should also be
evaluated to determine whether they
meet the criteria for Category II.
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Response: NMFS proposed to elevate
the ‘‘HI trolling, rod and reel’’ and ‘‘HI
charter vessel’’ fisheries based on a suite
of information, including NMFS reports,
Western Pacific Regional Fishery
Management Council reports, input
from staff in the Pacific Islands Regional
Office’s Sustainable Fisheries Division,
reports to the Pacific SRG, the SARs,
consideration of the fishing gear and
techniques of the fishery and the
documented risk that they present to
marine mammals, anecdotal reports
from researchers, including researcher
observations and researcher’s
discussions with fishermen, and
information from a newspaper article
(Rizzuto, 2007) (see 76 FR at 37720–
37721, June 28, 2011). NMFS clarifies
that the Agency does not rely
exclusively on anecdotal reports of
marine mammal interactions to support
reclassifications of fisheries, but rather
considers anecdotal information when it
has been sufficiently corroborated by
other sources of information.
As a result of the proposal to elevate
the ‘‘HI trolling, rod and reel’’ and ‘‘HI
charter vessel’’ fisheries from Category
III to Category II, NMFS received an
abundance of information from the
public. This information, which is
summarized in the comments 16–26
above, provides NMFS with new
information the Agency had not been
aware of or considered when proposing
to elevate these fisheries to Category II.
In support of the proposed elevation,
NMFS received evidence that may
further corroborate the anecdotal reports
of hookings reported by fishermen to
researchers (comment 19), including
direct observations and a videotape of
troll and charter vessel operations in
close proximity to spotted dolphins
(information provided after the
comment period had closed). At the
same time, NMFS received multiple
comments suggesting that elevation may
not be warranted. First, multiple
commenters provided information to
suggest NMFS may have overestimated
the distribution and level of commercial
fishing effort ‘‘fishing on’’ dolphins
(comment 16). Second, the State of HI
provided license and trip report data
that indicate infrequent reporting of
catch lost to dolphin predation, which
suggests the frequency at which
dolphins are seriously injured may fall
below the projected take estimates
provided by NMFS in the proposed rule
(comment 18). Third, the author of the
newspaper article NMFS considered
(Rizutto, 2007) commented that NMFS
should not rely on his newspaper article
for purposes of elevating the fisheries,
that the instance described in the article
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was based on a third-hand account, and
that he reported on this one instance
because he believed it to be a rare event
(comment 16).
Based on the information described in
comments 16–26 and summarized in the
previous paragraph, it is apparent that
certain pieces of the new information
seem to indicate a Category II
classification is not warranted, while
other pieces of new information seem to
indicate a Category II classification is
warranted. Therefore, NMFS needs
additional time to consider and
investigate the information provided by
the public commenters to better
understand the nature and level of
interactions between these fisheries and
Pantropical spotted dolphins. For this
reason, NMFS is not elevating the ‘‘HI
trolling, rod and reel’’ and ‘‘HI charter
vessel’’ fisheries to Category II or adding
Pantropical spotted dolphins to the list
of species or stocks killed or injuries in
these fisheries in this final rule. Instead,
over the next year NMFS will continue
to review the information received from
the public, along with the information
on which the initial proposed fishery
elevations were based (see 76 FR
at37720–37721, June 28, 2011), and will
propose to elevate the ‘‘HI trolling, rod
and reel’’ and ‘‘HI charter vessel’’
fisheries to Category II on the 2013 LOF,
if warranted.
Comments on Commercial Fisheries in
the Atlantic Ocean, Gulf of Mexico and
Caribbean
Comment 27: The Garden State
Seafood Association submitted four
questions regarding the spatial
boundary NMFS uses to separate
fisheries in the northeast from the midAtlantic, including: (1) What is the
Agency’s justification for the spatial
boundary of 70° west long. separating
the northeast and mid-Atlantic?; (2)
What purpose does the clarification of
the boundary serve?; (3) How does the
spatial boundary impact the bycatch
analysis and the estimates?; (4) If
bycatch incidents are attributed to a
directed fishery, what is the purpose of
the spatial boundary?
Response: NMFS’ justification
originates from the review of the
northeast Fishing Vessel Trip Report
(VTR) data, as stated in the language for
the proposed change. Spatial data from
fishing effort reported on VTR’s were
used in conjunction with our current
state of knowledge regarding ecosystem,
habitat, spatial, and temporal
characteristics associated with marine
mammal stock distributions. This
information in aggregate was used to
define the Northeast and Mid-Atlantic
regions for the purpose of estimating
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bycatch of marine mammals in trawl
gear. The clarification was made to
provide more detail on the spatial
boundary and report to the public that
it is consistent with how scientists at
the NEFSC define the fishery. The
clarification of the spatial boundary will
have no impact on the bycatch analyses
as the NEFSC has been using the
reported spatial boundary since 2006
when the Atlantic Trawl Gear Take
Reduction Team was first convened.
Bycatch incidents of marine mammals
are not attributed to a directed fishery.
Marine mammal bycatch rates are
estimated by gear type operating within
the defined spatial strata. The Northeast
and Mid-Atlantic regions essentially
perform as spatial strata that can be
further stratified by temporal and/or
environmental parameters that show
strong correlation with bycatch events
(Rossman, 2010).
Comment 28: In addition to providing
the estimated number of vessels in a
particular fishery in the annual LOF,
which NMFS acknowledges is
‘‘inflated,’’ the Garden State Seafood
Association asks why NMFS does not
also provide the number of vessels
reporting landings in a particular fishery
per year, because it would be
informative for the public to see the
difference?
Response: After investigating the use
of landings data as an indicator of active
fishery participants, NMFS has
determined that landings databases that
include state fisheries do not always
record unique values or permit
information that would result in
differentiating one fishery participant
from another. This may have a
significant impact on estimating the
number of active vessels or permit
holders, though it is not clear whether
or not these numbers would represent
inflations or deflations of actual effort.
While the numbers provided in Table 2
may be inflated compared to actual
effort, they do represent potential effort.
NMFS feels this use is appropriate for
the purposes of the List of Fisheries
given that this information is used
solely for descriptive purposes and not
used in determining current or future
management of fisheries, observer
coverage designations, or bycatch rates.
Comment 29: The Commission
recommends that NMFS work on its
own and in collaboration with states to
develop new, consistent methods for
estimating fishing effort for several
Southeast Atlantic, Mid-Atlantic, and
New England fisheries because fisheries
managers should have clear measures of
effort for the fisheries they manage. The
Commission understands, based on
NMFS’ responses to previous
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recommendations on this issue, that the
newly proposed numbers of estimated
vessels/participants in these fisheries
are intended to reflect potential effort
(given that not all permitted fishermen
fish), and that ‘‘a clear measure of effort
for all state fisheries in the Northeast
and Mid-Atlantic has not been
determined due to the manner in which
many state permits allow for the use of
multiple gear types’’ (75 FR 68478, June
28, 2011). However, although NMFS has
tried to reassure the Commission that
these great fluctuations in vessel/person
numbers have no management or
observer implications, the Commission
remains concerned about the
uncertainty conveyed by these numbers.
Response: As stated in the Final 2011
LOF, Table 2 represents a description of
each fishery including the estimated
number of persons/vessels active in the
fishery. Currently, a clear measure of
effort for all state fisheries has not been
determined due to the way many state
permits allow for the use of multiple
gear types. Therefore, NMFS has
determined that this portion of the table
will be representative of current permit
holders, state and federal, that have the
potential to participate in a particular
fishery. As stated in the proposed LOF,
NMFS recognizes there may be disparity
between permit holders listed and
actual fishery effort; however, the
numbers provided in the LOF are solely
used for descriptive purposes and will
not be used in determining future
management of fisheries, observer
coverage designations, or bycatch rates.
Further, NMFS has communicated with
the states regarding the need for
consistent fishing effort data collection
methods across states to better assess
fisheries’ effects on marine mammal
stocks that have interstate distributions.
NMFS will continue to communicate
this need through TRT processes, LOF
yearly inquiries, and the MMAP’s
integrated registration process.
Comment 30: The Commission
concurs with NMFS’ proposal to add
Risso’s dolphin (WNA stock) to the list
of species or stocks incidentally killed
or seriously injured in the Category II
‘‘Mid-Atlantic bottom trawl’’ fishery
based on 15 Risso’s dolphins observed
killed in this fishery in 2010. The
Commission states that this level of take
is noteworthy, because although fisheryrelated mortality for this stock between
2004 and 2008 averaged 20 deaths or
serious injuries in all fisheries per year,
no deaths in this specific fishery were
reported during that 5-year period.
Therefore, the Commission also
recommends NMFS further investigate
any factors that may account for the
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notable recent increase in takes of
Risso’s dolphins in this fishery.
Response: NMFS agrees with the
Commission’s comment. There could be
several factors related to the increase in
observed bycatch of Risso’s dolphins in
the Mid-Atlantic region bottom trawl
fishery. It is unclear whether an increase
in observer coverage may have
contributed to number of takes observed
in 2010. The NEFSC intends to evaluate
the Risso’s dolphin bycatch events from
2010 and will reports its findings in the
2012 SAR.
Comment 31: The CBD applauds
NMFS’ proposal to add Risso’s dolphin
(WNA stock) to the list of species or
stocks incidentally killed or injured in
the Category II ‘‘Mid-Atlantic bottom
trawl’’ fishery despite the 2010 SAR’s
failure to include any mortality after
2008 to Risso’s dolphins; however, the
CBD asserts that this fishery should be
classified as Category I. The CBD notes
that the fifteen dolphins killed in 2010
were those observed and the actual
mortality should be estimated at several
times that based on levels of observer
coverage ranging from 0 to 13.3 percent.
Therefore, CBD asserts that it is very
likely that this multiplier causes
mortality in this fishery to represent
more than 50 percent of the stock’s PBR
of 124 (i.e., if observer coverage were 10
percent, observed mortality should be
multiplied by ten and actual mortality
estimated at 150 dolphins, exceeding
the PBR).
Response: For the 2012 LOF, a
reclassification of the ‘‘Mid-Atlantic
bottom trawl’’ fishery to a Category I is
not warranted. NMFS analyzes observer
data and applies observed takes against
calculated PBR levels during the process
of updating and publishing the annual
SARs. NMFS then classifies fisheries on
the LOF based on the most recent SARs
(including observer documented
interactions, stranding data, and other
data reported in the SARs). The current
timing of the LOF publication and
availability of both fishery dependent
and independent data (both needed to
estimate total mortality) to scientists are
not in sync making it difficult to fully
evaluate total bycatch mortality of a
given stock for annual updates to the
LOF. Using the count of takes seen by
fisheries observers is an approach that is
historically consistent with
documenting relative levels of
interactions with commercial fisheries
for the LOF. Total bycatch mortality for
Risso’s dolphins due to commercial
fishery interactions is scheduled to be
evaluated and reported in the 2012 SAR.
NMFS will revisit the classification of
the ‘‘Mid-Atlantic bottom trawl’’ fishery
once the 2012 SAR is published.
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Additionally, percent observer
coverage is not an appropriate metric to
use as a multiplier for evaluating the
risk a particular fishery poses to a
marine mammal stock. It is also not
appropriate to arbitrarily select 10
percent coverage from values ranging
from 0 to 13.3 percent. Observer
coverage has been increasing in small
increments in specific target fisheries
within the ‘‘Mid-Atlantic bottom trawl’’
fishery in recent years. What is
presently known is that all the reports
of observed bycatch of Risso’s dolphins
in 2010 originated from the MidAtlantic region where observer coverage
has averaged only three percent during
the last 5 years (2005–2009; draft 2011
SAR).
Comment 32: The USFWS provides
NMFS with a report and photos from
the Puerto Rico Department of Natural
and Environmental Resources briefly
describing the capture of a manatee by
seine gear in July 2009.
Response: NMFS thanks USFWS for
the report regarding the manatee take.
Based on Puerto Rico (PR) Fishing
Regulations 6768 of February 11, 2004
Article 15, use of beach seines in Puerto
Rican waters was prohibited at the time
of the take. Because this take was illegal
and the specifics of are unknown (e.g.,
gear design, soak time, location
specifics, etc.), NMFS is not including
manatees on the list of species or stocks
killed or injured by the Caribbean haul/
beach seine fishery on the LOF, and the
fishery will remain classified as
Category III. However, NMFS
recommends that the USFWS add this
take to the SAR for the Antillean
manatee. Furthermore, the PR Fishing
Regulations 7949 of November 29, 2010,
now allows the use of beach seines.
NMFS will work with USFWS to ensure
any future takes that occur in this
fishery are considered in the future
LOFs and SAR.
Comment 33: The Commission
concurs with NMFS’ proposal to list
bottlenose dolphins (Northern NC
estuarine system stock) as a stock
subject to incidental killing or serious
injury in the ‘‘VA pound net’’ fishery.
The Commission further recommends
that NMFS work with the State of VA
to develop a formal, scientifically sound
system for observing or otherwise
monitoring marine mammal interactions
in this fishery.
Response: NMFS agrees that
developing and implementing a formal
observer program for the VA pound net
fishery is important, and NMFS is
exploring mechanisms to accomplish
this with the State of VA. Meanwhile,
NMFS monitors marine mammal
interactions with this fishery in two
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ways: (1) Monitoring through the NMFS
Northeast Fishery Science Center and
(2) evaluating stranding data collected
by the Stranding Network since the late
1990s.
Comment 34: The Commission
concurs with the addition of bottlenose
dolphins (Gulf of Mexico bay, sound,
and estuarine stock) to the list of species
or stocks incidentally killed or injured
by the ‘‘Atlantic Ocean, Gulf of Mexico,
Caribbean commercial passenger fishing
vessel’’ fishery and recommends NMFS
elevate this fishery to Category II based
on evidence of interactions from 38
dolphins between 2002–2009 in gear
consistent with recreational hook and
line gear. The Commission believes that
even without a quantitative analysis of
average annual mortality and serious
injury or comparisons with PBR levels,
NMFS has sufficient evidence to
conclude that the fishery results in at
least occasional takes of bottlenose
dolphins and warrants a Category II
listing.
Response: At this time, there are not
sufficient data to elevate this fishery.
Hook and line fishing gear is used by
both individual recreational anglers and
commercial passenger fishing vessels;
thus, it is difficult to discern how many
animals are taken incidental to the
Atlantic Ocean, Gulf of Mexico,
Caribbean commercial passenger fishing
vessel fishery and how many animals
are taken by a similar recreational
fishery. NMFS will continue analyzing
all stranding information for future
LOFs to determine appropriate
classification for hook and line fishery
interactions.
Comment 35: The Commission
reiterated past concerns about the lack
of information on many species and
stocks of marine mammals in the Gulf
of Mexico and recommends that NMFS
work with the Commission to develop
an effective long-term strategy for
determining marine mammal stock
structure and abundance, potential
biological removal levels, and fisheries
mortality and serious injury rates in the
Gulf of Mexico. The Commission notes
that in responding to these past
recommendations, NMFS has
consistently stated that collection of
information about fishery interactions is
a high priority and will occur if
resources become available, also
emphasizing the value of information
gathered via fishermen self-reports and
stranding networks. In its response to
the Commission’s letter on the proposed
2011 LOF, NMFS noted how, as a result
of the BP/Deepwater Horizon MC252 oil
spill response and restoration efforts,
additional surveys and mark-recapture
studies were underway for some bay,
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sound, and estuarine stocks, and that
this work would provide updated
abundance estimates and potential
biological removal levels for some
stocks. The Commission appreciates
NMFS’ expressed intention to expand
its efforts and investments in these
areas; however, the Commission also
believes that these efforts and
investments would benefit from a more
comprehensive, aggressive, and
innovative strategy.
Response: NMFS agrees that
determining marine mammal stock
structure and abundance, potential
biological removal levels, and fisheries
mortality and serious injury rates in the
Gulf of Mexico are priorities. NMFS
Southeast Fisheries Science Center
(SEFSC) conducts all marine mammal
stock assessments for the Southeast,
which are provided annually in SARs
and include information on stock
structure and abundance, potential
biological removal levels, and fisheries
mortality and serious injury rates. While
NMFS uses this and other information
to classify fisheries on the LOF, NMFS
does not determine this information on
the annual LOF. Therefore, NMFS
recommends the Commission continue
to provide comments regarding
enhanced stock assessments during the
public comment period for the annual
SARs.
Comment 36: The Blue Water
Fishermen’s Association (BWFA)
recommends NMFS standardize
methods for analyzing data and observer
coverage in the Atlantic pelagic longline
fishery. BWFA states that the Atlantic
and Gulf of Mexico SARs maintain the
use of data that result in a gross
distortion of the impacts of the
shrinking longline fleet, including
estimates of total annual serious injury
and mortality extrapolated from an
imprecise ‘‘pooling’’ method, the
problems with which are compounded
by attempts to assess serious injury by
studying observer comments and
applying a percentage to all extrapolated
estimates. Further, BWFA asserts that
NMFS continues to use disparate
methods and different values to
calculate percentages of observer
coverage for the pelagic longline fishery
versus other fisheries, which presents a
skewed picture of the true rate of
observer coverage of fishing effort.
Response: NMFS responded to a
similar comment on the 2006 LOF (71
FR 48802, August 22, 2006, comment/
response 18). NMFS’ SEFSC develops
fishery observer programs and methods
for analyzing related data, and reports
this information in the annual SARs.
While NMFS uses this and other
information to classify fisheries on the
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LOF, NMFS does not determine this
information on the annual LOF.
Therefore, NMFS recommends the
BWFA provide comments regarding
these methods during the public
comment period for the annual SARs.
Comment 37: The BWFA hopes that
NMFS will provide financial support
through the establishment of specific
grants to help continue research efforts
for practical solutions to the problem of
marine mammal depredation on hooked
catches. The BWFA notes that with the
current requirements to use corrodible
circle hooks and to carry and use safe
handling and release tools and
techniques, along with BWFA’s support
for research efforts of the Consortium for
Wildlife Bycatch Reduction in helping
to expand the understanding of the
nature of pilot whale interactions, this
fishery is already leading the way
toward alleviating its interactions with
protected species.
Response: NMFS thanks BWFA for
their support of research efforts to
reduce marine mammal bycatch. While
the LOF does not include any funding
mechanisms to support research efforts,
NMFS provides funding for such
research via other sources. For example,
NMFS provides funding through NC Sea
Grant for cooperative research between
academics and fishermen to better
understand pilot whale interactions
with the pelagic longline fishery as
described in the Pelagic Longline Take
Reduction Plan.
Comment 38: The BWFA reiterated
past recommendations for NMFS to
subdivide the Atlantic Ocean, Caribbean
and Gulf of Mexico pelagic longline
fisheries for swordfish, tuna and sharks
into three regional fisheries, the Atlantic
(north), Caribbean (south), and Gulf of
Mexico, citing four arguments. First,
BWFA states that subdividing the
fishery would more accurately reflect
the geographical differences in target
species, scientific data on the stocks of
marine mammals listed as interacting
with the U.S. Atlantic pelagic longline
gear, and would take into account
NMFS’s regulations that have
permanently closed specific areas of the
southeast Atlantic coast. Second, BWFA
notes that the catch and effort
information for U.S. pelagic longline
gear is recorded in distinct geographical
regions and NMFS takes effort by area
into account when calculating estimates
of interactions; therefore, separating
these fisheries by fishing region would
facilitate establishing a standardized
process for monitoring effort, estimating
serious injury and incidental mortality
rates, and evaluating the effectiveness of
reduction methods. Third, BWFA
disagrees with past statements from
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NMFS that nearly all of the fishery
participants move across the proposed
boundaries, noting that the recent
available effort data shows a very high
percentage of the Gulf of Mexico vessels
fish nowhere else, most of the vessels
that fish north or south of the Georgia/
Florida border (within the EEZ) do not
travel north or south of their region, and
a small number (<12) of Atlantic
distant-water vessels customarily travel
north and south in international waters
beyond the U.S. EEZ. Lastly, BWFA
asserts that when compared to NMFS’s
division of various Pacific and Alaska
fisheries, including the AK gillnet
fisheries, the pelagic longline fisheries
in the Atlantic and the Gulf of Mexico
are being unjustly and incorrectly
grouped into one single fishery.
Response: NMFS responded to similar
comments in the 2001, 2003, and 2006
LOFs (66 FR 42780, August 15, 2001,
comment/response 16; 68 FR 41725,
July 15, 2003, comment/response 29; 71
FR 48802, August 22, 2006, comment/
response 16). NMFS designates fishery
descriptions on the LOF so as to be
consistent with the current management
structure for the fishery under the
Atlantic Highly Migratory Species
(HMS) FMP. The pelagic longline
fishery in the Atlantic is managed by
NMFS as one fishery under the Atlantic
HMSFMP encompassing all longline
fishing effort targeting highly migratory
species that may occur throughout the
Atlantic Ocean, Caribbean, and Gulf of
Mexico. The development of
management measures to reduce serious
injuries and mortalities of marine
mammals in the longline fishery has
focused primarily on those areas where
interactions pose particular risk to
marine mammals. However, as long as
interactions continue to occur
throughout the fishery, NMFS will
maintain the current fishery designation
on the LOF.
Comment 39: The Florida Fish and
Wildlife Conservation Commission
(FWC) agrees that the proposed LOF
would not affect the land or water uses
or natural resources of the coastal zone
as specified under section 307 of the
Coastal Zone Management Act.
However, the FWC recommends that,
should any changes be made to the
proposed LOF before it is finalized, the
decision by NMFS not to provide a
consistency determination for this
activity should be revisited. Further, the
FWC would appreciate consultation
prior to NMFS making a decision not to
provide a consistency determination for
future LOFs.
Response: In the future NMFS will
consult with the State of FL when
determining consistency determinations
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under CZMA for any LOF actions that
may impact fisheries managed by the
State.
Comment 40: The HSUS is supportive
of the inclusion of bottlenose dolphins
in the list of species or stocks that are
killed or injured with a number of
Atlantic gillnet, trawl and trap/pot
fisheries utilizing gear types known to
interact with bottlenose dolphins,
whose evolving changes in stock
structure may result in impacts from
these fisheries occurring at levels that
are greater than previously thought.
Response: NMFS acknowledges this
comment. The proposed additions of
bottlenose dolphins to the list of species
or stocks that are killed or injured to a
number of Atlantic gillnet, trawl and
trap/pot fisheries are finalized in this
final rule.
Comment 41: The FWC identifies
some mischaracterizations in the
description of the ‘‘Southeastern U.S.
Atlantic, Gulf of Mexico stone crab trap/
pot fishery,’’ including: (1) The
proposed rule is essentially correct that
traps are the only gear used in the
commercial portion of this fishery, but
stone crab claws are also lawfully
harvested by hand recreationally; (2)
Trap specifications for stone crab traps
may be found in FWC rule, Chapter
68B–13, FL Administrative Code
(F.A.C), not FL statutes; (3) In addition
to the requirement for buoys attached to
commercial traps to be marked with an
‘‘X,’’ the trap owner’s stone crab
endorsement number must be marked in
characters at least 2 inches high on each
buoy and harvester’s must attach a tag
that corresponds to a valid FWC-issued
trap certificate; and (4) Ch. 68B–
13.009(3), F.A.C. includes trap marking
requirements for recreational harvest,
stating the buoy attached to each trap,
except those fished from a dock, shall
have a permanently affixed and legible
‘‘R’’ at least 2 inches high, and the
harvester’s name and address.
Response: NMFS thanks the FWC for
providing this information. Based on
information provided by FWC, NMFS
has clarified the language characterizing
the ‘‘Southeastern U.S. Atlantic, Gulf of
Mexico stone crab trap/pot’’ in this final
LOF.
Comment 42: The Florida Keys
Commercial Fishermen’s Association
(FKCFA) requests NMFS continue to
classify the ‘‘South Atlantic, Gulf of
Mexico stone crab trap/pot’’ fishery as
Category III based on the real differences
between this fishery and the ‘‘Atlantic
blue crab trap/pot’’ fishery, questionable
data, a substantial law enforcement
presence in the areas fished, and the
extremely low number of interactions in
the past decade. First, the FKCFA notes
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that the stone crab trap/pot fishery
differs significantly from the blue crab
trap/pot fishery in the methods the gear
is fished, the location the gear is
deployed, and how the gear may
interact with marine mammals. Second,
the FKCFA requests additional details
about the stranding data used to propose
the classification change. Third, the
FKCFA notes that nearly 50 percent of
stone crab trap/pot fishing takes place in
the waters of the FL Keys and Monroe
County where there have been no
recorded deaths to dolphins associated
with the stone crab trap/pot fishery, and
where there is a tremendous presence
from law enforcement, marine
scientists, and charter/for-hire and
recreational boaters who are likely to
observe and report interactions.
Response: From 2002–2010 stranding
data, NMFS confirmed that three
bottlenose dolphin serious injuries and
mortalities were a result of interactions
with the stone crab fishery. The NMFS
Southeast Regional Office gear analysis
team analyzed the gear recovered on the
stranded dolphins and confirmed the
gear was from the stone crab fishery.
Seven additional bottlenose dolphin
serious injuries or mortalities were
confirmed to result from interactions
with trap/pot gear from a southeast trap/
pot fishery. Although specific fishery
attribution was not possible for the gear
found on these seven dolphins, NMFS
conducted a spatial and temporal
analysis of the fishery and interactions
and determined it is likely these
dolphins were also entangled in stone
crab gear. The three confirmed stone
crab takes and seven additional possible
takes by stone crab gear since 2002
provide reasonable evidence that the
stone crab fishery by itself is responsible
for the annual removal of between 1 and
50 percent of any stock’s PBR and
should be classified as a Category II
fishery. Two of the three confirmed
takes incidental to the stone crab fishery
occurred in Biscayne Bay, Florida,
within the range of the Biscayne Bay
bottlenose dolphin stock, representing
at least 4.4 percent of the Biscayne Bay
bottlenose dolphin stock’s total. NMFS
classifies each fishery on the LOF based
on the serious injury or mortality level
in the entire fishery; therefore,
regardless of the three serious injuries to
dolphins from trap/pot gear reported in
the FL Keys and Monroe County waters
between 2002–2010 (gear was not
analyzed by gear analysis team, but
based on spatial temporal analysis stone
crab gear is a possibility for all three
cases), the stranding data from Biscayne
Bay and by analogy to the ‘‘Atlantic blue
crab trap/pot’’ fishery indicate a
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Category II classification of the fishery
is warranted. Based on this information,
NMFS has classified this fishery as
Category II in this final rule.
Comment 43: The HSUS and the CBD
support the elevation of the
‘‘Southeastern U.S. Atlantic, Gulf of
Mexico stone crab trap/pot’’ fishery to a
Category II fishery. However, the CBD
asserts that given the small size and
complex stock structure of Gulf of
Mexico bottlenose dolphin stocks, the
stone crab fishery should be categorized
as a Category I fishery. The HSUS is also
concerned that the growing
understanding of the existence of
resident populations of bottlenose
dolphins in individual bays, sounds,
and estuaries underscores the need to
better inform management of fishery
interactions with dolphins. Both the
CBD and HSUS recommend that
observer coverage is necessary to better
monitor fisheries interaction effects on
these small, distinct dolphin stocks.
Response: The stranding data analyses
described in the proposed 2012 LOF
indicates that the ‘‘Southeastern U.S.
Atlantic, Gulf of Mexico stone crab trap/
pot’’ fishery is not responsible for a PBR
removal level of greater than 50 percent
for any stock. The removal calculation
of the two takes by stone crab gear was
estimated to be at least 4.4 percent of
the Biscayne Bay bottlenose dolphin
stock’s total. Therefore, based on the
best available information and
according to the definition of a Category
I fishery (‘‘annual mortality and serious
injury of a stock in a given fishery is
greater than or equal to 50 percent of the
PBR level’’), a Category I classification
for the ‘‘Southeastern U.S. Atlantic, Gulf
of Mexico stone crab trap/pot’’ is not
warranted. The fishery is classified as
Category II in this final rule. NMFS will
continue to monitor interactions with
this fishery each year to determine if
reclassification is warranted.
Furthermore, NMFS agrees that a greater
understanding of the operations of
fishery interactions with dolphins is
important to inform management.
Observer coverage for fisheries in which
historical data, anecdotal accounts, or
stranding data indicate a high
probability for serious injury or lethal
interactions to marine mammal
populations are a priority if funding
becomes available. For example, in 2011
NMFS was able to support observer
coverage for the Gulf of Mexico
Menhaden fishery in order to help better
understand the nature and scope of
marine mammal interactions with this
fishery.
Comment 44: The Commission
concurs with NMFS’ proposal to elevate
the ‘‘Southeastern Atlantic, Gulf of
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Mexico stone crab trap/pot’’ fishery to
Category II because it utilizes gear and
techniques common with other fisheries
that are known to entangle bottlenose
dolphins. The Commission recognizes
that while quantitative information on
mortality and serious injury rates and
PBR levels for 5 of the 7 stocks
confirmed or plausibly seriously injured
by this fishery are not available, the
many similarities with the Category II
‘‘Atlantic blue crab trap/pot’’ fishery
and information on dolphin stranding
events warrant a Category II
classification.
Response: NMFS acknowledges this
comment. The ‘‘Southeastern Atlantic,
Gulf of Mexico stone crab trap/pot’’
fishery is classified as Category II in this
final rule.
Comments on Commercial Fisheries on
the High Seas
Comment 45: The HLA disagrees with
NMFS’ proposal to add a number of
‘‘unknown’’ stocks to the list of species
or stocks injured or killed in the ‘‘HI
deep-set (tuna target)’’ and ‘‘HI shallowset (swordfish target)’’ longline/set line
fisheries, despite NMFS’ acknowledging
that the ‘‘proposed addition of these
unknown stocks is not due to additional
observed takes…’’ (76 FR 37716, June
28, 2011). The HLA asserts that the
inclusion of species or stocks for which
there has never been an observed
interaction is arbitrary and capricious
and violates the plain language of the
MMPA, which states that NMFS include
in the LOF ‘‘a statement describing the
marine mammal stocks interacting
with’’ a given fishery (MMPA section
118(c)). The HLA states that there is no
room in this language for the inclusion
of ‘‘unknown’’ marine mammal species
or stocks that NMFS speculates may, but
have not been observed to, interact with
the fishery.
Response: The proposed additions of
unknown stocks are for species that
have been observed to have been taken
by the HI-based deep-set and shallowset longline fisheries on the high seas,
but for which the stock identity could
not be determined. For this fishery, the
unknown stocks include stocks for
Blainville’s beaked whale, bottlenose
dolphin, Pantropical spotted dolphin,
Risso’s dolphin, short-finned pilot
whale, striped dolphin, Bryde’s whale,
and Kogia spp. whale. (Please refer to
the proposed rule at 76 FR 37716, June
28, 2011, for more information.) NMFS’
SARs for HI pelagic cetacean stocks note
that the stocks’ ranges extend into the
high seas, but the full offshore ranges
are unknown. For those animals taken
by the longline fisheries on the high
seas, it is unknown in most cases
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whether the animals belong to the HI
pelagic stocks, or whether the animals
are from stocks beyond the (unknown)
range of the HI pelagic stocks. This is
particularly true for takes that occur far
outside the U.S. EEZ. At this point,
NMFS cannot assume that all takes are
from HI pelagic stocks. Therefore,
NMFS’ inclusion of ‘‘unknown’’ stocks
that are known to interact with the
longline fisheries on the high seas
merely acknowledges the uncertainty in
stock identification.
Comment 46: The Commission
concurs with NMFS’ proposal to add
several marine mammal stocks, absent
information on stock identity and
fisheries interactions, to the list of those
subject to incidental killing or serious
injury in the Category I ‘‘Western Pacific
pelagic fishery, I deep-set component’’
and the Category II ‘‘Western Pacific
pelagic fishery, HI shallow-set
component’’ because such additions
better reflect the state of information
and need for caution in managing
interactions between marine mammals
and these high seas fisheries. Further,
the Commission notes that these
additions point to the need to work with
industry and increase investment and
initiatives to gather more information
about high seas marine mammal stocks,
including their boundaries and
interactions with fisheries. Therefore,
the Commission recommends that
NMFS work with its international and
industry partners to compile and
analyze information about marine
mammals on the high seas and their
interactions with fisheries, so that the
list of species incidentally killed or
seriously injured in high seas fisheries
can be refined in the near future.
Response: NMFS agrees that the
addition of these ‘‘unknown’’ stocks
reflects the lack of information on stock
structure and stock identity for marine
mammals on the high seas that interact
with the U.S. longline fisheries. NMFS
has and will continue to work with
international and industry partners to
gather information on marine mammal
stocks and high seas fishery interactions
to better understand the stocks and U.S.
fisheries’ impacts on them.
Comment 47: The Council argues that
while additions of ‘‘unknown stocks’’
are made for the high seas ‘‘Western
Pacific pelagic’’ fisheries, additions of
‘‘unknown stocks’’ are not made for
other high seas fisheries, including the
high seas ‘‘Atlantic highly migratory
species’’ fishery that has ten different
stocks of marine mammals known to be
incidentally injured or killed.
Response: There is not significant
evidence that ‘‘unknown stocks’’ are
currently incidentally killed or injured
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in the ‘‘Atlantic highly migratory
species longline’’ fishery; therefore,
‘‘unknown’’ stocks are not listed under
this fishery in Table 3. For detailed
information on why NMFS includes
‘‘unknown’’ stocks in on the list of
species or stocks killed or injured in the
high seas ‘‘Pacific highly migratory
species longline’’ fisheries (HI deep-set
and HI shallow-set), please see the
response to comment 45 above.
For the majority of high seas fisheries,
NMFS does not have data to create a list
of which marine mammal species or
stocks are killed or injured on the high
seas. For fisheries that occur only on the
high seas and are not extensions of
fisheries operating in U.S. waters, the
marine mammals species killed or
injured in those fisheries are listed as
‘‘undetermined’’ in Table 3. For high
seas fisheries that are extensions of a
fishery operating in U.S. waters, but for
which there are no data on takes on the
high seas, NMFS includes an identical
list of marine mammal species as are
listed as killed or injured in the portion
of the fishery operating in U.S. waters
(minus exclusively coastal stocks).
These fisheries are identified in Table 3
by a ‘‘¥’’ after their names. For high
seas fisheries that are extensions of a
fishery operating in U.S. waters for
which NMFS does have observed
mortalities or injuries on the high seas,
the species or stocked observed as killed
or injured on the high seas are listed.
These fisheries are identified in Table 3
by a ‘‘+’’ after their names.
Summary of Changes From the
Proposed Rule
In this final rule, NMFS is not
elevating the ‘‘HI trolling, rod and reel’’
or the ‘‘HI charter vessel’’ fisheries to
Category II as proposed, instead these
fisheries are retained as Category III. For
additional information, see comments
16–26, and the associated comment
response, under ‘‘Comments on the
Hawaii Troll and Charter Vessel
Fisheries’’ above.
In this final rule, NMFS is not adding
Pantropical spotted dolphins (HI stock)
to the list of species or stocks
incidentally killed or injured in the ‘‘HI
trolling, rod and reel’’ or ‘‘HI charter
vessel’’ fisheries. For additional
information, see comments 16–26, and
the associated comment response, under
‘‘Comments on the Hawaii Troll and
Charter Vessel Fisheries’’ above.
In this final rule, NMFS updates the
fishery description for the
‘‘Southeastern U.S. Atlantic, Gulf of
Mexico stone crab trap/pot’’ fishery to
clarify the State of Florida’s regulations
for this fishery, based on comments
received from the FL Fish and Wildlife
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Commission (see comment/response
41). The final fishery description is
provided above under the section
‘‘Fishery Descriptions.’’
NMFS corrects a typographical error
in the proposed rule, which stated the
‘‘CA pelagic longline’’ fishery occurs
within the EEZ, when in fact this fishery
has always occurred on the high seas,
seaward of the EEZ. The ‘‘CA pelagic
longline’’ fishery targets highly
migratory species (HMS) and the use of
longline gear to target HMS within the
EEZ off of CA is prohibited by NOAA
regulations under the MagnusonStevens Fishery Conservation and
Management Act, as well as by State of
CA.
Summary of Changes to the LOF for
2012
The following summarizes changes to
the LOF for 2012 in fishery
classification, fisheries listed in the
LOF, the estimated number of vessels/
participants in a particular fishery, and
the species or stocks that are
incidentally killed or injured in a
particular fishery. The classifications
and definitions of U.S. commercial
fisheries for 2012 are identical to those
provided in the LOF for 2011 with the
changes discussed below.
Commercial Fisheries in the Pacific
Ocean
Fishery Classification
The ‘‘CA thresher shark/swordfish
drift gillnet’’ fishery is elevated from
Category III to Category II.
Fishery Name and Organizational
Changes and Clarifications
NMFS corrects a typographical error
that appeared in the proposed 2012
LOF, which stated the ‘‘CA pelagic
longline’’ fishery occurs within the EEZ,
when in fact this fishery has always
occurred on the high seas, seaward of
the EEZ. The ‘‘CA pelagic longline’’
fishery targets highly migratory species
(HMS) and the use of longline gear to
target HMS within the EEZ off of CA is
prohibited by NOAA regulations under
the Magnuson-Stevens Fishery
Conservation and Management Act, as
well as by State of CA. This fishery is
the same as the ‘‘Pacific Highly
Migratory Species’’ longline fishery
listed in Table 3. The error in the
proposed 2012 LOF occurred when
NMFS provided a correction to the 2011
LOF to ensure that this one fishery,
although listed separately on Table 1
and Table 3 (the reasons for which are
explained in the preamble under ‘‘Are
High Seas Fisheries Included on the
LOF?’’), was classified as Category III on
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both tables and that marine mammal
species injured or killed is the same on
both tables.
Number of Vessels/Persons
The estimated numbers of persons/
vessels participating in several HI
fisheries are updated based on the most
recent numbers of federal permits or
state licenses for each fishery, as
outlined below.
Category I: ‘‘HI deep-set (tuna target)
longline/set line’’ from 127 to 124.
Category II: ‘‘American Samoa
longline’’ from 60 to 26; ‘‘HI shortline’’
from 21 to 13; and ‘‘HI trolling, rod and
reel’’ from 2,210 to 2,191.
Category III: ‘‘HI inshore gillnet’’ from
39 to 44; ‘‘HI crab net’’ from 8 to 5; ‘‘HI
Kona crab loop net’’ from 41 to 46; ‘‘HI
opelu/akule net’’ from 20 to 16; ‘‘HI
hukilau net’’ from 36 to 27; ‘‘HI lobster
tangle net’’ from 2 to 1; ‘‘HI inshore
purse seine’’ from 8 to 5; ‘‘HI throw net,
cast net’’ from 28 to 22; ‘‘HI crab trap’’
from 9 to 5; ‘‘HI fish trap’’ from 11 to
13; ‘‘HI lobster trap’’ from 3 to 1; ‘‘HI
shrimp trap’’ from 1 to 2; ‘‘HI kaka line’’
28 to 24; ‘‘HI vertical longline’’ from 18
to 10; ‘‘HI aku boat, pole, and line’’ from
6 to 2; ‘‘HI inshore handline’’ from 460
to 416; ‘‘HI tuna handline’’ from 531 to
445; ‘‘HI handpick’’ from 53 to 61; ‘‘HI
lobster diving’’ from 36 to 39; ‘‘HI
spearfishing’’ from 163 to 144; ‘‘HI fish
pond’’ from N/A to 16; and ‘‘HI Main
Hawaiian Islands deep-sea bottomfish
handline from 580 to 569.
List of Species or Stocks Incidentally
Killed or Injured
Humpback whale (CA/OR/WA stock)
is added to the list of species or stocks
incidentally killed or injured in the ‘‘CA
thresher shark/swordfish drift gillnet’’
fishery followed by the notation ‘‘1.’’
Commercial Fisheries in the Atlantic
Ocean, Gulf of Mexico, and Caribbean
Fishery Classification
The ‘‘Southeastern U.S. Atlantic, Gulf
of Mexico stone crab trap/pot’’ fishery is
elevated from Category III to Category II
followed by the notation ‘‘2.’’
Addition of Fisheries
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The ‘‘RI floating trap’’ fishery is added
to the LOF as Category III.
Fishery Name and Organizational
Changes and Clarifications
The spatial boundaries for the
Category II ‘‘Northeast bottom trawl,’’
‘‘Northeast mid-water trawl,’’ ‘‘MidAtlantic bottom trawl,’’ and ‘‘MidAtlantic mid-water trawl’’ fisheries are
updated and the fishery definitions are
updated to reflect this change.
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Number of Vessels/Persons
The estimated number of vessels/
persons participating in several New
England, Mid-Atlantic, and South
Atlantic fisheries are updated based on
the most recent numbers of federal
permits or state licenses for each
fishery, as outlined below.
Category I: ‘‘Mid-Atlantic gillnet’’
from 5,495 to 6,402; ‘‘Northeast sink
gillnet’’ from 7,712 to 3,828; and
‘‘Northeast/Mid-Atlantic American
lobster trap/pot’’ from 12,489 to 11,767.
Category II: ‘‘Southeastern U.S.
Atlantic, Gulf of Mexico stone crab trap/
pot’’ from 4,453 to 1,282; ‘‘Chesapeake
Bay inshore gillnet’’ from 1,167 to 3,328;
‘‘Northeast anchored float gillnet’’ from
662 to 414; ‘‘Northeast drift gillnet’’
from 608 to 414; ‘‘Mid-Atlantic midwater trawl’’ from 546 to 669; ‘‘MidAtlantic bottom trawl’’ from 1,182 to
1,388; ‘‘Northeast mid-water trawl
(including pair trawl)’’ from 953 to 887;
‘‘Northeast bottom trawl’’ from 1,635 to
2,584; Atlantic blue crab trap/pot from
6,479 to 10,008; ‘‘Atlantic mixed species
trap/pot’’ from 1,912 to 3,526; ‘‘MidAtlantic menhaden purse seine’’ from
54 to 56; ‘‘Mid-Atlantic haul/beach
seine’’ from 666 to 874; and ‘‘VA pound
net’’ from 52 to 231.
Category III: ‘‘FL spiny lobster trap/
pot’’ fishery from 2,145 to 1,268; ‘‘Gulf
of Maine, U.S. Mid-Atlantic sea scallop
dredge’’ from 258 to > 230; ‘‘Northeast,
Mid-Atlantic bottom longline/hook &
line’’ from 1,183 to > 1,281; ‘‘DE River
inshore gillnet’’ from 60 to unknown;
‘‘Long Island Sound inshore gillnet’’
from 20 to unknown; ‘‘RI, southern MA
(to Monomy Island), and NY Bight
(Raritan and Lower NY Bays) inshore
gillnet’’ from 32 to unknown; ‘‘Gulf of
Maine Atlantic herring purse seine’’
from > 7 to > 6; ‘‘U.S. Mid-Atlantic eel
trap/pot’’ from > 700 to unknown; and
‘‘Atlantic shellfish bottom trawl’’ from
> 67 to > 86.
List of Species or Stocks Incidentally
Killed or Injured
Killer whale (GMX oceanic stock),
sperm whale (GMX oceanic stock), and
Gervais beaked whale (GMX oceanic
stock) are added to the list of species or
stocks incidentally killed or injured in
the Category I ‘‘Atlantic Ocean,
Caribbean, Gulf of Mexico large pelagic
longline’’ fishery.
Atlantic spotted dolphin (Northern
GMX stock) stock name is updated to
Atlantic spotted dolphin (GMX
continental and oceanic) on the list as
species or stocks incidentally killed or
injured in the Category I ‘‘Atlantic
Ocean, Caribbean, Gulf of Mexico large
pelagic longline’’ fishery.
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Bottlenose dolphin (GA coastal stock)
and bottlenose dolphin (SC coastal
stock) are combined on the list as
species or stocks incidentally killed or
injured in the Category II ‘‘Southeast
Atlantic gillnet’’ fishery and renamed
bottlenose dolphin (SC/GA coastal
stock).
Bottlenose dolphin (Northern FL
coastal stock) is added to the list of
species or stocks incidentally killed or
injured in the Category II ‘‘Southeastern
U.S. Atlantic shark gillnet’’ fishery.
Bottlenose dolphin (Northern GMX
coastal stock) and bottlenose dolphin
(GMX continental shelf stock) are added
to the list of species or stocks
incidentally killed or injured in the
Category II ‘‘Southeastern U.S. Atlantic,
Gulf of Mexico shrimp trawl’’ fishery.
Atlantic spotted dolphin (Northern
GMX) is updated to Atlantic spotted
dolphin (GMX continental and oceanic)
on the list of species or stocks
incidentally killed or injured in the
Category II ‘‘Southeastern U.S. Atlantic,
Gulf of Mexico shrimp trawl’’ fishery.
Bottlenose dolphin (GA coastal stock)
and bottlenose dolphin (SC coastal
stock) are combined on the list of
species or stocks incidentally killed or
injured in the Category II ‘‘Southeastern
U.S. Atlantic, Gulf of Mexico shrimp
trawl’’ fishery and renamed bottlenose
dolphin (SC/GA coastal stock).
Bottlenose dolphin (GA coastal stock)
and bottlenose dolphin (SC coastal
stock) are combined on the list of
species or stocks incidentally killed or
injured in the Category II ‘‘Atlantic blue
crab trap/pot’’ fishery and renamed the
stock bottlenose dolphin (SC/GA coastal
stock).
Bottlenose dolphin (Southern NC
estuarine system stock) is added to the
list of species or stocks incidentally
killed or injured in the Category II ‘‘NC
long haul seine’’ fishery.
Bottlenose dolphin (Northern NC
estuarine system stock) is added to the
list of species or stocks incidentally
killed or injured in the Category II ‘‘VA
pound net’’ fishery.
Bottlenose dolphin (Central FL coastal
stock) is added to the list of species or
stocks incidentally killed or injured in
the Category III ‘‘FL spiny lobster trap/
pot’’ fishery.
Bottlenose dolphin (Central FL coastal
stock), bottlenose dolphin (Eastern GMX
coastal stock), bottlenose dolphin (FL
Bay stock), bottlenose dolphin (GMX
bay, sound, estuarine stock, FL west
coast portion), bottlenose dolphin
(Indian River Lagoon estuarine system
stock), bottlenose dolphin (Jacksonville
estuarine system stock), and bottlenose
dolphin (Northern GMX coastal stock)
are added to the list of species or stocks
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incidentally killed or injured in the
Category II ‘‘Southeastern U.S. Atlantic,
Gulf of Mexico stone crab trap/pot’’
fishery.
Bottlenose dolphin (GMX continental
shelf stock) is added to the list of
species or stocks incidentally killed or
injured in the Category III ‘‘Southeastern
U.S. Atlantic, Gulf of Mexico, and
Caribbean snapper-grouper and other
reef fish bottom longline/hook-and-line’’
fishery.
Bottlenose dolphin (GMX bay, sound,
and estuarine stock) is added to the list
of species or stocks incidentally killed
or injured in the Category III ‘‘Atlantic
Ocean, Gulf of Mexico, Caribbean
commercial passenger fishing vessel’’
fishery.
Risso’s dolphin (WNA stock) is added
to the list of species or stocks
incidentally killed or injured in the
Category II ‘‘Mid-Atlantic bottom trawl’’
fishery.
Harbor seal (WNA stock) is added to
the list of species or stocks incidentally
killed or injured in the Category II
‘‘Mid-Atlantic bottom trawl’’ fishery.
Bottlenose dolphin (WNA offshore
stock) is added to the list of species or
stocks incidentally killed or injured in
the Category II ‘‘Northeast bottom trawl’’
fishery.
Gray seal (WNA stock) is added to the
list of species or stocks incidentally
killed or injured in the Category II
‘‘Northeast bottom trawl’’ fishery.
Commercial Fisheries on the High Seas
Fishery Classification
The high seas ‘‘Pacific highly
migratory species drift gillnet’’ fishery is
elevated from Category III to Category II
because the component of the fishery
operating in U.S. waters is elevated in
this final rule.
To correct an error in the 2011 LOF,
the high seas ‘‘Pacific highly migratory
species longline’’ fishery from is
reclassified from Category II to Category
III.
Removal of Fisheries
The Category II high seas ‘‘Pacific
highly migratory species trawl’’ ‘‘South
Pacific albacore troll trawl’’ fisheries are
removed from the LOF.
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Fishery Name and Organizational
Changes and Clarifications
The name of the Category I high seas
‘‘Western Pacific pelagic (deep-set
component) longline’’ fishery is
changed to the ‘‘Western Pacific pelagic
(HI deep-set component) longline’’
fishery.
The name of the Category II high seas
‘‘Western Pacific pelagic (shallow-set
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component) longline’’ fishery is
changed to the ‘‘Western Pacific pelagic
(HI shallow-set component) longline’’
fishery.
Number of Vessels/Persons
The estimated number of HSFCA
permits is updated for several high seas
fisheries for multiple gear types, as
outlined below.
High seas ‘‘Atlantic highly migratory
species’’ fishery for the following gear
types: longline from 77 to 81; and
handline/pole and line from 2 to 3.
High seas ‘‘Pacific highly migratory
species’’ fishery for the following gear
types: Pot from 7 to 3; longline from 75
to 85; handline/pole and line from 25 to
30; multipurpose from 7 to 5; purse
seine from 8 to 7; and troll from 271 to
258.
High seas ‘‘South Pacific albacore
troll’’ fishery for the following gear
types: Pot from 5 to 3; and troll from 59
to 51.
High seas ‘‘South Pacific tuna’’ fishery
for the following gear types: Longline
from 8 to 11; and purse seine from 35
to 33.
High seas ‘‘Western Pacific pelagic’’
fishery for the following gear types:
Deep-set longline from 127 to 124; pot
from 7 to 3; handline/pole and line from
10 to 8; multipurpose from 5 to 4; trawl
from 3 to 1; and troll from 40 to 32.
List of Species or Stocks Incidentally
Killed or Injured
Humpback whale (CA/OR/WA stock)
is added to the list of marine mammal
stocks incidentally killed or injured in
the high seas ‘‘Pacific highly migratory
species gillnet’’ fishery.
Risso’s dolphin (CA/OR/WA stock) is
removed from the list of marine
mammal stocks incidentally killed or
injured in the high seas ‘‘Pacific highly
migratory species longline’’ fishery.
Blainville’s beaked whale (unknown
stock), bottlenose dolphin (unknown
stock), Pantropical spotted dolphin
(unknown stock), Risso’s dolphin
(unknown stock), short-finned pilot
whale (unknown stock), and striped
dolphin (unknown stock) are added to
the list of species or stocks killed or
injured in the Category I high seas
‘‘Western Pacific pelagic (HI deep-set
component)’’ fishery.
Bottlenose dolphin (unknown stock),
Byrde’s whale (unknown stock), Kogia
spp. whale (unknown stock), Risso’s
dolphin (unknown stock), and striped
dolphin (unknown stock) are added to
the list of species or stocks killed or
injured in the Category II high seas
‘‘Western Pacific pelagic (HI shallow-set
component)’’ fishery.
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List of Fisheries
The following tables set forth the 2012
list of U.S. commercial fisheries
according to their classification under
section 118 of the MMPA. Table 1 lists
commercial fisheries in the Pacific
Ocean (including Alaska); Table 2 lists
commercial fisheries in the Atlantic
Ocean, Gulf of Mexico, and Caribbean;
Table 3 lists commercial fisheries on the
high seas; and Table 4 lists fisheries
affected by TRPs or TRTs.
In Tables 1 and 2, the estimated
number of vessels/persons participating
in fisheries operating within U.S. waters
is expressed in terms of the number of
active participants in the fishery, when
possible. If this information is not
available, the estimated number of
vessels or persons licensed for a
particular fishery is provided. If no
recent information is available on the
number of participants, vessels, or
persons licensed in a fishery, then the
number from the most recent LOF is
used for the estimated number of
vessels/persons in the fishery. NMFS
acknowledges that, in some cases, these
estimations may be inflations of actual
effort, such as for many of the MidAtlantic and New England fisheries.
However, in these cases, the numbers
represent the potential effort for each
fishery, given the multiple gear types
several state permits may allow for.
Changes made to Mid-Atlantic and New
England fishery participants will not
affect observer coverage or bycatch
estimates as observer coverage and
bycatch estimates are based on vessel
trip reports and landings data. Table 1
and 2 serve to provide a description of
the fishery’s potential effort (state and
Federal). If NMFS is able to extract more
accurate information on the gear types
used by state permit holders in the
future, the numbers will be updated to
reflect this change. For additional
information on fishing effort in fisheries
found on Table 1 or 2, NMFS refers the
reader to contact the relevant regional
office (contact information included
above in SUPPLEMENTARY INFORMATION).
For high seas fisheries, Table 3 lists
the number of currently valid HSFCA
permits held. Although this likely
overestimates the number of active
participants in many of these fisheries,
the number of valid HSFCA permits is
the most reliable data on the potential
effort in high seas fisheries at this time.
Tables 1, 2, and 3 also list the marine
mammal species or stocks incidentally
killed or injured in each fishery based
on observer data, logbook data,
stranding reports, disentanglement
network data, and MMAP reports. This
list includes all species or stocks known
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to be injured or killed in a given fishery,
but also includes species or stocks for
which there are anecdotal records of an
injury or mortality. Additionally,
species identified by logbook entries,
stranding data, or fishermen self-reports
(i.e., MMAP reports) may not be
verified. In Tables 1 and 2, NMFS has
designated those stocks driving a
fishery’s classification (i.e., the fishery is
classified based on serious injuries and
mortalities of a marine mammal stock
that are greater than 50 percent
[Category I], or greater than 1 percent
and less than 50 percent [Category II], of
a stock’s PBR) by a ‘‘1’’ after the stock’s
name.
In Tables 1 and 2, there are several
fisheries classified as Category II that
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have no recent documented injuries or
mortalities of marine mammals, or
fisheries that did not result in a serious
injury or mortality rate greater than 1
percent of a stock’s PBR level based on
known interactions. NMFS has
classified these fisheries by analogy to
other Category I or II fisheries that use
similar fishing techniques or gear that
are known to cause mortality or serious
injury of marine mammals, as discussed
in the final LOF for 1996 (60 FR 67063,
December 28, 1995), and according to
factors listed in the definition of a
‘‘Category II fishery’’ in 50 CFR 229.2
(i.e., fishing techniques, gear used,
methods used to deter marine mammals,
target species, seasons and areas fished,
qualitative data from logbooks or fisher
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reports, stranding data, and the species
and distribution of marine mammals in
the area, or at the discretion of the
Assistant Administrator for Fisheries).
NMFS has designated those fisheries
listed by analogy in Tables 1 and 2 by
a ‘‘2’’ after the fishery’s name.
There are several fisheries in Tables 1,
2, and 3 in which a portion of the
fishing vessels cross the EEZ boundary,
and therefore operate both within U.S.
waters and on the high seas. These
fisheries, though listed separately
between Table 1 or 2 and Table 3, are
considered the same fishery on either
side of the EEZ boundary. NMFS has
designated those fisheries in each table
by a ‘‘*’’ after the fishery’s name.
BILLING CODE 3510–22–P
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BILLING CODE 3510–22–C
Classification
The Chief Counsel for Regulation of
the Department of Commerce certified
to the Chief Counsel for Advocacy of the
Small Business Administration that this
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rule would not have a significant
economic impact on a substantial
number of small entities. The factual
basis for this certification was published
with the proposed rule and is not
repeated here. No comments were
received regarding the economic impact
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of this rule. As a result, a final
regulatory flexibility analysis is not
required, and none was prepared.
This final rule contains collection-ofinformation requirements subject to the
Paperwork Reduction Act. The
collection of information for the
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registration of individuals under the
MMPA has been approved by the Office
of Management and Budget (OMB)
under OMB control number 0648–0293
(0.15 hours per report for new
registrants and 0.09 hours per report for
renewals). The requirement for
reporting marine mammal injuries or
mortalities has been approved by OMB
under OMB control number 0648–0292
(0.15 hours per report). These estimates
include the time for reviewing
instructions, searching existing data
sources, gathering and maintaining the
data needed, and completing and
reviewing the collection of information.
Send comments regarding these
reporting burden estimates or any other
aspect of the collections of information,
including suggestions for reducing
burden, to NMFS and OMB (see
ADDRESSES and SUPPLEMENTARY
INFORMATION).
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 unless that collection of
information displays a currently valid
OMB control number.
This final rule has been determined to
be not significant for the purposes of
Executive Order 12866.
An environmental assessment (EA)
was prepared under the National
Environmental Policy Act (NEPA) for
regulations to implement section 118 of
the MMPA in June 1995. NMFS revised
that EA relative to classifying U.S.
commercial fisheries on the LOF in
December 2005. Both the 1995 EA and
the 2005 EA concluded that
implementation of MMPA section 118
regulations would not have a significant
impact on the human environment. This
final rule would not make any
significant change in the management of
reclassified fisheries, and therefore, this
final rule is not expected to change the
analysis or conclusion of the 2005 EA.
The Council of Environmental Quality
(CEQ) recommends agencies review EAs
every five years; therefore, NMFS
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reviewed the 2005 EA in 2009. NMFS
concluded that, because there have been
no changes to the process used to
develop the LOF and implement section
118 of the MMPA (including no new
alternatives and no additional or new
impacts on the human environment),
there was no need to update the 2005
EA at that time. If NMFS takes a
management action, for example,
through the development of a TRP,
NMFS would first prepare an
environmental document, as required
under NEPA, specific to that action.
NMFS will next review the EA to
determine if updates are necessary in
2014.
This final rule would not affect
species listed as threatened or
endangered under the Endangered
Species Act (ESA) or their associated
critical habitat. The impacts of
numerous fisheries have been analyzed
in various biological opinions, and this
final rule will not affect the conclusions
of those opinions. The classification of
fisheries on the LOF is not considered
to be a management action that would
adversely affect threatened or
endangered species. If NMFS takes a
management action, for example,
through the development of a TRP,
NMFS would conduct consultation
under ESA section 7 for that action.
This final rule would have no adverse
impacts on marine mammals and may
have a positive impact on marine
mammals by improving knowledge of
marine mammals and the fisheries
interacting with marine mammals
through information collected from
observer programs, stranding and
sighting data, or take reduction teams.
This final rule would not affect the
land or water uses or natural resources
of the coastal zone, as specified under
section 307 of the Coastal Zone
Management Act.
Report of the Serious Injury Technical
Workshop, 10–13 September 2007,
Seattle, Washington. NOAA Technical
Memorandum NMFS–OPR–39, 94p.
Baker, J.D., A.L. Harting, T.A. Wurth, and
T.C. Johanos. 2011. Dramatic shifts in
Hawaiian monk seal distribution
predicted from divergent regional trends.
Marine Mammal Science, 27: 78–93.
Forney, K.A. 2010. Serious injury
determinations for cetaceans caught
Hawaii longline fisheries during 1994–
2008. NOAA Technical Memorandum
NOAA–TM–NMFS–SWFSC–462. 24 p.
Hatfield, B.B, J.A. Ames, J.A. Estes, M.T.
Tinker, A.B. Johnson, M.M. Staedler,
M.D. Harris. 2011. Sea otter mortality in
fish and shellfish traps: estimating
potential impacts and exploring possible
solutions. Endang. Species Res., 13:219–
229.
McCracken, M.L. 2010. Adjustments to False
Killer Whale and Short-finned Pilot
Whale Bycatch Estimates. NMFS Pacific
Islands Fisheries Science Center
Working Paper WP–10–007. Issued 7
December 2010. 23 p.
NMFS 2008a. Endangered Species Act—
Section 7 Consultation Biological
Opinion and Incidental Take Statement
on the Implementation of Bottomfish
Fishing Regulations within Federal
Waters of the Main Hawaiian Islands.
Issued March 18, 2008. 37 p.
NMFS 2008b. Endangered Species Act—
Section 7 informal consultation on the
continued authorization of crustacean
fisheries in the Hawaiian Archipelago.
April 4, 2008. 10 p.
NMFS Pacific Islands Regional Observer
Program. 2004–2008. Pacific Islands
Regional Observer Program annual status
reports. Available online: https://
www.fpir.noaa.gov/OBS/
obs_qrtrly_annual_rprts.html
Rizzuto, J. 2007. Big fish await HIBT teams.
West Hawaii Today 39(218): 1B, 4B.
Rossman, M. C. 2010. Estimated bycatch of
small cetaceans in northeast U.S. bottom
trawl fishing gear during 2000–2005. J.
Northw. Atl. Fish. Sci., 42: 77–101.
doi:10.2960/J.v42. m650.
References
Dated: November 21, 2011.
Samuel D. Rauch III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
Andersen, M.S., K.A. Forney, T.V.N. Cole, T.
Eagle, R. Angliss, K. Long, L. Barre, L.
Van Atta, D. Borggaard, T. Rowles, B.
Norberg, J. Whaley, and L. Engleby.
2008. Differentiating Serious and NonSerious Injury of Marine Mammals:
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[FR Doc. 2011–30607 Filed 11–28–11; 8:45 am]
BILLING CODE 3510–22–P
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Agencies
[Federal Register Volume 76, Number 229 (Tuesday, November 29, 2011)]
[Rules and Regulations]
[Pages 73912-73953]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-30607]
[[Page 73911]]
Vol. 76
Tuesday,
No. 229
November 29, 2011
Part V
Department of Commerce
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National Oceanic and Atmospheric Administration
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50 CFR Part 229
List of Fisheries for 2012; Final Rule
Federal Register / Vol. 76, No. 229 / Tuesday, November 29, 2011 /
Rules and Regulations
[[Page 73912]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 229
[Docket No. 110207104-1536-02]
RIN 0648-BA76
List of Fisheries for 2012
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The National Marine Fisheries Service (NMFS) publishes its
final List of Fisheries (LOF) for 2012, as required by the Marine
Mammal Protection Act (MMPA). The final LOF for 2012 reflects new
information on interactions between commercial fisheries and marine
mammals. NMFS must classify each commercial fishery on the LOF into one
of three categories under the MMPA based upon the level of serious
injury and mortality of marine mammals that occurs incidental to each
fishery. The classification of a fishery in the LOF determines whether
participants in that fishery are subject to certain provisions of the
MMPA, such as registration, observer coverage, and take reduction plan
(TRP) requirements.
DATES: This final rule is effective January 1, 2012.
ADDRESSES: Comments regarding the burden-hour estimates, or any other
aspect of the collection of information requirements contained in this
final rule, should be submitted in writing to Chief, Marine Mammal and
Sea Turtle Conservation Division, Office of Protected Resources, NMFS,
1315 East-West Highway, Silver Spring, MD 20910, or to Nathan Frey,
OMB, by fax to (202) 395-7285 or by email to Nathan_Frey@omb.eop.gov.
FOR FURTHER INFORMATION CONTACT: Melissa Andersen, Office of Protected
Resources, (301) 713-2322; David Gouveia, Northeast Region, (978) 281-
9280; Laura Engleby, Southeast Region, (727) 551-5791; Elizabeth
Petras, Southwest Region, (562) 980-3238; Brent Norberg, Northwest
Region, (206) 526-6733; Bridget Mansfield, Alaska Region, (907) 586-
7642; Lisa Van Atta, Pacific Islands Region, (808) 944-2257.
Individuals who use a telecommunications device for the hearing
impaired may call the Federal Information Relay Service at 1-(800) 877-
8339 between 8 a.m. and 4 p.m. Eastern time, Monday through Friday,
excluding Federal holidays.
SUPPLEMENTARY INFORMATION:
Availability of Published Materials
Information regarding the LOF and the Marine Mammal Authorization
Program, including registration procedures and forms, current and past
LOFs, information on each Category I and II fishery, observer
requirements, and marine mammal injury/mortality reporting forms and
submittal procedures, may be obtained at: https://www.nmfs.noaa.gov/pr/interactions/lof/, or from any NMFS Regional Office at the addresses
listed below:
NMFS, Northeast Region, 55 Great Republic Drive, Gloucester, MA
01930-2298, Attn: Allison Rosner;
NMFS, Southeast Region, 263 13th Avenue South, St. Petersburg, FL
33701, Attn: Laura Engleby;
NMFS, Southwest Region, 501 W. Ocean Blvd., Suite 4200, Long Beach,
CA 90802-4213, Attn: Charles Villafana;
NMFS, Northwest Region, 7600 Sand Point Way NE., Seattle, WA 98115,
Attn: Protected Resources Division;
NMFS, Alaska Region, Protected Resources, P.O. Box 22668, 709 West
9th Street, Juneau, AK 99802, Attn: Bridget Mansfield; or
NMFS, Pacific Islands Region, Protected Resources, 1601 Kapiolani
Boulevard, Suite 1110, Honolulu, HI 96814-4700, Attn: Lisa Van Atta.
What is the list of fisheries?
Section 118 of the MMPA requires NMFS to place all U.S. commercial
fisheries into one of three categories based on the level of incidental
serious injury and mortality of marine mammals occurring in each
fishery (16 U.S.C. 1387(c)(1)). The classification of a fishery on the
LOF determines whether participants in that fishery may be required to
comply with certain provisions of the MMPA, such as registration,
observer coverage, and TRP requirements. NMFS must reexamine the LOF
annually, considering new information in the Marine Mammal Stock
Assessment Reports (SAR) and other relevant sources, and publish in the
Federal Register any necessary changes to the LOF after notice and
opportunity for public comment (16 U.S.C. 1387(c)(1)(C)).
How does NMFS determine in which category a fishery is placed?
The definitions for the fishery classification criteria can be
found in the implementing regulations for section 118 of the MMPA (50
CFR 229.2). The criteria are also summarized here.
Fishery Classification Criteria
The fishery classification criteria consist of a two-tiered, stock-
specific approach that first addresses the total impact of all
fisheries on each marine mammal stock, and then addresses the impact of
individual fisheries on each stock. This approach is based on
consideration of the rate, in numbers of animals per year, of
incidental mortalities and serious injuries of marine mammals due to
commercial fishing operations relative to the potential biological
removal (PBR) level for each marine mammal stock. The MMPA (16 U.S.C.
1362(20)) defines the PBR level 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. This definition can also be found in the
implementing regulations for section 118 of the MMPA (50 CFR 229.2).
Tier 1: If the total annual mortality and serious injury of a
marine mammal stock, across all fisheries, is less than or equal to 10
percent of the PBR level of the stock, all fisheries interacting with
the stock would be placed in Category III (unless those fisheries
interact with other stock(s) in which total annual mortality and
serious injury is greater than 10 percent of PBR). Otherwise, these
fisheries are subject to the next tier (Tier 2) of analysis to
determine their classification.
Tier 2, Category I: Annual mortality and serious injury of a stock
in a given fishery is greater than or equal to 50 percent of the PBR
level (i.e., frequent incidental mortality and serious injuries of
marine mammals).
Tier 2, Category II: Annual mortality and serious injury of a stock
in a given fishery is greater than 1 percent and less than 50 percent
of the PBR level (i.e., occasional incidental mortality and serious
injuries of marine mammals).
Tier 2, Category III: Annual mortality and serious injury of a
stock in a given fishery is less than or equal to 1 percent of the PBR
level (i.e., a remote likelihood or no known incidental mortality and
serious injuries of marine mammals).
While Tier 1 considers the cumulative fishery mortality and serious
injury for a particular stock, Tier 2 considers fishery-specific
mortality and serious injury for a particular stock. Additional details
regarding how the categories were determined are provided in the
preamble to the final rule implementing section 118 of the MMPA (60 FR
45086, August 30, 1995).
[[Page 73913]]
Because fisheries are classified on a per-stock basis, a fishery
may qualify as one Category for one marine mammal stock and another
Category for a different marine mammal stock. A fishery is typically
classified on the LOF at its highest level of classification (e.g., a
fishery qualifying for Category III for one marine mammal stock and for
Category II for another marine mammal stock will be listed under
Category II).
Other Criteria That May Be Considered
There are several fisheries on the LOF classified as Category II
that have no recent documented injuries or mortalities of marine
mammals, or fisheries that did not result in a serious injury or
mortality rate greater than 1 percent of a stock's PBR level based on
known interactions. NMFS has classified these fisheries as Category II
by analogy to other Category I or II fisheries (NMFS does not classify
fisheries as Category I based on analogy) that are sufficiently
analogous to the fishery in question (e.g., use similar fishing
techniques or gear that are known to cause mortality or serious injury
of marine mammals), or according to factors discussed in the final LOF
for 1996 (60 FR 67063, December 28, 1995) and listed in the regulatory
definition of a Category II fishery. The regulations at 50 CFR 229.2
state that in the absence of reliable information indicating the
frequency of incidental mortality and serious injury of marine mammals
by a commercial fishery, NMFS will determine whether the incidental
serious injury or mortality is ``occasional'' or ``remote'' by ``* * *
evaluating other factors such as fishing techniques, gear used, methods
used to deter marine mammals, target species, seasons and areas fished,
qualitative data from logbooks or fisher reports, stranding data, and
the species and distribution of marine mammals in the area, or at the
discretion of the Assistant Administrator for Fisheries.'' Further,
eligible commercial fisheries not specifically identified on the LOF
are deemed to be Category II fisheries until the next LOF is published
(50 CFR 229.2).
Information That May Be Considered When Classifying Fisheries
Under regulations pursuant to section 118 of the MMPA, observer
data, logbook data, stranding data, fishers' reports, anecdotal
reports, and information on incidental serious injury or mortality to
marine mammals reported in SARs are used to classify fisheries (60 FR
45086, August 30, 1995; 60 FR 67063, December 28, 1995). Further, the
factors for consideration laid out in 50 CFR 229.2 (fishing techniques,
gear used, methods used to deter marine mammals, target species,
seasons and areas fished, qualitative data from logbooks or fisher
reports, stranding data, and the species and distribution of marine
mammals in the area, or at the discretion of the Assistant
Administrator for Fisheries), generally termed ``analogy'' in the LOF,
are used to classify fisheries in the absence of reliable data on the
frequency of interactions.
How does NMFS determine which species or stocks are included as
incidentally killed or injured in a fishery?
The LOF includes a list of marine mammal species or stocks
incidentally killed or injured in each commercial fishery. To determine
which species or stocks are included as incidentally killed or injured
in a fishery, NMFS annually reviews the information presented in the
current SARs. The SARs are based upon the best available scientific
information and provide the most current and inclusive information on
each stock's PBR level and level of interaction with commercial fishing
operations. NMFS also reviews other sources of new information,
including observer data, stranding data, fisher self-reports, and
anecdotal reports.
In the absence of reliable information on the level of mortality or
injury of a marine mammal stock, or insufficient observer data, NMFS
will determine whether a species or stock should be added to, or
deleted from, the list by considering other factors such as: changes in
gear used, increases or decreases in fishing effort, increases or
decreases in the level of observer coverage, and/or changes in fishery
management that are expected to lead to decreases in interactions with
a given marine mammal stock (such as a TRP or a fishery management plan
(FMP)). NMFS will provide case-specific justification in the LOF for
changes to the list of species or stocks incidentally killed or
injured.
How does NMFS determine the levels of observer coverage in a fishery on
the LOF?
Data obtained from the observer program and the observer coverage
levels in a particular fishery are important tools in estimating the
level of annual marine mammal mortality and serious injury in
commercial fishing operations. The best available information on the
level of observer coverage, and the spatial and temporal distribution
of observed marine mammal interactions, is presented in the SARs.
Starting with the 2005 SARs, each SAR includes an appendix with
detailed descriptions of each Category I and II fishery on the LOF,
including observer coverage in those fisheries. The SARs generally do
not provide detailed information on observer coverage in Category III
fisheries because, under the MMPA, Category III fisheries are not
required to accommodate observers aboard vessels due to the remote
likelihood of mortality and serious injury of marine mammals. Fishery
information presented in the SARs' appendices includes: level of
observer coverage, target species, levels of fishing effort, spatial
and temporal distribution of fishing effort, characteristics of fishing
gear and operations, management and regulations, and interactions with
marine mammals. Copies of the SARs are available on the NMFS Office of
Protected Resources' Web site at: https://www.nmfs.noaa.gov/pr/sars/.
Information on observer coverage levels in Category I and II fisheries
can also be found in the Category I and II fishery fact sheets on the
NMFS Office of Protected Resources Web site: https://www.nmfs.noaa.gov/pr/interactions/lof/. Additional information on observer programs in
commercial fisheries can be found on the NMFS National Observer
Program's Web site: https://www.st.nmfs.gov/st4/nop/.
How do I find out if a specific fishery is in category I, II, or III?
This final rule includes three tables that list all U.S. commercial
fisheries by LOF Category. Table 1 lists all of the commercial
fisheries in the Pacific Ocean (including Alaska); Table 2 lists all of
the commercial fisheries in the Atlantic Ocean, Gulf of Mexico, and
Caribbean; and Table 3 lists all U.S.-authorized commercial fisheries
on the high seas. A fourth table, Table 4, lists all commercial
fisheries managed under applicable TRPs or take reduction teams (TRT).
Are high seas fisheries included on the LOF?
NMFS includes high seas fisheries in Table 3 of the LOF, along with
the number of valid High Seas Fishing Compliance Act (HSFCA) permits in
each fishery. As of 2004, NMFS issues HSFCA permits only for high seas
fisheries analyzed in accordance with the National Environmental Policy
Act (NEPA) and the Endangered Species Act (ESA). The authorized high
seas fisheries are broad in scope and encompass multiple specific
fisheries identified by gear type. For the purposes of the LOF, the
high seas fisheries are
[[Page 73914]]
subdivided based on gear type (e.g., trawl, longline, purse seine,
gillnet, troll, etc.) to provide more detail on composition of effort
within these fisheries. Many fisheries operate in both U.S. waters and
on the high seas, creating some overlap between the fisheries listed in
Tables 1 and 2 and those in Table 3. In these cases, the high seas
component of the fishery is not considered a separate fishery, but an
extension of a fishery operating within U.S. waters (listed in Table 1
or 2). NMFS designates those fisheries in Tables 1, 2, and 3 by a ``*''
after the fishery's name. The number of HSFCA permits listed in Table 3
for the high seas components of these fisheries operating in U.S.
waters does not necessarily represent additional effort that is not
accounted for in Tables 1 and 2. Many vessels/participants holding
HSFCA permits also fish within U.S. waters and are included in the
number of vessels and participants operating within those fisheries in
Tables 1 and 2.
HSFCA permits are valid for five years, during which time FMPs can
change. Therefore, some vessels/participants may possess valid HSFCA
permits without the ability to fish under the permit because it was
issued for a gear type that is no longer authorized under the most
current FMP. For this reason, the number of HSFCA permits displayed in
Table 3 is likely higher than the actual U.S. fishing effort on the
high seas. For more information on how NMFS classifies high seas
fisheries on the LOF, see the preamble text in the final 2009 LOF (73
FR 73032; December 1, 2008).
Where can I find specific information on fisheries listed on the LOF?
NMFS maintains summary documents, or fishery fact sheets, for each
Category I and II fishery on the LOF. These fishery fact sheets provide
the full history of each Category I and II fishery, including: when the
fishery was added to the LOF, the basis for the fishery's initial
classification, classification changes to the fishery, changes to the
list of species or stocks incidentally killed or injured in the
fishery, fishery gear and methods used, observer coverage levels,
fishery management and regulation, and applicable TRPs or TRTs, if any.
These fishery fact sheets are updated after each final LOF and can be
found under ``How Do I Find Out if a Specific Fishery is in Category I,
II, or III?'' on the NMFS Office of Protected Resources' Web site:
https://www.nmfs.noaa.gov/pr/interactions/lof/, linked to the ``List of
Fisheries by Year'' table. NMFS is developing similar fishery fact
sheets for each Category III fishery on the LOF. However, due to the
large number of Category III fisheries on the LOF and the lack of
accessible and detailed information on many of these fisheries, the
development of these fishery fact sheets will take significant time to
complete. NMFS anticipates posting the Category III fishery fact sheets
along with the final 2013 LOF, although this timeline may be revised as
this exercise progresses.
Am I required to register under the MMPA?
Owners of vessels or gear engaging in a Category I or II fishery
are required under the MMPA (16 U.S.C. 1387(c)(2)), as described in 50
CFR 229.4, to register with NMFS and obtain a marine mammal
authorization to lawfully take non-endangered and non-threatened marine
mammals incidental to commercial fishing operations. Owners of vessels
or gear engaged in a Category III fishery are not required to register
with NMFS or obtain a marine mammal authorization.
How do I register and receive my authorization certificate and injury/
mortality reporting forms?
NMFS has integrated the MMPA registration process, implemented
through the Marine Mammal Authorization Program (MMAP), with existing
state and Federal fishery license, registration, or permit systems for
Category I and II fisheries on the LOF. Participants in these fisheries
are automatically registered under the MMAP and are not required to
submit registration or renewal materials directly under the MMAP.
In the Southwest, Northwest, and Alaska regions, NMFS will issue
vessel or gear owners an authorization certificate and/or injury/
mortality reporting forms via U.S. mail or with their state or Federal
license at the time of renewal.
In the Pacific Islands region, NMFS will issue vessel or gear
owners who hold a Federal permit an authorization certificate and/or
injury/mortality reporting forms via U.S. mail or with their Federal
permit at the time of renewal; for vessel or gear owners holding state
licenses only, NMFS will issue an authorization certificate via U.S.
mail automatically at the beginning of each calendar year. Individuals
participating in Category I or II fisheries who obtain state commercial
marine licenses after the beginning of the calendar year may request an
authorization certificate and/or injury/mortality reporting forms by
contacting the NMFS Pacific Islands Regional Office at (808) 944-2200.
In the Northeast region, NMFS will issue vessel or gear owners an
authorization certificate via U.S. mail automatically at the beginning
of each calendar year; but vessel or gear owners must request or print
injury/mortality reporting forms by contacting the NMFS Northeast
Regional Office at (978) 281-9328 or by visiting the Northeast Regional
Office Web site (https://www.nero.noaa.gov/).
In the Southeast region, NMFS will issue vessel or gear owners
notification of registry and vessel or gear owners may receive their
authorization certificate and/or injury/mortality reporting form by
contacting the Southeast Regional Office at (727) 209-5952 or by
visiting the Southeast Regional Office Web site (https://sero.nmfs.noaa.gov/pr/mm/mmap.htm) and following the instructions for
printing the necessary documents.
The authorization certificate, or a copy, must be on board the
vessel while it is operating in a Category I or II fishery, or for non-
vessel fisheries, in the possession of the person in charge of the
fishing operation (50 CFR 229.4(e)). Although efforts are made to limit
the issuance of authorization certificates to only those vessel or gear
owners that participate in Category I or II fisheries, not all state
and Federal permit systems distinguish between fisheries as classified
by the LOF. Therefore, some vessel or gear owners in Category III
fisheries may receive authorization certificates even though they are
not required for Category III fisheries. Individuals fishing in
Category I and II fisheries for which no state or Federal permit is
required must register with NMFS by contacting their appropriate
Regional Office (see ADDRESSES).
How do I renew my registration under the MMPA?
In Pacific Islands, Southwest, Alaska or Northeast regional
fisheries, registrations of vessel or gear owners are automatically
renewed and participants should receive an authorization certificate by
January 1 of each new year. In Northwest regional fisheries, vessel or
gear owners receive authorization with each renewed state fishing
license, the timing of which varies based on target species. Vessel or
gear owners who participate in these regions and have not received
authorization certificates by January 1 or with renewed fishing
licenses must contact the appropriate NMFS Regional Office (see
ADDRESSES).
[[Page 73915]]
In Southeast regional fisheries, vessel or gear owners may receive
an authorization certificate by contacting the Southeast Regional
Office or visiting the Southeast Regional Office Web site (https://sero.nmfs.noaa.gov/pr/mm/mmap.htm) and following the instructions for
printing the necessary documents.
Am I required to submit reports when I injure or kill a marine mammal
during the course of commercial fishing operations?
In accordance with the MMPA (16 U.S.C. 1387(e)) and 50 CFR 229.6,
any vessel owner or operator, or gear owner or operator (in the case of
non-vessel fisheries), participating in a fishery listed on the LOF
must report to NMFS all incidental injuries and mortalities of marine
mammals that occur during commercial fishing operations, regardless of
the category in which the fishery is placed (I, II or III) within 48
hours of the end of the fishing trip. 50 CFR 229.2 defines an injury as
``a wound or other physical harm,'' and includes examples of signs of
injury. In addition, any animal that ingests fishing gear or any animal
that is released with fishing gear entangling, trailing, or perforating
any part of the body is considered injured, regardless of the presence
of any wound or other evidence of injury, and must be reported. Injury/
mortality reporting forms and instructions for submitting forms to NMFS
can be downloaded from: https://www.nmfs.noaa.gov/pr/pdfs/interactions/mmap_reporting_form.pdf or by contacting the appropriate Regional
office (see ADDRESSES). Reporting requirements and procedures can be
found in 50 CFR 229.6.
Am I required to take an observer aboard my vessel?
Individuals participating in a Category I or II fishery are
required to accommodate an observer aboard their vessel(s) upon request
from NMFS. MMPA section 118 (16 U.S.C. 1387) states that an observer
will not be placed on a vessel if the facilities for quartering an
observer or performing observer functions are inadequate or unsafe;
thereby, exempting vessels too small to accommodate an observer from
this requirement. However, observer requirements will not be exempted,
regardless of vessel size, for U.S. Atlantic Ocean, Caribbean, Gulf of
Mexico large pelagics longline vessels operating in special areas
designated by the Pelagic Longline Take Reduction Plan implementing
regulations (50 CFR 229.36(d)). Observer requirements can be found in
50 CFR 229.7.
Am I required to comply with any marine mammal take reduction plan
regulations?
Table 4 in this final rule provides a list of fisheries affected by
TRPs and TRTs. TRP regulations can be found at 50 CFR 229.30 through
229.36. A description of each TRT and copies of each TRP can be found
at: https://www.nmfs.noaa.gov/pr/interactions/trt/.
Sources of Information Reviewed for the Final 2012 LOF
NMFS reviewed the marine mammal incidental injury, serious injury
and mortality information presented in the SARs for all fisheries. The
SARs are based on the best scientific information available at the time
of preparation, including the level of serious injury and mortality of
marine mammals that occurs incidental to commercial fishery operations
and the PBR levels of marine mammal stocks. The information contained
in the SARs is reviewed by regional Scientific Review Groups (SRGs)
representing Alaska, the Pacific (including Hawaii), and the U.S.
Atlantic, Gulf of Mexico, and Caribbean. The SRGs were created by the
MMPA to review the science that informs the SARs, and to advise NMFS on
marine mammal population status, trends, and stock structure,
uncertainties in the science, research needs, and other issues.
NMFS also reviewed other sources of new information, including
marine mammal stranding data, observer program data, fisher self-
reports, reports to the SRGs, conference papers, anecdotal reports,
FMPs, and ESA documents.
The final LOF for 2012 was based on information provided in the
NEPA and ESA documents analyzing authorized high seas fisheries;
stranding data; fishermen self-reports through the MMAP; observer
program reports; anecdotal reports; and the final SARs for 1996 (63 FR
60, January 2, 1998), 2001 (67 FR 10671, March 8, 2002), 2002 (68 FR
17920, April 14, 2003), 2003 (69 FR 54262, September 8, 2004), 2004 (70
FR 35397, June 20, 2005), 2005 (71 FR 26340, May 4, 2006), 2006 (72 FR
12774, March 19, 2007), 2007 (73 FR 21111, April 18, 2008), 2008 (74 FR
19530, April 29, 2009), 2009 (75 FR 12498, March 16, 2010), and 2010
(76 FR 34054, June 10, 2011). The SARs are available at: https://www.nmfs.noaa.gov/pr/sars/.
Fishery Descriptions
Beginning with the final 2008 LOF (72 FR 66048, November 27, 2007),
NMFS describes each Category I and II fishery on the LOF. Below, NMFS
describes the fisheries classified as Category I or II on the 2012 LOF
that were not classified as such on a previous LOF (and therefore have
not yet been defined on the LOF). Additional details for Category I and
II fisheries operating in U.S. waters are included in the SARs, FMPs,
and TRPs, through state agencies, or through the fishery fact sheets
available on the NMFS Office of Protected Resources Web site (https://www.nmfs.noaa.gov/pr/interactions/lof/). Additional details for
Category I and II fisheries operating on the high seas are included in
various FMPs, NEPA, or ESA documents.
State and regional abbreviations used in the following text
include: AK (Alaska), BSAI (Bering Sea, Aleutian Islands), CA
(California), DE (Delaware), FL (Florida), GMX (Gulf of Mexico), HI
(Hawaii), MA (Massachusetts), ME (Maine), MHI (Main Hawaiian Islands),
NC (North Carolina), NY (New York), OR (Oregon), RI (Rhode Island), SC
(South Carolina), VA (Virginia), WA (Washington), and WNA (Western
North Atlantic).
Southeastern U.S. Atlantic, Gulf of Mexico Stone Crab Trap/Pot Fishery
The ``Southeastern U.S. Atlantic, Gulf of Mexico stone crab trap/
pot'' fishery operates primarily nearshore in the State of FL. Stone
crab fishing outside of this area is likely very minimal. In 2010, the
State of FL issued 1,282 commercial stone crab licenses and 1,190,285
stone crab trap tags. FL state regulations limit recreational stone
crab trap/pot numbers to five per person (FL Administrative Code
(F.A.C.) Chapter 68B-13). The season for commercial and recreational
stone crab harvest is from October 15 to May 15. Traps are the most
typical gear type used for the commercial and recreational stone crab
fishery. Commercial traps must be designed to conform to the
specifications established under U.S. 50 CFR 654.22, as well as F.A.C.
Chapter 68B-13. Baited traps are frequently set in waters of 65 ft
(19.8 m) depth or less in a double line formation, generally 100-300 ft
(30.5-91.4 m) apart, running parallel to a bottom contour. The margins
of seagrass flats and bottoms with low rocky relief are also favored
areas for trap placement. Buoys are attached to the trap/pot via float
line. In FL, commercial trap/pot buoys are required to be marked with
the letter ``X,'' the trap owner's stone crab endorsement number (in
characters at
[[Page 73916]]
least 2 inches high), and a tag that corresponds to a valid FWC-issued
trap certificate. Recreational trap/pot buoys, except those fished from
a dock, must have a permanently affixed and legible ``R'' at least 2
inches high and the harvester's name and address (Ch. 68B-13.009(3),
F.A.C).
Comments and Responses
NMFS received 19 comment letters on the proposed 2012 LOF (76 FR
37716, June 28, 2011). Comments were received from the Blue Water
Fishermen's Association, Center for Biological Diversity, Florida Fish
and Wildlife Conservation Commission, Florida Keys Commercial
Fishermen's Association, Freezer Longline Coalition, Garden State
Seafood Association, Hawaii Longline Association, Humane Society of the
United States, Marine Mammal Commission, Natural Resources Defense
Council, State of Hawaii, U.S. Fish and Wildlife Service, Western
Pacific Regional Fishery Management Council, and 6 individuals.
Comments on issues outside the scope of the LOF were noted, but are
generally not responded to in this final rule.
General Comments
Comment 1: An individual commenter recommends NMFS inform the U.S.
Department of Defense (DOD) of the LOF, NMFS, and MMPA. The commenter
further wondered whether the Navy is also a contributor of injury or
death of animals listed on the LOF, if the process is complying with
Advisory Council on Historic Preservation Section 106, and, if so,
which Native Hawaiian Organizations are involved.
Response: Certain military readiness activities are subject to
sections 101(a)(5)(A) and (D) of the MMPA, which authorizes the
Secretary of Commerce to allow, upon request, the incidental, but not
intentional taking of marine mammals subject to required notifications
and determinations. However, the Navy is not subject to section 118 of
the MMPA, which applies to commercial fisheries. National Historic
Preservation Act (NHPA) section 106 generally requires federal agencies
to consult the appropriate State Historic Preservation Office (SHPO)
and/or Tribal or Native Hawaiian groups on undertakings, including
projects, activities, and programs that may affect qualifying historic
properties. The LOF only involves classification determinations for
commercial fisheries based upon marine mammal interactions, and is not
a federal undertaking under the NHPA.
Comment 2: The Marine Mammal Commission (Commission) acknowledges
NMFS' efforts for summarizing and providing information about observer
coverage and other characteristics of listed fisheries, and commends
NMFS for its efforts to centralize information used to classify
Category III fisheries and looks forward to seeing this effort come to
fruition. The Commission appreciates that NMFS has considered their
concerns and is exploring ways to fully and effectively convey the
reasons for listing fisheries, which must be based on the best
available information and may or may not include observer-derived data.
Response: NMFS agrees that summarizing the information used as the
basis to classify each fishery on the LOF in one location could be
useful for interested readers. NMFS has posted information on each
Category I and II fishery on the LOF on the NMFS Office of Protected
Resources Web site, where it can be considered at the readers'
discretion, and is pleased the Commission finds the information useful
while reviewing the LOF. NMFS is developing similar fishery fact sheets
for each Category III fishery and anticipates posting those fishery
fact sheets along with the final 2013 LOF. However, due to the large
number of Category III fisheries on the LOF and the lack of accessible
and detailed information on many of these fisheries, this timeline may
be revised as this exercise progresses.
Comment 3: The Center for Biological Diversity (CBD) notes that the
proposed 2012 LOF once again includes aquaculture operations as
Category III fisheries and reiterates comments on past LOFs that
aquaculture facilities are not ``commercial fishing operations''
eligible for the take authorization contained in Section 118 of the
MMPA. The CBD states that these operations consistently compete with
marine mammals for habitat and resources due to their stationary
nature; therefore, aquaculture facilities and activities are more
appropriately subject to the take prohibitions and permitting regimes
contained in Section 101 of the MMPA.
Response: NMFS received similar comments on the 2009 and 2010 LOFs.
Section 118 of the MMPA governs the ``taking of marine mammals
incidental to commercial fishing operations.'' The MMPA does not
provide a definition of a commercial fishing operation; therefore, NMFS
defined ``commercial fishing operation'' in regulations at 50 CFR
229.2. The definition was presented in the proposed and final rules
implementing the regulations for section 118 of the MMPA (60 FR 31666,
June 16, 1995; 60 FR 65086, August 30, 1995). As noted in those
proposed and final rules, and in the responses to comments on the 2009
and 2010 LOFs (73 FR 73032, December 1, 2008, comment/response 5; 74 FR
58859, November 16, 2009, comment/response 11), the definition of a
``commercial fishing operation'' includes aquaculture. The regulations
in 50 CFR 229.2 define a ``commercial fishing operation'' as ``the
catching, taking, or harvesting of fish from the marine environment * *
*. The term includes * * * aquaculture activities.'' Further, ``fishing
or to fish'' is defined as ``any commercial fishing operation.''
Therefore, aquaculture fisheries are considered commercial fisheries
that are managed under section 118 of the MMPA and are therefore
included on the annual LOF.
Comment 4: The CBD urges NMFS not to reclassify fisheries to a less
serious category when information on the fishery and its interactions
with marine mammals is scant. In these cases, the CBD urges NMFS to
instead rely more heavily upon the known impacts of the fishery's gear
and the marine mammals known to inhabit the area being fished, rather
than relying, for example, on the lack of reported interactions in
fisheries with little or no observer coverage. The CBD states that
every Federal FMP by law must include ``a standardized reporting
methodology to assess the amount and type of bycatch,'' and that the
ESA and MMPA make no exceptions to protection on the basis of state
versus Federal fisheries. The CBD asserts that failure to assess marine
mammal bycatch is an unacceptable justification for denying marine
mammals protection via the LOF.
Response: NMFS considers a broad range of information when
proposing or making fishery classification decisions on the LOF, and
does not classify fisheries based solely on the presence or absence of
serious injuries or mortalities obtained through observer programs.
Under regulations pursuant to section 118, NMFS uses observer data,
logbook data, stranding data, fishers' reports, anecdotal reports,
qualitative factors outlined in 50 CFR 229.2 (i.e., fishing techniques,
gear used, methods used to deter marine mammals, target species,
seasons and areas fished, qualitative data from logbooks or fisher
reports, stranding data, and the species and distribution of marine
mammals in the area), information on incidental serious injury or
mortality to marine mammals reported in SARs (50 CFR 229.2; 60 FR
45086, August 30, 1995; 60 FR 67063, December 28, 1995), and input
received during the public comment periods.
[[Page 73917]]
NMFS considers all of the information to determine whether the fishery
can be classified on the LOF based on quantitative information analyzed
through the Tier 1 and 2 analyses; or whether the fishery can be
classified on the LOF based on the qualitative information outlined in
NMFS regulations at 50 CFR 229.2 (and presented above).
Comments on Commercial Fisheries in the Pacific Ocean
Comment 5: The Freezer Longline Coalition (FLC) recommends the
``BSAI Pacific cod longline'' fishery be reclassified as Category III
because the annual serious injury and mortality for all stocks listed
as killed or injured in this fishery is less than 1 percent of PBR for
the most recent five-year period (2004-2008). The FLC states that the
2010 SAR shows that there are no serious injuries or mortalities of
killer whales (AK resident stock) or ribbon seals from 2004-2008, and
the mean annual serious injury and mortality of Steller sea lions
(Western distinct population segment) is 0.488 percent of PBR; however,
the fishery continues to be classified as Category II based on serious
injury and mortality of resident killers whales from 2002-2006. The FLC
asserts that the fishery should not continue to be classified based on
outdated data simply because NMFS has been unable to ``finalize'' data
for 2007 and 2008, which is inconsistent with the MMPA's best available
science mandate, the Information Quality Act, and NMFS' associated
guidelines.
Response: The classification of fisheries for the proposed 2012 LOF
was based on the best available scientific information at the time the
fishery classifications were made. In this case, the most current
available information on serious injury and mortality of marine mammals
was presented in the final 2010 SAR, which included an analysis data
from 2002-2006. More recent data from a new analysis for the 2007-2010
period will be available for use in classifying fisheries on the 2013
LOF. At that time, NMFS will consider the information available from
the new analysis and consider a reclassification for the BSAI Pacific
cod longline fishery, if appropriate.
Comment 6: The FLC asserts that the estimated mortality reported in
the SARs for AK longline fisheries uses incorrect observer coverage
percentages, resulting in significant overestimation of mortality. The
FLC further asserts that the default recovery factors used for multiple
AK marine mammal stocks need to be re-evaluated for populations that
are increasing, have a large population, or whose population status is
known.
Response: NMFS does not calculate observer percentages or recovery
factors in the annual LOF, instead this information is provided in the
SARs after NMFS and the Alaska SRG have evaluated the information
during their annual review. Therefore, NMFS suggests the FLC submit
this comment during the public comment period for the draft 2011 SARs.
Further, NMFS responded to similar comments on the 2009 SARs and
therefore refers the FLC to that Federal Register notice for additional
information (75 FR 12498, March 16, 2010; comment/response 13 and 16).
Comment 7: The Commission concurs that the ``CA thresher shark/
swordfish drift gillnet'' fishery meets the criteria for Category II
and concurs with the designation of the CA/OR/WA stock of humpback
whales as the basis for that classification.
Response: NMFS acknowledges this comment. The ``CA thresher shark/
swordfish drift gillnet'' fishery is classified as Category II in this
final rule.
Comment 8: The Humane Society of the United States (HSUS) supports
the elevation of the ``CA thresher shark/swordfish drift gillnet''
fishery to Category II. The HSUS notes that there is a long-standing
record of interactions between drift gillnet fisheries and protected
species worldwide and feels it is appropriate for NMFS to develop a
better understanding of this driftnet fishery and the extent to which
it interacts with marine mammals through use of observer coverage,
which is more likely for a fishery placed in Category II.
Response: NMFS acknowledges this comment and notes that this
fishery is subject to requirements under the Pacific Offshore Cetacean
Take Reduction Plan and is regulated under the Fishery Management Plan
for U.S. West Coast Fisheries for Highly Migratory Species, which
authorizes NOAA to place observers on fishing vessels in west coast
highly migratory species fisheries (such as drift gillnet), regardless
of the LOF category.
Comment 9: The U.S. Fish and Wildlife Service (USFWS) reiterated a
recommendation made on the 2011 LOF to include southern sea otters on
the list of species/stocks killed or injured in the Category III ``CA
spiny lobster trap'' or the ``CA coonstripe shrimp, rock crab, tanner
crab pot or trap'' fisheries because experiments have shown that sea
otters can enter these traps and drown. The USFWS provided a
publication by Hatfield et al. (2011) to support this recommendation.
Response: NMFS responded to a similar comment on the 2011 LOF (75
FR 68475, November 8, 2010, comment/response 13) and provided detailed
information on an extensive review of marine mammal interactions with
West Coast trap and pot gear in the proposed 2009 LOF (73 FR 33760,
June 13, 2008). In 2008, NMFS Southwest Regional Office (SWRO)
consulted with experts on marine mammals and pot/trap fisheries
including the NMFS Southwest Fisheries Science Center, NMFS Northwest
Fisheries Science Center, NMFS Northwest Regional Office, and CA
Department of Fish and Game (CDFG) to evaluate which fisheries may be
affecting marine mammals. The primary intent of the analysis was to
review interactions between trap/pot gear and humpback whales, but all
marine mammals were addressed in the review. During the 2008 review,
the only information available on southern sea otter interactions with
trap/pot gear were stranding records of from 1987 and 1991 (2008 SAR;
pers. comm. with staff from CDFG). At that time, NMFS determined that
sea otters should be removed from the list of species killed or injured
in the ``CA spiny lobster trap'' and the ``CA coonstripe shrimp, rock
crab, tanner crab pot or trap'' fisheries because the information was
approximately 20 years old and there had been no indications of
interactions since that time. NMFS SWRO continues to consult with NMFS
and CDFG specialists regarding marine mammal interactions with trap/pot
gear. NMFS has not received additional information since 2008 to
suggest that southern sea otters are currently being incidentally
killed or injured in pot and trap gear.
As part of their public comment, the USFWS submitted a paper by
Hatfield et al. (2011), detailing experiments that indicate sea otters
can enter and become entrapped in traps with openings of certain sizes.
However, this paper presented no evidence of such takes occurring
during commercial fishing activities off CA. The possibility of an
interaction is insufficient justification to include southern sea
otters on the list of species incidentally injured or killed in the
``CA spiny lobster trap'' or the ``CA coonstripe shrimp, rock crab,
tanner crab pot or trap'' fisheries. Instead, NMFS needs some
indication that takes are occurring or have occurred in these fisheries
in recent years (e.g., fisher self reports, observer data, stranding
data). If additional information becomes available to indicate that
southern sea otters have been injured or killed in CA trap/pot
fisheries in recent years, NMFS
[[Page 73918]]
will consider including this species on the LOF at that time.
Comment 10: The Hawaii Longline Association (HLA) believes that the
abundance estimate for the false killer whale (pelagic stock) is not
scientifically sound and, because the survey data used for that
abundance estimate was collected in 2002, that NMFS is using data it
knows to be stale to make LOF determinations for the 2012 LOF (as
defined by NMFS guidelines). The HLA views these errors to be
particularly acute because NMFS completed a new marine mammal survey in
the Hawaiian EEZ in 2010; however, this current, available data are not
the data upon which the proposed 2012 LOF is based. Therefore, the HLA
asserts that if the 2012 LOF is issued as proposed (i.e., not based on
the 2010 data), it would violate the MMPA's ``best available science''
mandate.
Response: NMFS used the best available science in preparing the
2012 LOF. Proposed changes to the 2012 LOF were developed in spring and
summer 2011, and were largely based on the draft and final 2010 SARs,
which were the most recent SARs available. NMFS conducted a new
cetacean assessment survey in the U.S. EEZ around the Hawaiian Islands
(HICEAS II) in August-December 2010, with the goal of updating
abundance estimates for all Hawaiian cetaceans. The survey data are
currently being analyzed, and abundance estimates and PBR calculations
based on the data are not yet available. Preliminary estimates of
abundance based on the visual sightings data will be included in the
draft 2012 SAR, which is expected to be published and available for
public review and comment in spring 2013. The acoustic and other data
collected during the survey will take longer to analyze, and abundance
estimates will likely be revised in future SARs to incorporate the new
analysis. The currently available data and estimates still constitute
the best available information within existing NMFS parameters and
therefore are appropriately included in the final 2010 SARs, draft 2011
SARs, and the 2012 LOF.
Comment 11: The Western Pacific Fishery Management Council
(Council) and the HLA both recommend that the ``HI shallow-set
(swordfish target) longline/set line'' fishery be classified as a
Category III. The Council and the HLA note that this fishery is
classified as Category II based on one serious injury of a bottlenose
dolphin (HI stock) within the HI EEZ. The commenters note that the only
other fishery to have incidental serious injury or mortality of this
stock is the ``HI deep-set (tuna target) longline/set line'' fishery,
and the combined serious injury and mortality rate for these two
fisheries is less than 10 percent of PBR. The Council and HLA further
note that the analysis for fishery classification places all fisheries
interacting with a stock in Category III if the total interaction rate
is equal to or less than 10 percent of the PBR unless a fishery
qualifies for another Category for a different stock; however, no other
marine mammal stock qualifies the HI shallow-set fishery for Category I
or II.
Response: NMFS concurs that, based on the marine mammal
interactions within the U.S. EEZ reported in the final 2010 SAR, the
shallow-set longline fishery would meet the definition of a Category
III fishery. There are no marine mammal stocks within the EEZ that have
mortality and serious injury that exceed 10 percent of PBR across all
fisheries and that individually exceed 1 percent of PBR in the shallow-
set fishery. However, there are documented injuries and mortalities of
numerous species and stocks of marine mammals by the shallow-set
longline fishery on the high seas, which are listed in Table 3 for the
high seas component of the shallow-set longline fishery (``Western
Pacific Pelagic (HI Shallow-set component)''). Because there currently
are no abundance estimates or PBRs available for most of these marine
mammal stocks on the high seas, quantitative comparison of mortality
and serious injury against PBR is currently not possible.
MMPA regulations (50 CFR 229.2) provide that in the absence of
reliable information indicating the frequency of incidental mortality
and serious injury of marine mammals by a commercial fishery, NMFS will
determine whether the incidental serious injury or mortality is
``occasional'' by evaluating other factors such as fishing techniques,
gear used, methods used to deter marine mammals, target species,
seasons and areas fished, qualitative data from logbooks or fisher
reports, stranding data, and the species and distribution of marine
mammals in the area, or at the discretion of the Assistant
Administrator. HI-based shallow-set fishing vessels operating within
the U.S. EEZ and on the high seas employ the same vessels, the same
fishing methods and gear, target the same fish stocks, and employ the
same marine mammal mitigation and deterrence measures. A review of NMFS
observer data indicates that approximately 7 percent of shallow-set
trips from 2004-2008 had marine mammal interactions, including
interactions with Bryde's whale, Risso's dolphin, humpback whale,
striped dolphin, bottlenose dolphin, and Kogia sp. whale (pygmy or
dwarf sperm whale). The number and rate of marine mammal interactions
increased each year in that 5-year timeframe. Of the 22 total marine
mammal interactions observed on 325 shallow-set trips from 2004-2008,
19 were taken on the high seas. Seventeen of the total 22 observed
interactions resulted in mortality or serious injury, 16 of which
occurred on the high seas (Forney, 2010; NMFS Pacific Islands Regional
Observer Program, 2004-2008). Although NMFS is currently unable to
quantitatively establish the impact of these interactions on high seas
marine mammal stocks because of the lack of population information,
these interactions do provide qualitative evidence that the shallow-set
fishery continues to have ``occasional'' interactions with marine
mammals and should remain a Category II commercial fishery.
As noted in the preamble of the proposed 2012 LOF and the response
to a comment in the final 2010 LOF (74 FR 58859, November 16, 2009;
comment/response 17) regarding high seas fisheries classification, the
high seas portion of the shallow-set longline fishery is an extension
of the fishery operating within U.S. waters, and is not a separate
fishery. A fishery is classified on the LOF as its highest level of
classification (e.g., a fishery qualifying for Category II for one
marine mammal stock and Category III for another marine mammal stock
will be listed as Category II). Because the ``Western Pacific Pelagic
(HI Shallow-set component)'' and ``HI shallow-set (swordfish target)
longline/set line'' are two components of the same fishery, both
components are classified as Category II.
The Category II classification is further supported by data in the
draft 2011 SAR, which was not available when the proposed 2012 LOF was
drafted. The draft 2011 SAR reports an observed serious injury to a
false killer whale in the shallow-set fishery within the U.S. EEZ in
2009. Based on one observed non-serious injury in 2008 and one observed
serious injury in 2009, the shallow-set fishery has an average annual
mortality and serious injury rate of 0.2 HI pelagic false killer whales
per year within the EEZ. This represents approximately 8 percent of the
stock's PBR level, which also qualifies it as a Category II fishery.
Comment 12: The HLA disagrees with the addition of the insular
stock of false killer whales to the list of stocks incidentally injured
or killed in the ``HI deep-set (tuna target) longline/set line''
fishery because the inclusion is based
[[Page 73919]]
on NMFS' proration of an isolated non-serious interaction between this
fishery's insular stock and pelagic stock interaction rate, which is
not based on the best available science. The HLA asserts that this
fishery has never been observed to interact with the insular stock and
that the interaction in question occurred in an area where no member of
the insular stock has ever been observed in or near, and that NMFS has
no genetic evidence showing that the deep-set fishery has ever
interacted with a member of the insular stock. The HLA also disagrees
with NMFS' extension of the 140 km insular stock ``range'' uniformly
around the MHI based on a single tagged animal over 100 km to the south
of the MHI.
Response: NMFS determines which species or stocks are included as
incidentally killed or injured in a fishery by annually reviewing the
information presented in the current SARs, among other relevant
sources. The SARs are based on the best available scientific
information and provide the most current and inclusive information on
each stock, including range, abundance, PBR level, and level of
interaction with commercial fishing operations. The LOF does not
analyze or evaluate the SARs. The commenter questions the validity of
the data and calculations contained within the SAR for false killer
whales; and, thus, NMFS encourages the commenter to submit this comment
during the public comment period for the draft SAR.
The draft 2011 SAR for false killer whales indicates an average of
0.6 mortalities or serious injuries of HI insular false killer whales
per year incidental to the HI-based deep-set longline fishery. One non-
serious injury to a false killer whale was observed within the overlap
zone between the HI insular and HI pelagic stocks of false killer
whales. In the SAR, all estimated takes, and observed takes for which
an injury severity determination could not be made, were prorated based
on the proportions of observed interactions that resulted in death or
serious injury, or non-serious injury between 2000-2009. Further, takes
of false killer whales of unknown stock origin within the insular/
pelagic stock overlap zone were prorated assuming that the density of
the insular stock declines and the density of the pelagic stock
increases with increasing distance from shore. No genetic samples are
available to establish stock identity for these takes, but both stocks
are considered at risk of interacting with longline gear within this
region.
Additionally, the draft 2011 SAR reports that from 2005-2009, eight
unidentified cetaceans, known to be either false killer whales or
short-finned pilot whales (together termed ``blackfish'') were
seriously injured in the deep-set longline fishery within U.S. EEZ
waters, two of which were taken within the insular stock range. The
draft 2011 SAR prorates blackfish to each species and stock based on
their distance from shore (see McCracken, 2010 for details on the
distance-from-shore model).
For these reasons, NMFS is not changing its proposal to add the HI
insular stock of false killer whales on the list of marine mammal
stocks incidentally killed or injured in the HI deep-set longline
fishery. For a more complete analysis of the methodology for
determining mortality and serious injury of insular and pelagic false
killer whales, the commenter is referred to the draft 2011 SAR.
Comment 13: The CBD recommends NMFS classify ``American Samoa
longline'' fishery as Category I based on analogy to the ``HI deep-set
(tuna target) longline/set line'' fishery, interactions with false
killer whales, and interactions with rough-toothed dolphins, citing
three arguments. First, CBD notes that NMFS has proposed to require
longline hooks in this fishery are set at depths of 100 meters or
deeper to reduce interactions with Pacific green sea turtles (76 FR
32929, June 7, 2011), which will make the gear and methods like the
Category I Hawaii deep-set longline fishery. Second, CBD asserts that
even though abundance estimates are unavailable for the American Samoa
false killer whale stocks, the human-caused mortality falls within the
range of likely PBRs for both of these marine mammal stocks and the
2010 SAR concludes that the false killer whales in American Samoa would
probably be strategic if abundance estimates were available. Lastly,
CBD notes that this fishery also interacts with the American Samoa
stock of rough-toothed dolphins, for which the 2010 SAR indicates the
estimated rate of fisheries-related mortality or serious injury (3.6
dolphins per year) is within the range of likely PBRs (3.4-22).
Response: Abundance estimates for the American Samoa stocks of
false killer whales and rough-toothed dolphins are unknown, and PBRs
cannot be calculated. The final 2010 SARs present a plausible range of
abundance estimates for each stock based on density estimates of the
species in other areas of the Pacific, and calculate a range of likely
PBRs using those ranges of abundance. The SARs further note that
estimated mortality and serious injury of false killer whales exceeds
the range of the stock's likely PBRs, and mortality and serious injury
of rough-toothed dolphin falls within the range of the stock's likely
PBRs. These estimates provide an indication that cetacean bycatch in
the fishery is not insignificant. However, without an actual
calculation of PBR, NMFS cannot accurately evaluate the effect of
mortality and serious injury on the stocks to determine whether the
fishery meets the definition of a Category I fishery. Under NMFS
regulations, a Category I is one that cause frequent mortality or
serious injury of marine mammals, which is defined as ``one that is by
itself responsible for the annual removal of 50 percent or more of any
stock's potential biological removal level'' (50 CFR 229.2). Only in
the absence of reliable information indicating the frequency of
incidental mortality and serious injury of marine mammals does NMFS
consider other factors that may be used to classify the fishery as
either Category II or III, including evaluation of fishing techniques,
gear used, methods used to deter marine mammals, target species,
seasons and areas fished, qualitative data from logbooks or fisher
reports, stranding data, and the species and distribution of marine
mammals in the area, or at the discretion of the Assistant
Administrator (50 CFR 229.2). Until quantitative information is
available to allow a calculation of PBR, NMFS will retain the American
Samoa longline fishery as Category II, by analogy to other longline
fisheries.
Comment 14: The CBD recommended NMFS classify the ``HI vertical
longline'' and ``HI kaka line'' fisheries as Category I based on
serious injury and mortality of false killer whales (HI insular stock),
which is proposed to be listed as endangered under the ESA (75 FR
70169, November 17, 2010). The CBD notes that the ESA scientific
Biological Review Team (BRT) for this stock found a high level of
current and future risk from interactions with troll, handline,
shortline, and kaka line fisheries (Id. at 70180), and the BRT stated
that although ``each of these fisheries is required by law under the
MMPA to report interactions with marine mammals, the low number of
reports strongly suggests that interactions are occurring and are not
being reported'' (Id. at 70179). Lastly, the CBD asserts that a high
level of anecdotal evidence, including fishermen that have reported
shooting at false killer whales and a high rate of dorsal fin
disfigurements consistent with injuries from unidentified fishing line,
and the fact that the State of HI does not monitor
[[Page 73920]]
bycatch of marine mammals in any of its state fisheries, also suggest
that the fisheries are having a greater impact than is reported.
Therefore, the CBD asserts that the scientific information and opinion
show that fisheries interactions present a high risk of extinction to
the insular false killer whale, compelling NMFS to list these fisheries
as Category I, especially in light of what appears to be deliberate
efforts to obscure fishery mortality in order to prevent further
protection for an endangered marine mammal.
Response: At this time, there is no quantitative information to
support a Category I classification for either of these fisheries. As
stated in the response to comment 13, a Category I fishery is one that
NMFS determines has frequent incidental mortality and serious injury of
marine mammals, defined as one that is, by itself, responsible for the
annual removal of 50 percent or more of any stock's PBR level (50 CFR
229.2). NMFS considers other factors when determining whether a fishery
meets the definition of a Category II or III fishery, including
evaluation of fishing techniques, gear used, methods used to deter
marine mammals, target species, seasons and areas fished, qualitative
data from logbooks or fisher reports, stranding data, and the species
and distribution of marine mammals in the area, or at the discretion of
the Assistant Administrator (50 CFR 229.2). Currently, NMFS does not
have reliable information that either of these fisheries causes
frequent incidental mortality and serious injury of marine mammals,
such that would support classification of a Category I fishery, as that
term is defined. Based on the currently available information, NMFS
continues to believe that these two fisheries present a remote
likelihood of interactions with marine mammals. NMFS is retaining these
fisheries on the LOF as Category III fisheries but will consider any
information that supports a reevaluation of the fisheries'
classification in the future.
Comment 15: The CBD comments that the various fisheries that are
known or suspected of interacting with Hawaiian monk seals should be
classified as Category I because, given the critically endangered
status of the monk seal, any interaction is significant. The CBD notes
that fishery interactions are becoming more common (Baker et al.,
2011), yet all Hawaiian fisheries known or suspected of interactions
with monk seals, such as the Hawaii lobster trap and the Hawaii tuna
handline, are listed as Category III. Further, the CBD asserts that,
while a PBR is not calculated for this stock (final 2010 SAR), any
mortality from fisheries would qualify the fishery for Category I if a
PBR was calculated.
Response: The LOF lists the Hawaiian monk seal on the list of
species and stocks incidentally killed or injured in the Category III
``HI lobster trap'' and ``HI Main Hawaiian Islands (MHI) deep sea
bottomfish handline'' fisheries. In the 2009 LOF, NMFS removed the
Hawaiian monk seal from the list of species/stocks killed/injured in
the ``HI tuna handline fishery,'' under which the stock had been listed
since the 1996 LOF, because NMFS has never received a report of
interactions between monk seals and tuna handline gear. The available
information on Hawaiian monk seal interactions with the other two
fisheries is:
(1) ``HI lobster trap'' fishery: There have not been any reported
interactions since the mid-1980s, when one seal died in a trap; and
(2) ``HI Main Hawaiian Islands deep sea bottomfish handline
fishery:'' A Federal observer program of the Northwestern Hawaiian
Islands (NWHI) bottomfish handline fishery was conducted from the
fourth quarter of 2003 through 2005, and no monk seal interactions were
observed. The fishery has since been phased out as required under the
Proclamation establishing the Papahanaumokuakea Marine National
Monument. While fishing in the NWHI has been phased out, in previous
years when commercial bottomfish boats were fishing in this area, NMFS
received one self-reported incident (a hooking in 1994), and bottomfish
hooks were observed in two seals at the French Frigate Shoals (one