List of Fisheries for 2010, 58859-58901 [E9-27431]
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Federal Register / Vol. 74, No. 219 / Monday, November 16, 2009 / Rules and Regulations
(vi) Court/Jurisdiction.
(vii) The nature and circumstances
surrounding the conviction.
(viii) Protective measures taken by the
individual or business concern to reduce or
eliminate the risk of further misconduct.
(ix) Whether the individual has made full
restitution for the felony.
(x) Whether the individual has accepted
responsibility for past misconduct resulting
in the felony conviction.
(6) Upon the request of the Contracting
Officer, and prior to contract award, in
addition to information described in
paragraph (d)(5) of this clause, the business
concern must provide such other
documentation as is requested by the
Contracting Officer to use in determining and
evaluating ownership, control, or operation;
the nature of the felonies committed; and
such other information as is needed to make
a decision on whether award should be made
to the offeror under the Federal Protective
Service Guard Contracting Reform Act of
2008. The refusal to timely provide such
documentation may serve as grounds to
preclude contract award.
(e)(1) Privacy Statement. The offeror shall
provide the following statement to any
individual whose information will be
submitted in an award request pursuant to
(d)(5) and (6) of this clause.
(2) Privacy Notice. The collection of this
information is authorized by the Federal
Protective Service Guard Contracting Reform
Act of 2008 (Pub. L. 110–356) and
Department of Homeland Security (DHS)
implementing regulations at Homeland
Security Acquisition Regulation (HSAR) 48
CFR 3009.171. This information is being
collected to determine whether an individual
that owns, controls, or operates the business
concern submitting this offer has been
convicted of a felony that would disqualify
the offeror from receiving an award. This
information will be used by and disclosed to
DHS personnel and contractors or other
agents who require this information to
determine whether an award request should
be approved or denied. Additionally, DHS
may share this personal information with the
U.S. Justice Department and other Federal
and State agencies for collection,
enforcement, investigatory, or litigation
purposes, or as otherwise authorized.
Submission of this information by the
individual is voluntary, however, failure to
provide it may result in denial of an award
to the offeror. Individuals who wish to
correct inaccurate information in or to
remove their information from an offer that
has been submitted should contact the
business concern submitting the offer and
request correction. Should individuals seek
to correct inaccurate information or remove
their information from an offer that has been
submitted in response to a solicitation for
FPS guard services prior to contract award,
an authorized representative of the business
concern submitting the offer must contact the
contracting officer of record and request that
the firm’s offer be formally withdrawn or
submit a correction to the award request.
After contract award, it is recommended that
an authorized representative of the business
concern that submitted the inaccurate or
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erroneous information contact the
contracting officer of record. The contracting
officer will handle such requests on a case by
case basis.
(f) Disclosure. The offeror under this
solicitation represents that [Check one]:
lIt is not a business concern owned,
controlled, or operated by an individual
convicted of a felony.
lIt is a business concern owned,
controlled, or operated by an individual
convicted of a felony, and has submitted an
award request pursuant to paragraph (d) of
this clause.
(g) If an award request is applied for, the
offeror shall attach the request with
supporting documentation, to the bid or
proposal. The supporting documentation
may include copies of prior award requests
granted to the offeror.
(h) The notification in this paragraph
applies if this is an indefinite delivery/
indefinite quantity contract, blanket purchase
agreement, or other contractual instrument
that may result in the issuance of task orders,
calls or option to extend the terms of a
contract. The Contractor must immediately
notify the Contracting Officer in writing upon
any felony conviction of personnel who own,
control or operate a business concern as
defined in paragraph (c) of this clause at any
time during the performance of this contract.
Upon notification of a felony conviction the
Contracting Officer will review and make a
new determination of eligibility prior to the
issuance of any task order, call or exercise of
an option.
(End of clause)
[FR Doc. E9–27330 Filed 11–13–09; 8:45 am]
BILLING CODE 9111–28–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 229
[Docket No. 090218194–91045–02]
RIN 0648–AX65
List of Fisheries for 2010
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 2010, as
required by the Marine Mammal
Protection Act (MMPA). The final LOF
for 2010 reflects new information on
interactions between commercial
fisheries and marine mammals. NMFS
must categorize 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
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mammals that occurs incidental to each
fishery. The categorization 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 requirements.
DATES: This final rule is effective
January 1, 2010.
ADDRESSES: See SUPPLEMENTARY
INFORMATION for a listing of all Regional
Offices. 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 David Rostker, OMB, by fax
to 202–395–7285 or by email to
DavidlRostker@omb.eop.gov.
FOR FURTHER INFORMATION CONTACT:
Melissa Andersen, Office of Protected
Resources, 301–713–2322; David
Gouveia, Northeast Region, 978–281–
9280; Anne Ney, Southeast Region, 727–
551–5758; 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, 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: Marcia Hobbs;
NMFS, Southeast Region, 263 13th
Avenue South, St. Petersburg, FL 33701,
Attn: Anne Ney;
NMFS, Southwest Region, 501 W.
Ocean Blvd., Suite 4200, Long Beach,
CA 90802–4213, Attn: Lyle Enriquez;
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
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9th Street, Juneau, AK 99802, Attn:
Bridget Mansfield; or
NMFS, Pacific Islands Region,
Protected Resources, 1601 Kapiolani
Boulevard, Suite 1100, 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 take
reduction plan 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)).
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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
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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.
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.
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.
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 proposed rule
implementing section 118 of the MMPA
(60 FR 45086, August 30, 1995).
Because fisheries are categorized 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 categorized 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
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 of 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 for Fisheries
(50 CFR 229.2). Further, eligible
commercial fisheries not specifically
identified on the LOF are deemed to be
Category II fisheries until the next LOF
is published.
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How Does NMFS Determine which
Species and Stocks are Included as
Incidentally Killed or Injured in a
Fishery?
The LOF includes a list of marine
mammal species and stocks incidentally
killed or injured in each commercial
fishery. To determine which species and
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, and fisher
self-reports.
When reliable information and
sufficient levels of observer coverage are
available, the most recent five years of
data are used to determine whether a
species or stock should be added to, or
deleted from, the list of species and
stocks incidentally killed or injured in
each commercial fishery. 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
fishery management plan (FMP) or a
take reduction plan (TRP)). NMFS will
provide case-specific justification in the
LOF for changes to the list of species
and stocks incidentally killed or
injured.
How Does NMFS Determine the Level of
Observer Coverage in a Fishery?
Data obtained from observers and the
level of observer coverage are important
tools in estimating the level of 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 in the
LOF, including observer coverage. The
SARs generally do not provide detailed
information on observer coverage in
Category III fisheries because, under the
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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. 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 Resource’s website at: https://
www.nmfs.noaa.gov/pr/sars/.
Additional information on observer
programs in commercial fisheries can be
found on the NMFS National Observer
Program’s website: https://
www.st.nmfs.gov/st4/nop/.
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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
fisheries in the Pacific Ocean (including
Alaska); Table 2 lists all of the fisheries
in the Atlantic Ocean, Gulf of Mexico,
and Caribbean; Table 3 lists all U.S.authorized fisheries on the high seas. A
fourth table, Table 4, lists all fisheries
managed under applicable take
reduction plans or teams.
Are High Seas Fisheries Included on
the LOF?
Beginning with the 2009 LOF, NMFS
includes high seas fisheries in Table 3
of the LOF, along with the number of
valid High Sea 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 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 the fishery operating
within U.S. waters (listed in Table 1 or
2). In these fisheries, a single vessel may
set both within the U.S. Exclusive
Economic Zone (EEZ) and on the high
seas during a single fishing trip. NMFS
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designates those fisheries in Tables 1, 2,
and 3 by an ‘‘*’’ 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
do not necessarily represent additional
fishers that are not accounted for in
Tables 1 and 2. Many fishers holding
these permits also fish within U.S.
waters and are included in the number
of vessels and participants operating
within those fisheries in Table 1 and 2.
HSFCA permits are valid for five
years, during which time FMPs can
change. Therefore, some fishers 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).
Are Treaty Tribal Fisheries Included on
the LOF?
In the final rule implementing section
118 of the MMPA (60 FR 45086, August
30, 1995) NMFS concluded that treaty
tribal fisheries are conducted under the
authority of the Indian treaties; the
MMPA’s requirements in section 118 do
not apply to treaty Indian tribal
fisheries. NMFS explained this decision
in the final rule stating (the remaining
text in this paragraph is quoted
direction from the final rule at 60 FR
45086, August 30, 1995), ‘‘ the rights to
fish and hunt are already secured
separately for Northwest tribes pursuant
to their treaties with the United States.
NMFS reviewed the relationship of the
Northwest Indian treaties to the MMPA
and did not find clear evidence that
Congress intended to abrogate treaty
Indian rights. Section 14 of the
Amendments to the MMPA (Public Law
No. 103–238) states ’Nothing in this Act,
including any amendments to the
Marine Mammal Protection Act of 1972
made by this Act -- alters or is intended
to alter any treaty between the United
States and one or more Indian tribes.’
This provision clarifies that existing
treaty Indian fishing rights are not
affected by the amendments to the
MMPA. Therefore, tribal fisheries are
conducted under the authority of the
Indian treaties rather than the MMPA,
and the MMPA’s mandatory registration
systems do not apply to treaty Indian
fishers operating in their usual and
accustomed fishing areas. Since
inclusion of the treaty Indian fisheries
in the LOF would also establish an
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58861
obligation to obtain an MMPA
registration under section 118, NMFS
has deleted reference to tribal fisheries
in the LOF. The registration
requirements for Category I or II
fisheries will not apply to treaty Indian
tribes.’’ (60 FR 45086, August 30, 1995.)
NMFS considered, among other
things, the public comments received on
the proposed 2010 LOF and the 1994
amendments to the MMPA and
accompanying legislative history to reevaluate its 1995 conclusion to exempt
tribal fisheries from the LOF (60 FR
45086, August 30, 1995) should be
changed due to Anderson v. Evans.
NMFS determined that Anderson v.
Evans did not alter NMFS’ original
analysis in the final rule implementing
section 118 of the MMPA (60 FR 45086,
August 30, 1995); therefore, the
inclusion of tribal fisheries on the LOF
at this time is not warranted. NMFS will
continue to work on a government-togovernment basis with the affected
treaty tribal governments to gather data
on injuries and mortalities of marine
mammals incidental to tribal fisheries.
Additional information on NMFS’
decision to continue to exclude tribal
fisheries from the LOF is provided
below in the response to comments 1–
5 in the section ‘‘Comments and
Responses.’’
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 be
registered with NMFS and obtain a
marine mammal authorization to
lawfully take a non-endangered and
non-threatened marine mammal
incidental to commercial fishing.
Owners of vessels or gear engaged in a
Category III fishery are not required to
be registered with NMFS or obtain a
marine mammal authorization.
What is the Registration Process?
NMFS has integrated the MMPA
registration process, known as 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 Pacific
Islands, Southwest, Northwest, and
Alaska regions, NMFS will issue vessel
or gear owners an authorization
certificate; in the Northeast and
Southeast Regions, NMFS will issue
vessel or gear owners notification of
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registry and directions on obtaining an
authorization certificate. 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).
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How Do I Receive My Authorization
Certificate and Injury/Mortality
Reporting Forms?
All vessel or gear owners that
participate in Pacific Islands,
Southwest, Northwest, or Alaska
regional fisheries will receive their
authorization certificates and/or injury/
mortality reporting forms via U.S. mail,
or with their state or Federal license at
the time of renewal. Vessel or gear
owners participating in the Northeast
and Southeast Regional Integrated
Registration Program will receive their
authorization certificates as follows:
1. Northeast Region vessel or gear
owners participating in Category I or II
fisheries for which a state or Federal
permit is required may receive their
authorization certificate and/or injury/
mortality reporting form by contacting
the Northeast Regional Office at 978–
281–9328 or by visiting the Northeast
Regional Office Web site (https://
www.nero.noaa.gov/protlres/mmap/
certificate.html) and following
instructions for printing the necessary
documents.
2. Southeast Region vessel or gear
owners participating in Category I or II
fisheries for which a state or Federal
permit is required will receive notice of
registry and may receive their
authorization certificate and/or injury/
mortality reporting form by contacting
the Southeast Regional Office at 727–
551–5758 or by visiting the Southeast
Regional Office Web site (https://
sero.nmfs.noaa.gov/pr/pr.htm) and
following instructions for printing the
necessary documents.
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How Do I Renew My Registration
Under the MMPA?
Vessel or gear owners that participate
in Pacific Islands, Southwest, or Alaska
regional fisheries are automatically
renewed and should receive an
authorization certificate by January 1 of
each new year. Vessel or gear owners in
Washington and Oregon fisheries
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).
Vessel or gear owners participating in
Southeast or Northeast regional fisheries
may receive an authorization certificate
by calling the relevant NMFS Regional
Office or visiting the relevant NMFS
Regional Office Web site (see ‘‘How Do
I Receive My Authorization Certificate
and Injury/Mortality Reporting Forms’’).
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 Category I,
II, or III fishery must report to NMFS all
incidental injuries and mortalities of
marine mammals that occur during
commercial fishing operations. ‘‘Injury’’
is defined in 50 CFR 229.2 as a wound
or other physical harm. In addition, any
marine mammal that ingests fishing gear
or any marine mammal 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/
mmaplreportinglform.pdf. Reporting
requirements and procedures can be
found in 50 CFR 229.6.
Am I Required to Take an Observer
Aboard My Vessel?
Fishers participating in a Category I or
II fishery are required to accommodate
an observer aboard vessel(s) upon
request. MMPA Section 118 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,
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thereby exempting vessels too small to
accommodate an observer from this
requirement. However, observer
requirements will not be exempted 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)) or vessels operating in North
Carolina fisheries observed under the
Alternative Platform Program. Observer
requirements can be found in 50 CFR
229.7.
Am I Required to Comply With Any
Take Reduction Plan Regulations?
Fishers participating in a Category I or
II fishery are required to comply with
any applicable TRP regulations. Table 4
in this final rule provides a list of
fisheries affected by take reduction
teams and plans. Take reduction plan
regulations can be found at 50 CFR
229.30 through 229.36.
Sources of Information Reviewed for
the Final 2010 LOF
NMFS reviewed the marine mammal
incidental serious injury and mortality
information presented in the SARs for
all observed fisheries to determine
whether changes in fishery
classification were warranted. 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 fisheries and the PBR levels
of marine mammal stocks. The
information contained in the SARs is
reviewed by three 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, fishery
management plans, and ESA
documents.
The final LOF for 2010 was based,
among other things, on information
provided in the NEPA and ESA
documents analyzing authorized high
seas fisheries, 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
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26340, May 4, 2006), 2006 (72 FR 12774,
March 19, 2007), 2007 (73 FR 21111,
April 18, 2008), and 2008 (74 FR 19530,
April 29, 2009). 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
fisheries on the 2010 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, or through state
agencies. Additional details for Category
I and II fisheries operating on the high
seas are included in various FMPs,
NEPA, or ESA documents.
American Samoa Longline Fishery
The Category II ‘‘American Samoa
longline’’ fishery operates in waters
around American Samoa targeting tuna
(mainly albacore, also skipjack,
yellowfin and bigeye). Wahoo, sharks,
billfish, and other miscellaneous pelagic
species are also caught, with most of the
sharks and billfish released. In 2000, the
‘‘American Samoa longline’’ fishery
began to expand rapidly with the influx
of large (more than 50 ft (15.2 m) overall
length) conventional monohull vessels,
similar to the type used in the Hawaiibased longline fisheries. Vessels over 50
ft (15.2 m) may set 1,500 2,500 hooks
and have a greater fishing range and
capacity for storing fish (8 40 metric
tons). The fleet reached a peak of 66
vessels in 2001, and set a peak of almost
7,000 sets in 2002.
The rapid expansion of longline
fishing effort within the EEZ waters
around American Samoa prompted the
Western Pacific Fishery Management
Council (WPFMC) to develop a limited
entry system for the fishery,
implemented by NMFS in 2005. Under
the limited access program, NMFS
issued a total of 60 initial longline
limited entry permits in 2005 to
qualified candidates, spread among 4
vessel size classes (72 FR 10711, March
9, 2007): 22 permits issued in Class A
(less than or equal to 40 ft (12.2 m)
length); 5 in Class B (40–50 ft (12.2–15.2
m)); 12 in Class C (50–70 ft (15.2–21.3
m)); and 21 in Class D (more than 70 ft
(21.3 m)). The limited entry program
regulations cap the maximum number of
permits to the 60 initial permits issued.
Permits may be transferred, upgraded,
and renewed. In 2008, the American
Samoa longline fishery had 28 active
vessels. Observers were first placed on
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American Samoa longline vessels in
April 2006 to monitor protected species
interactions, with observer coverage
averaging approximately 6–8 percent
each year.
Under the limited entry program,
vessel operators must submit Federal
longline logbooks, vessels over 40 ft
(12.2 m) must carry observers if
requested by NMFS, and vessels over 50
ft (15.2 m) must have an operational
vessel monitoring system. In addition,
vessel owners and operators of vessels
registered to an American Samoa
longline limited entry permit must
attend a protected species workshop
annually, carry and use dip nets, line
clippers, and bolt cutters, and follow
handling, resuscitation, and release
requirements for incidentally hooked or
entangled sea turtles (70 FR 69282,
November 15, 2005). There are existing
regulations intended to mitigate sea
turtle incidental hookings, and in 2009
the WPFMC recommended additional
measures be implemented to minimize
interactions with green sea turtles,
including modifications to gear to place
hooks below 100 m (328 ft) depth and
to increase observer coverage (WPFMC
144th Meeting, March 23–26, 2009).
Current regulations include a
prohibition on U.S. vessels greater than
50 ft (15.2 m) in length from using
longline gear within 50 nmi around the
islands of American Samoa. American
Samoa longline fishery regulations can
be found at 50 CFR 665.36–38.
HI Shortline Fishery
The Category II ‘‘HI shortline’’ fishery
is a small-scale system operating off the
State of HI, and targeting bigeye tuna
(Thunnus obesus) or the lustrous
pomfret (Eumigistes illustris). This
fishery was developed to target these
fish species when they concentrate over
the summit of Cross Seamount (290 km
(180 mi) south of the State of HI). The
gear style is designed specifically to
target the aggregating fish species over
seamount structures. The primary gear
type used is a horizontal main line
(monofilament) less than 1 nmi long,
and includes two baskets of
approximately 50 hooks each. The gear
is set before dawn and has a short soak
time, with the gear retrieved about two
hours after it is set. This fishery has no
seasonal component and may operate
year-round. There are no specific fishing
permits issued for this fishery. However,
all persons with a State of Hawaii
Commercial Marine License (CML) may
participate in any fishery, including the
‘‘HI shortline’’ fishery. Of those persons
possessing CMLs, shortline
participation has changed from 5 to 11
vessels during 2003–2008. From 2003–
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2008, there was an average of 135,757
pounds (lbs) of fish landed each year. In
2008 alone, 104,152 lbs of fish were
landed. Currently, there is no reporting
system in place to document potential
marine mammal interactions in this
fishery. However, there are anecdotal
reports of interactions off the north side
of the island of Maui, but the species
and extent of interactions are unknown.
Comments and Responses
NMFS received 11 comment letters on
the proposed 2010 LOF (74 FR 27739,
June 11, 2009). Comments were received
from the California Department of Fish
and Game, California Wetfish Producers
Association, Center for Biological
Diversity, Columbia River Inter-Tribal
Fish Commission, Eighteen Western
Washington Indian Tribes, Garden State
Seafood Association, Hawaii Longline
Association, Makah Tribal Council,
Makah Tribe’s marine mammal
biologist, Marine Conservation Alliance,
and Marine Mammal Commission.
Comments on issues outside the scope
of the LOF were noted, but are not
responded to in this final rule.
Comments on Tribal Treaty Fisheries
Inclusion on the 2010 LOF
During the public comment phase for
the then-proposed 2009 LOF, NMFS
received a comment requesting the 2009
LOF be amended to include tribal
fisheries. The commenter stated that ‘‘in
light of the subsequent holding of the
Ninth Circuit in Anderson v.
Evans...finding that the MMPA applies
to the Makah application to the gray
whale hunt NMFS’ 1995 conclusion
exempting tribal fisheries from the LOF
and the Section 118 authorization
process is no longer valid’’ (73 FR
73039, December 1, 2008; comment/
response 4). In response to this 2009
LOF comment, NMFS included a
request for public comment in the
proposed 2010 LOF (74 FR 27739, June
11, 2009) on whether or not to include
treaty tribal fisheries on future LOFs.
Below, NMFS summarizes each
comment received on the 2010 proposed
LOF related to tribal fisheries and issues
one response following the collective
tribal fisheries comments.
Comment 1: The Center for Biological
Diversity (CBD) reiterated a comment on
the 2009 LOF (73 FR 73039, December
1, 2008; comment/response 4), noting
that in an earlier decision the Ninth
Circuit Court of Appeals determined
that MMPA requirements applied to the
Makah application to hunt gray whales
(Anderson v. Evans, 371 F.3d 475 (9th
Cir. 2004)). The CBD stated that the
decision demonstrated that MMPA
requirements can be harmonized with
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treaty rights. Therefore, the CBD
encouraged NMFS to move forward
with determining how best to
harmonize tribal fishing and treaty
rights with MMPA requirements such
that all fisheries operating in US waters
are included in the LOF and categorized
as I, II or III, as appropriate.
Comment 2: The Marine Mammal
Commission (MMC) recommended
NMFS (1) include tribal fisheries on the
LOF, (2) revise its regulations
implementing section 118 (e.g., 50
C.F.R. § 229.1 (d)) to clarify that treaty
tribal fisheries are subject to the
requirements of the MMPA, including
section 118, and (3) begin working with
the affected tribes to integrate the
registration process with existing
licensing or permitting systems if it
appears that some tribal fisheries will be
listed as category I or category II
fisheries.
Comment 3: The Makah Tribe
presented data indicating that tribal
incidental takes of marine mammals do
not present any conservation issues
notwithstanding NMFS’ 1995 decision
to exclude treaty tribal fisheries from
the LOF. The Makah Tribe compiled
data regarding incidental take in its
treaty fisheries and requires that all
mortality or injury resulting from an
incidental take, required in Makah
Tribal regulations to be reported to the
Tribe, and submits an annual report to
NMFS. Records of these reports have
been kept since the Tribe hired a marine
mammal biologist in 2003. In general
the rate of incidental take of marine
mammals during fishing operations is
low. From 2003–2009, the Makah Tribal
fisheries incidentally killed 12 harbor
seals (1 in 2003, 6 in 2004, 4 in 2008,
1 in 2009), 1 Dall’s porpoise (in 2004),
5 harbor porpoise (2 in 2004, 3 in 2008),
6 unknown small odontocetes (in 2005),
1 Steller sea lion (in 2008), 1
unidentified sea lion (in 2008), and 2
sea otters (in 2004). One unidentified
whale and one gray whale were
successfully released after entanglement
(in 2005 and 2009, respectively).
The Makah tribe noted that, despite a
long history of interactions between
Makah Tribal fishers and marine
mammals, these animals remain
abundant, as indicated by NMFS’ SARs.
Observed take of marine mammals by
the Makah Tribe’s treaty fisheries is well
below PBR for each stock. In addition,
populations of marine mammal stocks
which are most likely to interact with
Makah tribal fisheries have either
increased or remained stable since the
MMPA was amended in 1994 and
NMFS determined that treaty tribal
fisheries would not be included in the
LOF: CA sea lions have increased 5.6
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percent/year since the 1970s; WA/OR
stock of harbor seals has been stable
since 1996; Inland WA stock of harbor
seals has been stable at carrying
capacity since 1994; Outer coast stock of
harbor porpoises has been stable; Inland
WA stock of harbor porpoise 2002
population estimate is three times more
than the 1996 estimate; Eastern stock of
Steller sea lions increased 3.1 percent/
year (with regional variances); and WA
stock of sea otters increased at 8
percent/year.
Comment 4A: The Makah Indian
Tribe outlined three arguments
(comments 4A, 4B, and 4C in this final
rule) for the continued exclusion of
treaty tribal fisheries from the LOF,
based on its experience with the MMPA
and as a party to Anderson v. Evans.
The Makah Indian Tribe also joined and
fully incorporated the comments in the
joint tribal letter submitted by eighteen
other Western Washington treaty tribes
(see comments 5A, 5B, and 5C in this
final rule) asserting that NMFS’ 1995
rule interpreting the relationship
between the Tribe’s treaty-reserved right
to take fish and Section 118 of the
MMPA has not been affected by
Anderson v. Evans and continues to be
valid. Therefore, the Makah Tribe
recommends that NMFS reaffirm its
1995 decision that treaty tribal fisheries
are not subject to the MMPA’s
mandatory registration and that treaty
tribal fisheries will not be included in
the LOF.
The Makah Tribe’s first argument for
the continued exclusion of treaty tribal
fisheries from the LOF was that the
proper reading of the 1994 MMPA
Amendments’ treaty savings clause
(section 14) protects incidental take of
marine mammals by tribal fishers
because the treaty fishing right, as
understood by the Indian signatories,
includes the right to take marine
mammals incidental to tribal fisheries.
Comment 4B: The Makah Tribe’s
second argument for the continued
exclusion of treaty Tribal fisheries from
the LOF was that Anderson v. Evans
was wrongly decided (a position which
the United States has also repeatedly
expressed) and, therefore, should not be
extended to the LOF. The Makah Tribe
asserted that although Anderson v.
Evans addressed direct take of marine
mammals such as the Makah gray whale
hunt, by its own terms it does not apply
to the question of incidental take in
treaty tribal fisheries. Therefore, the
Makah Tribe believed NMFS need not
and should not extend the decision to
the issues of mandatory registration and
inclusion in the LOF.
During the Anderson v. Evans case,
the United States took the position that
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the panel opinion was incorrectly based
on numerous fundamental errors in
reaching its conclusion. In the Makah
Tribe’s opinion, if NMFS were to extend
Anderson v. Evans to the LOF issue, it
would further reinforce the panel’s
numerous incorrect applications of
settled precedent and directly contradict
the United States’ ongoing disagreement
with the case. Moreover, the Makah
Tribe concluded that it would
substantially undermine the Makah’s
and other western Washington Tribes’
treaty rights notwithstanding their
express protection by the 1994
Amendments. The Makah Tribe
believed such a decision would
contravene Congress’s express intent.
Comment 4C: The Makah Tribe’s third
argument for the continued exclusion of
treaty Tribal fisheries from the LOF was
that the Makah Tribe does and will
continue to work with NMFS to protect
marine mammals. The Makah Tribe
noted that NMFS’ 1995 rule excluding
treaty tribal fisheries from the LOF was
based in part on the extensive
cooperation between the tribes and
NMFS in managing tribal fisheries,
including their interactions with marine
mammals (See 60 FR at 45096, Aug. 30,
1995). The Makah Tribe noted that in
the 1995 final rule, NMFS found that
tribal self-regulation and cooperation
with NMFS were instrumental to the
agency achieving its responsibilities to
protect marine mammals.
Comment 5A: NMFS received two
separate letters, each representing
multiple Washington Indian tribes that
were similar to each other in the
arguments presented. Therefore, the two
comments presented in the two letters
are summarized together below. The
first letter represented the comments of
the Columbia River Inter-Tribal Fish
Commission (Nez Perce, Umatilla,
Warm Springs and Yakama Tribes), the
second letter represented the joint
comments of eighteen Indian Tribes of
western Washington State (Lummi
Nation, Quinault Indian Nation,
Swinomish Indian Tribal Community,
and Nooksack, Tulalip, Suquamish,
Squaxin Island, Nisqually, Puyallup,
Sauk-Suiattle, Skokomish, Muckleshoot,
Port Gamble, Jamestown, Lower Elwha,
Upper Skagit, Quileute, and
Stillaguamish Indian Tribes),
collectively, the ‘‘Tribes.’’ The Tribes
outlined three arguments (comments
5A, 5B, and 5C in this final rule)
asserting that NMFS’ 1995 conclusion
that treaty fisheries are properly
excluded from the LOF (60 FR 45086,
August 30, 2009; at 45096) was correct,
and remains correct.
The Tribes’ first argument was that
NMFS’ 1995 conclusion remains correct
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because the Tribes’ rights are reserved
by various treaties and the U.S. has
broad trust responsibility to the Tribes.
Comment 5B: The Tribes’ second
argument was that NMFS’ 1995
conclusion regarding Tribal fisheries
remains correct because it is not affected
by the rulings of the Ninth Circuit in
Anderson v. Evans. The Tribes asserted
that Anderson v. Evans involved the
Makah Tribe’s exercise of its express
whaling rights in the Treaty of Neah
Bay, and was wholly unrelated to the
Makah Tribe’s - or any other Tribes’ treaty right to take fish. The Tribes
argued that the Anderson v. Evans court
did not address the applicability of the
1994 MMPA amendments to treaty
fisheries or the exercise of any other
treaty rights, but instead focused solely
on the applicability of the MMPA’s
general take prohibition, which has no
Indian treaty savings clause, to the
Makah Tribe’s gray whale hunt. The
Tribes asserted that as a result of the
narrow scope of the case, the court did
not address - nor did it have any reason
to address - the MMPA’s provisions
governing incidental take of marine
mammals in commercial fisheries, much
less treaty tribal fisheries. In the Tribes’
opinion, because Anderson v. Evans did
not address Section 118 of the Act, the
1994 amendments (including the treaty
savings clause) or the 1995 rule, it is
inapplicable to the 2010 LOF
rulemaking. The Tribes also asserted
that the incidental take of marine
mammals in treaty fisheries is well
within the treaty rights protected by the
1994 treaty savings clause, a statute
which must be construed liberally in
favor of the Indians.
Comment 5C: The Tribes’ third
argument was that NMFS’ 1995
conclusion regarding Tribal fisheries
remains accurate because the Tribes’
regulate their fisheries (including
interactions with marine mammals) and
NMFS retains authority to regulate tribal
fisheries should the principle of
conservation necessity deem it
necessary. In the Tribes’ opinion, NMFS
need not take the radical step of
reversing its 1995 rule with respect to
treaty tribal fisheries and the LOF
because, as a practical and legal matter,
the agency is fully capable of protecting
marine mammals under the existing
rule. Finally, the Tribes noted that, just
as in 1995 when NMFS asserted its
authority to regulate tribal fisheries
under the treaty rights principle of
conservation necessity, NMFS retains
that option should the impact of treaty
tribal fisheries on certain marine
mammal species reach the threshold to
apply the conservation necessity
principle. Thus, NMFS retains the
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authority to regulate treaty fisheries
under appropriate circumstances.
Response: In the final rule
implementing section 118 of the MMPA
(60 FR 45086, August 30, 1995) NMFS
concluded that treaty tribal fisheries are
conducted under the authority of Indian
treaties; therefore, the MMPA’s
requirements in section 118 do not
apply to treaty Indian tribal fisheries.
NMFS explained this decision in the
1995 final rule stating (the remaining
text in this paragraph is quoted directly
from the final rule at 60 FR 45086,
August 30, 1995), ‘‘ the rights to fish and
hunt are already secured separately for
Northwest tribes pursuant to their
treaties with the United States. NMFS
reviewed the relationship of the
Northwest Indian treaties to the MMPA
and did not find clear evidence that
Congress intended to abrogate treaty
Indian rights. Section 14 of the
Amendments to the MMPA (Public Law
No. 103–238) states ‘‘Nothing in this
Act, including any amendments to the
Marine Mammal Protection Act of 1972
made by this Act -- alters or is intended
to alter any treaty between the United
States and one or more Indian tribes. ’’
This provision clarifies that existing
treaty Indian fishing rights are not
affected by the amendments to the
MMPA. Therefore, tribal fisheries are
conducted under the authority of the
Indian treaties rather than the MMPA,
and the MMPA’s mandatory registration
systems do not apply to treaty Indian
fishers operating in their usual and
accustomed fishing areas. Since
inclusion of the treaty Indian fisheries
in the LOF would also establish an
obligation to obtain an MMPA
registration under section 118, NMFS
has deleted reference to tribal fisheries
in the LOF. The registration
requirements for Category I or II
fisheries will not apply to treaty Indian
tribes.’’ (60 FR 45086, August 30, 1995.)
NMFS considered the public
comments received on the proposed
2010 LOF, existing Indian treaties
providing rights for tribal fisheries, the
statutory provisions and context of the
MMPA, and the legislative history of the
1994 amendments to the MMPA in
evaluating whether the 1995 decision to
exempt treaty tribal fisheries from the
LOF should be changed due to
Anderson v. Evans, 371 F.3d 475 (9th
Cir. 2004). NMFS has determined that
the facts and holding of Anderson v.
Evans do not alter NMFS’ original
analysis in the final rule implementing
section 118 of the MMPA (60 FR 45086,
August 30, 1995). Anderson v. Evans
applied to directed hunt of marine
mammals and not incidental take of
marine mammals by fishers. Section 118
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58865
of the MMPA specifically regulates
incidental take of marine mammals by
commercial fishers. The court in
Anderson v. Evans did not address the
treaty savings clause, which restricts the
application of section 118 in the context
of tribal treaty rights. In addition, NMFS
continues to adhere to a policy of
implementing the Federal trust
responsibility by protecting treaty
fishing rights of tribes. NMFS also will
continue to work closely with the
affected tribal governments on a
government-to-government basis to
gather data on injuries and mortalities of
marine mammals incidental to tribal
fisheries. In light of the above, NMFS
did not include in the 2010 LOF the
treaty tribal fisheries where tribal fishers
exercise their treaty-protected fishing
rights.
Based on the information presented in
the final 2008 SARs and provided in
Indian Tribal self-reports, there is no
indication that any marine mammal
bycatch associated with tribal fisheries
presents a biological concern for
applicable stocks. In the event this
becomes an issue, NMFS would
consider invoking the treaty-rights
principle of ‘‘conservation necessity’’ to
protect marine mammals.
The 2008 SARs show that nine
species have been or are incidentally
seriously injured and killed in Pacific
Northwest treaty tribe fisheries, though
many of these species have not been
seriously injured or killed in recent
years. All of the takes by tribal fisheries
listed in the 2008 SARs are from nondepleted stocks of marine mammals.
One take occurring after publication of
the 2008 SARs was from a depleted
stock. Below is a summary of the
information provided in the 2008 SARs
as well as information available from
tribal self-reporting since publication of
the 2008 SARs. Please see the 2008
SARs for more detailed information on
these stocks and/or their interactions
with treaty tribal fisheries.
(1) California sea lions: Current
estimates of annual serious injury or
mortality of this stock in tribal fisheries
is zero to two animals/year. The stock’s
PBR level is 8,511.
(2) Harbor seal (OR/WA coast): The
Northern WA marine set gillnet (tribal
fishery in coastal waters) fishery
seriously injured or killed 3 harbor seals
in 2000 and 6 in 2004. The PBR for this
stock is 1,343 and the minimum total
fishery mortality and serious injury is
less than 10 percent of the PBR.
Therefore, fishery mortality and serious
injury appears to be insignificant and
approaching a zero mortality and
serious injury rate.
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(3) Harbor seal (WA inland waters):
The Puget Sound treaty and non-treaty
sockeye salmon gillnet fishery seriously
injured or killed one harbor seal in
1994. The PBR for this stock is 771 and
the minimum estimated fishery
mortality and serious injury for this
stock appears to be less than 10 percent
of the PBR. Therefore, fishery mortality
and serious injury appears to be
insignificant and a approaching zero
mortality and serious injury rate.
(4) Harbor Porpoise (Northern CA/
Southern OR): One harbor porpoise
mortality was documented for the
Klamath River tribal salmon gillnet
fishery in 1995. The PBR for this stock
is 259 and the minimum estimated
fishery mortality and serious injury for
this stock appears to be less than 10
percent of the PBR. Therefore, fishery
mortality and serious injury appears to
be insignificant and approaching a zero
mortality and serious injury rate.
(5) Harbor Porpoise (OR/WA coast):
The Northern WA marine set gillnet
(tribal fishery in coastal waters) fishery
seriously injured or killed 3 harbor
porpoise in 2000. In addition, 2 harbor
porpoise (stock unknown) were reported
killed in 2004 in a Makah Tribal fishery
(Makah Tribe self-reports). Based on the
range of the stock and the location of the
Makah fisheries, the animals were either
part of the OR/WA coast stock or the
WA Inland Waters stock. The PBR for
this stock is 277 and the minimum
estimated fishery mortality and serious
injury for this stock appears to be less
than 10 percent of the PBR. Therefore,
fishery mortality and serious injury
appears to be insignificant and
approaching zero mortality and serious
injury rate.
(6) Harbor Porpoise (WA inland
waters): The Puget Sound treaty and
non-treaty sockeye salmon gillnet
fishery seriously injured or killed one
harbor porpoise in 1994. As stated
above, 2 harbor porpoise (stock
unknown) were reported killed in 2004
in a Makah Tribal fishery (Makah Tribe
self-reports). Based on the range of the
stock and the location of the Makah
fisheries, the animals were either part of
the OR/WA coast stock or the WA
Inland Waters stock. The PBR for this
stock is 63. While the status of the WA
Inland Waters stock relative to its
Optimum Sustainable Population level
and population trends is unknown, the
uncorrected estimate of abundance in
Washington inland waters was
significantly greater in 2002–2003 than
in 1996.
(7) Dall’s Porpoise (CA/OR/WA): The
Puget Sound salmon drift gillnet tribal
fishery seriously injured or killed one
Dall’s porpoise in the period from 2000
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to 2004. The PBR for this stock is 318
and the minimum estimated fishery
mortality and serious injury for this
stock appears to be less than 10 percent
of the PBR. Therefore, fishery mortality
and serious injury appears to be
insignificant and approaching a zero
mortality and serious injury rate.
(8) Sea otter (WA): Sea otters (WA) are
managed by the U.S. Fish and Wildlife
Service. According to the Service’s 2008
SAR, the Makah Northern Washington
marine set-gillnet fishery seriously
injured or killed 11 sea otters over a
period of 13 years between 1988 and
2001 (2008 SAR) and 2 sea otters in
2004 (Makah Indian Tribe self-report).
The stock has increased at a rate of 8
percent since 1989. The PBR for this
stock is 11 per year. The Service was
unable to determine whether the level of
human-caused mortalities and serious
injuries are insignificant and
approaching a zero mortality and
serious injury rate, based on a lack of
information on the level of all sources
of human-caused serious injury and
mortality of this stock. However, the
current population estimate of 1,125 is
above the lower end of the Optimum
Sustainable Population (60 percent of
the maximum carrying capacity for the
stock) (2008 SAR).
In addition to the information
provided in the 2008 SARs, recent selfreports from the Makah Indian Tribe
show additional serious injury and
mortality of marine mammal stocks not
yet represented in the SARs (see
comment 3 above). The Makah Indian
Tribe’s self-reported data indicate that
Makah fisheries interacted with three
marine mammal stocks in 2008 and
2009.
(1) In 2009, a gray whale was
entangled in a Makah fishery and
released alive. The Eastern North Pacific
gray whales are currently considered to
be at the stock’s Optimum Sustainable
Population size (2008 SAR).
(2) In 2008, a Steller sea lion was
killed in a Makah fishery. Based on the
geographical range of the species, this
animal was most likely from the Eastern
stock of Steller sea lions, which is listed
as threatened under the ESA and
therefore considered depleted under the
MMPA. Based on currently available
data, the minimum estimated U. S.
commercial fishery-related mortality
and serious injury for Eastern Steller sea
lions is less than that 10 percent of the
stock’s PBR of 200 per year; therefore,
fishery mortality and serious injury
appears to be insignificant and
approaching a zero mortality and
serious injury rate (2008 SAR). In
addition, the Eastern Steller sea lion
population has been consistently
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increasing at an overall annual rate of
3.1 percent throughout most of the range
(Oregon to southeastern Alaska), which
may indicate that this stock is reaching
Optimum Sustainable Population size
(2008 SAR).
(3) In 2008, 3 harbor porpoises were
killed in a Makah fishery. While the
stock is unknown, based on the
geographic range of the stock and the
location of the Makah fisheries, the
animals were either part of the OR/WA
coast stock or the WA Inland Waters
stock. As stated above, the PBR for this
OR/WA coast stock is 277 and the
minimum estimated fishery mortality
and serious injury for this stock appears
to be less than 10 percent of the PBR.
Therefore, fishery mortality and serious
injury appears to be insignificant and
approaching zero mortality and serious
injury rate. Also stated above, while the
status of the WA Inland Waters stock
relative to its Optimum Sustainable
Population level and population trends
is unknown, the uncorrected estimate of
abundance in Washington inland waters
was significantly greater in 2002–2003
than in 1996 (2008 SARs).
NMFS will continue to work closely
with the affected tribal governments on
a government-to-government basis to
gather data on injuries and mortalities of
marine mammals incidental to tribal
fisheries.
General Comments
Comment 6: The MMC recommended,
based on their recommendation that
tribal fisheries be included on the LOF
(comment/response 2 above), that
NMFS notify all treaty tribes believed to
be engaged in hunting that any directed
taking of marine mammals requires
authorization under the MMPA. In
reviewing the SARs prepared by NMFS
under section 117 of the MMPA, the
MMC noted that tribal hunting of harbor
seals and California sea lions is
included as a possible source of
mortality. The MMC asserted that if
such hunting is in fact ongoing, it would
be subject to the same analysis as the
proposed taking of gray whales at issue
in Anderson v. Evans and would
presumably require authorization under
the MMPA.
Response: NMFS acknowledges this
comment; however, this comment is not
applicable to the LOF rulemaking at
hand. The LOF categorizes fisheries
based solely on the incidental, not
intentional, serious injury and mortality
to marine mammals. However, this
comment is relevant to the SARs
rulemaking process; therefore, NMFS
will address this comment as part of the
comments received during the comment
period for the proposed 2009 SARs
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(June 26, 2009–September 24, 2009;
overlapping with the comment period
for the proposed 2010 LOF).
Comment 7: The MMC recommended
NMFS incorporate into the applicable
SARs language similar to that included
in the SAR for the Washington stock of
sea otters prepared by the U.S. Fish and
Wildlife Service to clarify that, in
accordance with the ruling in Anderson
v. Evans, any such taking requires
authorization under the MMPA.
Response: NMFS acknowledges this
comment; however, this comment is not
applicable to the LOF rulemaking at
hand. This comment is relevant to the
SARs rulemaking process; therefore,
NMFS will address this comment as
part of the comments received during
the comment period for the proposed
2009 SARs (June 26, 2009–September
24, 2009; overlapping with the comment
period for the proposed 2010 LOF).
Comment 8: The Garden State
Seafood Association (GSSA) requested
that NMFS provide the number of
vessels which reported landings for
specific fisheries and gear types, along
with estimated number of vessels or
persons in individual fisheries currently
reported on the LOF. The GSSA noted
that this information would be
specifically pertinent when considering
the ‘‘Mid Atlantic mid-water trawl’’
fishery and the ‘‘Northeast mid-water
trawl’’ fishery. The GSSA stated that
recently the number of vessels who
reported landings using a mid-water
trawl in the Mid-Atlantic was
approximately 17 vessels.
Response: NMFS agrees that
including information on the number of
vessels landing catches to compare to
the estimated number of permit holders
could be helpful for providing an
accurate description of effort in each
fishery. However, while this
information is readily available for some
fisheries, gathering this information in
other fisheries may be more
complicated. It is unclear if the
information would be readily available
from state agencies. NMFS will consult
with the responsible state agencies and
consider incorporating this additional
data for each fishery in future LOFs.
Comment 9: The CBD reiterated a
comment made on the 2009 LOF that
the LOF lists over 40 fisheries that are
known to interact with ESA-listed
marine mammals. Only one fishery, the
‘‘CA/OR thresher shark/swordfish drift
gillnet’’ fishery, has authorization to
take ESA-listed marine mammals. The
CBD asserted that each of the other
fisheries is therefore operating in
violation of the both the ESA and
MMPA. The CBD further asserted that
NMFS must either issue permits for
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these fisheries authorizing take under
these statutes, or take appropriate
enforcement action, including, as
necessary, closure of the fisheries, to
ensure such illegal take does not
continue to occur.
Response: NMFS received a similar
comment on the 2009 LOF. As noted in
NMFS’ response to comments in the
final 2009 LOF (73 FR 73032, December
1, 2008; comment/response 2), the
CBD’s comment refers to how NMFS
authorizes takes of ESA listed marine
mammals incidental to commercial
fishing. The MMPA requires fishermen
to obtain a permit granted under section
101(a)(5)(E) of the MMPA if they
participate in a fishery that takes ESAlisted marine mammals. A 101(a)(5)(E)
permit does not authorize the operation
of a fishery. Instead, a 101(a)(5)(E)
permit authorizes the incidental take of
ESA-listed marine mammals in
commercial fisheries, if certain
provisions are met. Any incidental take
of an ESA-listed species in an otherwise
legally-operating fishery, without a
101(a)(5)(E) permit, is not authorized. If
an ESA-listed species is taken by a
fishermen in a fishery that has not been
granted a MMPA 101(a)(5)(E) permit,
then the fisher may be subject to
enforcement proceedings.
NMFS acknowledges that the LOF
includes fisheries in which ESA-listed
species are listed as incidentally killed
or injured, but for which NMFS has not
issued a permit under section
101(a)(5)(E) of the MMPA. To issue a
permit under section 101(a)(5)(E) of the
MMPA, NMFS must determine that (1)
the incidental mortality and serious
injury from commercial fisheries will
have a negligible impact on such species
and stocks; (2) a recovery plan has been
developed or is being developed for
such species or stock pursuant to the
ESA; and (3) where required under
section 118 of the MMPA, a monitoring
program is established, vessels engaged
in such fisheries are registered, and a
take reduction plan has been developed
or is being developed for such species
or stock. NMFS is continuing this
process of making these determinations
in various fisheries on the LOF. Since
the publication of the final 2009 LOF,
NMFS has been reviewing available
bycatch data for ESA-listed species in
fisheries on the LOF.
Comment 10: The CBD reiterated a
comment made on the 2008 and 2009
LOFs that the proposed 2010 LOF
includes a table of fisheries subject to
take reduction teams. While CBD found
this table is very useful, they noted that
there are Category I and II fisheries not
yet subject to take reduction teams that
also meet the statutory criteria for the
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convening of such teams. The CBD
asserted that Category I and II fisheries
not yet subject to take reduction teams
which interact with strategic stocks
must have take reduction teams
promptly convened. The CBD viewed
the Hawaii pelagic longline fishery as
the highest priority for such a team as
take continues to exceed PBR for the
false killer whale.
Response: NMFS received similar
comments on the 2008 and 2009 LOFs.
As noted in the responses to comments
on the 2008 LOF (72 FR 66048,
November 27, 2007; comment/response
6) and 2009 LOF (73 FR 73032,
December 1, 2008; comment/response
3), at this time, NMFS’ resources for
TRTs are fully utilized and new TRTs
will be initiated when additional
resources become available. When
NMFS lacks sufficient funding to
convene a TRT for all stocks that
interact with Category I and II fisheries,
NMFS will give highest priority for
developing and implementing new take
reduction plans to species and stocks
whose level of incidental mortality and
serious injury exceeds PBR, has a small
population size, and are declining most
rapidly, pursuant to MMPA section
118(f)(3).
Comment 11: The CBD reiterated a
comment made on the 2009 LOF that
the LOF once again includes ‘‘Marine
Aquaculture Fisheries’’ as Category III
fisheries. As stated in the past, the CBD
does not believe aquaculture facilities
are properly considered ‘‘commercial
fishing operations’’ eligible for the take
authorization contained in Section 118
of the MMPA. The CBD asserted that
these facilities and activities, to the
degree they interact with marine
mammals, should be subject to the take
prohibitions and permitting regimes
contained in Section 101 of the MMPA.
Response: NMFS received a similar
comment on the 2009 LOF. As noted in
the responses to comments on the 2009
LOF (73 FR 73032, December 1, 2008;
comment/response 5), eight aquaculture
fisheries are listed on the MMPA LOF,
all as Category III fisheries. NMFS’
regulations implementing section 118 of
the MMPA (50 CFR 229) specifically
include aquaculture as a commercial
fishing operation. 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
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MMPA, including inclusion on the
annual LOF.
Comment 12: Consistent with its
recommendations regarding the 2005
through 2009 LOFs, the MMC reiterated
its previous recommendation that
NMFS indicate the level of observer
coverage for each fishery as part of the
LOF.
Response: NMFS received similar
comments on the 2005 through 2009
LOFs. As noted in the responses to
comments on the 2005 LOF (71 FR 247,
January 2, 2006; comment/response 6),
2006 LOF (71 FR 48802, August 22,
2006; comment response 4), 2007 LOF
(72 FR 14466, March 28, 2007;
comment/response 8), 2008 LOF (72 FR
66048, November 27, 2007; comment/
response 4), and 2009 LOF (73 FR
73032, December 1, 2008; comment/
response 1), NMFS continues to feel that
the LOF is not the appropriate avenue
for reporting this data because it will
confuse rather than clarify if presented
without all the associated information
supplied in the SARs. Also, the LOF is
not meant to be redundant to the SARs,
but to base fishery classifications based
on the information presented in the
SARs.
NMFS continues to agree that
observer coverage information would be
useful for the reader to reference when
determining whether a given fishery
was adequately observed and no marine
mammals were taken or the fishery was
not adequately observed and mortality
and serious injury may have occurred
but were not documented. Therefore,
NMFS is developing summaries for each
Category I and II fishery on the LOF,
which include a description of each
fishery, the history of the fishery and it’s
interactions with marine mammals, and
the level of observer coverage in recent
years. When completed, these
summaries will be placed on the NMFS
Office of Protected Resources website
for easy public access, the citation for
which will be included in each LOF.
NMFS hopes to have these summaries
available for reference during the public
comment period on the 2011 LOF.
NMFS also continues to refer readers
to the SARs and the National Observer
Program for information on observer
coverage. The SARs can be accessed
through the NMFS Office of Protected
Resources’ Web site at https://
www.nmfs.noaa.gov/pr.sars/.
Additional information can also be
found on the National Observer Program
Web site at https://www.st.nmfs.gov/st4/
nop/.
Comment 13: The Marine
Conservation Alliance (MCA) stated that
there is a significant legal and structural
issue associated with the fishery
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categorization process which is
completely ignored by NMFS. The MCA
asserted that the formula NMFS has
developed for placing fisheries into
Category I, II, or III is arbitrary and
capricious and may well violate the
equal protection and due process
clauses of the U.S. Constitution. The
MCA asserted that if a fishery is the
only one interacting with a strategic
marine mammal stock and it is
responsible for the serious injury or
death of 1 percent of the PBR, the
fishery is placed into Category III and
subject to no further regulation under
this section of the MMPA. However, the
MCA stated that if a second and new
fishery enters the scene and it is
responsible for taking 10 percent or
more of the PBR, then the first fishery,
which a moment ago was determined to
be having no impact on the marine
mammal stock, is suddenly transformed
into a fishery having a significant
impact and a fishery that must be
subject to additional regulation as a
Category II fishery. The MCA asserted
that the regulations provide that if only
one fishery is interacting with a strategic
marine mammal stock, and it is
responsible for 10 percent or less of the
PBR, then it is a Category III fishery
since it, together with all other fisheries
interacting with that marine mammal
stock, is responsible for the serious
injury and mortality of 10 percent or
less of the PBR. The MCA asserts that
classifying fisheries into Categories II or
III based on such methodology is
inconsistent and arbitrary.
Response: The current fishery
classification system continues to be
widely accepted as accurate by NMFS,
the scientific community,
environmental organizations and the
fishing industry. As noted in a response
to a similar comment on the 2008 LOF
(72 FR 66048, November 27, 2007;
comment/response 7), NMFS
implemented the LOF fishery
classification criteria in the final
regulations to implement the 1994
amendments to the MMPA (60 FR
45086, August 30, 1995) after ample
consideration of comments and
suggestions from the public. NMFS
refers the reader to the response to
comments 5 through 9 in that rule for
a detailed explanation of the reasoning
for setting the dividing thresholds
between Category II and III as 1 percent
of PBR. NMFS also finalized an
Environmental Assessment (EA) in
August 1995, to analyze the impacts of
the regulations implementing the 1994
amendments on the environment and
the public. NMFS finalized a revised EA
in December 2005 on the process of
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classifying U.S. commercial fisheries. A
full copy of the updated 2005 EA can be
found at https://www.nmfs.noaa.gov/pr/
pdfs/interactions/loflea.pdf.
The fishery classification criteria
consider the rate of incidental serious
injury and mortality of marine mammals
in commercial fisheries on a stock
specific basis. Therefore, the rate of
interaction of a fishery with a marine
mammal stock with a low PBR can be
significant even if it appears to be a
minimal problem based on the size of
the fishery or frequency of the
interactions. The chosen approach
allows NMFS to focus management
actions where fishery interactions have
a significant negative effect on the
population. In addition to the 1 percent
threshold, the definitions of Category II
and III fisheries include qualitative
criteria that allow the Assistant
Administrator for Fisheries to place a
fishery into Category II or III in the
absence of reliable information. These
qualitative criteria will allow the
Assistant Administrator to take into
consideration cases where the PBR level
for a particular stock is very low and/
or where the level of incidental
interaction with commercial fisheries is
low and not likely to delay the
population’s attainment of its Optimum
Sustainable Population. See the general
description of the two-tiered scheme
and qualitative criteria that may be used
to classify a fishery in the preamble in
this rule under Fishery Classification
Criteria.
Comments on High Seas Fisheries
Comment 14: The CBD reiterated
previous concerns that the Commission
for the Conservation of Antarctic Marine
Living Resources (CCAMLR) fisheries
are listed in the LOF as Category II
fisheries. The CBD asserted that the
CCAMLR trawl fishery for krill should
be listed as Category I. The CBD noted
that a 2006 Federal Register notice
indicated that observer data from three
vessels, including a U.S. flagged vessel,
reported that 95 fur seals were caught in
the 2004/2005 season and 156 fur seals
were caught in the 2003/2004 season in
two CCAMLR areas (71 FR 39642,
39646, July 13, 2006). The CBD also
noted that the Final Programmatic
Environmental Impact Statement (EIS)
for CCAMLR fisheries noted that a
single U.S.-flagged krill vessel killed
138 Antarctic fur seals in a five-week
period in 2004. The CBD asserted that
this fishery is clearly not operating at a
‘‘zero mortality and serious injury rate’’
and must be listed in the LOF as a
Category I fishery.
Response: NMFS received similar
comments on the 2008 and 2009 LOFs.
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As noted in the responses to comments
on the 2008 LOF (72 FR 66048,
November 27, 2007; comment/response
5) and 2009 LOF (73 FR 73032,
December 1, 2008; comment/response
9), and in the final rule implementing
measures adopted by CCAMLR (72 FR
48496, August 23, 2007; comment/
response 29), the CCAMLR trawl fishery
for krill does not qualify as a Category
I fishery.
To be considered Category I, a fishery
must have a serious injury or mortality
rate of marine mammals at greater than
50 percent of a stock’s PBR level (50
CFR 229.2). While NMFS does not have
sufficient information to calculate PBR
level for marine mammal stocks found
outside of the U.S. waters, including
Antarctic fur seals, there is available
information on the relative abundance
of this species. The relative abundance
of Antarctic fur seals was estimated as
1.5 million in 1990 and is thought to
have since increased to over 4 million
(CCAMLR Final Programmatic EIS,
October 2006). Further, at the 2006
Antarctic Treaty Consultative Meeting,
the Antarctic Treaty Parties delisted the
Antarctic fur seal from its listed of
Specially Protected Species. The
delisting reflected the much-increased
abundance of fur seals. In 2003/2004, a
total of 158 Antarctic fur seals were
observed taken by the single U.S.permitted trawl krill fishing vessel in
the CCAMLR region, 142 of which were
mortalities. As a result, a permit
provision was added requiring the use
of a seal excluder device and any other
gear modifications or fishing practice
that reduces or eliminates Antarctic fur
seal bycatch. In the 2004/2005 fishing
season the U.S. vessel used the required
seal excluder device; and, as a result, 24
Antarctic fur seals were incidentally
taken, 16 of which were mortalities
(2005 Report of the CCAMLR Scientific
Committee). This modification would be
a requirement of any CCAMLR fishing
permit NMFS would issue to the vessel.
Ninety-five fur seals were reported
caught during fishing operations in
2005/2006, during which time no U.S.
krill trawl vessel was operating. Given
the large estimated abundance of
Antarctic fur seals, the current low rate
of incidental serious injury and
mortality would likely be well below 50
percent of PBR if NMFS were to
calculate a PBR for this stock. Therefore,
the fishery does not qualify as a
Category I fishery. In addition, no U.S.
vessels have participated in this fishery
in recent years and NMFS has not
received any requests for a permit to
participate in this fishery in the
upcoming fishing season.
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Comment 15: In comments on the
proposed 2009 LOF, the CBD raised the
concern that NMFS was treating single
fisheries that have both a high seas and
within-EEZ component as two separate
fisheries for LOF purposes. The CBD
was pleased that NMFS has clarified
that the high seas operations of certain
fisheries are extensions or components
of existing fisheries operating in U.S.
waters and therefore injure and kill the
same marine mammal species and share
the same LOF category. The CBD noted
that this change reduces the risk that the
total marine mammal take from such a
fishery may be inappropriately
apportioned into two separate fisheries
(the high seas and non-high seas
components of a single fishery) and
therefore result in an underestimation of
the true environmental effect, and LOF
classification, of what is more properly
considered a single fishery.
Response: NMFS will continue to
include language in the preamble of
future LOFs to clarify that 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 the same
fishery operating within U.S. waters
(listed in Table 1 or 2). NMFS will
continue to designate those fisheries in
Tables 1, 2, and 3 by an ‘‘*’’ after the
fishery’s name.
Comment 16: The MMC supported
NMFS’ inclusion of high-seas fisheries
on the LOF. The MMC noted that the
descriptions and evaluations of highseas fisheries on the LOF highlight the
lack of data on both the status and the
incidental take of marine mammals
outside the U.S. EEZ, a lack of data that
is not surprising because current U.S.
marine mammal stock assessment
programs are focused on U.S. waters.
The MMC commented that gathering
data to support the management of highseas fisheries will be difficult but will
provide many ancillary benefits,
including the development of useful
tools for managing transboundary
stocks. Therefore, the MMC reiterated
its previous recommendation that
NMFS develop and implement the
research and monitoring programs
needed to manage high-seas fisheries in
a manner consistent with the
requirements of the MMPA and the
High Seas Driftnet Fishing Moratorium
Protection Act.
Response: NMFS continues to agree
that the development of a research and
monitoring plan to manage high seas
fisheries in a manner consistent with
the requirements of the MMPA will
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58869
require novel stock assessment
techniques and the development, and/or
continuation, of international
partnerships (please see the 2009 LOF,
74 FR 73032, December 1, 2008;
comment/response 8). NMFS is
currently developing a strategic action
plan for addressing international marine
mammal conservation issues, including
the need to gather the necessary data
and strengthen international
partnerships to effectively manage
marine mammal bycatch in domestic
and foreign high seas fisheries.
Comment 17: The Hawaii Longline
Association (HLA) stated that NMFS
should use fishery- and marine
mammal-specific information to classify
high seas fisheries according to their
interactions and, where such
information is not available, should
designate high seas fisheries as Category
II regardless of the classification of their
EEZ components. The HLA asserted
that, as a threshold matter, the proposed
LOF arbitrarily and inaccurately
justifies its categorization of the high
seas deep-set fishery on the assumption
that the fishery interacts with the socalled ‘‘pelagic’’ false killer whale stock.
The HLA noted that by NMFS’s
definition, the ‘‘pelagic’’ false killer
whale stock occurs only in the U.S. EEZ
- an area that does not include the high
seas. The HLA stated that NMFS is
arbitrarily picking and choosing when
and where it will split or combine
artificially-constructed false killer whale
stocks for purposes of estimating
abundance and establishing a given
fishery’s rate of interaction with the
stock (and, hence, the fishery’s LOF
categorization). The HLA asserted that
either NMFS must acknowledge that all
false killer whales outside the ‘‘insular’’
zone belong to the Eastern North Pacific
stock, the size of which is unknown, or
it must consistently apply its arbitrary
and scientifically unsound ‘‘pelagic’’
stock definition.
The HLA also commented that recent
reports call into question the proposed
LOF’s assumption that the high seas
deep-set fishery interacts with
noncoastal marine mammals to the same
extent as the U.S. EEZ fishery (Forney
and McCracken, 2008), and suggest that
false killer whales may be sufficiently
abundant on the high seas between
Hawaii and Palmyra Atoll that already
low deep-set fishery interaction rates
may warrant at least a Category II
classification (Barlow and Rankin,
2007).
Response: This comment questions:
(1) NMFS’ criteria for classifying high
seas fisheries in general; (2) The manner
in which NMFS classifies the high seas
portion of the HI-based deep-set
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longline fishery (the ‘‘Western Pacific
pelagic deep-set longline’’) based on
serious injury and mortality levels of
false killer whales (HI pelagic stock);
and (3) Information regarding false killer
whale stock delineation, and false killer
whale abundance and fishery takes on
the high seas. NMFS responded to a
similar comment in the final 2009 LOF
(73 FR 73032, December 1, 2008;
comment/response 11).
(1) The first part of this comment
questioned NMFS’ criteria for
classifying high seas fisheries. NMFS
agrees that fisheries should be classified
on the LOF according to their
interactions with marine mammals.
Although information on interaction
rates (per trip or per set) are available
for the high seas deep-set and shallowset fisheries, PBR levels for marine
mammal stocks on the high seas are not
available. This is because, as mandated
by Section 117 of the MMPA (16 U.S.C.
1386), NMFS prepares SARs and
calculates PBR levels for marine
mammal stocks occurring ‘‘in waters
under the jurisdiction of the United
States.’’ NMFS does not generally
develop SARs or calculate PBR levels
for stocks on the high seas; therefore,
NMFS does not possess the same
information to categorize high seas
fisheries as is used to categorize
fisheries operating within U.S. waters.
As stated in the preamble of the
proposed 2010 LOF (74 FR 27739, June
11, 2009), many fisheries operate in
both U.S. waters and on the high seas,
and fishing gears and methods in these
fisheries remain virtually unchanged on
either side of the 200 nmi EEZ
boundary. In these cases, the high seas
component of the fishery (Table 3) 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. While NMFS recognizes
it is somewhat confusing to include
different components of the same
fishery in two tables on the LOF, listing
the two components separately on two
tables is necessary because of
differences in the Federal permitting
systems for vessels permitted to operate
only within U.S. waters versus those
permitted to operate within U.S. waters
and on the high seas.
(2) The second part of this comment
questioned the manner in which NMFS
classifies the high seas portion of the HIbased deep-set longline fishery (the
‘‘Western Pacific pelagic deep-set
longline’’) based on serious injury and
mortality levels of false killer whales (HI
pelagic stock). As stated in the preamble
of the proposed 2010 LOF, a fishery is
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categorized on the LOF at its highest
level of classification (e.g., a fishery
qualifying for Category II for one marine
mammal stock and a Category I for
another stock, will be listed as Category
I). This also applies to fisheries that
operate over a large geographic range.
The entire fishery is categorized on the
LOF at its highest level of classification,
regardless of where marine mammal
interactions occur within the fishery’s
range. Since the ‘‘Western Pacific
pelagic deep-set longline’’ and ‘‘HI
deep-set (tuna target)’’ are two
components of the same fishery,
distinguished from each other only by
which side of the 200 nmi EEZ
boundary they operate, and the
component of the fishery operating in
U.S. waters is classified as Category I,
the high seas component of the fishery
is also classified as Category I.
If NMFS receives information
indicating that the high seas component
of a fishery operates significantly
differently than the component
operating within U.S. waters, NMFS
would consider splitting that fishery
into two fisheries. However, the fishing
operations of the high seas component
of this fishery are not significantly
different than fishing operations within
the U.S. EEZ, and a single vessel may
set both within the U.S. EEZ waters and
on the high seas. Therefore, splitting
these components into separate
fisheries, and classifying them
separately, is not warranted.
(3) The third part of this comment is
related to information regarding false
killer whale stock delineation, and false
killer whale abundance and fishery
takes on the high seas. The commenter
is correct in that NMFS currently
defines the pelagic stock of false killer
whales as occurring from 75nmi to the
EEZ boundary (2008 SAR). However,
these animals are thought to move
across the EEZ boundary into the high
seas. NMFS truncated the stock
boundary as ending at the 200nmi EEZ
line because of the mandate in section
117 of the MMPA (16 U.S.C. 1386) for
NMFS to create SARs and calculate PBR
levels for marine mammal stocks
occurring ‘‘in waters under the
jurisdiction of the United States.’’ While
NMFS does not gather detailed
abundance information for the entire
range of Hawaiian false killer whales,
NMFS has estimated the density of false
killer whales on the high seas within the
area of operation of U.S. longline
fisheries to be 0.049 animals per 100
km2, which is not dramatically different
than the density within the Hawaiian
EEZ (0.022 animals per 100 km2)
(Barlow and Rankin 2007). Also, while
NMFS does not have information on the
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level of bycatch by international vessels
on the high seas, take rates by U.S.
vessels on the high seas (0.78 animals
per 1000 sets) are similar to take rates
by U.S. vessels within the Hawaiian
EEZ (0.71 per 1000 sets) (Forney and
Kobayashi, 2007). No complete
abundance estimate for false killer
whales on the high seas is available, but
an estimate made for part of the high
seas range of these fisheries is 906 (C.V.
= 0.68), which would result in a PBR of
5.2 false killer whales for all U.S. and
international fisheries combined. The
estimated mortality and serious injury
of false killer whales by U.S. vessels
operating on the high seas is 5.4 animals
per year (Draft 2009 SAR), which
already exceeds the PBR, without taking
into account international takes.
Comment 18: The HLA stated that the
proposed 2010 LOF nowhere mentions
longline fishing in and around Palmyra
Atoll, Johnston Atoll and other U.S.
possessions in the Pacific Ocean. The
HLA noted that the 2008 false killer
whale SAR estimates a population size
of 1,329 animals for the Palmyra Atoll
stock, butt is not clear how the proposed
2010 LOF takes into account, in any
manner, longline fishing in U.S. waters
around these possessions. The HLA
asked if the proposed LOF intended to
include these animals in its ‘‘pelagic’’
false killer whale stock definition? Or,
are fisheries in these areas considered
part of the deep-set fishery or a separate
longline fishery (which then should be
separately categorized)? The HLA then
asked, if the former, why is the fishery
categorized based only upon a
population estimate and PBR that does
not include the Palmyra population
estimate? The HLA asserted that NMFS
should clarify these issues in the final
2010 LOF, particularly because false
killer whale stock estimates exist for
Palmyra Atoll and Johnston Atoll and
could be used to derive a PBR that could
be measured against observer data for
longline fishing in those waters.
Response: As stated in the response to
a similar comment on the 2009 LOF (73
FR 73032, December 1, 2008; comment/
response 12), NMFS considers U.S.
vessels deep-set longline fishing in U.S.
waters around Palmyra Atoll, Johnston
Atoll, and other U.S. Territories in the
Pacific Ocean as operating in the same
fishery, the ‘‘HI deep-set (tuna target)
fishery’’ (and/or its high seas
component, the ‘‘Western Pacific
pelagic deep-set longline’’). The fishery
description provided in the final 2008
LOF (72 FR 66048, November 27, 2007),
states that Hawaii-based longline fishing
effort takes place over a huge geographic
range extending north-south from 40° N.
lat. to the equator and east-west from
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Kure Atoll to as far as 135° W. long.,
with fishing for tunas primarily
occurring around the main Hawaiian
Islands and south of the Hawaiian
Islands.
In the final 2008 SARs, there were
three recognized false killer whale
stocks in the Pacific Islands region,
including the Palmyra stock: (1) the
Hawaii insular stock, and (2) the Hawaii
pelagic stock, and (3) the Palmyra stock.
The status of false killer whales in
Palmyra Atoll EEZ waters relative to the
Optimal Sustainable Population is
unknown, and there are insufficient
data to evaluate trends in abundance.
The rate of mortality and serious injury
to false killer whales within the Palmyra
Atoll EEZ in the Hawaii-based longline
fishery (0.3 animals per year) does not
exceed the PBR (6.4) for this stock. The
total fishery mortality and serious injury
for Palmyra Atoll false killer whales is
less than 10 percent of PBR. Additional
injury and mortality of false killer
whales is known to occur in U.S and
international longline fishing operations
in international waters, and the
potential effect on the Palmyra stock is
unknown.
The ‘‘HI deep-set (tuna target)
longline’’ fishery is classified as a
Category I fishery based on its
interactions resulting in serious injury
and mortality levels that exceed the PBR
of the Hawaii pelagic stock of false killer
whales. As noted in the response to
comment 17, a fishery is categorized on
the LOF based at its highest level of
classification. Therefore, while the rate
of mortality and serious injury to false
killer whales within the Palmyra Atoll
EEZ in the Hawaii-based longline
fishery does not warrant a Category I
classification, the fishery remains a
Category I based on serious injury and
mortality levels of the pelagic stock of
false killer whales.
Commercial Fisheries in the Pacific
Ocean
Comment 19: The MCA believed that
NMFS’ proposed 2010 classification of
fisheries incorrectly designates the
‘‘Bering Sea Aleutian Islands (‘‘BSAI’’)
Pollock trawl’’ and the ‘‘BSAI flatfish
trawl’’ fisheries as Category II fisheries.
The MCA noted that the ‘‘BSAI flatfish
trawl’’ fishery is classified as Category II
because of interactions with the western
stock of Steller sea lions, and the ‘‘BSAI
Pollock trawl’’ fishery is classified as
Category II because of interactions with
the western stock of Steller sea lions;
eastern North Pacific, Gulf of Alaska,
BSAI transient killer whales; central
North Pacific humpback whales; and
western North Pacific humpback
whales. The MCA stated that, with
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respect to the two fisheries at issue, the
data and analyses on which NMFS
relied to calculate the PBR and mortality
and serious injury rates are flawed. The
MCA further stated that by utilizing this
flawed data, NMFS has seemingly made
an arbitrary and capricious decision not
to use the best scientific data available.
The MCA provided reasoning,
research results, and literature citations
to support the assertion that the data
used for stock delineations, PBR
calculations, and mortality and serious
injury calculations in the final 2008
SARs (for the marine mammal stocks
listed in the previous paragraph) are
flawed. The MCA stated that NMFS
double counts mortalities and injuries
because of the procedure NMFS uses to
calculate marine mammal bycatch
(including incorporating all observed
and unobserved fishing sets into
analyses and counting mortality and
serious injury twice for certain stocks).
The MCA commented that relying on
the flawed SARs has caused NMFS to
understate the PBR for marine mammal
stocks. The MCA asserted that the errors
in the PBR calculations in the SARs
require that these errors be corrected
and PBRs recalculated before NMFS
proceeds with any final LOF
designations.
Response: NMFS acknowledges this
comment; however, this comment is not
applicable to the LOF rulemaking
process at hand. This comment is
concerned with the calculation of PBRs
and mortality and serious injury rates,
which NMFS’ reports in the annual
SARs. NMFS then categorizes fisheries
on the LOF based on the information
presented in the SARs. NMFS does not
complete any PBR or serious injury and
mortality-related analysis in the LOF
rulemaking process. Also, this comment
references information in the final 2008
SARs, which is not relevant to the
proposed 2009 SARs rulemaking public
comment period that overlapped with
the proposed 2010 LOF comment period
and was therefore not directed to the
SARs for consideration in the 2009
SARs rulemaking process. The
commenter may resubmit these
comments during the next SARs open
public comment period.
Comment 20: The MCA stated that
there is a serious disconnect between
the proposed 2010 LOF and the SARs.
In the proposed 2010 LOF, NMFS stated
the ‘‘BSAI Pollock trawl’’ fishery is
placed into Category II in part because
of interactions with the central and
western North Pacific stocks of
humpback whales (74 FR at 27752, June
11, 2009). The MCA stated that the SAR
assigns 100 percent of the fisheries
related mortality for these two stocks of
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58871
humpback whales to other fisheries. The
MCA noted that the SAR never
mentions the ‘‘BSAI Pollock trawl’’
fishery as causing humpback whale
deaths or serious injury (final 2008 SAR
at page 165, 173). The MCA asserted
that since the LOF is based on the SAR,
the ‘‘BSAI Pollock trawl’’ fishery cannot
be placed in Category II based on
humpback whale interactions that are
not reported in the SAR.
Response: The classification of a
fishery as a Category II fishery is based
on the annual mortality and serious
injury of a stock in a given fishery
exceeding 1 percent and less than 50
percent of the PBR level (72 FR 66048,
27 November 2007). While there are
known historical interactions between
the BSAI pollock trawl fishery and the
central and western North Pacific stocks
of humpback whales, these interactions
are not the basis for classifying the
‘‘BSAI Pollock trawl’’ fishery as a
Category II fishery (i.e., the level of
serious injury and mortality of these
stocks in the ‘‘BSAI Pollock trawl’’
fishery is below 1 percent of the stocks’
PBR levels). The continued inclusion of
the superscript ‘‘1’’ following these
stocks in this fishery on Table 1 was a
typographical error, which NMFS has
corrected in this final rule. The Tier 1
approach to classifying fisheries
considers the cumulative fishery
mortality and serious injury for a
particular stock; however, Tier 2
classification of fisheries considers
fishery-specific mortality and serious
injury for a particular stock. A fishery is
typically categorized on the LOF at its
highest level of classification. In the
‘‘BSAI Pollock trawl’’ fishery, the
estimated annual level of serious injury
and mortality of the Eastern North
Pacific, Gulf of Alaska, Aleutian Islands,
and Bering Sea transient killer whale
stock is 0.4, or 12.9 percent of PBR (PBR
is 3.1), and the western Steller sea lion
stock is 3.8, or 1.6 percent of PBR (PBR
is 234). Therefore, this fishery is
classified as a Category II fishery under
the Tier 2 approach to fishery
classification.
Comment 21: The MMC and the CBD
recommended the ‘‘Gulf of Alaska
sablefish longline’’ fishery be elevated
above a Category III. The CBD based this
recommendation on frequent
interactions with sperm and killer
whales, qualifying this fishery for
Category I or II. The MMC noted the
2008 SARs indicate that observers
reported that three sperm whales were
seriously injured in this fishery in 2006.
The MMC asserted that, given the
estimated number of injuries or deaths
based on 2002 to 2006 data, NMFS’
inability to calculate a potential
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biological removal level for the North
Pacific sperm whale stock is not a
sufficient basis for maintaining the
current Category III classification for
this fishery. The MMC further noted
that NMFS is unable to estimate PBR
levels for 57 percent of the marine
mammal stocks that occur in Alaska
because of inadequate or outdated data.
The MMC asserted that NMFS cannot
continue to use this lack of information
as the basis for failing to classify
fisheries that incidentally kill or
seriously injure marine mammals. Doing
so is inconsistent with NMFS’ own
guidance for addressing such situations,
which directs placement in category II
when the available information is not
sufficient to categorize a fishery
accurately (74 FR at 27740, June 11,
2009).
Response: NMFS received similar
comments on the 2009 LOF (73 FR
73032, December 1, 2008; comment/
response 22). The PBR level for the
North Pacific sperm whale stock is
unknown because a reliable abundance
estimate is not available. NMFS is in the
process of analyzing bycatch data from
2007 and 2008 and will re-evaluate the
category placement for the ‘‘Gulf of
Alaska sablefish longline’’ fishery on the
2011 LOF.
The commenter’s interpretation of
NMFS’ guidance is not entirely correct.
NMFS’ guidance provided in the
preamble of each proposed LOF,
including the proposed 2010 LOF (74
FR at 27740, June 11, 2009), states, ‘‘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 of 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 for Fisheries
(50 CFR 229.2).’’ NMFS has such
information on some of the ‘‘other
factors’’ related to the ‘‘Gulf of Alaska
sablefish longline’’ fishery, such as
fishing techniques, gear used, and
qualitative data and stranding data. As
stated above, NMFS is in the process of
evaluating available data and will reevaluate the category placement of this
fishery in the 2011 LOF.
Comment 22: The MMC and the CBD
disagreed with NMFS’ proposal to
reclassify the ‘‘Alaska southeast salmon
purse seine’’ fishery from Category II to
Category III based on lack of data
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regarding humpback whale takes. The
MMC noted that high levels of
entanglement-related scarring have been
documented for humpback whales in
Alaska. The MMC further noted that the
lack of evidence for interactions does
not provide a reliable basis for
reclassifying this fishery to category III
if NMFS has failed to institute an
observer program for it. The MMC stated
that given that the fishery has no
observer coverage and analogous
fisheries are known to seriously injure
humpback whales, NMFS should
maintain the fishery’s Category II
classification.
Response: In this case a 15–year lack
of evidence of serious injury and
mortality in this fishery, even in the
absence of an observer program, is
enough to warrant its re-categorization.
Under the annual LOF, fishery
categories are assigned via NMFS’ welldocumented process of analyzing
known or estimated levels of serious
injury and mortalities relative to a
stock’s PBR. In some cases, a fishery
with no recent documented injuries or
mortalities of marine mammals may be
classified in Category II by analogy to
similar gear types in similar areas that
are known to cause mortality or serious
injury of marine mammals. However, in
those instances, additional available
information (such as stranding data,
fishermen self-reports, or anecdotal
information) suggests serious injury or
mortality of marine mammals may be
occurring that is likely to exceed the
Category III threshold. Only marine
mammal serious injuries and mortalities
that can be assigned to a specific fishery
are included in fisheries’ categorization.
The re-categorization of the ‘‘Southeast
Alaska purse seine’’ fishery in the 2010
LOF is consistent with this practice,
albeit somewhat delayed. NMFS
delayed the re-categorization of this
fishery until this year as a precautionary
measure, and is satisfied at this time
that this fishery meets the criteria for
Category III.
While humpback whale scarring is
documented in Alaska, at this time there
is no accepted method to establish a
reliable rate of fishing-related serious
injury or mortality from documented
scarring. Scarring alone is not valid
evidence for classifying a fishery as
Category II. Further, in the few cases of
known serious injury or mortality of
humpback whales in purse seines in
Alaska, unique scarring patterns from
purse seine gear have been shown to be
easily identifiable. NMFS recognizes
that the lack of observer coverage due to
funding constraints is not ideal;
however, the lack of observer coverage
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along is not reason for classifying a
fishery as Category II.
Comment 23: The CBD asserted that
all other Alaska pot fisheries should be
classified as Category II rather than
Category III.
Response: Categorization of
individual Alaska fisheries in Category
II due to interactions with humpback
whales are based on documented
serious injury and mortality levels of
humpback whales in each of those
fisheries, including the ‘‘AK Bering Sea
sablefish pot’’ fishery. Other Alaska pot,
ring net, or trap fisheries either have no
documented humpback whale serious
injuries or mortalities or have low levels
that do not meet the Category II
requirements.
Comment 24: The HLA supported the
re-labeling of the false killer whale stock
with which the deep-set fishery
interacts as the ‘‘HI pelagic’’ stock (as
opposed to the ‘‘HI’’ stock), but only
insofar as this change purports to
distinguish the false killer whale
‘‘pelagic’’ stock from the false killer
whale ‘‘insular’’ stock. As HLA has
repeatedly commented (including
comments submitted on the draft 2008
SARs), the HLA believes there are
significant uncertainties and errors
perpetuated in NMFS’ false killer whale
SAR year after year, which is then used
to generate inaccurate LOFs.
Specifically, the HLA disagreed with the
continued division of false killer whales
into three fictional stocks based on U.S.
EEZ boundaries and NMFS’
underestimate for the population
abundance of false killer whales with
which the deep-set fishery interacts.
Thus, while HLA agreed with the
proposed LOF’s recognition of separate
‘‘pelagic’’ and ‘‘insular’’ false killer
whale stocks, it did not agree with the
cramped manner in which NMFS has
defined the ‘‘pelagic’’ stock. The HLA
asserted that NMFS must address these
concerns or, at a minimum,
acknowledge the significant
uncertainties that underlie the
determinations made in the proposed
LOF.
Response: NMFS acknowledges this
comment and the reference to the false
killer whale stock with which the deepset fishery interacts has been changed to
the ‘‘HI pelagic’’ stock on the final 2010
LOF. The comment is also concerned
that there are uncertainties with the
designation of the Hawaii pelagic stock
of false killer whales. This comment is
not relevant to the LOF rulemaking at
hand. NMFS reports stock delineations
and discussions surrounding the
uncertainties in the data used to base
stock delineations, after opportunity for
public review and comment, in the
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annual SARs. NMFS determines which
species and stocks are included as
incidentally killed or injured in a
fishery on the LOF in part by annually
reviewing the information presented in
the current SARs, which 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, and fisher self-reports.
The LOF is not intended to repeat the
information included in the SARs, but
rather to incorporate the SARs with
other sources of information in order to
make determinations based on the best
available science. However, this
comment is relevant to the SARs
rulemaking process and NMFS is aware
of the concerns raised by the HLA and
the MMC in recent years. Therefore,
NMFS will address this comment as
part of the comments received during
the comment period for the proposed
2009 SARs (June 26, 2009–September
24, 2009; overlapping with the comment
period for the proposed 2010 LOF).
Comment 25: The HLA supported
NMFS’s proposal to remove spinner
dolphin (HI stock) and pantropical
spotted dolphin (stock unknown) from
the list of species and stocks that
interact with the deep-set fishery and
shallow-set fishery, respectively.
Response: NMFS acknowledges this
comment. These stocks are removed
from the list of species and stocks
incidentally killed or injured in this
final rule.
Comment 26: The CBD reiterated a
previous comment from the 2009 LOF
that various Hawaiian fisheries are
known or suspected of interacting with
Hawaiian monk seals. The CBD asserted
that, given the critically endangered
status of the monk seal, any interaction
is significant and these fisheries should
be reclassified as Category I or II.
Response: NMFS received a similar
comment on the 2009 LOF (73 FR
73032, December 1, 2008; comment/
response 13). 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), Northwestern Hawaiian Islands
(NWHI) deep sea bottomfish’’ fisheries.
The available information on Hawaiian
monk seal interactions with these
fisheries is:
(1) ‘‘HI lobster trap’’ fishery: There
have not been any reported interactions
since the mid–1980s; and
(2) ‘‘HI Main Hawaiian Islands,
Northwestern Hawaiian Islands deep
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18:47 Nov 13, 2009
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sea bottomfish’’ fishery: The final 2008
SAR states that in the past, monk seal
interactions with fisheries in the NWHI
were documented, but direct
interactions have since become rare or
non-existent, and issues related to
competition have also somewhat abated.
A Federal observer program of the
NWHI bottomfish handline fishery was
conducted from the fourth quarter of
2003 through 2006, and no monk seal
interactions were observed. This fishery
has not been observed since 2006. The
NWHI lobster fishery closed in 2000,
and on June 15, 2006, former President
Bush signed a proclamation that created
the Northwestern Hawaiian Islands
Marine National Monument.
Subsequent regulations prohibit
commercial fishing in the Monument
except for the bottomfish fishery (and
associated pelagic species catch), which
may continue until 2011. The MHI
bottomfish handline fishery may also
interact with monk seals as evidenced
by recent fatty acid research; however,
no mortalities or serious injuries have
been attributed to this fishery.
While serious injuries and mortalities
have not been documented 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
Main Hawaiian Islands are hooked and
entangled at a rate that has not been
reliably assessed and the true
interaction rate cannot be estimated
without purpose-designed observation
effort. Also, the PBR level for monk
seals is currently ‘‘undetermined.’’ Due
to the fact that the PBR level for monk
seals is undetermined and that the
hooking and entanglement rate cannot
be reliably assessed, NMFS will retain
the ‘‘HI lobster trap’’ and ‘‘HI Main
Hawaiian Islands, Northwestern
Hawaiian Islands deep sea bottomfish’’
fisheries as Category III fisheries on the
LOF, until more information becomes
available to determine whether
reclassification is warranted.
Comment 27: The CBD noted that
available information indicates that the
‘‘American Samoa longline’’ fishery
should be listed as Category I based on
its interactions with false killer whales.
Response: As stated in the preamble
for each LOF, a fishery is classified as
Category I if the annual mortality and
serious injury of a stock in a given
fishery is greater than or equal to 50
percent of a stock’s PBR level. A fishery
is classified as Category II if the 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. NMFS stated in the proposed
LOF for 2010 (73 FR 27739, June 11,
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58873
2009) that the abundance estimate and
the PBR for the false killer whales
interacting with the American Samoa
longline fishery are unknown. NMFS
biologists at the Southwest Fisheries
Science Center will analyze the
information on false killer whale
abundance and interactions with the
‘‘American Samoa longline’’ fishery
during the development of the 2010
SAR. NMFS will revisit whether
reclassification of this fishery is
warranted based on the updated SAR
analyses at that time.
At this time a fishery classification of
Category I cannot be scientifically
substantiated. The fishing gear and
methods used in the American Samoa
longline fishery are similar to those of
other Category I and II longline fisheries
elsewhere in tropical/sub-tropical
latitudes of the Pacific that are taking
false killer whales. Therefore,
classification of this fishery as Category
II by analogy is warranted. NMFS
recognizes the uncertainties with the
false killer whale stock structure in
American Samoa and will continue to
assess false killer whale abundance and
take estimates as resources become
available. Please also see the discussion
of a similar comment on the 2009 LOF
(73 FR 73032, December 1, 2008;
comment/response 14).
Comment 28: The MMC concurred
with NMFS’ proposal to reclassify the
‘‘American Samoa longline’’ fishery
from Category III to Category II. The
MMC further recommended that NMFS
not postpone the injury determinations
for the animals released alive from
interactions with longline gear in 2008.
Response: NMFS acknowledges the
concurrence and ‘‘American Samoa
longline’’ fishery is reclassified from
Category III to Category II in this final
rule. NMFS understands the concerns
about the fishery impacts to false killer
whales in American Samoa, especially
since there is a the lack of population
abundace or stock status information
from this area. In response to this
concern NMFS began observing this
fishery. In 2008, the observer coverage
was 6.4 percent. NMFS will continue to
assess false killer whale abundance and
take estimates as resources become
available. NMFS is not postponing
determinations of the three marine
mammal interactions reported in this
fishery in 2008. NMFS is analyzing the
2008 observer data and making the
necessary injury determinations during
the development of the 2010 SARs. This
timeline is in line with NMFS’ process
for reviewing and updating each annual
NMFS SAR. The data presented in the
annual SARs have an average of a twoyear time delay because of the time
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needed to properly analyze the data and
complete the peer-review process.
Comment 29: The CBD stated that the
‘‘Hawaii shallow-set longline’’ fishery
should be listed as a Category I fishery,
since observer data from 2008 show
takes of false killer whales and
humpback whales in this fishery.
Response: For the 2010 LOF, a
reclassification of the Hawaii shallowset longline fishery to a Category I is not
warranted. As noted in NMFS’ response
to comments on the 2009 LOF (73 FR
73032, December 1, 2008; comment/
response 15), 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 2010
LOF is based on information in the final
2008 SARs, which includes analysis of
the observer takes against calculated
PBR levels through 2006. As noted in
the response to comment 28 above, the
data presented in the annual SARs have
an average of a two-year time delay
because of the time needed to properly
analyze the data and complete the peerreview process. Observer data from 2008
has not yet been analyzed and included
in the current SARs or included in the
level of annual mortality and serious
injury for false killer whales. NMFS will
reexamine the categorization of this
fishery on a future LOF if the analysis
of the 2008 observer data reported in the
SARs indicates that a change in
categorization is warranted.
Comment 30: The MMC concurred
with NMFS’ proposal to classify the
‘‘Hawaii shortline’’ fishery as Category
II.
Response: NMFS acknowledges this
comment and has added the ‘‘Hawaii
shortline’’ fishery as a Category II
fishery in this final rule.
Comment 31: The CA Wetfish
Producers Association (CWPA) agreed
with NMFS’ proposal to remove shortfinned pilot whales (CA/OR/WA) from
the list of species and stocks killed or
injured in the Category II ‘‘CA squid
purse seine’’ fishery.
Response: NMFS acknowledges this
comment and has removed short-finned
pilot whales (CA/OR/WA) from the list
of species and stocks killed or injured
in the Category II ‘‘CA squid purse
seine’’ fishery.
Comment 32: The CWPA requested
NMFS utilize the most recent scientific
information in terms of observer data
from 2004–2008 to update the list of
species and stocks killed or injured in
the ‘‘CA squid purse seine’’ fishery and
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reclassify the fishery to a Category III.
The CWPA noted that observer data
from the California Coastal Pelagic
Purse Seine Observer Program contains
a single observed mortality of an
‘‘unidentified common dolphin’’ in this
fishery on January 3, 2005, and past
LOFs have represented this interaction
as ‘‘common dolphin, unknown.’’ The
CWPA stated that, while the two
cetacean species do exhibit some
overlapping distribution, there are
substantially more recent data and
robust observer data available to NMFS
than just 2006: there were more than
193 interaction-free trips observed by
Federal observers during 2004 to 2006,
80 more clean sets observed in mid to
late 2007, and 13 interaction-free
observed seine sets (4 trips) in 2008.
Response: NMFS received similar
comments on the 2008 and 2009 LOFs.
As noted in the final 2008 LOF (72 FR
66048, November 27, 2007; comment/
response 19) and final 2009 LOF (73 FR
73032, December 1, 2008; comment/
response 32), NMFS based this listing
on observer information from this
fishery collected from 2004 through
2007. When able, NMFS bases serious
injury and mortality estimates on the
most recent 5 years for which data have
been analyzed (NMFS 2005, Guidelines
for Assessing Marine Mammal Stocks
[GAMMS] II). If the total fishing effort
has changed substantially over the last
5 years, NMFS may use only the most
recent relevant data to most accurately
reflect the current level of annual
mortality. In some cases where
information is lacking, such as in cases
where there is no observer coverage,
information that is more than 5 years
old may not be ignored if it is the most
appropriate information available in a
particular case (NMFS 2005, GAMMS II
report).
In each year from 2004–2007,
observer coverage in the ‘‘CA squid
purse seine’’ was low, under 2 percent.
There was one mortality of a shortbeaked common dolphin in 2005 and in
2006 one unidentified common dolphin
was observed seriously injured. There
are no available biological samples or
photographs of the injured dolphin;
therefore, there is insufficient
information to identify the species. Both
species, long-beaked common dolphins
and short-beaked common dolphins,
utilize much of the same habitat and
overlap in areas with the squid purse
seine fishery; therefore, it is possible
that either species could have been
taken and NMFS cannot eliminate the
possibility that a long-beaked common
dolphin was seriously injured during
this event. Extrapolating these sightings
to the entire fishery and averaging over
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the four years of available information,
the estimated annual serious injury or
mortality is 22 long-beaked common
dolphins (draft 2009 SAR). The current
PBR for long-beaked common dolphins
is 95/year (final 2008 SAR). Therefore
the serious injury or mortality rate is 23
percent, meeting the Category II criteria
(less than 50 percent and greater than 1
percent of the stock’s PBR).
Comment 33: The California
Department of Fish and Game (CDFG)
disagreed with NMFS’ proposal to
elevate the ‘‘California spiny lobster
trap’’ fishery from Category III to
Category II. The CDFG stated that the
report of the 2007 humpback whale
entanglement event, submitted by CDFG
to NMFS Southwest Region’s stranding
coordinator, was submitted with the
emphasis that the report was a third
hand report. The CDFG stated that this
report was based on information
provided to the CDFG biologist from
friends who heard it from a recreational
fisherman. CDFG assumed that neither
the whale species nor the gear type was
verified. Also, since the 2007
entanglement event occurred in the first
week of July, CDFG had doubts as to
whether the trap involved in the
entanglement was a lobster trap.
Response: NMFS published criteria
for evaluating reports from the LWDN in
the proposed 2009 LOF (73 FR 33760,
June 13, 2008). Each year, the LWDN
receives reports of whales entangled in
fishing gear. For some fisheries,
particularly pot and trap fisheries, this
is currently the only information NMFS
has on which to assess the level of large
whale entanglement in fisheries on the
west coast. NMFS used the criteria to
elevate four pot and trap fisheries to
Category II in the 2009 LOF based upon
interactions with humpback whales.
NMFS acknowledged and identified the
assumptions that need to be made in
using the criteria in the proposed 2009
LOF.
When evaluating an entanglement
event, NMFS’ first criterion is whether
a specific fishery has been positively
identified as causing the entanglement
(73 FR 33760, June 13, 2008). Different
types of pot and trap gear have
distinguishing characteristics (e.g.,
marking requirements on buoys) that
make it possible to identify the gear to
a particular fishery. NMFS second
criterion is whether the fishery operates
in the area and time when a humpback
whale was reported entangled in pot
and trap gear (73 FR 33760, June 13,
2008). Most pot and trap fisheries have
discrete seasons, thus gear can be
associated with certain fisheries in
certain areas based on the time of year.
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NMFS proposed to elevate the spiny
lobster fishery to Category II on the 2010
LOF based on available information that
indicated a humpback whale was
observed entangled in spiny lobster gear
on July 10, 2007, south of Newport
Harbor, CA. The available information
came from a staff member from CDFG
and was thus considered reliable.
Unfortunately, there are no photographs
available to aid in identification of the
fishing gear that entangled the whale
and no other information available. In
CDFG’s comment they state that they do
not consider the report to be reliable.
The information on the humpback
whale and gear came not from a CDFG
staff member, so CDFG does not have
confidence in the accuracy of the
information. NMFS spoke with staff
from CDFG to discuss the sighting and
the spiny lobster fishery. Based upon
those discussions and memos from
CDFG, NMFS agrees that the sighting of
a humpback entangled in spiny lobster
gear can not be considered reliable and
does not meet our first criterion for recategorizing fisheries based upon LWDN
reports.
NMFS then considered the report
using the second criterion to propose
the fishery’s elevation to Category II:
does the fishery operate at a time and
area consistent with the observed
entanglement (73 FR at 33772, June 13,
2008). The season for the spiny lobster
trap fishery is October through March
and occurs in the southern California
Bight, so the reported entanglement was
observed almost 4 months after the
fishery closed, within the geographic
region in which the spiny lobster trap
fishery occurs. The information
provided by CDFG and a review of the
fishery indicates that neither of the two
criteria for re-categorizing the spiny
lobster fishery have been met. Based on
this information, NMFS is not elevating
this fishery to Category II in the final
2010 LOF. This fishery will remain a
separate Category III fishery. NMFS will
continue to evaluate reports of pot and
trap interactions with large whales on
the west coast and may consider
elevating this fishery in the future if
additional information or analysis
supports such a change.
Comment 34: The CBD agreed with
NMFS’ proposal to reclassify the ‘‘CA
spiny lobster trap’’ fishery as a Category
II. The CBD further asserted that all pot
or trap fisheries that occur within the
range of the humpback whale should be
classified as Category II until and unless
observer coverage demonstrates that
they do not pose a risk of entanglement
to the species.
Response: Since the publication of the
proposed 2010 LOF, NMFS has received
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information to suggest that recategorizing the spiny lobster fishery to
Category II at this time is not supported
by the available data. Please see
response to comment number 33 above.
Regarding the recommendation that all
pot or trap fisheries be placed in
Category II until observers can show
that the fisheries do not pose a threat to
humpback whales, NMFS received and
responded to a similar comment from
the CBD on the final 2009 LOF (73 FR
73032, December 1, 2008; comment/
response 29). It may not be appropriate
to place observers onboard fishing
vessels in pot and trap fisheries to
detect interactions with marine
mammals. Observers in pot and trap
fisheries have very limited ability to
detect interactions with the gear. In
most instances, an entangled large
whale is likely to swim away with gear
and not be observed on the fishing
grounds. Therefore alternative
monitoring methods are needed. NMFS
continues to work with other
government agencies, the scientific and
fishing communities, and the public to
collect information on entanglements
events and methods for tracking
interactions between marine mammals
and pot and trap gear. NMFS is
continuing to address the problem of
large whale entanglements and is
committing resources to the issue,
including hiring additional staff to help
advance NMFS’ Southwest Region’s
efforts on this issue. As noted in
previous LOFs, when and if additional
information and/or analysis become
available, NMFS would consider
reclassifying of pot and trap fisheries, as
appropriate.
Comment 35: The MMC reiterated its
previous recommendation that NMFS
classify all West Coast pot/trap fisheries
(i.e., those off Washington, Oregon, and
California) as Category II. The MMC
asserted that dividing and renaming the
West Coast pot/trap fisheries based on
observed entanglement events is not
appropriate, given the small fraction of
entanglements likely to be observed and
the fact that the gear cannot be
distinguished. The MMC also stated that
the existing evidence on large whale
entanglement events is not sufficient to
make an informed assessment regarding
the entanglement rates for pot/trap
fisheries on the West Coast.
Response: Please see the responses to
comments 33 and 34 above. NMFS
received a similar comment from the
MMC on the 2009 LOF. As noted in
NMFS’ response to comments on the
2009 LOF (73 FR 73032, December 1,
2008; comment/response 30), NMFS
must use the best available information
in making recommendations for the
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58875
LOF. NMFS reviewed all of the
available data on entangled large whales
off the U.S. West Coast, the distribution
of species entangled, and the spatial and
temporal characteristics of pot and trap
fisheries to develop criteria for
categorizing fisheries. NMFS is
continuing to work on methods for
improved data collection and analysis
and will consider re-categorizing
additional pot and trap fisheries when
and if more information and/or analysis
become available, as appropriate. As
noted in the response to comment 34,
NMFS is continuing to dedicate
resources to address the issue of large
whale entanglements in fishing gear,
including hiring additional staff to help
NMFS’ Southwest Region’s ongoing
efforts.
Comment 36: The MMC concurred
with NMFS’ proposal to reclassify the
‘‘CA pelagic longline’’ fishery from
Category II to Category III.
Response: NMFS acknowledges this
comment and has reclassified the ‘‘CA
pelagic longline’’ fishery from Category
II to Category III in this final rule.
Comment 37: The CBD urged NMFS
to maintain 100 percent observer
coverage in the ‘‘CA pelagic longline’’
fishery, as recent proposals to expand
that fishery if brought to fruition are
likely to result in significant increases
in interactions with marine mammals.
Response: The ‘‘CA pelagic longline’’
fishery is re-categorized as a Category III
fishery in the 2010 LOF due to the low
observed bycatch of marine mammals.
The current fishery has 100 percent
observer coverage. If a proposed
shallow-set longline fishery exempted
fishing permit is approved, one of the
conditions of issuing the permit would
be 100 percent observer coverage. There
are currently no other proposals to
expand the existing ‘‘CA pelagic
longline’’ fishery.
Comment 38: The MMC responded to
NMFS’ request for public comment and
information on two large whale
entanglements in gillnet gear in 2007.
The MMC asserted that observer
coverage is insufficient to provide
reliable data on marine mammal take
rates in both of the Category II California
set gillnet fishery (3.5–in mesh) for
halibut, white seabass, and other species
or the California drift gillnet fisheries
(mesh size ≥3.5 in and <14 in) for
yellowtail, barracuda, and white
seabass. The MMC further asserted that
the size of these fisheries and the
number of species they take warrant
increased observer coverage. For that
purpose, the MMC recommended that
NMFS develop and implement
expanded monitoring programs for the
‘‘CA halibut, white seabass, and other
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species set gillnet fishery (3.5–in mesh)’’
and the ‘‘CA yellowtail, barracuda, and
white seabass drift gillnet fisheries
(mesh size ≥3.5 in and <14 in)’’
fisheries.
Response: NMFS is working to
expand observer coverage of the
California state gillnet fisheries. NMFS
plans to place observers on the
California set gillnet fishery (3.5–in
mesh) for halibut, white seabass, and
other species beginning January 2010.
Available observer funds should yield
coverage of up to 25 percent. NMFS
plans to place observers on the
California drift gillnet fisheries (mesh
size ≥3.5 in and <14 in) for yellowtail,
barracuda, and white seabass beginning
in summer 2010 if observer funds are
available.
NMFS did not receive additional
information from the public on the two
large whale entanglements in 2007 that
NMFS believes may have been caused
by either the California set gillnet
fishery (3.5–in mesh) for halibut, white
seabass, and other species or the
California drift gillnet fishery (mesh size
≥3.5 in and <14 in). NMFS will continue
to evaluate new and existing
entanglement information to better
understand the nature of large whale
interactions with fishing gear along the
U.S. West Coast. When and if new
information or analysis is available,
NMFS will assign these entanglements
to the appropriate fisheries. At this time,
these reports will continue to be listed
as entangled in unknown gillnet gear.
Comments on Fisheries in the Atlantic
Ocean, Gulf of Mexico, and Caribbean
Comment 39: The MMC
recommended NMFS review the
available information on state and
Federal permit holders in Northeast and
Mid-Atlantic fisheries and revise the
published LOF to accurately reflect the
number of active vessels and
participants in each fishery. The MMC
noted that NMFS revised its estimates of
the number of participants for Northeast
and Mid-Atlantic fisheries in the
proposed 2010 LOF based on state and
Federal permit information without
removing any duplication (i.e.,
individuals holding both state and
Federal permits for a particular fishery)
or accounting for inactive permits.
Thus, although the information
previously included in the LOF may
have underestimated the number of
participants, the new information likely
overestimates the level of participation
in some fisheries.
Response: NMFS concurs that the
updated number of estimated
participants for each fishery may
complicate management efforts due to
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uncertainty around the number of active
versus passive participants and
duplicative permit information.
Therefore, NMFS will not make the
changes proposed in the proposed 2010
LOF (74 FR 27739, June 11, 2009) and
will revert back to the estimates of
Federal permits from the 2009 LOF (73
FR 73032. December 1, 2008) in this
final 2010 LOF for the ‘‘Mid-Atlantic
gillnet,’’ Northeast sink gillnet,’’
‘‘Atlantic mixed species trap/pot,’’
‘‘Mid-Atlantic menhaden purse seine,’’
‘‘Mid-Atlantic haul/beach seine,’’ ‘‘MidAtlantic mid-water trawl,’’ ‘‘Northeast
bottom trawl,’’ ‘‘Northeast mid-water
trawl,’’ and ‘‘Gulf of Maine Atlantic
herring purse seine’’ fisheries. NMFS
will work with the relevant state
agencies to obtain more reliable
information on state permits for these
fisheries to be incorporated in future
LOFs. Based on updated information
received from the Virginia Marine
Resource Commission on the 2008
license year, the estimated number of
Virginia Pound Net fishery participants
will be updated to ‘‘41.’’ In summary,
the estimated numbers of fishery
participants in this final rule, for the
previously mentioned fisheries, are:
Category I ‘‘Mid-Atlantic gillnet’’ fishery
to ≤370; Category I ‘‘Northeast sink
gillnet’’ fishery to 341; Category II
‘‘Atlantic mixed species trap/pot’’
fishery to unknown; Category II ‘‘MidAtlantic menhaden purse seine’’ fishery
to 22; Category II ‘‘Mid-Atlantic haul/
beach seine’’ fishery to 25; Category II
‘‘Mid Atlantic mid water trawl’’ fishery
to 620; Category II ‘‘Northeast bottom
trawl’’ fishery to 1052; Category II
‘‘Northeast mid-water trawl’’ fishery to
17; Category II ‘‘VA pound net’’ fishery
to 41; and Category III ‘‘Gulf of Maine
Atlantic herring purse seine’’ fishery to
30.
Comment 40: The MMC concurred
with NMFS’ proposal to add the Gulf of
Maine/Bay of Fundy harbor porpoise
stock to the list of species and stocks
incidentally killed or injured in the
Category II ‘‘Northeast bottom trawl’’
fishery. The MMC further noted that the
combined mortality of harbor porpoises
from this stock in the Category I
‘‘Northeast sink gillnet,’’ Category I
‘‘Mid-Atlantic gillnet,’’ and Category II
‘‘Northeast bottom trawl’’ fisheries
exceeds the stock’s PBR level. For that
reason, the MMC commented that
NMFS should recognize the harbor
porpoise as a stock incidentally injured
or killed in the ‘‘Northeast bottom
trawl’’ fishery and work jointly with the
Harbor Porpoise Take Reduction Team
and the Atlantic Trawl Gear Take
Reduction Team to reduce the stock’s
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total incidental serious injury and
mortality levels.
Response: NMFS acknowledges the
comment and will continue to monitor
all marine mammal takes within the
‘‘Northeast bottom trawl’’ fishery. NMFS
recognizes the harbor porpoise as a
stock incidentally injured or killed in
the ‘‘Northeast bottom trawl’’ fishery, as
depicted by its current listing in Table
2 of the 2010 LOF. NMFS recently
proposed modifications to the Harbor
Porpoise Take Reduction Plan (74 FR
36058, July 21, 2009) to further reduce
the serious injury and mortality of
harbor porpoises from incidental
interactions with Northeast sink and
Mid-Atlantic gillnet fisheries to below
the stock’s PBR level. NMFS will
continue to coordinate with the Harbor
Porpoise Take Reduction Team and the
Atlantic Trawl Gear Take Reduction
Team to ensure that the stock’s total
incidental serious injury and mortality
is reduced to below its PBR level and,
ultimately, to an insignificant level
approaching a zero mortality and
serious injury rate.
Comment 41: The MMC
recommended that NMFS not remove
the superscript ‘‘1’’ after Gulf of Maine/
Bay of Fundy harbor porpoise in its
listing of the Category I ‘‘Mid-Atlantic
gillnet’’ fishery until NMFS has more
definitive information indicating that
the number of removals is, and is likely
to remain, below 50 percent of the
stock’s PBR level. The MMC asserted
that it would be premature to conclude
that the taking of harbor porpoises is no
longer driving the classification of the
‘‘Mid-Atlantic gillnet’’ fishery. The
MMC noted that the estimated take is
only a single percentage point (or 11
animals) below the threshold that would
trigger a Category I classification. The
MMC asserted that, given the level of
observer coverage in the fishery (2.2
percent) and the resulting uncertainty
around the estimates of incidental
serious injury and mortality, this
difference is not significant or
justification for removal of the
superscript notation. The MMC further
noted that NMFS’ proposal fails to
recognize the increasing trend in the
deaths of harbor porpoises in this
fishery in recent years.
Response: The superscript ‘‘1’’ in
Table 3 of the LOF is defined to depict
‘‘Fishery classified based on serious
injuries of this stock which are greater
than 50 percent (Category I) or greater
than 1 percent and less than 50 percent
(Category II) of the stock’s PBR.’’
According to the 2008 SAR, the average
annual harbor porpoise (Gulf of Maine/
Bay of Fundy stock) mortality and
serious injury in the ‘‘Mid-Atlantic
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gillnet’’ fishery from 2002 to 2006 was
299, which represented the 4–year
average estimate from 2003, 2004, 2005,
and 2006. Using this average, the fishery
was responsible for taking 49 percent of
the stock’s PBR, which is not greater
than 50 percent. As the commenter
stated, regulations (50 CFR 229.2) define
a Category I fishery as ‘‘one that is by
itself responsible for the annual removal
of 50 percent or more of any stock’s
potential biological removal level’’ and
a Category II fishery as ‘‘is by itself
responsible for the annual removal of
between 1 and 50 percent, exclusive, of
any stock’s potential biological removal
level.’’ Therefore, given the specific
regulatory reference to 50 percent for
the cut off for Category I, while harbor
porpoises are being taken in this fishery,
this stock currently does not qualify as
driving the Category I definition for the
‘‘Mid-Atlantic gillnet’’ fishery. Harbor
porpoise serious injuries and mortalities
were responsible for the elevation of the
‘‘Mid-Atlantic gillnet’’ fishery from
Category III to Category II on the 1996
LOF (December 28, 1995; 60 FR 67063)
but serious injuries and mortalities of
coastal bottlenose dolphins were
responsible for the elevation of the
fishery to Category I on the 2003 LOF
(July 15, 2003; 68 FR 41725). Currently,
coastal bottlenose dolphin serious
injuries and mortalities still drive the
Category I definition for this fishery.
The placement of the superscript for
Category I and Category II fisheries is
evaluated on a yearly basis and if in the
future harbor porpoise serious injuries
and mortalities in this fishery increase
to 50 percent of PBR or greater, the
superscript will be added to Table 2.
Comment 42: The GSSA requested
that NMFS consider that the proposal to
update the estimated number of vessels
or participants in the 2010 proposed
LOF to 7,596 for the ‘‘Mid-Atlantic
gillnet’’ fishery is counting the number
of North Carolina state permits that are
issued to thousands of people who use
gillnets for personal consumption in
North Carolina bays and sounds.
Response: NMFS will work with state
agencies to obtain more specific state
permit information. See response to
number 39 for additional discussion on
this topic.
Comment 43: The CBD reiterated
previous years’ comments stating
concerns regarding NMFS’ failure to
adequately classify certain Gulf of
Mexico fisheries as Category I or
Category II in light of known or
estimated mortality and serious injury
to marine mammals from those
fisheries. Specifically, they suggested
the ‘‘Gulf of Mexico menhaden purse
seine fishery’’ and the ‘‘Gulf of Mexico
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gillnet fishery’’ be elevated from
Category II to Category I, based on
known or likely impacts to bottlenose
dolphin stocks. The CBD expressed
pleasure that NMFS proposed to
reclassify the Gulf of Mexico blue crab
trap/pot fishery. Finally, the CBD stated
that NMFS should make it a high
priority to place observer coverage on
the ‘‘Gulf of Mexico menhaden purse
seine’’ fishery and convene a take
reduction team to address bottlenose
dolphin takes in the Gulf from this and
other fisheries.
Response: The commenter incorrectly
states that NMFS has proposed to
elevate the blue crab trap/pot fishery.
This fishery remains a Category III on
the final 2010 LOF. NMFS does not
believe elevation of the Gulf of Mexico
blue crab trap/pot, menhaden purse
seine, or gillnet fisheries is supported by
currently available information. There is
no observer program for these fisheries,
and NMFS relies on stranding data and
fishermen’s self-reports to document
fishery interactions with marine
mammals. NMFS acknowledges that,
while these sources show only a low
level of interactions, these sources are
unreliable and likely to be biased low.
In addition, PBR is unknown for these
stocks because of insufficient
information on stock structure and
abundance. NMFS will continue
monitoring fishermen’s self-reports and
stranding data. Observer coverage for
these fisheries also remains a priority if
resources become available.
In the ‘‘Gulf of Mexico blue crab trap/
pot’’ fishery, stranding data indicate
there were two confirmed bottlenose
dolphin interactions with crab pot
fishing gear between 2002–2006, one
animal which was released alive. In the
same time period, four dead bottlenose
dolphins stranded with rope or rope
marks that may have been from trap/pot
gear, but cause of death could not be
determined.
The ‘‘Gulf of Mexico menhaden purse
seine’’ fishery was observed by
researchers from Louisiana State
University in 1992, 1994, and 1995. The
observers documented nine bottlenose
dolphin captures, three of which were
mortalities. Using observed and total
fishery effort data, the number of takes
was linearly extrapolated to an estimate
of 68 animals. On the basis of this
information, the fishery was elevated
from Category III to Category II on the
1999 LOF (64 FR 9067, February 24,
1999). Since that time, there has been no
observer coverage in this fishery.
Fishermen’s self-reports through the
MMAP reveal 11 dolphin mortalities in
the menhaden purse seine fishery from
2000–2008: two in 2005, one in 2004,
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two in 2002, one in 2001 and five in
2000. Nine of these mortalities were
confirmed to be bottlenose dolphins.
However, it is not possible to
extrapolate these numbers to obtain an
estimate of total takes in this fishery.
No marine mammal mortalities
associated with gillnet fisheries in the
Gulf of Mexico have been reported
through the MMAP; however, four
dolphin mortalities occurred in gillnet
research gear between 2003–2007.
Stranding data also suggests that marine
mammal interactions with gillnets do
occur, causing mortality and serious
injury. NMFS acknowledges that
stranding data likely underestimates the
extent of fishery-related mortality and
serious injury. Interpreting the data is
difficult due to varying ability among
the stranding network to detect and
respond to strandings in all areas and
accurately document human
interactions and the condition of the
carcass when stranded. To address this,
NMFS conducted multiple stranding
and human interaction workshops in
Texas, Louisiana, Mississippi and
Alabama in 2008, and provided
additional human interaction training to
the Southeast Stranding Network at
their Biennial Conference in 2009. In
addition, in 2009 NMFS awarded nearly
$292,000 in Prescott Grants to increase
stranding network capabilities
throughout the Gulf of Mexico. Prescott
Grant 2010 Southeast Regional priorities
include research into ways to enhance
stranding response coverage, capability,
Level A data collection, and number of
necropsies in areas where there is little
or no coverage, including along the
Northern Gulf of Mexico.
Because population size and PBR are
undetermined for the three coastal
stocks and most of the bay, sound, and
estuary stocks of bottlenose dolphins,
NMFS is unable to assess the population
level impacts of serious injury and
mortality from fisheries to determine
whether annual mortality is greater than
or equal to 50 percent of PBR. Thus, the
currently available information dues not
support convening a TRT.
Comment 44: The MMC reiterated its
previous recommendations on the 2003
through 2009 LOFs that NMFS expedite
its investigation of bottlenose dolphin
stock structure in the Gulf of Mexico,
expand its efforts to collect reliable
information on serious injury and
mortality rates of marine mammals
incidental to Gulf of Mexico fisheries,
and reevaluate the classification of Gulf
of Mexico fisheries as information
becomes available.
Response: NMFS agrees that it is
important to further investigate stock
structure and abundance of bottlenose
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dolphins in the Gulf of Mexico. PBR is
undetermined for most Gulf of Mexico
stocks because the population size
estimates are more than 8 years old and
resources are unavailable to conduct
additional surveys. Collecting reliable
information on serious injury and
mortality of marine mammals in the
Gulf of Mexico is also essential.
However, there are currently no
resources to fund observer programs in
the Gulf of Mexico fisheries. Therefore,
NMFS is focusing on building volunteer
stranding network capacity in the Gulf
and increasing the level and quality of
stranding response and has taken
concrete steps to improve stranding
capacity, as discussed in the response to
Comment 43 above. NMFS expects these
efforts will increase the effectiveness of
the stranding networks and better
inform management decisions in the
future.
Summary of Changes to the LOF for
2010
The following summarizes changes to
the LOF for 2010 in fishery
classification, fisheries listed in the
LOF, the number of participants in a
particular fishery, and the species and
stocks that are incidentally killed or
injured in a particular fishery. The
classifications and definitions of U.S.
commercial fisheries for 2010 are
identical to those provided in the LOF
for 2009 with the changes outlined
below.
Commercial Fisheries in the Pacific
Ocean
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Fishery Classification
The ‘‘American Samoa longline’’
fishery is elevated from Category III to
Category II.
The ‘‘AK southeast salmon purse
seine’’ fishery is reclassified from
Category II to Category III.
The ‘‘CA pelagic longline’’ fishery is
reclassified from Category II to Category
III.
Addition of Fisheries to the LOF
The ‘‘CA spiny lobster trap’’ fishery is
added as a separate Category III fishery
(split from the ‘‘CA spiny lobster,
coonstripe shrimp, rock crab, tanner
crab pot or trap’’ fishery, renamed the
‘‘CA coonstripe shrimp, rock crab,
tanner crab pot or trap’’ fishery in this
final rule).
The ‘‘HI shortline’’ fishery is added as
a Category II fishery.
Fishery Name and Organizational
Changes and Clarifications
The Category III ‘‘CA spiny lobster,
coonstripe shrimp, rock crab, tanner
crab pot or trap’’ fishery is renamed to
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the ‘‘CA coonstripe shrimp, rock crab,
tanner crab pot or trap’’ fishery.
killed or injured in the ‘‘CA pelagic
longline’’ fishery.
List of Species and Stocks That are
Incidentally Killed or Injured
Commercial Fisheries in the Atlantic
Ocean, Gulf of Mexico, and Caribbean
The stock name for false killer whales
incidentally killed or injured in the ‘‘HI
deep-set (tuna-target) longline/set line’’
fishery is changed from ‘‘HI’’ to ‘‘HI
pelagic.’’
Pantropical spotted dolphin (stock
unknown) is added to the list of species
and stocks incidentally killed or injured
in the Category I ‘‘HI deep-set (tuna
target) longline/set line’’ fishery.
Spinner dolphin (HI) is removed from
the list of species and stocks
incidentally killed or injured in the
Category I ‘‘HI deep-set (tuna target)
longline/set line’’ fishery.
Pantropical spotted dolphin (stock
unknown) is removed from the list of
species and stocks incidentally killed or
injured in the Category II ‘‘HI shallowset (swordfish target) longline/set line’’
fishery.
False killer whale (stock unknown) is
added to the list of species and stocks
incidentally killed or injured in the
‘‘American Samoa longline’’ fishery
(elevated to Category II in this final
rule).
Humpback whale (Central North
Pacific) is removed from the list of
species and stocks incidentally killed or
injured in the Category III ‘‘AK
southeast salmon purse seine’’ fishery.
The superscript ‘‘1’’ is removed after
humpback whale (Central North Pacific)
and humpback whale (Western North
Pacific) in the list of species and stocks
incidentally killed or injured in the
Category II ‘‘AK Bering Sea Aleutian
Islands Pollock trawl’’ fishery to correct
a typographical error.
The stock name for Northern fur seals
is changed on the list of species and
stocks incidentally killed or injured in
the Category II ‘‘AK Bering Sea,
Aleutian Islands flatfish trawl’’ fishery
from ‘‘Eastern North Pacific’’ to ‘‘Eastern
Pacific.’’
Short-finned pilot whale (CA/OR/
WA) is removed from the list of species
and stocks incidentally killed or injured
in the Category II ‘‘CA squid purse
seine’’ fishery.
A superscript ‘‘1’’ is added after longbeaked common dolphin (CA) in the list
of species and stocks incidentally killed
or injured in the Category II ‘‘CA squid
purse seine’’ fishery.
Gray whale (Eastern North Pacific) is
added to the list of species and stocks
incidentally killed or injured in the
Category III ‘‘CA spiny lobster’’ fishery.
CA sea lion (U.S.) is removed from the
list of species and stocks incidentally
Fishery Name and Organizational
Changes and Clarifications
The description of the Category I
‘‘Mid-Atlantic gillnet’’ fishery is
replaced with the following: ‘‘The
Category I Mid-Atlantic gillnet fishery
targets monkfish, spiny dogfish, smooth
dogfish, bluefish, weakfish, menhaden,
spot, croaker, striped bass, large and
small coastal sharks, Spanish mackerel,
king mackerel, American shad, black
drum, skate spp., yellow perch, white
perch, herring, scup, kingfish, spotted
seatrout, and butterfish. The fishery
uses drift and sink gillnets, including
nets set in a sink, stab, set, strike, or
drift fashion, with some unanchored
drift or sink nets used to target specific
species. The dominant material is
monofilament twine with stretched
mesh sizes from 2.5 12 in (6.4 30.5 cm),
and string lengths from 150 8,400 ft. (46
2,560 m). This fishery operates yearround west of a line drawn at 72° 30′ W.
long. south to 36° 33.03′ N. lat. (VA/NC
border) and east to the eastern edge of
the EEZ and north of the NC/SC border,
not including waters where Category II
and Category III inshore gillnet fisheries
operate in bays, estuaries, and rivers.
This fishery includes any residual large
pelagic driftnet effort in the midAtlantic, any shark and dogfish gillnet
effort in the mid-Atlantic, and those
North Carolina small and large mesh
beach-anchored gillnets formerly placed
in the Category II Mid-Atlantic haul/
beach seine fishery in the mid-Atlantic
zone described. This NC component
fishing effort is prosecuted right off the
beach (6 ft [1.8 m]) or in nearshore
coastal waters to offshore waters (250 ft
[76 m]). Gear in this fishery is managed
by several Federal and interstate FMPs
managed by the Atlantic States Marine
Fisheries Commission (ASMFC), the
Atlantic Large Whale Take Reduction
Plan (ALWTRP), the Harbor Porpoise
Take Reduction Plan (HPTRP), and the
Bottlenose Dolphin Take Reduction
Plan (BDTRP). Fisheries are primarily
managed by total allowable catch limits;
individual trip limits (quotas); effort
caps (limited number of days at sea per
vessel); time and area closures; and gear
restrictions and modifications.’’
The description of the Category II
‘‘Mid-Atlantic haul/beach seine’’ fishery
is replaced with the following: ‘‘The
Category II Mid-Atlantic haul/beach
seine fishery targets striped bass, mullet,
spot, weakfish, sea trout, bluefish,
kingfish, and harvestfish using seines
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with one end secured (e.g., swipe nets
and long seines) and seines secured at
both ends or those anchored to the
beach and hauled up on the beach. The
beach seine system also uses a bunt and
a wash net that are attached to the beach
and extend into the surf. The fishery
occurs in waters west of 72° 30′ W. long.
and north of a line extending due east
from the NC/SC border. The only haul/
beach seine gear operating in NC
included in this Category II fishery is
the ‘‘Atlantic Ocean striped bass beach
seine fishery’’ during the winter, as
regulated by NC Marine Fisheries
Commission rules (NCDMF) and
NCDMF proclamations. NCDMF defines
a beach seine operating under the
Atlantic Ocean Striped Bass beach seine
fishery as a ‘‘swipe net constructed of
multifilament, multifiber webbing
fished from the ocean beach that is
deployed from a vessel launched from
the ocean beach where the fishing
operation takes place, and one end of
the beach seine is attached to the shore
at all times during the operation.’’ All
other NC small and large mesh beachanchored gillnets with webbing
constructed of all monofilament
material or a combination of
monofilament and multifilament
material were moved to the Category I
Mid-Atlantic gillnet fishery in the final
2009 LOF because their construction
and fishing technique were more similar
to a gillnet than a traditional beach
seine. A description of the gear and
fishing practices for the haul/beach
seine and small and large mesh beachanchored gillnets operating in NC are
found in the final 2008 LOF (72 FR
66048; November 27, 2007) and final
2009 LOF (73 FR 73032, December 1,
2008). In addition to the NC component
as described above, the ’Mid-Atlantic
haul/beach seine’ fishery also includes
haul/beach seining in other areas of the
mid-Atlantic, including NY through VA.
Because the net materials and fishing
practices of the Atlantic Ocean striped
bass beach seine fishery in NC are
different from haul seining in other
areas, NMFS may consider splitting this
fishery in the future. The Mid-Atlantic
haul/beach seine fishery is managed
under several state and Interstate FMPs
and is an affected fishery under the
BDTRP.’’
Number of Vessels/Persons
Based on public comments on the
proposed 2010 LOF, NMFS agreed that
the proposed updates to the estimated
number of vessels/persons in several
Northeast and Mid-Atlantic fisheries by
including available state permit
information may complicate
management efforts due to uncertainty
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around the number of active versus
passive participants and duplicative
permit information. Therefore, NMFS is
not finalizing those proposed updates in
this final rule. The number of vessels/
persons in Atlantic fisheries remains the
same as those reported in the 2009 LOF.
The estimated number of vessels or
persons in the Category II ‘‘VA pound
net’’ fishery is updated from 187 to 41.
List of Species and Stocks That are
Incidentally Killed or Injured
Harbor porpoise (Gulf of Maine/Bay of
Fundy (GME/BF)) is added to the list of
marine mammal species and stocks
incidentally killed or injured in the
Category II ‘‘Northeast bottom trawl
fishery.
Fin whale (Western North Atlantic
(WNA)) is removed from the list of
species and stocks incidentally killed or
injured in the Category I ‘‘Northeast/
Mid-Atlantic American lobster trap/pot’’
fishery.
The superscript ‘‘1’’ after humpback
whale (Gulf of Maine) and minke whale
(Canadian east coast) is removed from
the list of species and stocks
incidentally killed or injured in the
Category I ‘‘Northeast/Mid-Atlantic
American lobster trap/pot’’ fishery.
The superscript ‘‘1’’ after minke
whale (Canadian east coast), humpback
whale (Gulf of Maine), and North
Atlantic right whale (WNA) is removed
from the list of species and stocks
incidentally killed or injured in the
Category I ‘‘Northeast sink gillnet’’
fishery.
The superscript ‘‘1’’ after harbor
porpoise (GME/BF) and humpback
whale (Gulf of Maine) is removed from
the list of species and stocks
incidentally killed or injured in the
Category I ‘‘Mid-Atlantic gillnet’’
fishery.
Pygmy sperm whale (WNA) is
removed from the list of species and
stocks incidentally killed or injured in
the Category I ‘‘Atlantic Ocean,
Caribbean, Gulf of Mexico large pelagics
longline’’ fishery.
Commercial Fisheries on the High Seas
Removal of Fisheries
All unspecified high seas fisheries for
all gear types are removed, except for
trawl gear. Four trawl gear HSFCA
permits remain valid for an unspecified
fishery.
Number of HSFCA Permits
As stated in the preamble under
‘‘How Does NMFS Authorize U.S.
Vessels to Participate in High Seas
Fisheries?,’’ some fishers possess valid
HSFCA permits for gear types that are
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no longer authorized for use (therefore,
the fishers are unable to fish under the
permit). For this reason, the number of
HSFCA permits updated below and
displayed in Table 3 of this final rule
may not accurately represent actual
fishing effort by U.S. vessels on the high
seas.
The estimated number of HSFCA
permits in the High Seas Atlantic Highly
Migratory Species fishery is updated for
the following gear types: longline, from
75 to 72; trawl, from 3 to 2; handline/
pole-and-line from 2 to 1; and troll, from
5 to 7.
The estimated number of HSFCA
permits in the High Seas Pacific Highly
Migratory Species fishery is updated for
the following gear types: drift gillnet,
from 5 to 4; trawl, from 14 to 3; purse
seine, from 5 to 8; pot, from 8 to 7;
longline, from 56 to 62; handline/pole
and line, from 18 to 22; liners not
elseware identified (NEI), from 3 to 1;
multipurpose vessels, from 9 to 7; and
troll, from 222 to 249.
The estimated number of HSFCA
permits in the High Seas South Pacific
Albacore Troll fishery is updated for the
following gear types: trawl, from 5 to 2;
longline, from 12 to 11; handline/pole
and line, from 7 to 8; troll, from 45 to
53; multipurpose vessels, from 6 to 4.
The estimated number of HSFCA
permits in the High Seas South Pacific
Tuna fishery is updated for the
following gear types: purse seine from
23 to 36; longline, from 2 to 3; troll,
from 1 to 3.
The estimated number of HSFCA
permits in the High Seas Western
Pacific Pelagic fishery is updated for the
following gear types: trawl, from 11 to
4; purse seine, from 4 to 3; pot, from 8
to 7; handline/pole and line, from 8 to
9; liners NEI, from 2 to 1; multipurpose
vessels, from 7 to 5.
List of Species That are Incidentally
Killed or Injured
The stock name for false killer whales
incidentally killed or injured in the
‘‘High Seas Western Pacific Pelagic
(Deep-set component)’’ fishery is
changed from ‘‘HI’’ to ‘‘unknown.’’ This
fishery is a component of the ‘‘HI deepset (tuna target) longline/set line’’
fishery operating in U.S. waters, which
interacts with the ‘‘HI pelagic’’ stock of
false killer whales. While the animals in
this stock are thought to move across the
EEZ boundary into the high seas, the
stock is currently defined as occurring
from 75nmi to the EEZ boundary (2008
SAR). NMFS truncated the stock
boundary as ending at the 200nmi EEZ
line because of the mandate in section
117 of the MMPA (16 U.S.C. 1386) for
NMFS to create SARs and calculate PBR
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levels for marine mammal stocks
occurring ‘‘in waters under the
jurisdiction of the United States.’’
Therefore, to be consistent with the
stock definition in the final 2008 SARs,
NMFS has changed the stock name to
‘‘unknown’’ at this time. See the
response to comment 17 above for
additional information.
Pantropical spotted dolphin (stock
unknown) is added to the list of species
and stocks incidentally killed or injured
in the Category II ‘‘High Seas Western
Pacific Pelagic (Deep-set component)’’
fishery. This fishery is a component of
the ‘‘HI deep-set (tuna target) longline/
set line’’ fishery operating in U.S.
waters.
Spinner dolphin (HI) is removed from
the list of species and stocks
incidentally killed or injured in the
Category I ‘‘High Seas Western Pacific
Pelagic (Deep-set component)’’ fishery.
This fishery is a component of the ‘‘HI
deep-set (tuna target) longline/set line’’
fishery component operating in U.S.
waters.
Pantropical spotted dolphin (stock
unknown) is removed from the list of
species and stocks incidentally killed or
injured in the Category II ‘‘High Seas
Western Pacific Pelagic (Shallow-set
component)’’ fishery. This fishery is a
component of the ‘‘HI shallow-set
(swordfish target) longline/set line’’
fishery operating in U.S. waters.
List of Fisheries
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The following tables set forth the final
list of U.S. commercial fisheries
according to their classification under
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section 118 of the MMPA. In Tables 1
and 2, the estimated number of vessels/
persons 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
in a fishery, the number from the most
recent LOF is used. For high seas
fisheries, Table 3 lists the number of
currently valid HSFCA permits held by
fishers. 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 at this time.
Tables 1, 2, and 3 also list the marine
mammal species and stocks incidentally
killed or injured in each fishery based
on observer data, logbook data,
stranding reports, disentanglement
network data, and fisher reports. This
list includes all species and stocks
known to be injured or killed in a given
fishery, but also includes species and
stocks for which there are anecdotal
records of an injury or mortality.
Additionally, species identified by
logbook entries may not be verified.
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 greater than 50 percent
[Category I], or greater than 1 percent
and less than 50 percent [Category II], of
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a stock’s PBR) by a ‘‘1’’ after the stock’s
name.
In Tables 1 and 2, there are several
fisheries classified in Category II that
have no recent documented injuries or
mortalities of marine mammals, or that
did not result in a serious injury or
mortality rate greater than 1 percent of
a stock’s PBR level. NMFS has classified
these fisheries by analogy to other gear
types 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. 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,
operating within U.S. waters and on the
high seas. These fisheries, while listed
on both Table 1 or 2, and 3, are not
separate fisheries. Instead, they are
components of a single fishery
organized on Table 1, 2, or 3 by
geographic region. NMFS has
designated those fisheries in each Table
by an ‘‘*’’ after the fishery’s name.
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; Table 4 lists
fisheries affected by Take Reduction
Plans or Teams.
BILLING CODE 3510–22–S
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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
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Small Business Administration that this
rule would not have a significant
economic impact on a substantial
number of small entities. The factual
basis leading to the certification is set
forth below.
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Under existing regulations, all fishers
participating in Category I or II fisheries
must register under the MMPA and
obtain an Authorization Certificate. The
Authorization Certificate authorizes the
taking of marine mammals incidental to
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commercial fishing operations.
Additionally, fishers may be subject to
a Take Reduction Plan (TRP) and
requested to carry an observer. NMFS
has estimated that approximately 44,600
fishing vessels, most of which are small
entities, operate in Category I or II
fisheries, and therefore, are required to
register with NMFS. The MMPA
registration process is integrated with
existing state and Federal licensing,
permitting, and registration programs.
Therefore, fishers who have a state and
Federal fishery permit or landing
license, or who are authorized through
another related state and Federal fishery
registration program, are currently not
required to register separately under the
MMPA or pay the $25 registration fee.
Therefore, there are no direct costs to
small entities under this final rule.
If a vessel is requested to carry an
observer, fishers will not incur any
direct economic costs associated with
carrying that observer. Potential indirect
costs to individual fishers required to
take observers may include: lost space
on deck for catch, lost bunk space, and
lost fishing time due to time needed to
process bycatch data. For effective
monitoring, however, observers will
rotate among a limited number of
vessels in a fishery at any given time
and each vessel within an observed
fishery has an equal probability of being
requested to accommodate an observer.
Therefore, the potential indirect costs to
individual fishers are expected to be
minimal because observer coverage
would only be required for a small
percentage of an individual’s total
annual fishing time. In addition, section
118 of the MMPA 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. As a
result of this certification, an initial
regulatory flexibility analysis is not
required and was not prepared. In the
event that reclassification of a fishery to
Category I or II results in a TRP,
economic analyses of the effects of that
plan will be summarized in subsequent
rulemaking actions.
This final rule contains collection-ofinformation requirements subject to the
Paperwork Reduction Act. The
collection of information for the
registration of fishers 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
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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
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 is no need to update the 2005 EA
at this time. If NMFS takes a
management action, for example,
through the development of a TRP,
NMFS will first prepare an
environmental document, as required
under NEPA, specific to that action.
This final rule will 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
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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 will 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 will 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.
References
Barlow, J., and S. Rankin. 2007. False
killer whale abundance and density:
preliminary estimates for PICEAS study
area south of Hawaii and new estimates
for the US EEZ around Hawaii.
Administrative Report LJ–07–02.
Southwest Fisheries Science Center,
National Marine Fisheries Service, 8604
La Jolla Shores Drive La Jolla, CA 92037.
Forney, K. A., and D. R. Kobayashi.
2007. Updated Estimates of Mortality
and Injury of Cetaceans in the Hawaiibased Longline Fishery, 1994–2005.
U.S. Department of Commerce, NOAA
Technical Memorandum NMFS, NOAATM-NMFS-SWFSC–412, 30 p.
NMFS. 2005. Revisions to Guidelines
for Assessing Marine Mammal Stocks.
24 pp. Available at: https://
www.nmfs.noaa.gov/pr/pdfs/sars/
gamms2005.pdf
Dated: November 9, 2009.
Samuel D. Rauch III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
[FR Doc. E9–27431 Filed 11–13–09; 8:45 am]
BILLING CODE 3510–22–S
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Agencies
[Federal Register Volume 74, Number 219 (Monday, November 16, 2009)]
[Rules and Regulations]
[Pages 58859-58901]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-27431]
=======================================================================
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 229
[Docket No. 090218194-91045-02]
RIN 0648-AX65
List of Fisheries for 2010
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 2010, as required by the Marine
Mammal Protection Act (MMPA). The final LOF for 2010 reflects new
information on interactions between commercial fisheries and marine
mammals. NMFS must categorize 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 categorization 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
requirements.
DATES: This final rule is effective January 1, 2010.
ADDRESSES: See SUPPLEMENTARY INFORMATION for a listing of all Regional
Offices. 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 David Rostker,
OMB, by fax to 202-395-7285 or by email to David_Rostker@omb.eop.gov.
FOR FURTHER INFORMATION CONTACT: Melissa Andersen, Office of Protected
Resources, 301-713-2322; David Gouveia, Northeast Region, 978-281-9280;
Anne Ney, Southeast Region, 727-551-5758; 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, 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: Marcia Hobbs;
NMFS, Southeast Region, 263 13th Avenue South, St. Petersburg, FL
33701, Attn: Anne Ney;
NMFS, Southwest Region, 501 W. Ocean Blvd., Suite 4200, Long Beach,
CA 90802-4213, Attn: Lyle Enriquez;
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
[[Page 58860]]
9th Street, Juneau, AK 99802, Attn: Bridget Mansfield; or
NMFS, Pacific Islands Region, Protected Resources, 1601 Kapiolani
Boulevard, Suite 1100, 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 take reduction plan 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.
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.
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.
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 proposed rule implementing section 118 of the MMPA (60
FR 45086, August 30, 1995).
Because fisheries are categorized 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
categorized 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
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 of 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 for Fisheries (50 CFR 229.2). Further, eligible
commercial fisheries not specifically identified on the LOF are deemed
to be Category II fisheries until the next LOF is published.
How Does NMFS Determine which Species and Stocks are Included as
Incidentally Killed or Injured in a Fishery?
The LOF includes a list of marine mammal species and stocks
incidentally killed or injured in each commercial fishery. To determine
which species and 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, and fisher self-reports.
When reliable information and sufficient levels of observer
coverage are available, the most recent five years of data are used to
determine whether a species or stock should be added to, or deleted
from, the list of species and stocks incidentally killed or injured in
each commercial fishery. 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 fishery
management plan (FMP) or a take reduction plan (TRP)). NMFS will
provide case-specific justification in the LOF for changes to the list
of species and stocks incidentally killed or injured.
How Does NMFS Determine the Level of Observer Coverage in a Fishery?
Data obtained from observers and the level of observer coverage are
important tools in estimating the level of 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 in the LOF, including observer coverage. The SARs generally do
not provide detailed information on observer coverage in Category III
fisheries because, under the
[[Page 58861]]
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. 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 Resource's website at:
https://www.nmfs.noaa.gov/pr/sars/. Additional information on observer
programs in commercial fisheries can be found on the NMFS National
Observer Program's website: 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 fisheries in the
Pacific Ocean (including Alaska); Table 2 lists all of the fisheries in
the Atlantic Ocean, Gulf of Mexico, and Caribbean; Table 3 lists all
U.S.-authorized fisheries on the high seas. A fourth table, Table 4,
lists all fisheries managed under applicable take reduction plans or
teams.
Are High Seas Fisheries Included on the LOF?
Beginning with the 2009 LOF, NMFS includes high seas fisheries in
Table 3 of the LOF, along with the number of valid High Sea 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 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 the
fishery operating within U.S. waters (listed in Table 1 or 2). In these
fisheries, a single vessel may set both within the U.S. Exclusive
Economic Zone (EEZ) and on the high seas during a single fishing trip.
NMFS designates those fisheries in Tables 1, 2, and 3 by an ``*'' 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 do
not necessarily represent additional fishers that are not accounted for
in Tables 1 and 2. Many fishers holding these permits also fish within
U.S. waters and are included in the number of vessels and participants
operating within those fisheries in Table 1 and 2.
HSFCA permits are valid for five years, during which time FMPs can
change. Therefore, some fishers 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).
Are Treaty Tribal Fisheries Included on the LOF?
In the final rule implementing section 118 of the MMPA (60 FR
45086, August 30, 1995) NMFS concluded that treaty tribal fisheries are
conducted under the authority of the Indian treaties; the MMPA's
requirements in section 118 do not apply to treaty Indian tribal
fisheries. NMFS explained this decision in the final rule stating (the
remaining text in this paragraph is quoted direction from the final
rule at 60 FR 45086, August 30, 1995), `` the rights to fish and hunt
are already secured separately for Northwest tribes pursuant to their
treaties with the United States. NMFS reviewed the relationship of the
Northwest Indian treaties to the MMPA and did not find clear evidence
that Congress intended to abrogate treaty Indian rights. Section 14 of
the Amendments to the MMPA (Public Law No. 103-238) states 'Nothing in
this Act, including any amendments to the Marine Mammal Protection Act
of 1972 made by this Act -- alters or is intended to alter any treaty
between the United States and one or more Indian tribes.' This
provision clarifies that existing treaty Indian fishing rights are not
affected by the amendments to the MMPA. Therefore, tribal fisheries are
conducted under the authority of the Indian treaties rather than the
MMPA, and the MMPA's mandatory registration systems do not apply to
treaty Indian fishers operating in their usual and accustomed fishing
areas. Since inclusion of the treaty Indian fisheries in the LOF would
also establish an obligation to obtain an MMPA registration under
section 118, NMFS has deleted reference to tribal fisheries in the LOF.
The registration requirements for Category I or II fisheries will not
apply to treaty Indian tribes.'' (60 FR 45086, August 30, 1995.)
NMFS considered, among other things, the public comments received
on the proposed 2010 LOF and the 1994 amendments to the MMPA and
accompanying legislative history to re-evaluate its 1995 conclusion to
exempt tribal fisheries from the LOF (60 FR 45086, August 30, 1995)
should be changed due to Anderson v. Evans. NMFS determined that
Anderson v. Evans did not alter NMFS' original analysis in the final
rule implementing section 118 of the MMPA (60 FR 45086, August 30,
1995); therefore, the inclusion of tribal fisheries on the LOF at this
time is not warranted. NMFS will continue to work on a government-to-
government basis with the affected treaty tribal governments to gather
data on injuries and mortalities of marine mammals incidental to tribal
fisheries. Additional information on NMFS' decision to continue to
exclude tribal fisheries from the LOF is provided below in the response
to comments 1-5 in the section ``Comments and Responses.''
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 be registered with NMFS and obtain a marine mammal
authorization to lawfully take a non-endangered and non-threatened
marine mammal incidental to commercial fishing. Owners of vessels or
gear engaged in a Category III fishery are not required to be
registered with NMFS or obtain a marine mammal authorization.
What is the Registration Process?
NMFS has integrated the MMPA registration process, known as 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
Pacific Islands, Southwest, Northwest, and Alaska regions, NMFS will
issue vessel or gear owners an authorization certificate; in the
Northeast and Southeast Regions, NMFS will issue vessel or gear owners
notification of
[[Page 58862]]
registry and directions on obtaining an authorization certificate. 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 Receive My Authorization Certificate and Injury/Mortality
Reporting Forms?
All vessel or gear owners that participate in Pacific Islands,
Southwest, Northwest, or Alaska regional fisheries will receive their
authorization certificates and/or injury/mortality reporting forms via
U.S. mail, or with their state or Federal license at the time of
renewal. Vessel or gear owners participating in the Northeast and
Southeast Regional Integrated Registration Program will receive their
authorization certificates as follows:
1. Northeast Region vessel or gear owners participating in Category
I or II fisheries for which a state or Federal permit is required may
receive their authorization certificate and/or injury/mortality
reporting form by contacting the Northeast Regional Office at 978-281-
9328 or by visiting the Northeast Regional Office Web site (https://www.nero.noaa.gov/prot_res/mmap/certificate.html) and following
instructions for printing the necessary documents.
2. Southeast Region vessel or gear owners participating in Category
I or II fisheries for which a state or Federal permit is required will
receive notice of registry and may receive their authorization
certificate and/or injury/mortality reporting form by contacting the
Southeast Regional Office at 727-551-5758 or by visiting the Southeast
Regional Office Web site (https://sero.nmfs.noaa.gov/pr/pr.htm) and
following instructions for printing the necessary documents.
How Do I Renew My Registration Under the MMPA?
Vessel or gear owners that participate in Pacific Islands,
Southwest, or Alaska regional fisheries are automatically renewed and
should receive an authorization certificate by January 1 of each new
year. Vessel or gear owners in Washington and Oregon fisheries 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).
Vessel or gear owners participating in Southeast or Northeast
regional fisheries may receive an authorization certificate by calling
the relevant NMFS Regional Office or visiting the relevant NMFS
Regional Office Web site (see ``How Do I Receive My Authorization
Certificate and Injury/Mortality Reporting Forms'').
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 Category I, II, or III
fishery must report to NMFS all incidental injuries and mortalities of
marine mammals that occur during commercial fishing operations.
``Injury'' is defined in 50 CFR 229.2 as a wound or other physical
harm. In addition, any marine mammal that ingests fishing gear or any
marine mammal 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.
Reporting requirements and procedures can be found in 50 CFR 229.6.
Am I Required to Take an Observer Aboard My Vessel?
Fishers participating in a Category I or II fishery are required to
accommodate an observer aboard vessel(s) upon request. MMPA Section 118
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 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)) or vessels operating in
North Carolina fisheries observed under the Alternative Platform
Program. Observer requirements can be found in 50 CFR 229.7.
Am I Required to Comply With Any Take Reduction Plan Regulations?
Fishers participating in a Category I or II fishery are required to
comply with any applicable TRP regulations. Table 4 in this final rule
provides a list of fisheries affected by take reduction teams and
plans. Take reduction plan regulations can be found at 50 CFR 229.30
through 229.36.
Sources of Information Reviewed for the Final 2010 LOF
NMFS reviewed the marine mammal incidental serious injury and
mortality information presented in the SARs for all observed fisheries
to determine whether changes in fishery classification were warranted.
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
fisheries and the PBR levels of marine mammal stocks. The information
contained in the SARs is reviewed by three 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, fishery management plans, and ESA documents.
The final LOF for 2010 was based, among other things, on
information provided in the NEPA and ESA documents analyzing authorized
high seas fisheries, 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
[[Page 58863]]
26340, May 4, 2006), 2006 (72 FR 12774, March 19, 2007), 2007 (73 FR
21111, April 18, 2008), and 2008 (74 FR 19530, April 29, 2009). 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 fisheries on the
2010 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, or through state agencies. Additional details
for Category I and II fisheries operating on the high seas are included
in various FMPs, NEPA, or ESA documents.
American Samoa Longline Fishery
The Category II ``American Samoa longline'' fishery operates in
waters around American Samoa targeting tuna (mainly albacore, also
skipjack, yellowfin and bigeye). Wahoo, sharks, billfish, and other
miscellaneous pelagic species are also caught, with most of the sharks
and billfish released. In 2000, the ``American Samoa longline'' fishery
began to expand rapidly with the influx of large (more than 50 ft (15.2
m) overall length) conventional monohull vessels, similar to the type
used in the Hawaii-based longline fisheries. Vessels over 50 ft (15.2
m) may set 1,500 2,500 hooks and have a greater fishing range and
capacity for storing fish (8 40 metric tons). The fleet reached a peak
of 66 vessels in 2001, and set a peak of almost 7,000 sets in 2002.
The rapid expansion of longline fishing effort within the EEZ
waters around American Samoa prompted the Western Pacific Fishery
Management Council (WPFMC) to develop a limited entry system for the
fishery, implemented by NMFS in 2005. Under the limited access program,
NMFS issued a total of 60 initial longline limited entry permits in
2005 to qualified candidates, spread among 4 vessel size classes (72 FR
10711, March 9, 2007): 22 permits issued in Class A (less than or equal
to 40 ft (12.2 m) length); 5 in Class B (40-50 ft (12.2-15.2 m)); 12 in
Class C (50-70 ft (15.2-21.3 m)); and 21 in Class D (more than 70 ft
(21.3 m)). The limited entry program regulations cap the maximum number
of permits to the 60 initial permits issued. Permits may be
transferred, upgraded, and renewed. In 2008, the American Samoa
longline fishery had 28 active vessels. Observers were first placed on
American Samoa longline vessels in April 2006 to monitor protected
species interactions, with observer coverage averaging approximately 6-
8 percent each year.
Under the limited entry program, vessel operators must submit
Federal longline logbooks, vessels over 40 ft (12.2 m) must carry
observers if requested by NMFS, and vessels over 50 ft (15.2 m) must
have an operational vessel monitoring system. In addition, vessel
owners and operators of vessels registered to an American Samoa
longline limited entry permit must attend a protected species workshop
annually, carry and use dip nets, line clippers, and bolt cutters, and
follow handling, resuscitation, and release requirements for
incidentally hooked or entangled sea turtles (70 FR 69282, November 15,
2005). There are existing regulations intended to mitigate sea turtle
incidental hookings, and in 2009 the WPFMC recommended additional
measures be implemented to minimize interactions with green sea
turtles, including modifications to gear to place hooks below 100 m
(328 ft) depth and to increase observer coverage (WPFMC 144th Meeting,
March 23-26, 2009). Current regulations include a prohibition on U.S.
vessels greater than 50 ft (15.2 m) in length from using longline gear
within 50 nmi around the islands of American Samoa. American Samoa
longline fishery regulations can be found at 50 CFR 665.36-38.
HI Shortline Fishery
The Category II ``HI shortline'' fishery is a small-scale system
operating off the State of HI, and targeting bigeye tuna (Thunnus
obesus) or the lustrous pomfret (Eumigistes illustris). This fishery
was developed to target these fish species when they concentrate over
the summit of Cross Seamount (290 km (180 mi) south of the State of
HI). The gear style is designed specifically to target the aggregating
fish species over seamount structures. The primary gear type used is a
horizontal main line (monofilament) less than 1 nmi long, and includes
two baskets of approximately 50 hooks each. The gear is set before dawn
and has a short soak time, with the gear retrieved about two hours
after it is set. This fishery has no seasonal component and may operate
year-round. There are no specific fishing permits issued for this
fishery. However, all persons with a State of Hawaii Commercial Marine
License (CML) may participate in any fishery, including the ``HI
shortline'' fishery. Of those persons possessing CMLs, shortline
participation has changed from 5 to 11 vessels during 2003-2008. From
2003-2008, there was an average of 135,757 pounds (lbs) of fish landed
each year. In 2008 alone, 104,152 lbs of fish were landed. Currently,
there is no reporting system in place to document potential marine
mammal interactions in this fishery. However, there are anecdotal
reports of interactions off the north side of the island of Maui, but
the species and extent of interactions are unknown.
Comments and Responses
NMFS received 11 comment letters on the proposed 2010 LOF (74 FR
27739, June 11, 2009). Comments were received from the California
Department of Fish and Game, California Wetfish Producers Association,
Center for Biological Diversity, Columbia River Inter-Tribal Fish
Commission, Eighteen Western Washington Indian Tribes, Garden State
Seafood Association, Hawaii Longline Association, Makah Tribal Council,
Makah Tribe's marine mammal biologist, Marine Conservation Alliance,
and Marine Mammal Commission. Comments on issues outside the scope of
the LOF were noted, but are not responded to in this final rule.
Comments on Tribal Treaty Fisheries Inclusion on the 2010 LOF
During the public comment phase for the then-proposed 2009 LOF,
NMFS received a comment requesting the 2009 LOF be amended to include
tribal fisheries. The commenter stated that ``in light of the
subsequent holding of the Ninth Circuit in Anderson v. Evans...finding
that the MMPA applies to the Makah application to the gray whale hunt
NMFS' 1995 conclusion exempting tribal fisheries from the LOF and the
Section 118 authorization process is no longer valid'' (73 FR 73039,
December 1, 2008; comment/response 4). In response to this 2009 LOF
comment, NMFS included a request for public comment in the proposed
2010 LOF (74 FR 27739, June 11, 2009) on whether or not to include
treaty tribal fisheries on future LOFs. Below, NMFS summarizes each
comment received on the 2010 proposed LOF related to tribal fisheries
and issues one response following the collective tribal fisheries
comments.
Comment 1: The Center for Biological Diversity (CBD) reiterated a
comment on the 2009 LOF (73 FR 73039, December 1, 2008; comment/
response 4), noting that in an earlier decision the Ninth Circuit Court
of Appeals determined that MMPA requirements applied to the Makah
application to hunt gray whales (Anderson v. Evans, 371 F.3d 475 (9th
Cir. 2004)). The CBD stated that the decision demonstrated that MMPA
requirements can be harmonized with
[[Page 58864]]
treaty rights. Therefore, the CBD encouraged NMFS to move forward with
determining how best to harmonize tribal fishing and treaty rights with
MMPA requirements such that all fisheries operating in US waters are
included in the LOF and categorized as I, II or III, as appropriate.
Comment 2: The Marine Mammal Commission (MMC) recommended NMFS (1)
include tribal fisheries on the LOF, (2) revise its regulations
implementing section 118 (e.g., 50 C.F.R. Sec. 229.1 (d)) to clarify
that treaty tribal fisheries are subject to the requirements of the
MMPA, including section 118, and (3) begin working with the affected
tribes to integrate the registration process with existing licensing or
permitting systems if it appears that some tribal fisheries will be
listed as category I or category II fisheries.
Comment 3: The Makah Tribe presented data indicating that tribal
incidental takes of marine mammals do not present any conservation
issues notwithstanding NMFS' 1995 decision to exclude treaty tribal
fisheries from the LOF. The Makah Tribe compiled data regarding
incidental take in its treaty fisheries and requires that all mortality
or injury resulting from an incidental take, required in Makah Tribal
regulations to be reported to the Tribe, and submits an annual report
to NMFS. Records of these reports have been kept since the Tribe hired
a marine mammal biologist in 2003. In general the rate of incidental
take of marine mammals during fishing operations is low. From 2003-
2009, the Makah Tribal fisheries incidentally killed 12 harbor seals (1
in 2003, 6 in 2004, 4 in 2008, 1 in 2009), 1 Dall's porpoise (in 2004),
5 harbor porpoise (2 in 2004, 3 in 2008), 6 unknown small odontocetes
(in 2005), 1 Steller sea lion (in 2008), 1 unidentified sea lion (in
2008), and 2 sea otters (in 2004). One unidentified whale and one gray
whale were successfully released after entanglement (in 2005 and 2009,
respectively).
The Makah tribe noted that, despite a long history of interactions
between Makah Tribal fishers and marine mammals, these animals remain
abundant, as indicated by NMFS' SARs. Observed take of marine mammals
by the Makah Tribe's treaty fisheries is well below PBR for each stock.
In addition, populations of marine mammal stocks which are most likely
to interact with Makah tribal fisheries have either increased or
remained stable since the MMPA was amended in 1994 and NMFS determined
that treaty tribal fisheries would not be included in the LOF: CA sea
lions have increased 5.6 percent/year since the 1970s; WA/OR stock of
harbor seals has been stable since 1996; Inland WA stock of harbor
seals has been stable at carrying capacity since 1994; Outer coast
stock of harbor porpoises has been stable; Inland WA stock of harbor
porpoise 2002 population estimate is three times more than the 1996
estimate; Eastern stock of Steller sea lions increased 3.1 percent/year
(with regional variances); and WA stock of sea otters increased at 8
percent/year.
Comment 4A: The Makah Indian Tribe outlined three arguments
(comments 4A, 4B, and 4C in this final rule) for the continued
exclusion of treaty tribal fisheries from the LOF, based on its
experience with the MMPA and as a party to Anderson v. Evans. The Makah
Indian Tribe also joined and fully incorporated the comments in the
joint tribal letter submitted by eighteen other Western Washington
treaty tribes (see comments 5A, 5B, and 5C in this final rule)
asserting that NMFS' 1995 rule interpreting the relationship between
the Tribe's treaty-reserved right to take fish and Section 118 of the
MMPA has not been affected by Anderson v. Evans and continues to be
valid. Therefore, the Makah Tribe recommends that NMFS reaffirm its
1995 decision that treaty tribal fisheries are not subject to the
MMPA's mandatory registration and that treaty tribal fisheries will not
be included in the LOF.
The Makah Tribe's first argument for the continued exclusion of
treaty tribal fisheries from the LOF was that the proper reading of the
1994 MMPA Amendments' treaty savings clause (section 14) protects
incidental take of marine mammals by tribal fishers because the treaty
fishing right, as understood by the Indian signatories, includes the
right to take marine mammals incidental to tribal fisheries.
Comment 4B: The Makah Tribe's second argument for the continued
exclusion of treaty Tribal fisheries from the LOF was that Anderson v.
Evans was wrongly decided (a position which the United States has also
repeatedly expressed) and, therefore, should not be extended to the
LOF. The Makah Tribe asserted that although Anderson v. Evans addressed
direct take of marine mammals such as the Makah gray whale hunt, by its
own terms it does not apply to the question of incidental take in
treaty tribal fisheries. Therefore, the Makah Tribe believed NMFS need
not and should not extend the decision to the issues of mandatory
registration and inclusion in the LOF.
During the Anderson v. Evans case, the United States took the
position that the panel opinion was incorrectly based on numerous
fundamental errors in reaching its conclusion. In the Makah Tribe's
opinion, if NMFS were to extend Anderson v. Evans to the LOF issue, it
would further reinforce the panel's numerous incorrect applications of
settled precedent and directly contradict the United States' ongoing
disagreement with the case. Moreover, the Makah Tribe concluded that it
would substantially undermine the Makah's and other western Washington
Tribes' treaty rights notwithstanding their express protection by the
1994 Amendments. The Makah Tribe believed such a decision would
contravene Congress's express intent.
Comment 4C: The Makah Tribe's third argument for the continued
exclusion of treaty Tribal fisheries from the LOF was that the Makah
Tribe does and will continue to work with NMFS to protect marine
mammals. The Makah Tribe noted that NMFS' 1995 rule excluding treaty
tribal fisheries from the LOF was based in part on the extensive
cooperation between the tribes and NMFS in managing tribal fisheries,
including their interactions with marine mammals (See 60 FR at 45096,
Aug. 30, 1995). The Makah Tribe noted that in the 1995 final rule, NMFS
found that tribal self-regulation and cooperation with NMFS were
instrumental to the agency achieving its responsibilities to protect
marine mammals.
Comment 5A: NMFS received two separate letters, each representing
multiple Washington Indian tribes that were similar to each other in
the arguments presented. Therefore, the two comments presented in the
two letters are summarized together below. The first letter represented
the comments of the Columbia River Inter-Tribal Fish Commission (Nez
Perce, Umatilla, Warm Springs and Yakama Tribes), the second letter
represented the joint comments of eighteen Indian Tribes of western
Washington State (Lummi Nation, Quinault Indian Nation, Swinomish
Indian Tribal Community, and Nooksack, Tulalip, Suquamish, Squaxin
Island, Nisqually, Puyallup, Sauk-Suiattle, Skokomish, Muckleshoot,
Port Gamble, Jamestown, Lower Elwha, Upper Skagit, Quileute, and
Stillaguamish Indian Tribes), collectively, the ``Tribes.'' The Tribes
outlined three arguments (comments 5A, 5B, and 5C in this final rule)
asserting that NMFS' 1995 conclusion that treaty fisheries are properly
excluded from the LOF (60 FR 45086, August 30, 2009; at 45096) was
correct, and remains correct.
The Tribes' first argument was that NMFS' 1995 conclusion remains
correct
[[Page 58865]]
because the Tribes' rights are reserved by various treaties and the
U.S. has broad trust responsibility to the Tribes.
Comment 5B: The Tribes' second argument was that NMFS' 1995
conclusion regarding Tribal fisheries remains correct because it is not
affected by the rulings of the Ninth Circuit in Anderson v. Evans. The
Tribes asserted that Anderson v. Evans involved the Makah Tribe's
exercise of its express whaling rights in the Treaty of Neah Bay, and
was wholly unrelated to the Makah Tribe's - or any other Tribes' -
treaty right to take fish. The Tribes argued that the Anderson v. Evans
court did not address the applicability of the 1994 MMPA amendments to
treaty fisheries or the exercise of any other treaty rights, but
instead focused solely on the applicability of the MMPA's general take
prohibition, which has no Indian treaty savings clause, to the Makah
Tribe's gray whale hunt. The Tribes asserted that as a result of the
narrow scope of the case, the court did not address - nor did it have
any reason to address - the MMPA's provisions governing incidental take
of marine mammals in commercial fisheries, much less treaty tribal
fisheries. In the Tribes' opinion, because Anderson v. Evans did not
address Section 118 of the Act, the 1994 amendments (including the
treaty savings clause) or the 1995 rule, it is inapplicable to the 2010
LOF rulemaking. The Tribes also asserted that the incidental take of
marine mammals in treaty fisheries is well within the treaty rights
protected by the 1994 treaty savings clause, a statute which must be
construed liberally in favor of the Indians.
Comment 5C: The Tribes' third argument was that NMFS' 1995
conclusion regarding Tribal fisheries remains accurate because the
Tribes' regulate their fisheries (including interactions with marine
mammals) and NMFS retains authority to regulate tribal fisheries should
the principle of conservation necessity deem it necessary. In the
Tribes' opinion, NMFS need not take the radical step of reversing its
1995 rule with respect to treaty tribal fisheries and the LOF because,
as a practical and legal matter, the agency is fully capable of
protecting marine mammals under the existing rule. Finally, the Tribes
noted that, just as in 1995 when NMFS asserted its authority to
regulate tribal fisheries under the treaty rights principle of
conservation necessity, NMFS retains that option should the impact of
treaty tribal fisheries on certain marine mammal species reach the
threshold to apply the conservation necessity principle. Thus, NMFS
retains the authority to regulate treaty fisheries under appropriate
circumstances.
Response: In the final rule implementing section 118 of the MMPA
(60 FR 45086, August 30, 1995) NMFS concluded that treaty tribal
fisheries are conducted under the authority of Indian treaties;
therefore, the MMPA's requirements in section 118 do not apply to
treaty Indian tribal fisheries. NMFS explained this decision in the
1995 final rule stating (the remaining text in this paragraph is quoted
directly from the final rule at 60 FR 45086, August 30, 1995), `` the
rights to fish and hunt are already secured separately for Northwest
tribes pursuant to their treaties with the United States. NMFS reviewed
the relationship of the Northwest Indian treaties to the MMPA and did
not find clear evidence that Congress intended to abrogate treaty
Indian rights. Section 14 of the Amendments to the MMPA (Public Law No.
103-238) states ``Nothing in this Act, including any amendments to the
Marine Mammal Protection Act of 1972 made by this Act -- alters or is
intended to alter any treaty between the United States and one or more
Indian tribes. '' This provision clarifies that existing treaty Indian
fishing rights are not affected by the amendments to the MMPA.
Therefore, tribal fisheries are conducted under the authority of the
Indian treaties rather than the MMPA, and the MMPA's mandatory
registration systems do not apply to treaty Indian fishers operating in
their usual and accustomed fishing areas. Since inclusion of the treaty
Indian fisheries in the LOF would also establish an obligation to
obtain an MMPA registration under section 118, NMFS has deleted
reference to tribal fisheries in the LOF. The registration requirements
for Category I or II fisheries will not apply to treaty Indian
tribes.'' (60 FR 45086, August 30, 1995.)
NMFS considered the public comments received on the proposed 2010
LOF, existing Indian treaties providing rights for tribal fisheries,
the statutory provisions and context of the MMPA, and the legislative
history of the 1994 amendments to the MMPA in evaluating whether the
1995 decision to exempt treaty tribal fisheries from the LOF should be
changed due to Anderson v. Evans, 371 F.3d 475 (9th Cir. 2004). NMFS
has determined that the facts and holding of Anderson v. Evans do not
alter NMFS' original analysis in the final rule implementing section
118 of the MMPA (60 FR 45086, August 30, 1995). Anderson v. Evans
applied to directed hunt of marine mammals and not incidental take of
marine mammals by fishers. Section 118 of the MMPA specifically
regulates incidental take of marine mammals by commercial fishers. The
court in Anderson v. Evans did not address the treaty savings clause,
which restricts the application of section 118 in the context of tribal
treaty rights. In addition, NMFS continues to adhere to a policy of
implementing the Federal trust responsibility by protecting treaty
fishing rights of tribes. NMFS also will continue to work closely with
the affected tribal governments on a government-to-government basis to
gather data on injuries and mortalities of marine mammals incidental to
tribal fisheries. In light of the above, NMFS did not include in the
2010 LOF the treaty tribal fisheries where tribal fishers exercise
their treaty-protected fishing rights.
Based on the information presented in the final 2008 SARs and
provided in Indian Tribal self-reports, there is no indication that any
marine mammal bycatch associated with tribal fisheries presents a
biological concern for applicable stocks. In the event this becomes an
issue, NMFS would consider invoking the treaty-rights principle of
``conservation necessity'' to protect marine mammals.
The 2008 SARs show that nine species have been or are incidentally
seriously injured and killed in Pacific Northwest treaty tribe
fisheries, though many of these species have not been seriously injured
or killed in recent years. All of the takes by tribal fisheries listed
in the 2008 SARs are from non-depleted stocks of marine mammals. One
take occurring after publication of the 2008 SARs was from a depleted
stock. Below is a summary of the information provided in the 2008 SARs
as well as information available from tribal self-reporting since
publication of the 2008 SARs. Please see the 2008 SARs for more
detailed information on these stocks and/or their interactions with
treaty tribal fisheries.
(1) California sea lions: Current estimates of annual serious
injury or mortality of this stock in tribal fisheries is zero to two
animals/year. The stock's PBR level is 8,511.
(2) Harbor seal (OR/WA coast): The Northern WA marine set gillnet
(tribal fishery in coastal waters) fishery seriously injured or killed
3 harbor seals in 2000 and 6 in 2004. The PBR for this stock is 1,343
and the minimum total fishery mortality and serious injury is less than
10 percent of the PBR. Therefore, fishery mortality and serious injury
appears to be insignificant and approaching a zero mortality and
serious injury rate.
[[Page 58866]]
(3) Harbor seal (WA inland waters): The Puget Sound treaty and non-
treaty sockeye salmon gillnet fishery seriously injured or killed one
harbor seal in 1994. The PBR for this stock is 771 and the minimum
estimated fishery mortality and serious injury for this stock appears
to be less than 10 percent of the PBR. Therefore, fishery mortality and
serious injury appears to be insignificant and a approaching zero
mortality and serious injury rate.
(4) Harbor Porpoise (Northern CA/Southern OR): One harbor porpoise
mortality was documented for the Klamath River tribal salmon gillnet
fishery in 1995. The PBR for this stock is 259 and the minimum
estimated fishery mortality and serious injury for this stock appears
to be less than 10 percent of the PBR. Therefore, fishery mortality and
serious injury appears to be insignificant and approaching a zero
mortality and serious injury rate.
(5) Harbor Porpoise (OR/WA coast): The Northern WA marine set
gillnet (tribal fishery in coastal waters) fishery seriously injured or
killed 3 harbor porpoise in 2000. In addition, 2 harbor porpoise (stock
unknown) were reported killed in 2004 in a Makah Tribal fishery (Makah
Tribe self-reports). Based on the range of the stock and the location
of the Makah fisheries, the animals were either part of the OR/WA coast
stock or the WA Inland Waters stock. The PBR for this stock is 277 and
the minimum estimated fishery mortality and serious injury for this
stock appears to be less than 10 percent of the PBR. Therefore, fishery
mortality and serious injury appears to be insignificant and
approaching zero mortality and serious injury rate.
(6) Harbor Porpoise (WA inland waters): The Puget Sound treaty and
non-treaty sockeye salmon gillnet fishery seriously injured or killed
one harbor porpoise in 1994. As stated above, 2 harbor porpoise (stock
unknown) were reported killed in 2004 in a Makah Tribal fishery (Makah
Tribe self-reports). Based on the range of the stock and the location
of the Makah fisheries, the animals were either part of the OR/WA coast
stock or the WA Inland Waters stock. The PBR for this stock is 63.
While the status of the WA Inland Waters stock relative to its Optimum
Sustainable Population level and population trends is unknown, the
uncorrected estimate of abundance in Washington inland waters was
significantly greater in 2002-2003 than in 1996.
(7) Dall's Porpoise (CA/OR/WA): The Puget Sound salmon drift
gillnet tribal fishery seriously injured or killed one Dall's porpoise
in the period from 2000 to 2004. The PBR for this stock is 318 and the
minimum estimated fishery mortality and serious injury for this stock
appears to be less than 10 percent of the PBR. Therefore, fishery
mortality and serious injury appears to be insignificant and
approaching a zero mortality and serious injury rate.
(8) Sea otter (WA): Sea otters (WA) are managed by the U.S. Fish
and Wildlife Service. According to the Service's 2008 SAR, the Makah
Northern Washington marine set-gillnet fishery seriously injured or
killed 11 sea otters over a period of 13 years between 1988 and 2001
(2008 SAR) and 2 sea otters in 2004 (Makah Indian Tribe self-report).
The stock has increased at a rate of 8 percent since 1989. The PBR for
this stock is 11 per year. The Service was unable to determine whether
the level of human-caused mortalities and serious injuries are
insignificant and approaching a zero mortality and serious injury rate,
based on a lack of information on the level of all sources of human-
caused serious injury and mortality of this stock. However, the current
population estimate of 1,125 is above the lower end of the Optimum
Sustainable Population (60 percent of the maximum carrying capacity for
the stock) (2008 SAR).
In addition to the information provided in the 2008 SARs, recent
self-reports from the Makah Indian Tribe show additional serious injury
and mortality of marine mammal stocks not yet represented in the SARs
(see comment 3 above). The Makah Indian Tribe's self-reported data
indicate that Makah fisheries interacted with three marine mammal
stocks in 2008 and 2009.
(1) In 2009, a gray whale was entangled in a Makah fishery and
released alive. The Eastern North Pacific gray whales are currently
considered to be at the stock's Optimum Sustainable Population size
(2008 SAR).
(2) In 2008, a Steller sea lion was killed in a Makah fishery.
Based on the geographical range of the species, this animal was most
likely from the Eastern stock of Steller sea lions, which is listed as
threatened under the ESA and therefore considered depleted under the
MMPA. Based on currently available data, the minimum estimated U. S.
commercial fishery-related mortality and serious injury for Eastern
Steller sea lions is less than that 10 percent of the stock's PBR of
200 per year; therefore, fishery mortality and serious injury appears
to be insignificant and approaching a zero mortality and serious injury
rate (2008 SAR). In addition, the Eastern Steller sea lion population
has been consistently increasing at an overall annual rate of 3.1
percent throughout most of the range (Oregon to southeastern Alaska),
which may indicate that this stock is reaching Optimum Sustainable
Population size (2008 SAR).
(3) In 2008, 3 harbor porpoises were killed in a Makah fishery.
While the stock is unknown, based on the geographic range of the stock
and the location of the Makah fisheries, the animals were either part
of the OR/WA coast stock or the WA Inland Waters stock. As stated
above, the PBR for this OR/WA coast stock is 277 and the minimum
estimated fishery mortality and serious injury for this stock appears
to be less than 10 percent of the PBR. Therefore, fishery mortality and
serious injury appears to be insignificant and approaching zero
mortality and serious injury rate. Also stated above, while the status
of the WA Inland Waters stock relative to its Optimum Sustainable
Population level and population trends is unknown, the uncorrected
estimate of abundance in Washington inland waters was significantly
greater in 2002-2003 than in 1996 (2008 SARs).
NMFS will continue to work closely with the affected tribal
governments on a government-to-government basis to gather data on
injuries and mortalities of marine mammals incidental to tribal
fisheries.
General Comments
Comment 6: The MMC recommended, based on their recommendation that
tribal fisheries be included on the LOF (comment/response 2 above),
that NMFS notify all treaty tribes believed to be engaged in hunting
that any directed taking of marine mammals requires authorization under
the MMPA. In reviewing the SARs prepared by NMFS under section 117 of
the MMPA, the MMC noted that tribal hunting of harbor seals and
California sea lions is included as a possible source of mortality. The
MMC asserted that if such hunting is in fact ongoing, it would be
subject to the same analysis as the proposed taking of gray whales at
issue in Anderson v. Evans and would presumably require authorization
under the MMPA.
Response: NMFS acknowledges this comment; however, this comment is
not applicable to the LOF rulemaking at hand. The LOF categorizes
fisheries based solely on the incidental, not intentional, serious
injury and mortality to marine mammals. However, this comment is
relevant to the SARs rulemaking process; therefore, NMFS will address
this comment as part of the comments received during the comment period
for the proposed 2009 SARs
[[Page 58867]]
(June 26, 2009-September 24, 2009; overlapping with the comment period
for the proposed 2010 LOF).
Comment 7: The MMC recommended NMFS incorporate into the applicable
SARs language similar to that included in the SAR for the Washington
stock of sea otters prepared by the U.S. Fish and Wildlife Service to
clarify that, in accordance with the ruling in Anderson v. Evans, any
such taking requires authorization under the MMPA.
Response: NMFS acknowledges this comment; however, this comment is
not applicable to the LOF rulemaking at hand. This comment is relevant
to the SARs rulemaking process; therefore, NMFS will address this
comment as part of the comments received during the comment period for
the proposed 2009 SARs (June 26, 2009-September 24, 2009; overlapping
with the comment period for the proposed 2010 LOF).
Comment 8: The Garden State Seafood Association (GSSA) requested
that NMFS provide the number of vessels which reported landings for
specific fisheries and gear types, along with estimated number of
vessels or persons in individual fisheries currently reported on the
LOF. The GSSA noted that this information would be specifically
pertinent when considering the ``Mid Atlantic mid-water trawl'' fishery
and the ``Northeast mid-water trawl'' fishery. The GSSA stated that
recently the number of vessels who reported landings using a mid-water
trawl in the Mid-Atlantic was approximately 17 vessels.
Response: NMFS agrees that including information on the number of
vessels landing catches to compare to the estimated number of permit
holders could be helpful for providing an accurate description of
effort in each fishery. However, while this information is readily
available for some fisheries, gathering this information in other
fisheries may be more complicated. It is unclear if the information
would be readily available from state agencies. NMFS will consult with
the responsible state agencies and consider incorporating this
additional data for each fishery in future LOFs.
Comment 9: The CBD reiterated a comment made on the 2009 LOF that
the LOF lists over 40 fisheries that are known to interact with ESA-
listed marine mammals. Only one fishery, the ``CA/OR thresher shark/
swordfish drift gillnet'' fishery, has authorization to take ESA-listed
marine mammals. The CBD asserted that each of the other fisheries is
therefore operating in violation of the both the ESA and MMPA. The CBD
further asserted that NMFS must either issue permits for these
fisheries authorizing take under these statutes, or take appropriate
enforcement action, including, as necessary, closure of the fisheries,
to ensure such illegal take does not continue to occur.
Response: NMFS received a similar comment on the 2009 LOF. As noted
in NMFS' response to comments in the final 2009 LOF (73 FR 73032,
December 1, 2008; comment/response 2), the CBD's comment refers to how
NMFS authorizes takes of ESA listed marine mammals incidental to
commercial fishing. The MMPA requires fishermen to obtain a permit
granted under section 101(a)(5)(E) of the MMPA if they participate in a
fishery that takes ESA-listed marine mammals. A 101(a)(5)(E) permit
does not authorize the operation of a fishery. Instead, a 101(a)(5)(E)
permit authorizes the incidental take of ESA-listed marine mammals in
commercial fisheries, if certain provisions are met. Any incidental
take of an ESA-listed species in an otherwise legally-operating
fishery, without a 101(a)(5)(E) permit, is not authorized. If an ESA-
listed species is taken by a fishermen in a fishery that has not been
granted a MMPA 101(a)(5)(E) permit, then the fisher may be subject to
enforcement proceedings.
NMFS acknowledges that the LOF includes fisheries in which ESA-
listed species are listed as incidentally killed or injured, but for
which NMFS has not issued a permit under section 101(a)(5)(E) of the
MMPA. To issue a permit under section 101(a)(5)(E) of the MMPA, NMFS
must determine that (1) the incidental mortality and serious injury
from commercial fisheries will have a negligible impact on such species
and stocks; (2) a recovery plan has been developed or is being
developed for such species or stock pursuant to the ESA; and (3) where
required under section 118 of the MMPA, a monitoring program is
established, vessels engaged in such fisheries are registered, and a
take reduction plan has been developed or is being developed for such
species or stock. NMFS is continuing this process of making these
determinations in various fisheries on the LOF. Since the publication
of the final 2009 LOF, NMFS has been reviewing available bycatch data
for ESA-listed species in fisheries on the LOF.
Comment 10: The CBD reiterated a comment made on the 2008 and 2009
LOFs that the proposed 2010 LOF includes a table of fisheries subject
to take reduction teams. While CBD found this table is very useful,
they noted that there are Category I and II fisheries not yet subject
to take reduction teams that also meet the statutory criteria for the
convening of such teams. The CBD asserted that Category I and II
fisheries not yet subject to take reduction teams which interact with
strategic stocks must have take reduction teams promptly convened. The
CBD viewed the Hawaii pelagic longline fishery as the highest priority
for such a team as take continues to exceed PBR for the false killer
whale.
Response: NMFS received similar comments on the 2008 and 2009 LOFs.
As noted in the responses to comments on the 2008 LOF (72 FR 66048,
November 27, 2007; comment/response 6) and 2009 LOF (73 FR 73032,
December 1, 2008; comment/response 3), at this time, NMFS' resources
for TRTs are fully utilized and new TRTs will be initiated when
additional resources become available. When NMFS lacks sufficient
funding to convene a TRT for all stocks that interact with Category I
and II fisheries, NMFS will give highest priority for developing and
implementing new take reduction plans to species and stocks whose level
of incidental mortality and serious injury exceeds PBR, has a small
population size, and are declining most rapidly, pursuant to MMPA
section 118(f)(3).
Comment 11: The CBD reiterated a comment made on the 2009 LOF that
the LOF once again includes ``Marine Aquaculture Fisheries'' as
Category III fisheries. As stated in the past, the CBD does not believe
aquaculture facilities are properly considered ``commercial fishing
operations'' eligible for the take authorization contained in Section
118 of the MMPA. The CBD asserted that these facilities and activities,
to the degree they interact with marine mammals, should be subject to
the take prohibitions and permitting regimes contained in Section 101
of the MMPA.
Response: NMFS received a similar comment on the 2009 LOF. As noted
in the responses to comments on the 2009 LOF (73 FR 73032, December 1,
2008; comment/response 5), eight aquaculture fisheries are listed on
the MMPA LOF, all as Category III fisheries. NMFS' regulations
implementing section 118 of the MMPA (50 CFR 229) specifically include
aquaculture as a commercial fishing operation. 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
[[Page 58868]]
MMPA, including inclusion on the annual LOF.
Comment 12: Consistent with its recommendations regarding the 2005
through 2009 LOFs, the MMC reiterated its previous recommendation that
NMFS indicate the level of observer coverage for each fishery as part
of the LOF.
Response: NMFS received similar comments on the 2005 through 2009
LOFs. As noted in the responses to comments on the 2005 LOF (71 FR 247,
January 2, 2006; comment/response 6), 2006 LOF (71 FR 48802, August 22,
2006; comment response 4), 2007 LOF (72 FR 14466, March 28, 2007;
comment/response 8), 2008 LOF (72 FR 66048, November 27, 2007; comment/
response 4), and 2009 LOF (73 FR 73032, December 1, 2008; comment/
response 1), NMFS continues to feel that the LOF is not the appropriate
avenue for reporting this data because it will confuse rather than
clarify if presented without all the associated information supplied in
the SARs. Also, the LOF is not meant to be redundant to the SARs, but
to base fishery classifications based on the information