List of Fisheries for 2009, 73032-73076 [E8-28378]
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excluding Federal holidays.
SUPPLEMENTARY INFORMATION:
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 229
[Docket No. 080204115–8832–02]
RIN 0648–AW48
List of Fisheries for 2009
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Department of Commerce.
ACTION: Final rule.
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AGENCY:
SUMMARY: The National Marine
Fisheries Service (NMFS) publishes its
final List of Fisheries (LOF) for 2009, as
required by the Marine Mammal
Protection Act (MMPA). The final LOF
for 2009 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 on
January 1, 2009.
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–
9328; Laura Engleby, Southeast Region,
727–824–5312; 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.
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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.
Regional Offices
NMFS, Northeast Region, One
Blackburn Drive, Gloucester, MA
01930–2298, Attn: Marcia Hobbs;
NMFS, Southeast Region, 263 13th
Avenue South, St. Petersburg, FL 33701,
Attn: Teletha Mincey;
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: Permits Office;
NMFS, Alaska Region, Protected
Resources, P.O. Box 22668, 709 West
9th Street, Juneau, AK 99802, Attn:
Bridget Mansfield; or
NMFS, Pacific Islands Region,
Protected Resources, 1601 Kapiolani
Boulevard, Suite 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 categorization of a
fishery in 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
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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
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LOF at its highest level of classification
(e.g., a fishery qualifying for Category III
for one marine mammal stock and for
Category II for another marine mammal
stock will be listed under Category II).
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Other Criteria That May Be Considered
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 or Stocks Are Included as
Incidentally Killed or Seriously Injured
in a Fishery?
The LOF includes a list of marine
mammal species or stocks incidentally
killed or seriously injured in each
commercial fishery, based on the level
of mortality or serious injury in each
fishery relative to the PBR level for each
stock. To determine which species or
stocks are included as incidentally
killed or seriously 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
mortality or serious injury incidental to
commercial fishing operations. NMFS
also reviews other sources of new
information, including observer data,
stranding data, and fisher self-reports.
In the absence of reliable information
on the level of mortality or serious
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 or a take reduction
plan). NMFS will provide case-specific
justification in the LOF for changes to
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the list of species or stocks incidentally
killed or seriously 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
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 Web site 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 Web site: https://
www.st.nmfs.gov/st4/nop/.
How Do I Find Out if a Specific Fishery
Is in Category I, II, or III?
This final rule includes three tables
that list all U.S. commercial fisheries by
LOF Category. Table 1 lists all of the
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. 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
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cases, the high seas component of the
fishery is not 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 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.
How Does NMFS Authorize U.S. Vessels
To Participate in High Seas Fisheries?
NMFS issues high seas fishing
permits, valid for five years, under the
HSFCA. To fish under a high seas
permit, a fisher must also possess any
required permits issued under the
Magnuson-Stevens Fishery
Conservation and Management Act
(MSA) (with the exception of the South
Pacific Tuna Treaty fisheries, the Pacific
Tuna Fisheries (Eastern Tropical Pacific
purse seine vessels) and the South
Pacific Albacore Troll fishery), and any
permits issued by NMFS to fish within
the convention area of a Regional
Fishery Management Organization.
Under the current permitting system,
however, a fisher can obtain a high seas
permit prior to obtaining any necessary
MSA permits. Similarly, a fisher may
have a HSFCA permit that was issued
prior to changes in permits issued under
the MSA. Therefore, some fishers
possess valid HSFCA permits without
the ability to fish under the permit. For
this reason, the number of HSFCA
permits displayed in Table 3 of this
final rule is likely higher than the actual
fishing effort by U.S. vessels on the high
seas.
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). There are currently seven U.S.authorized high seas fisheries: Atlantic
Highly Migratory Species Fisheries,
Pacific Highly Migratory Species
Fisheries, Western Pacific Pelagic
Fisheries, South Pacific Albacore Troll
Fishing, Pacific Tuna Fisheries, South
Pacific Tuna Fisheries, and Antarctic
Marine Living Resources. The LOF does
not include the ‘‘Pacific (Eastern
Tropical) Tuna Fisheries’’ because these
fisheries are managed under Title III of
the MMPA, separate from those fisheries
subject to the LOF under section 118.
Permits obtained prior to 2004 for
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fisheries that are no longer authorized
by the HSFCA, but for which the 5-year
permit is still valid, are included on the
LOF as ‘‘unspecified.’’ The
‘‘unspecified’’ fisheries will be removed
from the LOF once those permits have
expired, and the permit holder is
required to renew the permit under one
of the seven authorized fisheries.
The authorized high seas fisheries are
broad in scope and encompass multiple
specific fisheries identified by gear type.
Therefore, the seven U.S.-authorized
high seas fisheries, exclusive of the
‘‘Pacific (Eastern Tropical) Tuna
Fisheries,’’ are subdivided on the LOF
based on gear type (e.g., trawl, longline,
purse seine, gillnet, troll, etc.), as listed
on each fisher’s permit application, to
provide more detail on composition of
effort within these fisheries.
How Does NMFS Categorize High Seas
Fisheries on the LOF?
As discussed in the previous sections
of this preamble, commercial fisheries
operating within U.S. waters are
categorized on the LOF based on the
level of mortality and serious injury of
marine mammal stocks incidental to
commercial fishing as related to the
stock’s PBR level. PBR levels are
calculated based on the stock’s
abundance using data presented in the
SARs. Section 117 of the MMPA (16
U.S.C. 1386) requires NMFS to prepare
SARs for marine mammal stocks
occurring ‘‘in waters under the
jurisdiction of the United States.’’
NMFS does not develop SARs or
calculate PBR levels for marine mammal
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.
For this reason, NMFS categorizes the
majority of high seas fisheries on the
LOF as Category II. As discussed
previously in this preamble, Category II
is the appropriate category for
commercial fisheries not currently on
the LOF (e.g., new fisheries) and for
which NMFS does not have adequate
information to indicate the frequency of
incidental mortality and serious injury.
Classifying a fishery in Category II
allows NMFS to place observers on
vessels in that fishery, providing NMFS
the opportunity to obtain information
needed to assess the frequency of
bycatch in that fishery. For fisheries that
operate both within U.S. waters and on
the high seas, the high seas component
of the fishery is classified according to
the fishery’s status in U.S. waters
because it is not a separate fishery, but
an extension of the fishery. Therefore,
for a Category I or Category III fishery
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operating within U.S. waters, the high
seas component would also be classified
as Category I or Category III,
accordingly. NMFS will continue to
gather available information on the
authorized high seas fisheries and
reclassify fisheries in Table 3, if
necessary, as more information becomes
available.
How Does NMFS Determine Which
Species or Stocks To Include as
Incidentally Killed or Seriously Injured
in a High Seas Fishery?
All serious injury and mortality of
marine mammals incidental to
commercial fishing operations, both in
U.S. waters and on the high seas, must
be reported to NMFS. High seas fishers
are provided with Marine Mammal Take
Reporting Forms to record such
incidents. (Very few marine mammal
takes by U.S. vessels participating in
high seas fisheries, however, have been
reported on these forms to date.)
Observer programs for fisheries
operating within U.S. waters also collect
data on the high seas if the vessel
should cross into high seas waters.
Additionally, some fisheries that
operate exclusively on the high seas
have formal observer programs that
provide data on interactions. In these
cases, the MSA, NEPA, or ESA
documents supporting the authorization
of the seven U.S.-authorized high seas
fisheries review observer documented
interactions and list the marine mammal
species taken in those fisheries. This
information is used to identify marine
mammals killed or injured in these
fisheries in Table 3 on the LOF. For
other fisheries without observer data,
the MSA, NEPA, and ESA documents
supporting the authorization of the
seven U.S.-authorized high seas
fisheries present information on marine
mammal interactions from anecdotal
and other reports, which do not always
specify the marine mammal species
involved in the interactions. Therefore,
marine mammal species killed or
injured in the high seas fisheries
without observer data that are listed in
Table 3 are designated as
‘‘undetermined’’ until additional
information on marine mammal
populations and fishery interactions on
the high seas becomes available.
For high seas fisheries that are
extensions of fisheries operating within
U.S. waters, as discussed above, Table 3
lists the same marine mammal species
killed or injured in the high seas
components of fisheries (excluding
coastal species that would not be found
on the high seas) as those killed or
injured by the component of the fishery
operating within U.S. waters (Tables 1
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and 2). NMFS assumes that these
vessels pose the same risk to the species
on both sides of the Exclusive Economic
Zone (EEZ) boundary. NMFS will add
and delete species from the LOF as
additional information becomes
available.
Am I Required To Register Under the
MMPA?
Owners of vessels or gear engaging in
a Category I or II fishery are required
under the MMPA (16 U.S.C. 1387(c)(2)),
as described in 50 CFR 229.4, to register
with NMFS and obtain a marine
mammal authorization to lawfully take
a marine mammal incidental to
commercial fishing. Owners of vessels
or gear engaged in a Category III fishery
are not required to register with NMFS
or obtain a marine mammal
authorization.
How Do I Register?
NMFS has integrated the MMPA
registration process, 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 NMFS will issue vessel or
gear owners an authorization certificate.
Participants in these fisheries are not
required to submit registration or
renewal materials directly under the
MMAP. 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,
Northwest, or Alaska regional fisheries
will receive their authorization
certificates and/or injury/mortality
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reporting forms via U.S. mail, or with
their State or Federal license at the time
of renewal. Vessel or gear owners
participating in Southwest regional
fisheries or 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–
281–9300 x6505 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 Federal permit is
required, as well as fisheries permitted
by the states of North Carolina, South
Carolina, Georgia, Florida, Alabama,
Mississippi, Louisiana, and Texas may
receive their authorization certificate
and/or injury/mortality reporting form
by contacting the Southeast Regional
Office at 727–824–5312 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.
3. Southwest Region vessel or gear
owners participating in Category I or II
fisheries listed in the final 2008 LOF (72
FR 66048, published November 27,
2007) will receive their authorization
certificate and/or injury/mortality
reporting form as described above in the
integrated MMPA registration process.
A number of California state fisheries
are being re-categorized as Category II
fisheries in this final rule, and NMFS is
working with the State of California to
streamline the process of registering
vessel or gear owners participating in
these fisheries and issuing authorization
certificates, as required under MMPA
section 118. Fishermen may contact the
Southwest Regional Office at 562–980–
4025 for more information. The
Southwest Region plans to fully
integrate all California State Category I
and II fisheries for the 2009/2010 fishing
season.
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
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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 their authorization
certificates 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
animal that ingests fishing gear or any
animal that is released with fishing gear
entangling, trailing, or perforating any
part of the body is considered injured,
regardless of the presence of any wound
or other evidence of injury, and must be
reported. Injury/mortality reporting
forms and instructions for submitting
forms to NMFS can be downloaded
from: https://www.nmfs.noaa.gov/pr/
pdfs/interactions/
mmap_reporting_form.pdf. 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. 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 take reduction plans.
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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
229.30–35.
Sources of Information Reviewed for
the Final 2009 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 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 2009 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), the
final SARs for 2001 (67 FR 10671,
March 8, 2002), the final SARs for 2002
(68 FR 17920, April 14, 2003), the final
SARs for 2003 (69 FR 54262, September
8, 2004), the final SARs for 2004 (70 FR
35397, June 20, 2005), the final SARs for
2005 (71 FR 26340, May 4, 2006), the
final SARs for 2006 (72 FR 12774,
March 19, 2007), the final SARs for 2007
(73 FR 21111, April 18, 2008), and the
draft SARs for 2008 (73 FR 40299, July
14, 2008). The SARs are available at:
https://www.nmfs.noaa.gov/pr/sars/.
Fishery Descriptions
NMFS described each Category I and
II fishery on the 2008 LOF in the final
2008 LOF (72 FR 66048, November 27,
2007). Below, NMFS describes the
fisheries classified as Category I or II
fisheries on the 2009 LOF that were not
so categorized on the 2008 LOF.
Additional details for Category I and II
fisheries operating in U.S. waters are
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included in the SARs, fishery
management plans (FMPs), and take
reduction plans (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.
High Seas Atlantic Highly Migratory
Species Fisheries
The Atlantic Highly Migratory
Species (HMS) high seas fisheries are
virtually the same as fisheries targeting
Atlantic HMS within U.S. waters, but
primarily use pelagic longline gear.
Atlantic swordfish and bigeye tuna are
the primary target species on the high
seas, with Atlantic yellowfin, albacore
and skipjack tunas, and pelagic sharks
also caught and retained for sale.
Bluefin tuna are caught incidental to
pelagic longline operations, both on the
high seas and within U.S. waters, and
may be retained subject to specific target
catch requirements.
Within U.S. Atlantic waters, HMS
commercial fishers use several gear
types. Authorized gear for tuna include
rod and reel, handlines, bandit gear,
harpoon, pelagic longline, trap (pound
net and fish weir), and purse seine.
Purse seines used to target bluefin tuna
must have a mesh size of less than or
equal to 4.5 in (11.4 cm) and at least 24count thread throughout the net. Only
rod and reel gear may be used to target
billfish and commercial possession of
Atlantic billfish is prohibited.
Authorized gear for sharks includes rod
and reel, handline, bandit gear, longline,
and gillnet. Gillnets must be less than or
equal to 2.5 km (1.6 mi) in length and
must remain attached to the vessel
except during net checks. Authorized
gear for swordfish includes handline,
handgear (including buoy gear), and
longline for north Atlantic swordfish,
and longline for south Atlantic
swordfish. North Atlantic swordfish
incidentally taken in squid trawls may
be retained by federally permitted
vessels. The fishery management area
for Atlantic HMS includes U.S. waters
and the adjacent high seas.
Atlantic HMS are managed under
regulations implementing the
Consolidated Atlantic HMS FMP (2006),
under the authority of the MSA and the
Atlantic Tunas Convention Act (ATCA).
Regulations issued under the MSA
address the target fish species, as well
as bycatch of species protected by the
ESA, MMPA, and Migratory Bird Treaty
Act. The MSA regulations (50 CFR part
635) require vessel owners and
operators targeting Atlantic HMS with
longline or gillnet gear to complete
protected species (sea turtles and
marine mammals) safe handling,
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release, and identification workshops.
The regulations also require shark
dealers to complete an Atlantic shark
identification workshop.
The high seas components of Atlantic
HMS fisheries (Table 3) are extensions
of various Category I, II, and III fisheries
operating in U.S. waters (Table 2). The
longline fishery targeting Atlantic HMS
in U.S. waters is the Category I,
‘‘Atlantic Ocean, Caribbean, Gulf of
Mexico large pelagics longline fishery.’’
NMFS has issued proposed regulations
to implement the Pelagic Longline Take
Reduction Plan (PLTRP) for this fishery
(73 FR 35623, June 24, 2008). The
gillnet fishery targeting Atlantic HMS in
U.S. waters is the Category II,
‘‘Southeastern U.S. Atlantic shark
gillnet’’ fishery. In U.S. waters only, this
fishery is subject to the Bottlenose
Dolphin TRP (BDTRP) (50 CFR 229.35),
for coastal gillnetting only, and the
Atlantic Large Whale TRP (ALWTRP)
(50 CFR 229.32). The purse seine fishery
targeting Atlantic HMS in U.S. waters is
the Category III, ‘‘Atlantic tuna purse
seine fishery.’’
For more information on the Atlantic
HMS fisheries and details on the
management and regulations of these
fisheries, please see the Consolidated
Atlantic HMS FMP (https://
www.nmfs.noaa.gov/sfa/hms/
hmsdocument_files/FMPs.htm) and the
regulations for Atlantic HMS fisheries in
50 CFR part 635.
High Seas Pacific Highly Migratory
Species Fisheries
The Pacific HMS high seas fisheries
are virtually the same as fisheries
targeting Pacific HMS within U.S.
waters. Pacific HMS fisheries target
tunas (North Pacific albacore, yellowfin,
bigeye, skipjack, and bluefin), billfish
(striped marlin), sharks (common
thresher, pelagic thresher, bigeye
thresher, shortfin mako, and blue),
swordfish, and dorado (i.e., dolphinfish)
using several gear types. Authorized
gear include surface hook-and-line
(including troll, rod and reel, handline,
albacore jig, and live bait), harpoon
(non-mechanical), drift gillnet (14 in
(35.5 cm) stretch mesh or greater),
pelagic longline, and purse seine
(including ring, drum, and lampara
nets). Pacific HMS incidentally caught
by unauthorized gear may be landed
under certain circumstances. Species
prohibited in Pacific HMS fisheries
include any salmon species, great white
shark, basking shark, megamouth shark,
and Pacific halibut. The fishery
management area for Pacific HMS
covers U.S. waters from the U.S.-Mexico
border to the U.S.-Canada border, and
the adjacent high seas.
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Pacific HMS are managed under
regulations implementing the FMP for
U.S. West Coast Fisheries for HMS,
adopted in April 2004. The MSA
regulations (50 CFR part 660, subpart K)
address the target fish species as well as
species protected by the ESA and
MMPA. The MSA regulations lay out
multiple restrictions for fishing for
Pacific HMS with longline gear. Vessels
fishing longline gear may not target
HMS within U.S. waters. Targeting
swordfish with shallow set longline gear
or possessing a light stick on board the
vessel west of 150° W. long. and north
of the equator is prohibited. From April
1–May 31, longline gear is prohibited in
the area bounded on the south by the
equator, north by 15° N. lat., east by
145° W. long., and west by 180° long.
Longline vessels must have a valid
protected species workshop certificate
onboard, along with safe handling and
release tools for sea turtles and seabirds.
The use of shallow set longline gear to
target HMS east of 150° W. long. is
prohibited under a rule promulgated
through the ESA to protect threatened
loggerhead sea turtles.
Along with the MSA requirements,
including area closures for marine
mammal and sea turtle protection, drift
gillnet fishing for Pacific HMS is
managed under the MMPA through the
Pacific Offshore Cetacean Take
Reduction Plan (POCTRP) (50 CRF
229.31), both in U.S. waters and on the
high seas. The POCTRP regulations
require multiple gear modifications
during the May 1–January 31 fishing
season, including a requirement that all
extenders (buoy lines) be at least 6
fathoms (36 ft; 10.9 m) in length, all
floatlines be fished at a minimum of 36
ft (10.9 m) below the surface, and all
nets have operational pingers to a water
depth of a least 100 fathoms (600 ft;
182.9 m). Also, after notification from
NMFS, all drift gillnet vessel operators
must attend skipper education
workshops before each fishing season.
The high seas components of Pacific
HMS fisheries are extensions of various
Category I, II, and III fisheries operating
within U.S. waters (Tables 1 and 2). The
drift gillnet fishery targeting Pacific
HMS within U.S. waters, the Category I
‘‘CA/OR thresher shark/swordfish drift
gillnet (≥14 in. mesh) fishery,’’ is
managed under the POCTRP. The purse
seine fishery targeting Pacific HMS
within U.S. waters is the Category II
‘‘CA tuna purse seine fishery.’’ While
longline fishing for Pacific HMS is
prohibited within U.S. waters, the LOF
includes the Category II ‘‘CA pelagic
longline fishery’’ to account for HMS
caught outside U.S. waters, but landed
into the U.S. West coast. The troll
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fishery targeting Pacific HMS within
U.S. waters is the Category III ‘‘AK
North Pacific halibut, AK bottom fish,
WA/OR/CA albacore, groundfish,
bottom fish, CA halibut non-salmonid
troll fisheries.’’
For more information on the Pacific
HMS fisheries and details on the
management and regulations of these
fisheries, please see the Pacific HMS
FMP (https://www.pcouncil.org/hms/
hmsfmp.html#final), the Pacific HMS
FMP Biological Opinion (BiOp) (https://
swr.nmfs.noaa.gov/
HMS_FMP_Opinion_Final.pdf), and the
regulations for Pacific HMS in 50 CFR
part 660, subpart K.
High Seas Western Pacific Pelagic
Fisheries
The Western Pacific pelagic high seas
fisheries are virtually the same as
fisheries targeting Western Pacific
pelagic species in U.S. waters. Western
Pacific pelagic fisheries target tunas
(albacore, bigeye, yellowfin, bluefin,
and skipjack), billfish (Indo-Pacific blue
marlin, black marlin, striped marlin,
shortbill spearfish), sharks (pelagic
thresher, bigeye thresher, common
thresher, silky, oceanic whitetip, blue,
shortfin mako, longfin mako, and
salmon), swordfish, sailfish, wahoo,
kawakawa, moonfish, pomfret, oilfish,
and other tuna relatives. The main gear
types used to fish in the Western Pacific
Pelagic fisheries are pelagic longline,
troll, and handline. The Western Pacific
Pelagic fisheries take place in the
Western Pacific Fishery Management
Area (including waters shoreward of the
EEZ boundary around American Samoa,
Guam, Hawaii, the Northern Mariana
Islands, Midway, Johnston and Palmyra
Atolls, Kingman Reef, and Wake, Jarvis,
Baker, and Howland Islands) and the
adjacent high seas waters.
Western Pacific Pelagic fisheries are
managed under regulations
implementing the FMP for the Pelagic
Fisheries of the Western Pacific Region
developed by the Western Pacific
Fishery Management Council (WPFMC).
The MSA regulations (50 CFR part 665,
subpart C) address target fish species as
well as bycatch of species protected
under the ESA, MMPA, and Migratory
Bird Treaty Act. The MSA regulations
outline restrictions on effort, observer
coverage requirements, longline fishing
prohibited areas, sea turtle and seabird
bycatch mitigation measures, annual
fleetwide limits on interactions with
leatherback and loggerhead sea turtles,
and a requirement for owners of
longline vessels to participate in annual
protected species workshops. Drift
gillnet fishing in the fishery
management area is prohibited, except
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where authorized by an experimental
fishery permit.
The high seas components of the
Western Pacific Pelagic longline fishery
are extensions of the Category I ‘‘HI
deep-set (tuna target) longline/set line
fishery’’ and the Category II ‘‘HI
shallow-set (swordfish target) longline/
set line fishery’’ operating within U.S.
waters. All requirements for vessels
fishing longline gear in these two
fisheries operating within U.S. waters
remain effective in high seas waters (as
described in the above paragraph).
For more information on the Western
Pacific Pelagic fisheries and details on
the management and regulations of
these fisheries, please see the Western
Pacific Pelagic FMP BiOp (https://
www.fpir.noaa.gov/Library/PUBDOCs/),
the Western Pacific Pelagic FMP
Environmental Impact Statement (EIS)
(https://www.fpir.noaa.gov/Library/
PUBDOCs/), and the regulations for
Western Pacific Pelagic fisheries in 50
CFR 665, subpart C.
High Seas South Pacific Albacore Troll
Fisheries
The South Pacific albacore troll high
seas fisheries target South Pacific
albacore using mostly longline or troll
gear in waters solely outside of any
nation’s EEZ. Longline gear, set with
1,000 or more hooks suspended from a
horizontally buoyed mainline several
miles long, accounts for 86 percent of
the catch. Trolling vessels (including
jigs or live bait) attach 10–20 fishing
lines of various lengths to the vessel’s
outriggers on a slow-moving boat (5–6
knots). The total U.S. catch of South
Pacific albacore has accounted for less
than 5 percent of the total international
catch in recent years.
U.S. vessels fish in the South Pacific
albacore fishery from November/
December–April. Many vessels then
participate in the larger North Pacific
albacore fishery from April–October.
South Pacific albacore fishing occurs
outside any nation’s EEZ in an area
bounded by approximately 110° W.
long. and 180° W. long., and by 25° S.
lat. and 45° S. lat. Most U.S. troll vessels
depart from the U.S. West Coast or
Hawaii and land catch in American
Samoa, Fiji, or Tahiti.
The South Pacific albacore troll
fishery is not managed by regulations
implementing any FMP. The WPFMC
and NMFS have concluded that
conservation and management measures
for this fishery are not warranted
because the albacore stock in not
overfished and there are no known
protected species interactions. Sea
turtles and marine mammals do not
prey on the bait species used by these
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vessels and vessels are typically slowmoving and would therefore likely be
able to avoid a collision with a large
whale. As of 2001, the HSFCA requires
U.S. albacore troll vessel operators to
file logbooks with NMFS for fishing in
the South Pacific.
For more information on the South
Pacific albacore troll fishery, please see
the 2004 U.S. South Pacific albacore
troll fishery Environmental Assessment
(EA) (https://www.fpir.noaa.gov/Library/
PUBDOCs/).
High Seas South Pacific Tuna Fisheries
The South Pacific Tuna Treaty (SPTT)
manages access of U.S. purse seine
vessels targeting tuna (skipjack and
yellowfin) within the EEZs of 16 Pacific
Island Countries in the Western and
Central Pacific Ocean that are party to
the Treaty. The SPTT Area includes the
waters from north of 60° S. lat. and east
of 90° E. long. subject to the fishing
jurisdiction of Pacific Island parties to
the Treaty, and all waters within rhumb
lines connecting multiple geographic
coordinates, and north along the 152° E.
long. out to Australia’s EEZ border. The
Treaty Area includes portions of waters
in the EEZs of most of the Pacific Island
Countries included in the Treaty. The
SPTT was intended to apply only to
U.S. purse seine vessels; however,
provisions have been made to
accommodate fishing by U.S. albacore
tuna troll and U.S. longline vessels
within the Treaty Area. Both a SPTT
and a HSFCA permit are required to fish
in SPTT waters.
Under the SPTT, observers are
recruited from the Pacific Island
Countries and then trained and
deployed by the Forum Fisheries
Agency (FFA) in Honiara in the
Solomon Islands. Many of the FFA
deployed observers serve in and have
experience from domestic observer
programs active in each observer’s
respective country. The target observer
level coverage is 20 percent of U.S.
purse seine vessels, the full costs of
which are the responsibility of the U.S.
purse seine vessel owners. Observers
collect a range of data, including a form
for recording information on
interactions with seabirds, sea turtles,
marine mammals, and sharks. Fishery
observers undergo training in species
identification for target and bycatch
species; however, marine mammal
species identification has only recently
been placed as a priority matter for
reporting. Observer data from January
1997–June 2002 show that 11 sets
resulted in interactions with marine
mammals. However, the data indicate
only that the animals were
‘‘unidentified whales, marine mammals,
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or dolphin/porpoise.’’ The International
Fisheries Division of the NMFS Pacific
Islands Region is working with the FFA
observer program to better train
observers in marine mammal
identification.
For additional information on the
SPTT and details on the management
and regulations of these fisheries, see
the South Pacific Tuna Treaty EA
(https://www.fpir.noaa.gov/Library/
PUBDOCs/) and the regulations for the
SPTT in 50 CFR 300, subpart D.
High Seas Antarctic Living Marine
Resources Fisheries
The Commission for the Conservation
of Antarctic Marine Living Resources
(Convention or CCAMLR) conserves and
manages Antarctic marine living
resources (AMLR) in waters
surrounding Antarctica. The Convention
applies to AMLR in the waters from 60°
S. lat. south to the Antarctic
Convergence, with limited exceptions,
covering 32.9 million square kilometers.
Both an AMLR and a HSFCA permit are
required to fish in CCAMLR waters.
There are multiple gear types used to
target multiple species in the
Convention Area. Gear types include
pelagic and bottom trawl, trap/pot,
gillnet, and longline. Target species
include krill and Antarctic finfish
(rockcod species, toothfish species,
icefish species, silverfish, cod, and
lanternfish), mollusks, and crustaceans.
CCAMLR Conservation Measures
require or recommend several measures
for fisheries in the Convention area.
Mandatory measures include
requirements for reporting; operating a
Vessel Monitoring System while in the
Convention area; longline gear
modifications to reduce seabird
interactions; and mesh sizes restrictions
for trawl gear. Recommendations
include seal bycatch mitigation
measures, such as a seal excluder device
in trawl fisheries.
CCAMLR has identified two types of
scientifically trained observers to collect
information required in CCAMLRmanaged fisheries, including
information on entanglements and
incidental mortality of seabirds and
marine mammals. The first type of
observer is a ‘‘national observer,’’ such
as a U.S. observer placed on a U.S.
vessel by the U.S. government. The
second type of observer is an
‘‘international observer,’’ or an observer
operating in accordance with bilateral
arrangements between the nation whose
vessel is fishing and the nation
providing the observer. CCAMLR
Conservation measures require all
fishing vessels in the Convention area
(except vessels fishing for krill) to carry
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at least one international observer and,
where possible, an additional observer.
The United States requires all of its
vessels fishing in the CCAMLR area, for
any target species and with any gear, to
carry an observer. In certain exploratory
toothfish fisheries, the vessel must carry
two observers, with at least one being an
international observer.
For additional information on the
fishing activities in the CCAMLR region
and details on the management and
regulations of these fisheries, see the
CCAMLR Programmatic EIS (https://
www.nmfs.noaa.gov/sfa/domes_fish/
news_of_note.htm#ccamlr), the
CCAMLR Schedule of Conservation
Measures in Force (https://
www.ccamlr.org), and the regulations
for the harvesting of AMLR in 50 CFR
300, subpart D.
CA Spot Prawn Pot Fishery
The Category II ‘‘CA spot prawn pot
fishery’’ operates from Central CA
southward to the Mexican border.
Strings of 10–50 oblong cylindrical traps
are commonly fished at depths usually
greater than 100 fathoms. This is a
limited access fishery managed by the
state of CA. A tiered permit system
allows a maximum of 150 or 500 traps
to be fished at one time depending on
the fishing history associated with the
permit. A maximum of 300 traps may be
located within state waters (inside 3
miles), regardless of the permit tier.
North of Point Arguello, the season is
open from August 1–April 30. South of
Point Arguello, the season runs from
February 1–October 30.
CA Dungeness Crab Pot Fishery
The Category II ‘‘CA Dungeness crab
pot fishery’’ operates in the central and
northern coastal waters of CA in depths
typically from 10–40 fathoms. The
cylindrical or rectangular pots used in
the fishery are fished singly, or
individually, such that each pot has its
own buoy; although, fishing multiple
traps connected together (called
‘‘strings’’) is allowed in the central
region. There is no limit on the number
of traps which may be operated by a
fisher at one time. This is a limited
access fishery managed by the state of
CA and pursuant to the Tri-State
Committee agreement for Dungeness
crab, which also includes the states of
OR and WA. The fishery is divided into
two management areas. The fishing
season in the central region (south of the
Mendocino-Sonoma county line) is
open November 15–June 30. The fishing
season in the northern region (north of
the Mendocino-Sonoma county line)
can open on December 1, but may be
delayed by the California Department of
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Fish and Game based on the condition
of market crabs, and continues until July
15.
OR Dungeness Crab Pot Fishery
The Category II ‘‘OR Dungeness crab
pot fishery’’ operates in the coastal
waters of OR in depths typically from
10–40 fathoms. The cylindrical or
rectangular pots used in the fishery are
fished singly, or individually, such that
each pot has its own buoy. This is a
limited access fishery managed by the
OR Department of Fish and Wildlife and
pursuant to the Tri-State Committee
agreement for Dungeness crab, which
also includes the states of CA and WA.
A three-tiered pot limitation system,
based on previous landing history,
allows a maximum 200, 300, or 500
single pots to be fished by a fisher at
once. The Dungeness crab season runs
from December 1–August 14, although
the Oregon Department of Fish and
Wildlife may delay the opening based
on the condition of the market crabs.
Additionally, the state may close the
season after the end of May, if catch
rates are still high, to protect molting
crab. Logbook reporting of effort and
catch data to the state is required.
WA/OR/CA Sablefish Pot Fishery
The Category II ‘‘CA/OR/WA sablefish
pot fishery’’ operates in waters past the
100 fathom curve off the West coast of
the U.S. In CA, gear is set outside 150
fathoms, with an average depth of 190
fathoms. There are two separate trap
fisheries, open access and limited entry,
and both have quotas. Open access
fishers will usually fish 1 to 8 strings of
3–4 pots, each with a float line and buoy
stick. The gear sometimes soaks for long
periods. Fishers in the limited entry
fishery will normally fish 20–30 pot
strings. As with most pot gear fished out
in deeper waters, sablefish traps are set
in strings of multiple traps. The fishery
operates year round and effort varies
from southern CA to the Canadian
border.
This fishery is managed under
regulations implementing the West
Coast Groundfish FMP developed by
Pacific Fishery Management Council.
Access to the limited entry fishery is
granted under a limited entry permit
system, in addition to gear
endorsements required by the
individual states. Open access privileges
are currently available to any fisher with
the requisite state gear endorsement, but
involve much more restrictive
limitations in catch quotas and
additional area closures than the
primary limited entry permit. Open
access quotas vary based upon the area
being fished. The limited entry fishery
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is open from April 1–October 31, while
open access is available year-round.
Limited entry permits are tiered based
on the annual cumulative landings
allowed by each permit. Permits are
transferable, but the tier category
remains fixed. Up to three limited entry
permits may be stacked on a single
vessel.
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Comments and Responses
NMFS received 10 comment letters on
the proposed 2009 LOF (73 FR 33760,
June 13, 2008). Comments were received
from the Marine Mammal Commission,
Center for Biological Diversity (CBD),
Western Pacific Regional Fishery
Management Council (WPFMC), MidAtlantic Fishery Management Council
(MAFMC), North Carolina Division of
Marine Fisheries (NCDMF), Oregon
Department of Fish and Wildlife
(ODFW), California Department of Fish
and Game (CDFG), Garden State Seafood
Association, Hawaii Longline
Association (HLA), and California
Wetfish Producers Association.
Comments on issues outside the scope
of the LOF were noted, but are not
responded to in this final rule.
General Comments
Comment 1: The Marine Mammal
Commission reiterated comments made
on the 2005 through 2008 LOFs
recommending that NMFS describe the
level of observer coverage for each
fishery as part of the LOF. NMFS
indicated in its response to the
comments on the 2008 LOF that it ‘‘feels
that it will be of limited use to include
observer coverage data or percentages in
the LOF without also including the
confidence associated with mortality/
serious injury estimates generated from
the observer data.’’ The Commission
would welcome inclusion of
information on mortality and serious
injury estimates within the LOF, as they
recommended in comments on the 2005
LOF that such information be included.
The Commission continues to believe
observer coverage information is
important in itself, particularly for
evaluating cases where no marine
mammal interactions are reported.
Fisheries without recorded interactions
are not reported in the SARs and,
without information on observer
coverage, it is impossible to determine
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.
Response: NMFS continues to feel
that the LOF is not the appropriate
venue for reporting this data because it
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will confuse rather than clarify if
presented without all the associated
information supplied in the SARs.
However, NMFS agrees 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 exploring other options for
providing information on observer
coverage as it applies to the LOF and
will notify readers of these sources in
subsequent LOFs. In addition, NMFS is
preparing to release the National
Bycatch Report (NBR). The NBR will
provide a comprehensive summary of
regional and national bycatch estimates,
based on observer data and fisher
reports, of fish, marine mammals, sea
turtles, and sea birds in U.S. commercial
fisheries that have a Federal nexus. The
NBR will include observer coverage
information that can be referenced
while reviewing the 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 Resource’s
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 2: The CBD noted that the
proposed 2009 LOF lists over 40
fisheries that are known to interact with
ESA-listed marine mammals. Only one
fishery, the Category I ‘‘CA/OR thresher
shark/swordfish drift gillnet fishery,’’
has authorization to take ESA-listed
marine mammals. Each of these other
fisheries is therefore operating in
violation of both the ESA and MMPA.
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: CBD’s comment refers to
how NMFS authorizes takes of ESAlisted marine mammals incidental to
commercial fishing. The MMPA
requires fishers 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
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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 fisher 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/
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
or 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 in the process of
making these determinations in various
fisheries on the LOF.
Comment 3: The CBD noted that the
proposed 2009 LOF includes a table of
fisheries subject to take reduction teams
(TRT). This is very useful. However,
numerous Category I and II fisheries not
yet subject to TRTs also meet the
statutory criteria for convening such
teams. All Category I and II fisheries not
yet subject to TRTs which interact with
strategic stocks must have TRTs
promptly convened. The Hawaii pelagic
longline fishery should be the highest
priority for such a team as take
continues to exceed PBR for false killer
whales.
Response: Please see comment/
response 6 in the final 2008 LOF (72 FR
66048, November 27, 2007). 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 or stocks whose level of
incidental mortality and serious injury
exceeds PBR, those with a small
population size, and those which are
declining most rapidly, pursuant to
MMPA section 118(f)(3).
Comment 4: The CBD stated concerns
regarding groups of ‘‘fisheries’’ that
NMFS has excluded from the LOF. In
the final rule implementing section 118
of the MMPA (60 FR 45086, August 20,
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1995), NMFS concluded that tribal
fisheries were exempt from the
permitting requirements the MMPA. In
light of the subsequent holding of the
Ninth Circuit in Anderson v. Evans, 371
F.3d 475 (9th Cir. 2002) finding that the
MMPA applies to the Makah application
to the gray whale hunt, the CBD believes
that NMFS’ 1995 conclusion exempting
tribal fisheries from the LOF and the
Section 118 authorization process is no
longer valid. The 2009 LOF should be
amended to include tribal fisheries.
Response: NMFS will consider this
comment during the development of
future proposed LOFs.
Comment 5: The CBD does not believe
aquaculture facilities are properly
considered commercial fishing
operations eligible for the take
authorization contained in MMPA
section 118. These facilities and
activities, to the degree they interact
with marine mammals, should be
subject to the take prohibitions and
permitting regimes contained in MMPA
section 101.
Response: 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 ‘‘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.’’
Comment 6: The WPFMC continues to
be concerned that no recreational
fishing activities are assessed under the
LOF, although recreational fisheries
may have a much greater impact on
marine mammal stocks than their
commercial counterparts. This seems a
rather arbitrary application of the
MMPA to marine fisheries.
Response: NMFS agrees there are
documented cases of incidental injury
or death of marine mammals in
recreational fishing gear. However,
MMPA section 118 governs the ‘‘Taking
of Marine Mammals Incidental to
Commercial Fishing Operations.’’
Specifically, section 118(c)(1)(A) directs
NMFS to ‘‘publish * * * list of
commercial fisheries’’ that interact with
marine mammals.
Comments on High Seas Fisheries
Comment 7: The CBD supported
NMFS’ decision to include high seas
fisheries on the LOF, but they have
concerns with how NMFS is
implementing the process. NMFS treats
fisheries that have both a high seas and
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within-EEZ component as two separate
fisheries for LOF purposes. CBD
believes this raises 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), therefore resulting in an
underestimation of the true
environmental effect, and LOF
classification of what is more properly
considered the same fishery. For
example, if the total take from a fishery
operating both in and outside the EEZ
is 60 percent of PBR, the fishery should
be a Category I. However, if the fishery
is split into two components and take is
evenly apportioned, the total take from
each fishery is only 30 percent of PBR,
and therefore a Category II. NMFS must
clarify how it will apportion take so as
to not create this problem.
Response: Although the high seas
components of fisheries that operate
both within U.S. waters and on the high
seas are listed in a separate table in the
LOF, they are not considered separate
fisheries from their associated
components operating in U.S. waters.
Instead, NMFS considers these fisheries
as the same fishery that has extended
beyond the 200 nmi boundary of the
EEZ. Because of the organization and
format of Tables 1 and 2 in the LOF, and
because high seas fisheries have
additional management (permit)
requirements, it is necessary to list them
on a separate table on the LOF (Table 3).
NMFS clarifies which fisheries in Table
3 are extensions of fisheries operating in
U.S. waters by placing a ‘‘*’’ after the
fishery name. NMFS will not apportion
any incidental serious injury or
mortality in these fisheries separately
for purposes of categorization. Takes on
either side of the EEZ boundary are
included as takes in one fishery. As
stated in the preamble of this rule,
NMFS does not calculate PBR estimates
for marine mammals stocks on the high
seas. Therefore, at this time, the high
seas fisheries that are extensions of
fisheries operating within U.S. waters,
are categorized the same as the
component operating within U.S.
waters.
Comment 8: The Marine Mammal
Commission concurred with NMFS’
decision to describe and evaluate high
seas fisheries and include them on LOF.
Doing so makes the LOF more nearly
complete and more consistent with the
scope of the MMPA. The descriptions
and evaluations of high seas fisheries
highlight the lack of data on both the
status and the incidental take of marine
mammals outside the U.S. EEZ, and
information on status and incidental
take of marine mammals in foreign and
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international fisheries often is not
available. To address this need, the
Commission recommends that NMFS
develop and implement research and
monitoring programs needed to manage
high seas fisheries in a manner
consistent with the requirements of the
MMPA. Such approaches likely will
require novel stock assessment
techniques and development of
international partnerships. This task
may be difficult, but also will provide
many ancillary benefits, including the
development of useful tools for
managing transboundary stocks.
Response: NMFS acknowledges this
comment. The development of a
research and monitoring plan to manage
high seas fisheries in a manner
consistent with the requirements of the
MMPA will require novel stock
assessment techniques and the
development, and/or continuation, of
international partnerships. NMFS will
consider such stock assessment
techniques and components of a
research and monitoring program while
continuing to include high seas fisheries
on future LOFs.
Comment 9: The CBD noted that
NMFS proposed to categorize all high
seas fisheries operating in the CCAMLR
region as Category II. However, NMFS
also states that because there are no
currently valid HSFCA permits for
CCAMLR fisheries, none of these
fisheries will actually be listed in the
LOF. Given such fisheries are
authorized under existing CCAMLR
regulations, NMFS should either list
these fisheries on the LOF, or clearly
indicate that NMFS will not issue any
authorizations for these fisheries during
the duration of the time in which the
2009 LOF is operative. If NMFS does
include CCAMLR fisheries on the LOF,
the trawl fishery for krill should be
listed as a Category I based on observer
data from three CCAMLR vessels,
including a U.S. flagged vessel,
indicated that 95 fur seals were caught
in 2004/2005 season and 156 fur seals
were caught in the 2003/2004 season (71
FR 39642; July 13, 2006). Also, the Final
Programmatic EIS for CCAMLR fisheries
noted that a U.S.-flagged krill vessel
killed 138 Antarctic fur seals in five
weeks in 2004. This fishery is clearly
not operating as at ‘‘zero mortality and
serious injury rate’’ and must be listed
as a Category I.
Response: NMFS did propose to add
CCAMLR fisheries to the LOF as
Category II fisheries, but because there
were no current valid HSFCA permits
NMFS stated that, ‘‘CCAMLR fisheries
do not appear in Table 3’’ of the
proposed 2009 LOF (72 FR at 33770).
After considering this comment, NMFS
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views the addition of the CCAMLR
fisheries to the LOF without
representing them in Table 3 as
confusing. Therefore, NMFS has added
the trawl and longline CCAMLR
fisheries (the fisheries in which U.S.
vessels have participated in the recent
past) to Table 3 with a ‘‘0’’ indicating
the number of HSFCA permits for each
fishery. If/when a permit is issued for a
U.S. vessel to operate in a CCAMLR
fishery in the future, the number of
HSFCA permits listed in Table 3 of the
LOF will be updated accordingly.
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. While
NMFS does not have sufficient
information to calculate PBR level for
marine mammal stocks found outside of
the U.S. waters, there is available
information on the abundance of
Antarctic fur seals. 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. Ninety-five fur
seals were reported caught during
fishing operations in 2005/2006, during
which time no U.S. krill trawl vessel
was operating. 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.
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.
Comment 10: The WPFMC agreed
that, from a ‘‘best science’’ perspective,
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it is logical to include high seas fishing
activity by U.S. vessels on the LOF
because the EEZ boundaries are an
artificial construct which have no
meaning biologically or ecologically.
However, it seems excessive to
categorize the majority of high seas
fisheries as Category II in the absence of
reliable data, even if this is done with
the objective of collecting information
through the use of observers. Further, it
is one-sided, since in the absence of
stock assessments, the only information
that would be collected would be
interactions. The numbers of
interactions, even if substantial, will be
meaningless without stock assessments
against which to assess interactions.
Moreover, the HI pelagic longline
vessels already carry observers and
report marine mammal interactions.
Indeed, the observer coverage rates in
HI’s longline fishery are very high
(shallow set-100 percent; deep set-20
percent), and the American Samoa
longline fishery has a 7–8 percent
average coverage rate.
Response: At this time, NMFS has
little information with which to base a
Category I or III categorization for many
high seas fisheries that are not
extensions of fisheries operating within
U.S. waters. It is for this reason that
NMFS categorizes the majority of high
seas fisheries as Category II, the
appropriate category for new fisheries
for which NMFS does not have adequate
information to accurately categorize (as
stated in the final rule implementing
section 118 of the MMPA 60 FR 45086;
August 30, 1995). Because interactions
information alone, without the
associated marine mammal abundance
data, is of limited use in accurately
categorizing a fishery on the LOF,
NMFS would consider all available
abundance data along with interactions
data when determining whether the
reclassification of a given fishery is
warranted. Observer coverage in the HI
longline fisheries is high, and the
American Samoa longline fishery also
has adequate observer coverage. The
addition of the high seas components of
these fisheries will not impact observer
coverage levels or the categorization of
these fisheries at this time.
Comment 11: The 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
U.S. EEZ components. As a general rule,
it may be appropriate to assume that
high seas fisheries using the same gear
and operational strategies will have
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similar interaction rates if marine
mammals occur in equal numbers on
the high seas fishing grounds. However,
where equal numbers are not expected
or where fishing techniques and gear
vary from within-EEZ practices, NMFS
should assume that the high seas fishery
is a Category II until specific
information is available warranting a
different classification. In particular,
recent reports call into question the
assumption that the HI deep-set (tuna
target) fishery interacts with non-coastal
marine mammals to the same extent as
the U.S. waters fishery. First, several
species listed in Table 3, including
sperm whales and several species of
dolphin, have not interacted with the
high seas fishery for at least the past five
years. Second, a 2007 Southwest
Fisheries Science Center Report
indicates that false killer whale density
and abundance are greater on the high
seas south of HI and even greater in the
EEZ around Palmyra Atoll, showing that
they may be sufficiently abundant on
the high seas that already low deep-set
fishery interaction rates may warrant
something less than a Category I
classification for the high seas
component.
Response: As stated in the response to
comment 7 above, although the high
seas components of fisheries that
operate both within U.S. waters and on
the high seas are listed in a separate
table in the LOF, they are not
considered a separate fishery from their
associated component operating in U.S.
waters. Instead, these high seas
fisheries, indicated by a ‘‘*’’ in Table 3,
are the same fisheries that extend into
the high seas, not a separate fishery.
As stated in the preamble of this rule,
a fishery is categorized based on the
stock(s) incidentally seriously injured or
killed at the highest levels relative to the
stock-specific PBR level (i.e., driving
stocks identified by a ‘‘1’’ in Tables 1 or
2). Since the high seas ‘‘Western Pacific
pelagic deep-set longline fishery’’ is an
extension of the ‘‘HI deep-set (tuna
target) fishery’’ operating in U.S. waters,
and not a separate fishery, it is
categorized in the same manner as the
component in U.S. waters (i.e., based on
the serious injury and mortality of false
killer whales (HI stock), the stock
driving the categorization of this
fishery). Also, as noted in the preamble
of this rule, a fishery is 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). If NMFS
received information indicating that the
high seas component of a fishery
operates significantly different than the
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component operating within U.S.
waters, NMFS would consider splitting
that fishery into two fisheries at that
time. Fisheries that operate solely on the
high seas will remain categorized as
Category II until additional information
on marine mammal abundance and/or
fishery interaction data becomes
available to warrant a recategorization.
Also, the calculations of PBR levels
are reported in the SARs. NMFS uses
the PBR levels reported in the SARs in
the fishery categorization process under
the LOF. PBR and interaction levels are
not calculated through the LOF
rulemaking process. Therefore, NMFS
recommends that the commenter
present this comment regarding greater
false killer whale abundance on the high
seas south of HI and around Palmyra
and Johnston Atolls during the
comment period for the SARs.
Comments on Fisheries in the Pacific
Ocean
Comment 12: The HLA requested that
NMFS clarify in the final LOF whether
longline fishing in U.S. waters around
Palmyra Atoll, Johnston Atoll, and other
U.S. Possessions in the Pacific is
considered part of the Western Pacific
Pelagic deep-set fishery or a separate
longline fishery. NMFS should clarify
this 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: 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’’). NMFS
recognizes that the HI stock of false
killer whales is distinct from the stock
of false killer whales that resides around
Palmyra and Johnston Atolls and that a
PBR does not currently exist for these
animals. However, since this is the same
fishery throughout its operating range,
calculating a PBR for the false killer
whales residing around Palmyra and
Johnston Atolls would not impact the
classification of the fishery. As noted in
the preamble of this rule and in the
response to Comment 11 above, a
fishery is 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). Therefore, the fishery would
remain in Category I based on the level
of incidental mortality and serious
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injury exceeding PBR of the HI stock of
false killer whales (i.e., the stock driving
the classification of this fishery).
As stated in the response to Comment
11 above, PBR levels are reported in the
SARs. NMFS uses the PBR levels
reported in the SARs in the fishery
categorization process under the LOF.
PBR and interaction levels are not
calculated through the LOF rulemaking
process. Therefore, NMFS recommends
that the commenter present this
comment that a PBR could be derived
for false killer whales residing around
Palmyra and Johnston Atolls during the
comment period for the next draft SAR.
Comment 13: The CBD stated that
various Hawaiian fisheries are known or
suspected of interacting with Hawaiian
monk seals. Given the critically
endangered status of the monk seal, any
interaction is significant. Yet all
Hawaiian fisheries known or suspected
of interactions and entanglements with
this species are listed as Category III.
These fisheries should all be reclassified
as Category I or II.
Response: The LOF lists the Hawaiian
monk seal on the list of species killed/
injured in the Category III ‘‘HI lobster
trap,’’ ‘‘HI Main Hawaiian Islands,
Northwestern Hawaiian Islands deep
sea bottomfish,’’ and the ‘‘HI tuna
handline’’ fisheries. The information on
Hawaiian monk seal interactions with
these fisheries is outlined below.
(1) ‘‘HI lobster trap fishery’’: There
have not been any reported interactions
since the mid-1980s, when one seal died
in a trap.
(2) ‘‘HI Main Hawaiian Islands,
Northwestern Hawaiian Islands deep
sea bottomfish fishery’’: There were no
interactions during the bottomfish
observer program in 2004–2005, and the
fishery has not been observed since.
While fishing in the Northwestern
Hawaiian Islands will be phased out in
the coming years, in previous years
when more bottomfish boats were
fishing in this area, NMFS received one
self-reported incident (a hooking in
1994) and bottomfish hooks were
observed in two seals at the French
Frigate Shoals (one in 1982 and one in
1993). NMFS also had reports from the
mid 1990’s of seals stealing catch, seals
being fed bait or non-target species by
fishers to discourage seals from taking
catch, and some seals becoming hooked
and cut free.
(3) ‘‘HI Tuna handline fishery’’:
NMFS has never received a report of
interactions between Hawaiian monk
seals and tuna handline gear.
While there have been no observed or
reported interactions between monk
seals and the ‘‘HI lobster trap’’ and ‘‘HI
Main Hawaiian Islands, Northwestern
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Hawaiian Islands deep sea bottomfish’’
fisheries in recent years, NMFS has
retained Hawaiian monk seals as a
species/stock incidentally killed/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. The 2007 SAR states
that without a purpose-designed
observation effort, the true interactions
rate between these fisheries and monk
seals cannot be estimated. Also, the PBR
level for monk seals is currently
‘‘undetermined’’ (Final 2007 SAR). Due
to the fact that the PBR level for monk
seals is undetermined and 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.
NMFS is removing the Hawaiian
monk seal from the list of species/stocks
killed/injured in the ‘‘HI tuna handline
fishery,’’ under which the stock has
been listed since the 1996 LOF. As
stated above, NMFS has never received
a report of interactions between monk
seals and tuna handline gear. In a
thorough review of all of the past and
current Hawaiian monk seal SARs,
NMFS was unable to determine the
reason for this stock’s inclusion on the
list of species/stocks killed/injured in
this fishery. Therefore, NMFS removes
the stock from the list of species/stocks
killed/injured in the ‘‘HI tuna handline
fishery.’’
Comment 14: The CBD stated that
observer data from the American Samoa
longline fishery shows high levels of
take of false killer whales. This fishery
should be listed as Category I rather
than Category III.
Response: NMFS analyzes observer
data and applies observed takes against
calculated PBR levels during the process
of updating and publishing the annual
SARs. The LOF then categorizes
fisheries based on the most recent SARs
(including observer documented
interactions, stranding data, and other
data reported in the SARs). NMFS
recommends that the commenter
present this concern during the public
comment period for the SARs.
Also, NMFS notes that 10 trips, with
410 sets, were observed in this fishery
in 2007 with no observed marine
mammal interactions. NMFS will
reexamine the classification of this
fishery on a future LOF if the analysis
of the 2008 observer data reported in the
SARs indicated that a change in
categorization is warranted.
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Comment 15: The CBD stated that the
proposal to split the HI longline fishery
into separate deep-set and shallow-set
components appears appropriate.
However, they believe that both
components should be classified as
Category I. Observer data from 2008
shows take of false killer whales and
humpback whales from the shallow-set
component of the fishery, indicating
that it too meets the Category I criteria.
Response: As noted in the response to
comment 14, 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 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 peer-review
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 or
humpback whales. NMFS recommends
that the commenter present this concern
during the public comment period for
the next draft SAR. 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 16: The HLA supported
NMFS proposal to separately categorize
the deep-set and shallow-set HI-based
longline fisheries. As explained by
NMFS in the proposed rule, based on
the factors listed in the proposed rule
(and as HLA has previously
commented). Recognizing the welldocumented distinctions between these
fisheries, NMFS brings the LOF into
harmony with the purpose of the annual
LOF, to provide meaningful public
identification of fisheries by the extent
to which they interact with marine
mammals.
Response: NMFS acknowledges the
comment. The split is warranted based
on the several factors listed in the
proposed rule.
Comment 17: The WPFMC and HLA
stated that the shallow-set component of
the HI longline fishery must be based on
the best available population data, and
may be more appropriately classified as
a Category III fishery. NMFS bases the
Category II designation on a single
interaction from 2006 with a humpback
whale, thought to be from the Central
North Pacific stock, which has a PBR
level of 12.9 whales. However, NMFS
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recognized in the draft 2008 SAR (73 FR
40299, July 14, 2008) that this
information is outdated because it is
based on abundance estimates that are
more than eight years old. NMFS has
new, reliable population abundance
data from the Structure of Populations,
Levels of Abundance, and Status of
Humpbacks (SPLASH) project, which
reports a marked increase in North
Pacific humpback whale populations. In
a May 2008 press release, NMFS
announced that the overall population
of humpbacks in the North Pacific
Ocean ‘‘has rebounded to approximately
18,000 to 20,000 animals.’’ The HLA
added that the MMPA requires that
NMFS use the best available scientific
information in determining the
minimum population estimate used and
to classify fisheries on the LOF; which
is true regardless of whether the
information has been published yet.
Further, the WPFMC believes that there
should be a transparent peer reviewed
process for the designation of strategic
stocks.
Response: This comment refers to a
recalculation of the PBR for humpback
whales. Changes to population
estimates, trends, and PBR levels are
reported in the SARs, and NMFS then
categorizes fisheries on the LOF based
on the information presented in the
SARs. The most recent SARs have not
yet incorporated the published data
from the SPLASH project to calculate a
new and/or different PBR for humpback
whales. NMFS recommends that the
commenter present this concern during
the public comment period for the next
draft SAR. NMFS will reexamine the
categorization of this fishery on a future
LOF if future SARs report a change to
the current PBR for this stock of
humpback whales.
The process for designating strategic
stocks is both transparent and peerreviewed. The designation of a strategic
stock is first listed in the proposed
annual SARs, which are both peerreviewed by the Scientific Review
Groups and released for public review
and comment before becoming final.
Comment 18: The Marine Mammal
Commission concurred with NMFS’
proposal to split the HI longline fishery
into the Category II shallow-set and
Category I deep-set fisheries based on
the reasons provided in the proposed
rule. The reclassification of the shallowset fishery is warranted based on the
lack of information regarding
population structure and abundance of
marine mammals that the fishery
interacts with outside the U.S. EEZ.
NMFS based the proposed Category II
classification on observed interactions
rates that do not exceed 50 percent of
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PBR for stocks within the U.S. EEZ.
However, the PBR level is unknown for
stocks that occur outside the U.S. EEZ
and are taken incidentally by this
fishery. As stated in the proposed LOF,
Category II is the appropriate category
for new fisheries for which NMFS does
not have adequate information to
accurately categorize the fishery.
Response: NMFS acknowledges the
comment and will continue to conduct
and support research regarding the
population structure and abundance of
the marine mammals that are interacting
with these fisheries.
Comment 19: The WPFMC continues
to be concerned about the categorization
of all hookings on the exterior of the
head and in the jaw in cetaceans as
being likely to result in mortality. The
Council does not believe that there is
sufficient scientific information to
justify a 100 percent mortality rate for
these injuries, and suggests instead that
some realistic probability scale be
developed similar to that for longline
hooked turtles. For turtles, an external
hooking is given a 5 to 20 percent
probability of causing a post-release
mortality, while internal hookings range
from 10 to 60 percent probability, based
on various factors. It seems inconsistent
of NMFS to develop a precise defensible
system of categorization for turtle
hookings and a blanket 100 percent
mortality rate for cetaceans based on
any hooking to the head and internally.
Clearly, these are very different taxa, but
there must be sufficient scientific
observations available on cetaceans with
which to construct better evaluation
criteria for hookings. As such, the
interactions with cetaceans are always
going to be positively biased, with
excessive mortalities being ascribed to
fisheries.
Response: This comment is related to
the determination of a serious injury,
which NMFS scientists and/or the
authors of the SARs make and report in
the annual SARs. The SARs estimate
annual human-caused mortality and
serious injury caused by interactions
with commercial fisheries and other
human activities. NMFS does not make
serious injury determinations through
the LOF rulemaking process. NMFS
classifies fisheries on the LOF based on
the level of serious injury (and
mortality) presented in the SARs. NMFS
recommends that WPFMC submit this
comment during the public comment
period on the next draft SAR.
Comment 20: The WPFMC stated that
the proposed list of marine mammals
with which HI’s deep set longline
fishery interacts includes the Bryde’s
whale, pantropical spotted dolphin, and
sperm whale. A search of the observer
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data from 2003–2007 shows no records
of these three species interacting with
the fishery. If they are to be listed in
Table 1, there should be a footnote to
the effect that these cetaceans were not
seen within the past five years, which
the Council understands is the criteria
used when evaluating the fisheries for
the LOF.
Response: There are no records of
recent serious injuries or mortalities of
Bryde’s whales, sperm whales, or
pantropical spotted dolphins in the ‘‘HI
deep-set (tuna target) longline/set line
fishery.’’ The recorded interactions with
these species were in the shallow-set
component of the HI longline fishery.
These species were inadvertently
retained under the list of species/stocks
killed/injured in this fishery when
NMFS split the HI longline fishery into
the separate deep-set and shallow-set
components on the proposed 2009 LOF
(73 FR 33760, June 13, 2008).
NMFS has corrected this error and
removed Byrde’s whale, sperm whale,
and pantropical spotted dolphin from
the list of species/stocks killed/injured
in the ‘‘HI deep-set (tuna target)
longline/set line fishery’’ in the final
2009 LOF, and included the species on
the list for the shallow-set longline
fishery.
Comment 21: The WPFMC believes
that the evidence for categorizing the HI
deep-set tuna longline fishery as a
Category I is inadequate. The Council
does not dispute the existence of an
isolated, small false killer whale stock
around Hawaii. However, the current
longline exclusion zone around Hawaii
extends from 50–75 nmi and creates a
separation between these individuals
and the fishery. Available genetic data
suggests that the deep-set fishery
interacts primarily with a larger Eastern
Pacific false killer whale population.
Response: Based on the PBR and the
average annual serious injury and
mortality rate reported in the recent
SARs, the ‘‘HI deep-set (tuna target)
longline/set line fishery’’ qualifies as a
Category I fishery on the LOF (serious
injury and mortality exceeds 50 percent
of PBR for the HI stock of false killer
whales). NMFS calculates PBR levels
and determine the status of marine
mammal stocks during the annual
process of developing a SAR; then
NMFS classifies fisheries on the LOF
based on data reported in the annual
SARs. NMFS recommends the
commenter submit this comment, and
any other comments regarding the
stock’s PBR or strategic status, during
the public comment period for the next
draft SAR.
Comment 22: The CBD stated that the
‘‘Gulf of AK sablefish longline fishery’’
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is listed as a Category III. Due to
frequent interactions with sperm and
killer whales, this fishery should be
listed as a Category I or II.
Response: Fisheries are categorized in
the LOF based on the level of serious
injuries and mortalities relative to the
PBR levels for specific species, not the
frequency of ‘‘interactions.’’ At the time
the proposed 2009 LOF was developed,
the best available information was that
no marine mammals were seriously
injured or killed incidental to this
fishery between 2001 and 2005, the
most current data available in the SARs,
so the fishery is appropriately retained
in Category III. New information on
serious injuries and mortalities has been
included in the recent draft SARs which
indicates that 3 serious injuries of sperm
whales were observed in 2006, which
would extrapolate to an estimated 10
serious injuries or mortalities of sperm
whales incidental to this fishery, or 2
sperm whales per year for the 5-year
period from 2002–2006. This
information is still under review and
will be considered when the next LOF
(the proposed 2010 LOF) is developed.
Comment 23: The CBD noted
inconsistencies in the classification of
AK purse seine fisheries. Three salmon
purse seine fisheries are listed as
Category II, yet the description of the
Category III ‘‘AK salmon purse seine
(except Southeast AK, which is in
Category II) fishery’’ only excludes one
of these Category II fisheries from its
description. This should be corrected,
and the estimated number of vessels
altered as necessary for consistency.
Response: The Category III fishery
identified as ‘‘AK salmon purse seine
(except Southeast AK, which is in
Category II) fishery’’ was included in the
LOF when it was created under the
section 118 of the MMPA (i.e., under the
1994 MMPA Amendments). The ‘‘AK
salmon purse seine (except Southeast
AK, which is in Category II) fishery’’
was created to include all of the
numerous purse seine fisheries around
the state of AK, other than the Category
II ‘‘Southeast AK purse seine fishery.’’
Information on marine mammal
interactions with any of these purse
seine fisheries included in the ‘‘AK
salmon purse seine (except Southeast
AK, which is in Category II) fishery,’’
particularly serious injury and
mortality, was not available to NMFS
when the LOF was created at that time.
Since 1994, information on serious
injury and mortality to humpback
whales in the Cook Inlet and Kodiak
purse seine fisheries has been obtained.
Therefore, NMFS identified the ‘‘Cook
Inlet salmon purse seine fishery’’ and
the ‘‘Kodiak salmon purse seine fishery’’
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separately on the 2007 LOF (72 FR
14466, March 28, 2007) as Category II
fisheries based on the results from the
analysis of the respective serious injury
and mortality levels of humpback
whales in these fisheries. To clarify that
the Category III AK salmon purse seine
fishery includes all AK salmon purse
seine fisheries other than those listed as
Category II on the LOF, NMFS has
renamed the Category III ‘‘AK salmon
purse seine (except Southeast AK,
which is in Category II) fishery’’ as the
‘‘AK salmon purse seine (excluding
salmon purse seine fisheries listed as
Category II).’’ If additional information
on marine mammal serious injury and
mortality incidental to other discrete AK
salmon purse seine fisheries becomes
available in the future, and meets the
criteria for elevation to Category II,
those individual fisheries will be
removed from the broader ‘‘AK salmon
purse seine (excluding salmon purse
seine fisheries listed as Category II)’’
and elevated to Category II under
appropriate, specific fishery-identifying
nomenclature.
Comment 24: The CBD noted that
high levels of entanglement-related
scarring have been documented for
humpback whales in AK. While some
gillnet and purse seine fisheries are
listed as Category II due to humpback
interactions, the ‘‘AK Bering Sea
sablefish pot fishery’’ is the only pot,
ring net or trap fishery so categorized.
All other AK pot fisheries should also
be classified as Category II rather than
Category III.
Response: NMFS uses very careful
criteria in assigning marine mammal
serious injuries and mortalities to
specific fisheries for the purpose of
categorizing them in the LOF. In the
Alaska Region, these criteria include,
but are not limited to: Clear
identification of attached gear,
eyewitness accounts, or other credible
information. When those criteria have
been met, the individual serious injury
or mortality is included in the data set
used in the standard annual analysis
conducted to assign fisheries in the
LOF.
Current information on humpback
scarring in Alaska is not detailed
enough to allow NMFS to be able to
identify and link specific scars or
scarred animals to an individual fishery
or even a specific fishing gear type,
except under the rarest of
circumstances. Further, humpback
whales travel long distances and obtain
scars from gear originally set great
distances from the geographic location
where the scar was noted. Finally, the
analysis conducted for the annual LOF
uses a rolling five-year average. This
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allows for changes to fishing methods or
natural fluctuations in animal
distribution or behavior. Scars persist
for varying lengths of time and scarring
information would need to be much
better understood than it is currently to
be able to be used effectively in the
annual LOF analysis. Information
regarding serious injury or mortality
incidental to the ‘‘Gulf of Alaska
sablefish pot fishery’’ clearly indicates
the take of the humpback whale was
associated with that fishery, leading to
the Category II classification for that
fishery.
Without more detailed evidence,
NMFS cannot assume that all humpback
whale scars result from interactions
with specific commercial fisheries.
Further, NMFS cannot make
assumptions at this time as to what
proportion of entanglements that result
in scarring lead to serious injury or
mortality, the driving criteria for
classifying fisheries on the LOF.
Comment 25: If the ‘‘OR Dungeness
crab pot fishery’’ is elevated to a
Category II on the final 2009 LOF, the
ODFW requested NMFS advice and
assistance to fulfill, in the most efficient
manner possible, those requirements
under the ESA that would apply to the
fishery’s interactions with listed
humpback whales.
Response: This final rule classifies the
‘‘OR Dungeness crab pot fishery’’ as a
Category II fishery. NMFS will work
with the State of Oregon relative to
changes on the LOF that affect statemanaged fisheries.
Comment 26: If the ‘‘OR Dungeness
crab pot fishery’’ is elevated to a
Category II on the final 2009 LOF,
fishing vessel owners will be required to
register with NMFS and obtain a marine
mammal authorization certificate by
January 1, 2009. This would occur
during the height of effort in this fishery
and most participants will be actively
fishing when the new rule would take
effect. The ODFW requests that NMFS
strive to minimize any disruptions to
fishing activities in order to implement
any new requirements. ODFW and
NMFS regional staff have discussed
potential implementation issues,
particularly for the first year, and ODFW
staff remains available to work with
NMFS on these issues.
Response: NMFS will work with the
state fishery managers to integrate fisher
registration for the MMAP program with
state licensing processes, to the extent
possible. NMFS will request fisher
registration information from the state
licensing office in order to issue
authorization certificates to fishers in a
timely and cost efficient manner.
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Comment 27: ODFW supports the
addition of a separate Category II ‘‘OR
Dungeness crab pot fishery.’’ ODFW is
concerned about fishery interactions
with marine mammals and has
implemented several on-going
management measures for the OR
Dungeness crab pot fishery that will
reduce the risk of interactions in the
future. Fishing effort has been reduced
from an estimated high of 200,000 pots
in 2006, when the observed humpback
whale entanglement occurred, to a
maximum of 150,000 pots per season.
Logbook information including date,
location, and amount of gear fished is
now required for all crab vessels. This
information will be useful in the future
to assess the potential for interactions
and ways to reduce interactions. ODFW
has also implemented management
measures that restrict untended gear to
no more than 14 days and several
temporary rules to facilitate fishers
opportunistically retrieving lost or
derelict gear. ODFW has also partnered
with others to charter vessels
specifically to retrieve derelict and lost
crab pots. ODFW anticipates working
with NMFS to smoothly and efficiently
implement the new requirements.
Response: NMFS acknowledges the
State of Oregon’s positive steps in
reducing the incidental take of marine
mammals in the ‘‘OR Dungeness crab
pot fishery.’’
Comment 28: ODFW strongly
supports the proposal to split the
current ‘‘WA/OR/CA crab pot fishery’’
into three fisheries, one for each state.
Each state has different management
and permitting frameworks for
Dungeness crab trap/pot fishing, and
different amounts of gear in state waters.
Also, known interactions with marine
mammals differ between states,
probably mainly due to differences in
the timing and amount of gear fished,
and differences in timing and
distribution of marine mammals along
the coast. The potential risk of
humpback whale entanglements in
Dungeness crab pot gear appears to
progressively decrease from CA to WA,
based on the humpback whale
movement patterns, fishing intensity
patterns, and observed reports of
humpback whale entanglements. This
differential risk from south to north
justifies the proposed separation of the
west coast fishery into three fisheries.
Also, while there is a Tri-State
agreement that addresses some aspects
of the West Coast Dungeness crab
fishery, the individual states have the
primary role in managing their
respective fishery and the management
authorities and actions differ among
states. The different authorities and the
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lack of a true regional management
system provide added justification to
separate the fishery among states.
Response: NMFS has classified the
three fisheries by state in this final rule.
The presence of humpback whales along
the west coast varies seasonally and the
relationship between the presence of
whales and the peak periods of fishing
effort likely influences the potential for
entanglement. The management of the
fisheries by the individual states affords
added flexibility to respond to regional
differences more quickly to reduce the
risk of entanglement for the whales.
Comment 29: The CBD stated that,
while the proposed 2009 LOF includes
several West Coast pot and trap fisheries
as Category II due to interactions with
humpback whales, the proposed LOF
improperly excluded many similar
fisheries. CBD stated that NMFS
acknowledges humpback whale
entanglements are likely significantly
underreported, yet only includes those
fisheries as Category II if the fishery is
known to interact with humpbacks or if
there is a time/space overlap with a
reported entanglement. CBD believes
this method results in several fisheries
being classified as Category III when
Category II is the more appropriate
classification. 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: As described in the final
2008 LOF (72 FR 66048, 66066,
November 27, 2008), NMFS researched
the commercial pot and trap fisheries to
better understand which of those
fisheries may interact with humpback
whales along the coast of California.
NMFS extended its analysis for the 2009
LOF to include pot and trap fisheries
along the coasts of Washington and
Oregon and worked closely with
fisheries staff from the three states.
NMFS developed criteria described in
the proposed 2009 LOF to evaluate the
pot and trap fisheries along California,
Oregon, and Washington and determine
which are most likely to interact with
humpback whales. The first criterion
was whether there is direct evidence of
entanglements with a specific fishery
(e.g., the identification of spot prawn
gear on a humpback whale entangled in
September 2005). In the absence of
direct evidence on interactions, the
second criterion was used, (i.e., the
fishery occurs in an area and time where
humpback whale entanglements have
been observed and reported to NMFS).
This criterion was used to refine the
analysis with the limited information
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available. NMFS acknowledges the
uncertainties associated with this
analysis. However, NMFS believes that
the criteria described in the proposed
2009 LOF and used to assess the
fisheries is the most reasonable means at
this time of using the available
information and reclassifying certain
pot and trap fisheries.
The commenter suggests that all west
coast pot and trap fisheries in the range
of humpback whales be listed as
Category II, until observers can show
that the fisheries do not pose a threat to
marine mammals. However, observers
in pot and trap fisheries have very
limited ability to detect these types of
interactions. In most instances, trap/pot
gear is left to soak for some time and is
not actively tended by the fishing vessel
for the majority of the soak period.
Interactions (entanglements) between
large whales and trap/pot gear are
therefore unlikely to be observed from
the fishing vessel except in the rare
instance when the vessel is present at
the time the entanglement occurs.
Therefore, alternative monitoring
methods are needed for trap/pot
fisheries. NMFS has begun work (and
will cooperate with other agencies, the
scientific and fishing communities, and
the general public) to find ways to
monitor pot/trap fisheries and gather
additional data to better understand the
nature of the interactions between these
fisheries and marine mammals. As
noted in the 2009 LOF proposed rule,
when and if additional information
becomes available, NMFS would
consider reclassifying pot/trap fisheries.
Comment 30: The Marine Mammal
Commission recommended that NMFS
reclassify all currently recognized west
coast pot and trap fisheries as Category
II until additional information is
available to categorize a given fishery as
a Category I or III. Although the
Commission appreciates NMFS’ efforts
to evaluate information on observed
humpback whale entanglements and
attribute those entanglements to specific
trap/pot fisheries, the Commission
believes that the analysis and resulting
proposed reclassifications do not
account appropriately for the substantial
uncertainty in the number and location
of entanglements. The Commission
acknowledged that NMFS has shown
that humpback whales do become
entangled in trap/pot gear, and that
there is no evidence to suggest that
whales are more or less likely to become
entangled in gear from any specific trap/
pot fishery. NMFS noted in the
proposed 2009 LOF that ‘‘other pot and
trap fisheries may overlap in space and
time with humpback whales feeding or
migrating along the West coast, but in
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the absence of evidence of interactions,
NMFS cannot justify placing these
fisheries in Category II at this time.’’ The
Commission believes that this statement
misplaces the burden of proof and
removes the incentive for collecting
important information on entanglement
rates. The vast majority (90 to 97
percent) of humpback whale
entanglements are not observed
(Robbins and Matilla, 2001, 2004) and,
by implication, at least some
entanglements of endangered baleen
whales are not observed and reported.
Given that the majority of
entanglements are not observed, it is
reasonable to classify all west coast
trap/pot fisheries as Category II based on
their similarity to those trap/pot
fisheries that are known to have
incidentally entangled whales. Also,
NMFS acknowledges in the proposed
rule that ‘‘Category II is also the
appropriate category for fisheries for
which reliable information on the
frequency of marine mammal serious
injury or mortalities is lacking.’’
Response: Please see the response to
Comment 29 above. NMFS
acknowledges that there are likely
interactions with marine mammals that
are not observed or reported. However,
NMFS reviewed all of the records of
entanglements, the distribution of
humpback whales and the spatial and
temporal characteristics of the pot and
trap fisheries on the U.S. west coast and
developed criteria to reclassify fisheries
based upon the best available
information. NMFS is also working on
ways to increase the amount of
information available on interactions
between marine mammals and pot and
trap fisheries on the U.S. west coast.
The commenter suggests that other
species of endangered baleen whales
may be entangled in pot and trap gear,
but not observed. At this time, NMFS is
focused on interactions with humpback
whales and gray whales since these are
the only species observed entangled in
pot and trap gear on the U.S. west coast.
Also, other pot and trap fisheries in the
Pacific (including Hawaii and Alaska
fisheries) have not been observed to
interact with baleen whale species other
than humpback whales.
NMFS notes that there was a
typographical error in the proposed
2009 LOF on page 33772. The text
should have stated that Category II is
appropriate for new fisheries for which
NMFS does not have adequate
information. This is consistent with the
text throughout the proposed rule
related to the addition of high seas
fisheries, and as stated in the final rule
implementing the section 118
regulations (60 FR 45086, August 30,
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1995, at 45090) and the final 2006 LOF
(71 FR 48802, August 22, 2006;
Comment/Response 4). As noted on
page 33763, 33768, 33769, and 33770 of
the proposed 2009 LOF, ‘‘Category II is
the appropriate category for new
fisheries for which NMFS does not have
adequate information to accurately
categorize.’’ Fisheries previously
included on the LOF as a Category I or
III are reclassified as Category II after
evaluating the information in the SARs,
the type of gear being used, stranding
records, and the distribution of marine
mammals in the area. All west coast pot
and trap fisheries have been previously
included in the LOF as Category III
fisheries; therefore, NMFS conducted
this type of analysis on the west coast
pot and trap fisheries and detailed the
process in the proposed rule. As stated
in the proposed 2009 LOF, NMFS will
continue to review information related
to humpback and gray whale
entanglement events in pot and trap
gear and consider reclassifying other
west coast pot and trap fisheries if
additional information becomes
available.
Comment 31: The CA Wetfish
Producers Association requested NMFS
remove short-finned pilot whales from
the list of species killed/injured in the
Category II ‘‘CA squid purse seine
fishery’’ because the most recent
scientific information available does not
justify including this species for
interactions with this fishery. The
fishery is being monitored and was
observed during the expansion period.
The 2007 SAR indicates that 193 sets
were observed from 2004–2006. The
commenter examined the NMFS SWR
CA Coastal Pelagic Purse Seine Observer
Program database, which indicated that
95 sets were observed through March
2007, with an additional 80 sets
observed from July 2007–December
2007. Based on these data, there is not
evidence that short-finned pilot whales
were taken in this fishery during this
recent span of years.
Response: NMFS received a similar
comment on the proposed 2008 LOF (72
FR 66048, November 27, 2008;
comment/response 18). As noted in the
response to comment 18 in the 2008
LOF, there have been no observed takes
of short-finned pilot whales in this
fishery during the three years it was
monitored (2004–2006); however,
annual observer coverage was very low
(the estimated coverage was only 1.1
percent in 2005, and less than 2 percent
in the other years). The low level of
observer coverage over three years may
not reliably indicate the frequency of
incidental mortality or serious injury of
marine mammals in this fishery. In
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considering whether a fishery should be
listed as Category II, NMFS must
evaluate a variety of factors including
the fishing technique used, the seasons
and areas fished, stranding reports, and
the distribution of marine mammals in
the area. NMFS feels that based upon
the most recently available information,
including stranding reports over the
past few years, that a thorough
evaluation of the ‘‘CA squid purse seine
fishery,’’ as well as the ‘‘CA anchovy,
mackerel, sardine purse seine fishery’’
and the ‘‘CA tuna purse seine fishery,’’
is warranted. NMFS will thoroughly
evaluate the available information on
the three above referenced California
purse seine fisheries and will include
the results in the proposed 2010 LOF.
At that time, NMFS will determine
whether reclassifying some of the CA
purse seine fisheries, including the ‘‘CA
squid purse seine fishery,’’ is
appropriate.
Comment 32: The CA Wetfish
Producers Association requested NMFS
remove common dolphin, stock
unknown, from the list of species killed/
injured in the Category II ‘‘CA squid
purse seine fishery’’ based on the most
recent scientific information available.
The NMFS SWR CA Coastal Pelagic
Purse Seine Observer Program data
contain one single observed interaction
off Santa Barbara on January 3, 2005,
resulting in one dead unidentified
common dolphin. The most recent and
relevant scientific information indicates
there have been zero interactions with
either long- or short-beaked common
dolphins. There were more than 193
trips observed by federal observed
during 2004–2006, and 80 sets observed
in mid- to late-2007, with zero
interactions (except for the single 2005
incident). Clearly, this fishery
represents no current threat to either
stock of common dolphins.
Response: A similar comment was
made on the 2008 LOF. As described in
NMFS’ response to this comment in the
final 2008 LOF (72 FR 66048, November
27, 2007; Comment/Response 19), there
is insufficient information available to
identify the species of common dolphin
observed taken in the squid purse seine
fishery. 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. Further, the draft 2008
SARs includes an account in 2006 of
eight unidentified dolphins entangled in
a squid purse seine net. Seven of the
animals were released unharmed, and
one was seriously injured. The area in
which these interactions occurred is an
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area where long-beaked common
dolphins are known to occur. Given the
paucity of information on the
interaction, NMFS cannot eliminate the
possibility that a long-beaked common
dolphin was seriously injured during
this event.
To make the list of marine mammal
species and stocks incidentally killed/
injured in the ‘‘CA squid purse seine
fishery’’ more clear, NMFS is changing
the stock from ‘‘common dolphin,
unknown’’ to ‘‘short-beaked common
dolphin, CA/OR/WA’’ and ‘‘long-beaked
common dolphin, CA’’ to account for
the uncertainty of the species observed
seriously injured or killed in this
fishery. This is consistent with how
NMFS lists marine mammal stocks on
the LOF that are difficult to distinguish
from one another in the field and/or for
which additional genetic data is not
available for a given interaction (i.e.,
resident and transient killer whales in
Alaska fisheries, and long-finned and
short-finned pilot whales in Atlantic
fisheries).
Comment 33: The CA Wetfish
Producers Association requested NMFS
recategorize the Category II ‘‘CA squid
purse seine fishery’’ to a Category III
based on existing observer data from
2004–2007, the paucity of marine
mammal interactions with this fishery,
and because the number of participants
has reduced from 71 to 64 active
vessels. Recategorization of this fishery
to a Category III is justifiable and
consistent with the best scientific
information available. Also, a
recategorization would provide the
industry with validation that NMFS
actually utilizes observer data to adjust
the LOF annually to reflect current
circumstances in commercial fisheries.
Furthermore, the commenter requested
the LOF be updated to reflect the
reduction in the number of participants
to 64, consistent with CA Department of
Fish and Game records indication that
64 purse seine vessels landed squid in
2007.
Response: NMFS recognizes that the
squid purse seine fishery warrants
further evaluation based upon all
available information, including
observer records. Please see response to
Comment 31 above for more
information. NMFS appreciates the
information on the number of active
vessels in this fishery and has updated
the number of active vessels to 64 in the
final 2009 LOF.
Comment 34: The Marine Mammal
Commission concurred with NMFS’
proposal to reclassify the ‘‘CA halibut/
white seabass set net fishery’’ from
Category I to II based on the information
provided in the proposed rule.
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Response: NMFS acknowledges and
appreciates the comment.
Comment 35: The CDFG supported
reclassifying the ‘‘CA Dungeness crab
pot fishery’’ to a Category II fishery
given the relatively high likelihood of
humpback whale interactions. However,
as with the sablefish pot fishery, CDFG
believes that this fishery should have a
coastwide designation as the ‘‘(WA/OR/
CA) Dungeness crab pot fishery’’
because it is difficult to determine the
precise location of the original
entanglement or other incident, and
humpback whale migratory patterns are
such that an entangled whale might be
encountered and reported far from the
site of the incident. Also, there is no
evidence that primary fishing areas in
California, which are north of Point
Arena, differ from Oregon and coastal
Washington with respect to the
likelihood of these interactions.
Response: As explained in the
proposed 2009 LOF, NMFS believes that
because of the differences in
management of the Dungeness crab pot
fishery by each state, it is appropriate to
split the fishery into three separate
fisheries by state. Also, unlike the
sablefish fishery, fishermen targeting
Dungeness crab are limited to fishing
the waters off the state for which they
hold a permit. For example, a fisherman
with a Washington permit may only set
Dungeness crab pot gear off Washington,
while a fisherman with a California
permit may only set gear off California.
The sablefish fishery permit does not
have this same restriction. A fisherman
possessing a sablefish fishery permit
(open access) may set gear in the waters
off any of the three states.
As noted in the proposed 2009 LOF,
NMFS acknowledged some level of
uncertainty associated with the
assumption that the area in which an
entangled animal is observed is the area
where the entanglement occurred.
However, this assumption was
considered necessary in order to utilize
the available information and is
supported by the available data on
entanglements. For example, spot prawn
gear was identified on a humpback
during a time and in an area during high
levels of effort in the spot prawn trap
fishery (73 FR 33799, June 13, 2008).
NMFS believes that effort in the
fisheries is likely to affect the likelihood
of an interaction with a humpback
whale, since each fishery occurs at
slightly different times of the year off
the coasts of California, Oregon, and
Washington. For example, the effort in
the southern half of California in the
‘‘CA Dungeness crab pot fishery’’ may
begin in mid-November, overlapping
with the time that humpback whales are
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likely to be migrating through the
waters. However, in Oregon and
Washington the peak of the fishery is
December through February, at which
time most humpback whales have
migrated out of the area on their way to
winter breeding areas off Mexico. As
described in NMFS’ pot and trap fishery
characterization referenced in the
proposed 2009 LOF, Dungeness crab
pots may be fished through the spring,
in waters off each of the three states’
coasts, thus affecting the likelihood of
interactions with humpback whales
(i.e., Dungeness crab pot gear fished off
Oregon in May, is believed to be
responsible for the entanglement of a
humpback whale that stranded dead on
the Oregon coast). However, given the
typical fishery patterns and the
migratory behavior of humpbacks in
California waters, it is likely that gear
off California is more likely to entangle
humpbacks during their migration.
Comment 36: The CDFG supported
the evaluation of the ‘‘WA/OR/CA
sablefish pot fishery’’ to a Category II
fishery and supported the continuation
of the tri-state, coastwide designation of
the sablefish pot fishery. The limited
information available regarding
humpback whale interactions makes it
difficult to determine the precise
location of the original entanglement or
other incident, and humpback whale
migratory patterns are such that an
entangled whale might be encountered
and reported far from the site of the
incident.
Response: As described in the
proposed 2009 LOF and in the response
to comment 35 above, the existing
sablefish fishery regulations allow
fishers from one state to fish sablefish
pot gear off another state. Therefore, it
is most appropriate to list the sablefish
pot fishery on the LOF as one fishery
that includes effort in waters in all three
states.
Comment 37: The CDFG supported
the removal of Eastern North Pacific
humpback whales and CA sea otters
from the list of species and stocks
incidentally killed/injured in the
Category III ‘‘CA spiny lobster,
coonstripe shrimp, finfish, rock crab,
tanner crab pot or trap fishery,’’ based
on the 2008 analysis of humpback and
gray whale interactions, and the lack of
any known interactions with sea otters
since 1987.
Response: NMFS acknowledges this
comment.
Comment 38: The CDFG proposed
that NMFS remove finfish from the
Category III ‘‘CA spiny lobster,
coonstripe shrimp, finfish, rock crab,
tanner crab pot or trap fishery,’’ and that
the fishery be renamed to reflect this
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change, because the finfish trap fishery
is a separate and distinct fishery from
the various crustacean fisheries.
Additionally, finfish are included in the
Category III ‘‘CA finfish and shellfish
live trap/hook-and-line fishery.’’
Furthermore, finfish cannot be taken in
the lobster and rock crab trap fisheries
(Fish and Game Code Section 8250.5
and Title 14, CCR, Section 125.1).
However, if the reference to finfish in
this fishery is meant for hagfish, then it
should be specified as such. Finally, the
gray whale interaction listed in the LOF
table comes from an observation of a
gray whale with a lobster trap buoy line
attached, and not from a finfish trap.
Response: NMFS appreciates CDFG’s
clarification on these fisheries and has
removed finfish from the existing
fishery description and name. The name
of the fishery in the final 2009 LOF has
been renamed to the ‘‘CA spiny lobster,
coonstripe shrimp, rock crab, tanner
crab pot or trap fishery.’’ Finfish in this
fishery did not refer to hagfish, as the
hagfish pot/trap fishery is currently
listed separately on the LOF as the
Category III ‘‘OR/CA hagfish fishery.’’
NMFS acknowledges and appreciates
the clarification on the gray whale take
in the lobster trap fishery and will
continue to list gray whale as one of the
species incidentally killed or injured in
this fishery, as it is listed in the
proposed 2009 LOF.
Comment 39: The CDFG supported
the proposal to separate the spot prawn
trap fishery from the other crustacean
trap/pot fisheries and place it in
Category II. CDFG understands that the
change is being proposed so that the
other fisheries can remain in Category
III.
Response: NMFS acknowledges the
comment.
Comment 40: The CDFG proposed
removing shellfish from the ‘‘CA finfish
and shellfish live trap/hook-and-line
fishery’’ and renaming it the ‘‘CA
nearshore finfish live trap/hook-andline fishery,’’ maintaining the Category
III status because there are no
documented instances of marine
mammal interactions. Shellfish are
already covered in the proposed ‘‘CA
spiny lobster, coonstripe shrimp,
finfish, rock crab, tanner crab pot or trap
fishery.’’ Also, while these shellfish
species are taken live they are not taken
with hook-and-line gear. The majority of
nearshore finfish are landed in the live
condition. Nearshore finfish traps are
set in very shallow waters (two to eight
fathoms) in kelp beds and over rock
habitat off southern and central CA.
Traps are usually set and pulled
multiple times a day.
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Response: The proposal to rename
this fishery is appropriate for the
reasons stated by the commenter. NMFS
has renamed the Category III ‘‘CA finfish
and shellfish live trap/hook-and-line
fishery’’ as the ‘‘CA nearshore finfish
live trap/hook-and-line fishery’’ in the
final 2009 LOF.
Comments on Fisheries in the Atlantic
Ocean, Gulf of Mexico, and Caribbean
Comment 41: The MAFMC supported
the proposal to eliminate Loligo, Illex,
and butterfish from the list of species
targeted by the Category II ‘‘MidAtlantic Mid-Water trawl fishery.’’ In
addition, the MAFMC supports the
addition of these three species to the list
of species targeted by the Category II
‘‘Mid-Atlantic bottom trawl fishery.’’
The MAFMC notes that it was not
possible to determine what other
species were added to the species list
for this fishery given the information
provided in the proposed rule.
Response: After removing Illex squid,
Loligo squid, and butterfish from the
species targeted by the ‘‘Mid-Atlantic
mid-water trawl fishery,’’ NMFS added
‘‘chub mackerel and miscellaneous
other pelagic species’’ (73 FR 33775,
June 13, 2008) to the description of
species targeted by the Mid-Atlantic
mid-water trawl fishery based on
information provided in Appendix III of
the 2007 final SAR.
Comment 42: The MAFMC, the
NCDMF, and the Garden State Seafood
Association (reiterating a request made
as a comment on the 2007 LOF and in
a letter sent directly to NMFS in
November 2006) each requested that
NMFS conduct a Tier Analysis of the
bluefish gillnet and croaker gillnet
fisheries, currently included under the
Category I ‘‘Mid-Atlantic gillnet
fishery.’’ The commenters requested the
Tier Analysis to determine whether the
data support downgrading these
fisheries from Category I to Category II
or III (thereby also separating the
bluefish and croaker components from
the ‘‘Mid-Atlantic gillnet fishery’’).
Available observer data indicate that
from 2000–2005 there were 109 Atlantic
croaker gillnet trips and 70 bluefish
gillnet trips observed with no
documented marine mammal
interactions. Should these fisheries be
downgraded to a Category II or III, the
NCDMF recommends that observer
coverage be increased in other Category
I Mid-Atlantic gillnet fisheries.
Response: In 1998, NMFS determined
regulatory measures should be based on
the characteristics of the gillnet fisheries
that relate to marine mammal bycatch,
rather than to base the regulations on
target fisheries. NMFS determined that
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the nature of the gear and how the gear
is deployed determines whether marine
mammals become entangled.
Additionally, because the intended
target species is not always the actual
species landed, regulations based on
sub-fisheries would become very
difficult to enforce (See Harbor Porpoise
Take Reduction Plan Final
Environmental Assessment and Final
Regulatory Flexibility Analysis, NMFS,
1998). Since the characteristics of gillnet
gear targeting bluefish and croaker
cannot be differentiated from the ‘‘MidAtlantic gillnet’’ fishery gear definition,
NMFS has determined that the bluefish
and croaker fisheries cannot be
separated out for a separate tier analysis.
Therefore, NMFS retains the current
inclusion of the bluefish and croaker
gillnet fisheries in the ‘‘Mid-Atlantic
gillnet fishery’’ (Category I) and does not
find the suggested sub-division to be
warranted.
Comment 43: NMFS proposes to add
trotline gear as a new Category III
fishery. The proposed rule describes
trotline gear as a series of baited hooks
attached to a horizontal line targeting
blue crab, catfish, and other finfish
species throughout the coastal Atlantic
and Gulf of Mexico. The MAFMC states
that in the Mid-Atlantic region,
primarily in the Chesapeake Bay,
trotlines are fished for blue crab without
the use of hooks and asks if this fishery
should be included under the newly
proposed trotline category. If so, then
the LOF should recognize a separate
category for trotlines that do not use
hooks, or consider excluding this
fishery from the list because no hooks
are deployed in this fishery. Similarly,
the NCDMF did not support the
inclusion of the blue crab trotline
fishery in the proposed Category III
‘‘U.S. Atlantic Ocean, Gulf of Mexico
trotline fishery,’’ and recommended that
blue crab trotlines not be listed under
this fishery. Blue crab trotlines used in
North Carolina do not use hooks for
retention of bait. Instead, the bait is tied
to the trotline using small diameter
twine.
Response: At this time, the current
definition only includes trotlines with
hooks. However, in the future, NMFS
intends to evaluate all Category III
‘‘longline/hook and line fisheries’’
definitions for clarification purposes.
NMFS will investigate if the expansion
of the ‘‘U.S. Atlantic, Gulf of Mexico
trotline fishery’’ warrants including gear
without hooks or if non-hook trotline
gear is more specific, therefore requiring
a unique fishery definition.
Comment 44: The MAFMC supported
the addition of the North Carolina
striped bass beach haul seine fishery to
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the list of fisheries included in the MidAtlantic haul/beach seine fishery.
Response: NMFS has added the North
Carolina striped bass beach haul seine
fishery to the list of fisheries included
in the Category II ‘‘Mid-Atlantic haul/
beach seine fishery’’ based on current
gear practices and thus enabling more
effective conservation measures and
management.
Comment 45: The NCDMF supported
the proposed revisions to the
description of the Category II ‘‘MidAtlantic haul/beach seine fishery.’’ The
revised description will complement
NCDMF Proclamation FF–51–2008,
effective December 2008, which requires
seines used in the Atlantic Ocean
striped bass beach seine fishery to be
constructed of multifilament or multifiber webbing. NCDMF intends to
maintain the multifilament or multifiber webbing requirements throughout
the Atlantic Ocean beach seine season.
Response: NMFS will continue to
work collaboratively with NCDMF to
ensure descriptions and classifications
in the list of fisheries of beach-based
fisheries in North Carolina complement
NCDMF’s efforts.
Comment 46: The CBD and the
Marine Mammal Commission reiterated
previous years’ comments expressing
concerns about marine mammal
interactions with Gulf of Mexico
fisheries. The Commission
recommended that NMFS expedite its
investigation of bottlenose dolphin
stock structure, and both CBD and the
Commission recommended NMFS
reevaluate the classification of Gulf of
Mexico fisheries. The CBD believes that
the ‘‘Gulf of Mexico blue crab trap/pot
fishery’’ should be classified as at least
a Category II, and the ‘‘Gulf of Mexico
menhaden purse seine’’ and the ‘‘Gulf of
Mexico gillnet’’ fisheries should be
classified as Category I based on known
or likely impacts to bottlenose dolphin
stocks.
Response: NMFS does not believe
elevating the ‘‘Gulf of Mexico blue crab
trap/pot fishery,’’ ‘‘Gulf of Mexico
menhaden purse seine fishery,’’ or ‘‘Gulf
of Mexico gillnet fishery’’ is supported
by available information. There is no
observer program for these fisheries.
NMFS relies on stranding data and
fisher self-reports to document fishery
interactions with marine mammals.
While these sources show only a low
level of interactions, NMFS recognizes
that they are unreliable and likely to be
biased low. However, NMFS will
continue monitoring using self-reports
and stranding data. Observer coverage
for these fisheries also remains a
priority if resources become available.
In addition, PBR is unknown for these
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stocks because of insufficient
information on stock structure and
abundance.
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 of
which was released alive. In the same
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.
Fishers’ self-reports through the Marine
Mammal Authorization Program
(MMAP) reveal five bottlenose dolphin
mortalities from 2002–2006, with two
mortalities in 2002, one in 2004, and
two in 2005. However, information
gathered under the MMAP cannot be
verified, so 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. Stranding data
suggest that marine mammal
interactions with gillnets do occur,
causing mortality and serious injury.
NMFS acknowledges that stranding data
likely underestimate 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.
It is important to further investigate
stock structure and abundance of
bottlenose dolphins in the Gulf of
Mexico. There is currently no PBR
calculated for coastal stocks or bay,
sound, and estuarine stocks, preventing
NMFS from assessing the populationlevel impacts of serious injuries and
mortalities. To address this, NMFS is
working toward updating estimates of
bottlenose dolphin abundance and
refining bottlenose dolphin stock
structure in the Gulf of Mexico.
Specifically, in July and August 2007,
NMFS completed a ship-based survey of
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the Gulf of Mexico continental shelf and
completed winter and summer aerial
line-transect abundance surveys of
coastal bottlenose dolphin stocks. To
help characterize stock structure and
abundance in bays, sounds, and
estuaries, NMFS conducted a photo-ID
mark-recapture study and biopsy
sampling in Choctawhatchee Bay, FL, in
July and August 2007 and biopsy
sampling in Mississippi Sound in 2005
and 2006. Data collected during these
surveys are currently being analyzed,
and updated information on population
abundance and stock structure will
appear in the 2008 SARs. Once this
information is available and PBR is
calculated for each stock, NMFS will be
better able to assess the impacts of
mortality and serious injury of marine
mammals associated with commercial
fisheries in the Gulf.
Comment 47: The Marine Mammal
Commission recommended that NMFS
expand its efforts to collect reliable
information on serious injury and
mortality rates of marine mammals
incidental to Gulf of Mexico fisheries,
with priority being given to instituting
an observer program for the menhaden
purse seine fishery and expanding
efforts to evaluate bottlenose dolphin
entanglements in blue crab trap/pot
gear. The CBD also recommended that
NMFS make it a high priority to place
observer coverage in the ‘‘Gulf of
Mexico menhaden purse seine fishery’’
and further recommended that NMFS
convene a TRT to address bottlenose
dolphin take in the Gulf from this and
other fisheries.
Response: Collecting reliable
information on serious injury and
mortality of marine mammals in the
Gulf of Mexico is essential. However,
there are currently no resources to fund
observer programs in these fisheries.
Therefore, NMFS is focusing on
building volunteer stranding network
capacity in the Gulf and increasing the
level and quality of stranding response.
NMFS held training workshops for the
stranding network in Texas, Louisiana,
and Mississippi in May 2008 to train
responders how to recognize and
document human interaction and
conduct necropsies. NMFS expects
these efforts to increase the effectiveness
of the stranding networks and better
inform management decisions in the
future.
Observer coverage for the ‘‘Gulf of
Mexico menhaden purse seine fishery’’
and evaluating bottlenose dolphin
entanglements in the blue crab/trap pot
gear are priorities if resources become
available. Because population size and
PBR are unknown for the three coastal
and all the bay, sound, and estuary
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stocks, NMFS is unable to assess the
population level impacts of serious
injuries and mortalities from fisheries to
determine whether annual mortality is
greater than or equal to 50 percent of
PBR. Thus, NMFS does not believe a
TRT is supported by currently available
information. As stated in the response
comment 46, NMFS is working to
collect and analyze additional data.
Once this information is available and a
PBR is calculated for each stock, NMFS
will be better able to assess the impacts
of mortality and serious injury of marine
mammals associated with commercial
fisheries in the Gulf of Mexico.
Summary of Changes to the LOF for
2009
The following summarizes changes to
the LOF for 2009 in fishery
classification, fisheries listed in the
LOF, the number of participants in a
particular fishery, and the species/
stocks that are incidentally killed or
injured in a particular fishery. The
classifications and definitions of U.S.
commercial fisheries for 2009 are
identical to those provided in the LOF
for 2008 with the changes outlined
below.
Commercial Fisheries on the High Seas
Addition of Fisheries to the LOF
High Seas Atlantic Highly Migratory
Species Fisheries
The high seas Atlantic HMS fisheries
are added to the LOF. All gear types
targeting Atlantic HMS on the high seas
are categorized as Category II on the
LOF, with the exception of longline and
purse seine gear. The longline
component of this fishery is classified as
Category I because it is an extension of
the Category I ‘‘Atlantic Ocean,
Caribbean, Gulf of Mexico large pelagics
longline fishery’’ operating within U.S.
waters; and the purse seine component
of this fishery is classified as Category
III because it is an extension of the
Category III ‘‘U.S. Atlantic tuna purse
seine fishery’’ operating within U.S.
waters. There are 88 valid HSFCA
permits for fishers targeting Atlantic
HMS on the high seas with all gear
types. As noted in the preamble, the
number of valid permits may not
accurately account for annual fishing
effort on the high seas.
Observer information is available on
which marine mammal stocks are
incidentally killed or injured on the
high seas by the Atlantic HMS longline
fishery; therefore, NMFS lists the
marine mammal species that have been
documented killed or injured in the
Category I high seas longline component
of Atlantic HMS fisheries in Table 3.
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Similar observer data are not available
for the high seas Atlantic HMS purse
seine fishery, which is an extension of
the Category III ‘‘Atlantic tuna purse
seine fishery.’’ NMFS adds all noncoastal marine mammal species/stocks
killed or injured in the Category III
‘‘Atlantic tuna purse seine fishery’’ as
injured or killed in the high seas purse
seine component of the Atlantic HMS
fisheries.
There is little information on
interactions between marine mammals
and fishing gear used to target Atlantic
HMS on the high seas, other than that
listed in the previous paragraphs. Given
the lack of data on marine mammal
abundance and interactions with high
seas Atlantic HMS fisheries using gear
other than longline and purse seine,
NMFS lists the marine mammal species
killed or injured in these fisheries as
‘‘undetermined’’ in Table 3.
High Seas Pacific Highly Migratory
Species Fisheries
The high seas Pacific HMS fisheries
are added to the LOF. All gear types
targeting Pacific HMS on the high seas
are listed as Category II, with the
exception of drift gillnet and troll gear.
The drift gillnet component of this
fishery is listed as a Category I because
it is an extension of the Category I ‘‘CA/
OR thresher shark/swordfish drift
gillnet (≥14 in. mesh) fishery’’ operating
within U.S. waters; and the troll
component of this fishery is listed as a
Category III because it is an extension of
the Category III ‘‘AK North Pacific
halibut, AK bottom fish, WA/OR/CA
albacore, groundfish, bottom fish, CA
halibut non-salmonid troll fisheries’’
operating within U.S. waters. There are
344 valid HSFCA permits for fishers
targeting Pacific HMS on the high seas
using all gear types. As noted in the
preamble, the number of valid permits
may not accurately account for annual
fishing effort on the high seas.
Observer information is available for
which species/stocks are incidentally
killed or injured in the high seas
longline component of this fishery;
therefore, NMFS lists the marine
mammal species that have been
documented killed or injured in the
high seas longline component of
Atlantic HMS fisheries in Table 3. This
list of species/stocks is identical to
those listed as taken in the Category II
‘‘CA pelagic longline fishery’’ operating
in U.S. waters. This is because the
fishery is currently prohibited within
U.S. waters, but remains listed on Table
1 because catch is landed on the U.S.
West coast. Therefore, the marine
mammal species listed as killed or
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injured in this fishery were observed
taken on the high seas.
For those fisheries where no
interaction data (observer or other data)
exist on the high seas, NMFS lists all the
non-coastal marine mammal species/
stocks killed or injured in the portion of
the fishery that operates in U.S. waters
as injured or killed in the same fishery
operating on the high seas in Table 3.
NMFS adds all non-coastal marine
mammal species killed or injured in the
Category I ‘‘CA/OR thresher shark/
swordfish drift gillnet (≥14 in. mesh)
fishery’’ as injured or killed in the high
seas drift gillnet component of Pacific
HMS fisheries. NMFS adds all noncoastal marine mammal species killed
or injured in the Category II ‘‘CA tuna
purse seine fishery’’ as injured or killed
in the high seas purse seine component
of the Pacific HMS fisheries.
There is little information on
interactions between marine mammals
and fishing gear used to target Pacific
HMS on the high seas, other than that
listed in the previous paragraphs. Given
the lack of data on marine mammal
abundance and interactions with high
seas Pacific HMS fisheries using gear
other than longline, drift gillnet, and
purse seine, NMFS lists the marine
mammal species killed or injured in
these fisheries as ‘‘undetermined’’ in
Table 3.
rwilkins on PROD1PC63 with RULES4
High Seas Western Pacific Pelagic
Fisheries
The high seas Western Pacific pelagic
fisheries are added to the LOF. All gear
targeting Western Pacific pelagic species
are listed as Category II, with the
exception of deep-set longline gear. The
deep-set longline component of this
fishery is listed as a Category I because
it is an extension of the Category I ‘‘HI
deep-set (tuna target) longline/set line
fishery’’ operating in U.S. waters. There
are 219 valid HSFCA permits for fishers
targeting Western Pacific pelagic species
with all gear types on the high seas. As
noted in the preamble, the number of
valid permits may not accurately
account for annual fishing effort on the
high seas.
NMFS adds all non-coastal marine
mammal species/stocks killed or injured
in the Category I ‘‘HI deep-set (tuna
target) longline/set line fishery’’ as
injured or killed in the deep-set longline
component operating on the high seas.
NMFS adds all non-coastal marine
mammal species killed or injured in the
Category II ‘‘HI shallow-set (swordfish
target) longline/set line fishery’’ as
injured or killed in the shallow-set
longline component operating on the
high seas.
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There is little information on
interactions between marine mammals
and fishing gear used to target Western
Pacific pelagic species on the high seas,
other than that listed in the previous
paragraph. Given the lack of data on
marine mammal abundance and
interactions with high seas Western
Pacific pelagic fisheries using gear other
than longline, NMFS lists the marine
mammal species killed or injured in
these fisheries as ‘‘undetermined’’ in
Table 3.
High Seas South Pacific Albacore Troll
Fisheries
The high seas South Pacific albacore
troll fisheries are added to the LOF,
with all gear types listed as Category II.
There are 83 valid HSFCA permits for
vessels participating in the South
Pacific albacore troll fisheries on the
high seas with all gear types. As noted
in the preamble, the number of valid
permits may not accurately account for
annual fishing effort on the high seas.
There are no records of incidental
mortality or serious injury of marine
mammals in the South Pacific albacore
troll fisheries. While there is little
indication of marine mammal
interactions with South Pacific albacore
troll fishing, NMFS listed the marine
mammal species killed or injured in
these fisheries as ‘‘undetermined’’ in
Table 3 due to the lack of an observer
program covering these fisheries.
High Seas South Pacific Tuna Fisheries
The high seas South Pacific tuna
fisheries (as authorized under the SPTT)
are added to the LOF. All gear types are
listed as Category II because, while a
formal observer program exists for
fishing in the Treaty area, information
on marine mammal stock abundance in
the area is scarce and observer reports
of fishery interactions are not yet
specific enough to determine the level
of marine mammal serious injury and
mortality. There are 26 valid HSFCA
permits for vessels participating in the
South Pacific tuna fishery. This number
accurately reflects the effort by U.S.
vessels in the SPTT area because it
closely matches the number of U.S.
vessels with a valid SPTT license.
While available observer data
document interactions with marine
mammals, the data only currently
identify the animals as unidentified
whales, marine mammals, or dolphin/
porpoise. For this reason, Table 3 lists
the marine mammal species killed/
injured in these fisheries as
‘‘undetermined.’’
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High Seas Antarctic Living Marine
Resources Fisheries
The high seas Antarctic Living Marine
Resources (or CCAMLR) fisheries are
added to the LOF. All gear types are
listed as Category II because, while a
formal observer program exists for
fishing under CCAMLR, specific
information on marine mammal
abundance and fishery interactions
levels has not been calculated in the
manner necessary to categorize the
fisheries based on a marine mammal
stock’s PBR. There are no valid HSFCA
permits for vessels participating in the
CCAMLR fisheries for the 2008 fishing
season, which accurately reflects effort
by U.S. vessels in the CCAMLR area.
NMFS has included the trawl and
gillnet components of the CCAMLR
fisheries (the gear types used by U.S.
vessels in the recent past) on Table 3
with a zero indicating the number of
HSFCA permits for these fishery
components.
Observer information is available for
which species are incidentally killed or
injured in CCAMLR fisheries. Based on
observer data of interactions with trawl
gear, NMFS adds Antarctic fur seals as
incidentally killed or injured in the
trawl component of the fishery. There
are no documented injuries or
mortalities of other marine mammal
species and U.S. vessels when using
other gear types in the CCAMLR region;
therefore, Table 3 lists the marine
mammal species killed/injured in
longline gear as ‘‘none documented.’’
Commercial Fisheries in the Pacific
Ocean
Fishery Classification
HI Swordfish, Tuna, Billfish, Mahi
mahi, Wahoo, Oceanic Sharks Longline/
Set Line Fishery
The Category I ‘‘HI swordfish, tuna,
billfish, mahi mahi, wahoo, oceanic
sharks longline/set line fishery’’ is split
into two separately managed
commercial fisheries: (1) The ‘‘HI deepset (tuna target) longline/set line
fishery’’; and (2) the ‘‘HI shallow-set
(swordfish target) longline/set line
fishery.’’ The ‘‘HI deep-set (tuna target)
longline/set line fishery’’ is classified as
a Category I fishery, and the ‘‘HI
shallow-set (swordfish target) longline/
set line fishery’’ is classified as a
Category II fishery.
CA Halibut/White Seabass and Other
Species Set Gillnet (>3.5 in. mesh)
Fishery
The ‘‘CA halibut/white seabass and
other species set gillnet (>3.5 in. mesh)
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fishery’’ is recategorized from a Category
I to a Category II fishery.
rwilkins on PROD1PC63 with RULES4
West Coast Trap/Pot Fisheries
NMFS reclassifies multiple West
Coast trap and pot fisheries from
Category III to Category II based on
interactions with humpback whales
(CA/OR/WA stock).
The ‘‘CA spot prawn pot fishery’’ is
split from the Category III ‘‘CA lobster,
prawn, shrimp, rock crab, fish pot’’
(renamed the ‘‘CA spiny lobster,
coonstrip shrimp, rock crab, tanner crab
pot or trap’’ in this final rule) and listed
on the LOF as a Category II fishery. The
estimated number of vessels or
participants in this fishery is 29. In
addition to humpback whales, gray
whales remain listed as injured or killed
in this fishery because gray whales have
been listed as injured or killed in this
fishery on past LOFs.
The ‘‘WA/OR/CA sablefish pot
fishery’’ is elevated from Category III to
a Category II fishery. The estimated
number of vessels or participants in this
fishery is 155, including both limited
and open access permits (there are 32
limited access permits).
The ‘‘OR Dungeness crab pot fishery’’
is split from the Category III ‘‘WA/OR/
CA crab pot fishery’’ and elevated to
Category II. The estimated number of
vessels or participants in this fishery is
433 (433 permits exist, 364 landings
were made in 2006). In addition to
humpback whales, gray whales remain
listed as injured or killed in this fishery
because gray whales have been listed as
injured or killed in this fishery on past
LOFs.
The ‘‘CA Dungeness crab pot fishery’’
is split from the Category III ‘‘WA/OR/
CA crab pot fishery’’ and elevated to
Category II. The estimated number of
vessels or participants in this fishery is
625 (625 permits exist, 435 landings
were made in 2006). In addition to
humpback whales, gray whales remain
listed as injured or killed in this fishery
because gray whales have been listed as
injured or killed in this fishery on past
LOFs.
The ‘‘WA Dungeness crab pot fishery’’
is split from the Category III ‘‘WA/OR/
CA crab pot fishery’’ and remains a
Category III fishery. In addition to
humpback whales, gray whales remain
listed as injured or killed in this fishery
because gray whales have been listed as
injured or killed in this fishery on past
LOFs.
Addition of Fisheries to the LOF
The ‘‘HI deep-set (tuna target)
longline/set line fishery’’ is added to the
LOF as a Category I fishery.
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The ‘‘HI shallow-set (swordfish target)
longline/set line fishery’’ is added to the
LOF as a Category II fishery.
The ‘‘CA spot prawn trap fishery’’ is
added to the LOF as a Category II
fishery.
The ‘‘CA Dungeness crab pot fishery’’
is added to the LOF as a Category II
fishery.
The ‘‘OR Dungeness crab pot fishery’’
is added to the LOF as a Category II
fishery.
The ‘‘WA Dungeness crab pot fishery’’
is added to the LOF as a Category III
fishery.
The ‘‘AK statewide miscellaneous
finfish pot fishery’’ is added to the LOF
as a Category III fishery.
The ‘‘AK shrimp pot, except
Southeast fishery’’ is added to the LOF
as a Category III fishery.
Removal of Fisheries From the LOF
The Category II ‘‘AK Metlakatla/
Annette Island salmon drift gillnet
fishery’’ is removed from the LOF.
Fishery Name and Organizational
Changes and Clarifications
The Category II ‘‘CA angel shark/
halibut and other species set gillnet
(>3.5 mesh size) fishery’’ is renamed the
‘‘CA halibut/white seabass and other
species set gillnet (>3.5 in. mesh)
fishery.’’
The prawn portion of the Category III
‘‘CA lobster, prawn, shrimp, rock crab,
and fish pot fishery’’ is split into a
separate fishery, the Category II ‘‘CA
spot prawn fishery,’’ and the remaining
portion of the Category III fishery is
renamed the ‘‘CA spiny lobster,
coonstripe shrimp, rock crab, tanner
crab pot or trap fishery.’’
The Category III ‘‘WA/OR/CA crab pot
fishery’’ is split into three fisheries, the
Category II ‘‘CA Dungeness crab pot’’
and ‘‘OR Dungeness crab pot’’ fisheries,
and the Category III ‘‘WA Dungeness
crab pot fishery.’’
The Category III ‘‘CA finfish and
shellfish live trap/hook-and-line
fishery’’ is renamed the ‘‘CA nearshore
finfish live trap/hook-and-line fishery.’’
The Category III ‘‘AK state-managed
waters groundfish longline/set line
(including sablefish, rockfish, and
miscellaneous finfish’’ is renamed the
‘‘AK state-managed waters longline/set
line (including sablefish, rockfish,
lingcod, and miscellaneous finfish.’’
The Category III ‘‘AK North Pacific
halibut handline and mechanical jig
fishery’’ is renamed the ‘‘AK North
Pacific halibut handline/hand troll and
mechanical jig fishery.’’
The Category III ‘‘AK miscellaneous
finfish handline and mechanical jig
fishery’’ is renamed the ‘‘AK
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miscellaneous finfish handline/hand
troll and mechanical jig fishery.’’
The Category III ‘‘AK salmon purse
seine (except Southeast AK, which is in
Category II) fishery’’ is renamed the ‘‘AK
salmon purse seine (excluding salmon
purse seine fisheries listed as Category
II).
The superscript ‘‘1’’ following Steller
sea lion (Western U.S.) is removed
under the Category II ‘‘AK Bristol Bay
salmon drift gillnet fishery’’ in Table 1.
The superscript ‘‘2’’ remains after the
fishery’s name in Table 1.
Number of Vessels/Persons
The estimated number of vessels or
persons in the Category II ‘‘CA squid
purse seine fishery’’ is updated to 64.
The estimated number of vessels or
persons in the Category III ‘‘CA spiny
lobster, coonstripe shrimp, rock crab,
tanner crab pot or trap fishery’’ is
updated to 530.
The estimated number of vessels or
persons in the Category III ‘‘OR/CA
hagfish pot or trap fishery’’ is updated
to 54.
The estimated number of vessels or
persons in the majority of the AK
Category II fisheries are updated: AK
Southeast salmon drift gillnet fishery to
476; AK Yakutat salmon set gillnet to
166; AK Prince William Sound salmon
drift gillnet to 537; AK Cook Inlet
salmon drift gillnet to 571; AK Cook
Inlet salmon set gillnet to 738; AK
Peninsula/Aleutian Islands salmon drift
gillnet to 162; AK Peninsula/Aleutian
Islands salmon set gillnet to 115; AK
Bristol Bay salmon drift gillnet to 1,862;
AK Bristol Bay salmon set gillnet to 983;
AK Southeast salmon purse seine
fishery to 415; AK Bering Sea, Aleutian
Islands pollock trawl to 95; AK Bering
Sea, Aleutian Islands Pacific cod trawl
to 54; AK Bering Sea, Aleutian Islands
finfish trawl to 34.
The estimated number of vessels or
persons in the majority of the AK
Category III fisheries are updated: AK
Kuskokwim, Yukon, Norton Sound,
Kotzebue salmon gillnet to 1,824; AK
roe herring and food/bait herring gillnet
to 986; AK miscellaneous finfish set
gillnet to 0; AK salmon purse seine
(except Southeast AK, which is Category
II) to 936; AK salmon beach seine to 31;
AK roe herring and food/bait herring
purse seine to 361; AK roe herring and
food/bait herring beach seine to 4; AK
octopus/squid purse seine to 0; AK
salmon troll to 2,045; AK North Pacific
halibut/bottom fish troll to 1,302 (102
AK); AK state-managed waters
groundfish longline/set line (including
sablefish, rockfish, and miscellaneous
finfish) to 1,448; AK Gulf of Alaska
rockfish longline to 0; AK Gulf of Alaska
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sablefish longline to 291; AK Bering
Sea, Aleutian Islands Greenland turbot
longline to 29; AK Bering Sea, Aleutian
Islands rockfish longline to 0; AK Bering
Sea, Aleutian Islands sablefish longline
to 28; AK halibut longline/set line (State
and Federal waters) to 2,521; AK
octopus/squid longline to 2; AK shrimp
otter and beam trawl (statewide and
Cook Inlet) to 32; AK Gulf of Alaska
flatfish trawl to 41; AK Gulf of Alaska
Pacific cod trawl to 62; AK Gulf of
Alaska pollock trawl to 62; AK Gulf of
Alaska rockfish trawl to 34; AK Bering
Sea, Aleutian Islands Atka mackerel
trawl to 9; AK Bering Sea, Aleutian
Islands Pacific cod trawl to 93; AK
Bering Sea, Aleutian Islands rockfish
trawl to 10; AK miscellaneous finfish
otter or beam trawl to 317; AK food/bait
herring trawl to 4; AK Bering Sea,
Aleutian Islands Pacific cod pot to 68;
AK Bering Sea, Aleutian Islands crab
pot to 297; AK Gulf of Alaska crab pot
to 300; AK Southeast Alaska crab pot to
433; AK Southeast Alaska shrimp pot to
283; AK octopus/squid pot to 27; AK
snail pot to 1; AK North Pacific halibut
handline/hand troll and mechanical jig
to 228; AK miscellaneous finfish
handline/hand troll and mechanical jig
to 445; AK octopus/squid handline to 0;
AK Southeast herring roe/food/bait
pound net to 6; AK dungeness crab
(hand pick/dive) to 2; AK herring spawn
on kelp (hand pick/dive) to 266; AK
urchin and other fish/shellfish (hand
pick/dive) to 570; AK commercial
passenger fishing vessel from to >7,000
(2,702 AK).
rwilkins on PROD1PC63 with RULES4
Harbor porpoise (central CA) are
removed from the list of marine
mammal species/stock incidentally
killed/injured in the Category II ‘‘CA
halibut/white seabass and other species
set gillnet (>3.5 mesh size) fishery.’’
The following marine mammals
species/stocks are removed from the list
of species/stocks incidentally killed/
injured in the Category I ‘‘CA/OR
thresher shark/swordfish drift gillnet
(≥14 in. mesh) fishery’’: Dall’s porpoise
(CA/OR/WA), fin whale (CA/OR/WA),
gray whale (Eastern North Pacific),
humpback whale (CA/OR/WA), and
sperm whale (CA/OR/WA).
Humpback whales (CA/OR/WA) are
removed from the list of species/stocks
incidentally killed/injured in the
Category II ‘‘WA Dungeness pot
fishery.’’
Humpback whales (CA/OR/WA) and
sea otters (CA) are removed from the list
of species/stocks incidentally killed/
injured in the Category III ‘‘CA spiny
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Ocean, Gulf of Mexico, and Caribbean
Addition of Fisheries to the LOF
List of Species That Are Incidentally
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lobster, coonstripe shrimp, rock crab,
tanner crab pot or trap fishery.’’
The stock name of humpback whales
(Eastern North Pacific) is changed to
humpback whales (CA/OR/WA) for all
fisheries in Table 1 in which this stock
is listed as incidentally killed or injured
to match the stock name in the most
current SARs.
The stock of common dolphin listed
as incidentally killed or injured in the
Category II ‘‘CA squid purse seine
fishery’’ is changed from ‘‘common
dolphin, unknown’’ to ‘‘short-beaked
common dolphin, CA/OR/WA’’ and
‘‘long-beaked common dolphin, CA’’ to
account for the uncertainty of the
species observed seriously injured or
killed in this fishery.
Bryde’s whale, sperm whale, and
pantropical spotted dolphin are
removed from the list of species/stocks
killed/injured in the Category I ‘‘HI
deep-set (tuna target) longline/set line
fishery,’’ and added to the list of
species/stocks killed/injured in the
Category II ‘‘HI shallow-set (swordfish
target) longline/set line fishery,’’ to
correct a typographical error in the
proposed 2009 LOF.
Hawaiian monk seal is removed from
the list of species/stocks killed/injured
in the Category III ‘‘HI tuna handline
fishery.’’ NMFS has never received a
report of interactions between monk
seals with tuna handline.
The ‘‘U.S. Atlantic, Gulf of Mexico
trotline fishery’’ is added to the LOF as
a Category III fishery.
Fishery Name and Organizational
Changes and Clarifications
Gulf of Mexico Menhaden Purse Seine
Fishery
NMFS corrects a typographical error
that has persisted since the 2006 LOF
(71 FR 48802; August 22, 2006) and was
not proposed in the proposed 2009 LOF
(73 FR 33760, June 13, 2008). A
superscript ‘‘1’’ following bottlenose
dolphin (Western Gulf of Mexico
coastal) is added under the Category II
‘‘Gulf of Mexico menhaden purse seine
fishery’’ in Table 2, indicating that this
stock is driving the categorization of this
fishery. The 2006 LOF included a
superscript ‘‘1’’ following bottlenose
dolphin (Northern Gulf of Mexico
coastal); however, a superscript ‘‘1’’
should have been included for both the
Northern and the Western Gulf of
Mexico coastal stocks.
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Northeast Bottom Trawl Fishery
NMFS corrects a typographical error
that has persisted since the 2005 LOF
(71 FR 247; January 4, 2006). In the
proposed 2005 LOF (70 FR 70094;
December 2, 2004), NMFS proposed to
add harbor porpoise (Gulf of Maine/Bay
of Fundy) to the list of species/stocks
incidentally taken in the Category II
‘‘Northeast bottom trawl fishery.’’
However, NMFS decided not to include
this stock on the list based on a public
comment stating that the animal taken
in that fishery was badly decomposed
and the trawl duration was only five
hours (see comment/response 33 in the
final 2005 LOF). While this stock has
never been considered incidentally
killed/injured in this fishery, it
inadvertently remained listed in Table 2
of the LOF. NMFS corrects that error at
this time by removing harbor porpoise
(Gulf of Maine/Bay of Fundy) from
Table 2 following the ‘‘Northeast bottom
trawl fishery.’’
Northeast Sink Gillnet Fishery
The definition of the Category I
‘‘Northeast sink gillnet fishery’’ is
amended to clarify and correct the
boundary description by replacing
‘‘excluding Long Island Sound or other
waters where gillnet fisheries are listed
as Category III. At this time, these
Category II and II fisheries include
* * *’’ with ‘‘* * * excluding Long
Island Sound and other waters where
gillnet fisheries are listed as Category II
and III. At this time, these Category II
and III fisheries include * * *’’.
Northeast Anchored Float Gillnet
Fishery
The definition of the Category II
‘‘Northeast anchored float gillnet
fishery’’ is amended to clarify and
correct the boundary description by
replacing ‘‘ * * * from the U.S.-Canada
border to Long Island, NY, at 72°30″ W.
long south to 36°33.03″ N. lat. and east
to the eastern edge of the EEZ * * *’’
with ‘‘ * * * from the U.S.-Canada
border to Long Island, NY, at 72°30″ W.
long south to 36°33.03″ N. lat.
(corresponding with the VA/NC border)
and east to the eastern edge of the EEZ
* * *’’.
Northeast Drift Gillnet Fishery
The definition of the Category II
‘‘Northeast drift gillnet fishery’’ is
amended to clarify and correct the
boundary description by replacing
‘‘* * * at any depth in the water
column from the U.S.-Canada border to
Long Island, NY, at 72°30″ W. long.
south to 36°33.03″ N. lat. and east to the
eastern edge of the EEZ * * *’’ with ‘‘
* * * at any depth in the water column
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from the U.S.-Canada border to Long
Island, NY, at 72°30″ W. long. south to
36°33.03″ N. lat. (corresponding with
the VA/NC border) and east to the
eastern edge of the EEZ * * *’’.
rwilkins on PROD1PC63 with RULES4
Mid-Atlantic Mid-water Trawl Fishery
The fishery description for the
Category II ‘‘Mid-Atlantic mid-water
trawl fishery’’ is replaced with the
following description, ‘‘The ‘MidAtlantic mid-water trawl fishery’
primarily targets Atlantic mackerel,
chub mackerel, and miscellaneous other
pelagic species. This fishery consists of
both single and pair trawls, which are
designed, capable, or used to fish for
pelagic species with no portion of the
gear designed to be operated in contact
with the bottom. The fishery for Atlantic
mackerel occurs primarily from
southern New England through the midAtlantic from January to March and in
the Gulf of Maine during the summer
and fall (May to December). This fishery
is managed under the Federal Atlantic
Mackerel, Squid, and Butterfish FMP
using an annual quota system.’’
Mid-Atlantic Bottom Trawl Fishery
The fishery description for the
Category II ‘‘Mid-Atlantic bottom trawl
fishery’’ is replaced with the following
description: ‘‘The Category II ‘MidAtlantic bottom trawl fishery’ uses
bottom trawl gear to target species
including but not limited to: bluefish,
croaker, monkfish, summer flounder
(fluke), winter flounder, silver hake
(whiting), spiny dogfish, smooth
dogfish, scup, black sea bass, Atlantic
cod, haddock, pollock, yellowtail
flounder, witch flounder, windowpane
flounder, summer flounder, American
plaice, Atlantic halibut, redfish, red
hake, white hake, ocean pout, skate spp,
Atlantic mackerel, Loligo squid, Illex
squid, and Atlantic butterfish. These
fisheries occur year round from Cape
Cod, MA, to Cape Hatteras, NC, in
waters west of 72°30″ W. long. and
north of a line extending due east from
the NC/SC border. While the gear
characteristics for the mixed groundfish
bottom trawl gear have not yet been
determined, the Illex and Loligo squid
fisheries are dominated by small-mesh
otter trawls. The Loligo fishery occurs
mostly offshore near the edge of the
continental shelf during fall and winter
months (October to March) and inshore
during spring and summer (April–
September) though landings of Loligo
are also taken by inshore pound nets
and fish traps in the spring and summer.
The fishery for Illex occurs offshore,
mainly in continental shelf and slope
waters during summer months (June–
September). The Illex and Loligo
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fisheries are managed by moratorium
permits, gear and area restrictions,
quotas, and trip limits. Atlantic
butterfish are mainly caught as bycatch
in the directed squid and mackerel
fisheries and observer data has
suggested that there is a significant
amount of butterfish discarding that
occurs at sea.’’
Mid-Atlantic Haul/Beach Seine Fishery
The fishery description for the
Category II ‘‘Mid-Atlantic haul/beach
seine fishery’’ is replaced with the
following description: ‘‘The NC
component of this fishery operates
primarily along the Outer Banks using
small and large mesh nets. Small mesh
nets are generally used in the spring and
fall to target gray trout (weakfish),
speckled trout, spot, kingfish (sea
mullet), bluefish, and harvest fish (star
butters). Large mesh nets are used to
target Atlantic striped bass during the
winter and are regulated via NC Marine
Fisheries Commission rules and
NCDMF proclamations. Construction
and characteristics of the large and
small mesh nets differ, but they
generally both gill fish, rather than haul
fish to shore in the manner of a
traditional beach seine. Small mesh nets
are generally constructed with a
combination of multifilament and
monofilament webbing or all
monofilament webbing material. If a
combination of materials is used, the
construction design often consists of
monofilament for the inshore (wash)
and offshore (wing) portions of the net,
while the middle (bunt) is constructed
of twisted nylon. Conversely, large mesh
nets are constructed of all monofilament
material. Despite the difference in
construction, they are set and hauled
similarly. Nets are deployed out of the
stern of surf dories and set
perpendicular to the shoreline. A truck
is generally used to haul the net ashore
by attaching one end of the net to the
truck and pulling it ashore while the
other end remains fixed until the end of
the haul.
North Carolina fishers previously
referred to this type of gear as a beach
seine because of the way the gear was
set and hauled. Because of the manner
in which both large and small mesh nets
are constructed (i.e., inclusion of
monofilament material) and fished, they
operate as gillnets rather than beach
seines, and NMFS considers them a
component of the Category I, ‘‘MidAtlantic gillnet fishery.’’ Once NCDMF’s
regulation is effective, the Atlantic
Ocean striped bass beach seine fishery
will be the only fishery included under
the ‘‘Mid-Atlantic haul/beach seine
fishery’’ for North Carolina. Therefore,
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small and large mesh nets constructed
of monofilament and multifilament
material will be considered part of the
Category I ‘‘Mid-Atlantic gillnet
fishery.’’ NMFS is not currently
regulating this component of the ‘‘MidAtlantic gillnet fishery’’ (i.e., nets that
are anchored to the beach and
subsequently hauled onto the beach to
retrieve the catch). NMFS will discuss
the appropriate management measures
for this fishery component with the
Atlantic Large Whale Take Reduction
Team in the future.
In addition to the North Carolina
component as described above, the
‘‘Mid-Atlantic haul/beach seine fishery’’
also includes haul seining in other areas
of the mid-Atlantic, including VA, MD,
and NJ. Because the net materials and
fishing practices of the Atlantic Ocean
striped bass beach seine fishery in North
Carolina are different from haul seining
in other areas, NMFS may consider
splitting this fishery in the future.’’
List of Species That Are Incidentally
Killed or Injured
White-side dolphins (Western North
Atlantic [WNA]) are added to the list of
marine mammal species/stocks
incidentally injured or killed in the
Category II ‘‘Mid-Atlantic bottom trawl
fishery.’’
Harbor seals (WNA) are added to the
list of marine mammal species/stocks
incidentally injured or killed in the
Category II ‘‘Northeast bottom trawl
fishery.’’
Bottlenose dolphins (WNA coastal)
are added to the list of marine mammal
species/ stocks incidentally injured or
killed in the Category III ‘‘FL spiny
lobster trap/pot fishery.’’
Bottlenose dolphins (WNA coastal)
are added to the list of marine mammal
species/stocks incidentally injured or
killed in the Category III ‘‘Southeastern
U.S. Atlantic, Gulf of Mexico stone crab
trap/pot fishery.’’
List of Fisheries
The following tables set forth the final
list of U.S. commercial fisheries
according to their classification under
section 118 of the MMPA. In Tables 1
and 2, the estimated number of vessels/
participants 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
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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, and fisher reports.
This list includes all species or stocks
known to be injured or killed in a given
fishery, but also includes species or
stocks for which there are anecdotal
records of an injury or mortality.
Additionally, species identified by
logbook entries may not be verified.
NMFS has designated those stocks
driving a fishery’s classification (i.e., the
fishery is classified based on serious
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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
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
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those fisheries originally listed by
analogy in Tables 1 and 2 by a ‘‘2’’ after
the fishery’s name.
There are several fisheries in Tables 1,
2, and 3 in which a portion of the
fishing vessels cross the EEZ boundary,
and therefore operate within U.S. waters
and on the high seas. 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
Teams or Plans.
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Classification
The Chief Counsel for Regulation of
the Department of Commerce certified
to the Chief Counsel for Advocacy of the
Small Business Administration that this
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.
Under existing regulations, all fishers
participating in Category I or II fisheries
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must register under the MMPA and
obtain an Authorization Certificate. The
Authorization Certificate authorizes the
taking of marine mammals incidental to
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 44,200
fishing vessels, most of which are small
entities, operate in Category I or II
fisheries, and therefore, are required to
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73075
register with NMFS. The MMPA
registration process is integrated with
existing state and Federal licensing,
permitting, and registration programs.
Therefore, fishers who have a federal or
state fishery permit or landing license,
or who are authorized through another
related federal or state fishery
registration program, are currently not
required to register separately under the
MMPA or pay the $25 registration fee
under the MMPA. Therefore, there are
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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
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17:24 Nov 28, 2008
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hours per report for new registrants and
0.09 hours per report for renewals). The
requirement for reporting marine
mammal injuries or mortalities has been
approved by OMB under OMB control
number 0648–0292 (0.15 hours per
report). These estimates include the
time for reviewing instructions,
searching existing data sources,
gathering and maintaining the data
needed, and completing and reviewing
the collection of information. Send
comments regarding these reporting
burden estimates or any other aspect of
the collections of information, including
suggestions for reducing burden, to
NMFS and OMB (see ADDRESSES and
SUPPLEMENTARY INFORMATION).
Notwithstanding any other provision
of law, no person is required to respond
to nor shall a person be subject to a
penalty for failure to comply with a
collection of information subject to the
requirements of the Paperwork
Reduction Act unless that collection of
information displays a currently valid
OMB control number.
This final rule has been determined to
be not significant for the purposes of
Executive Order 12866.
An environmental assessment (EA)
was prepared under the National
Environmental Policy Act (NEPA) for
regulations to implement section 118 of
the MMPA in June 1995. NMFS revised
that EA relative to classifying U.S.
commercial fisheries on the LOF in
December 2005. Both the 1995 EA and
the 2005 EA concluded that
implementation of MMPA section 118
regulations would not have a significant
impact on the human environment. This
final rule would not make any
significant change in the management of
reclassified fisheries, and therefore, this
final rule is not expected to change the
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analysis or conclusion of the 2005 EA.
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
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.
Dated: November 24, 2008.
Samuel D. Rauch III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
[FR Doc. E8–28378 Filed 11–28–08; 8:45 am]
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Agencies
[Federal Register Volume 73, Number 231 (Monday, December 1, 2008)]
[Rules and Regulations]
[Pages 73032-73076]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-28378]
[[Page 73031]]
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Part V
Department of Commerce
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National Oceanic and Atmospheric Administration
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50 CFR Part 229
List of Fisheries for 2009; Final Rule
Federal Register / Vol. 73, No. 231 / Monday, December 1, 2008 /
Rules and Regulations
[[Page 73032]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 229
[Docket No. 080204115-8832-02]
RIN 0648-AW48
List of Fisheries for 2009
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Department of Commerce.
ACTION: Final rule.
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SUMMARY: The National Marine Fisheries Service (NMFS) publishes its
final List of Fisheries (LOF) for 2009, as required by the Marine
Mammal Protection Act (MMPA). The final LOF for 2009 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 on January 1, 2009.
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 e-mail to David_Rostker@omb.eop.gov.
FOR FURTHER INFORMATION CONTACT: Melissa Andersen, Office of Protected
Resources, 301-713-2322; David Gouveia, Northeast Region, 978-281-9328;
Laura Engleby, Southeast Region, 727-824-5312; 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.
Regional Offices
NMFS, Northeast Region, One Blackburn Drive, Gloucester, MA 01930-
2298, Attn: Marcia Hobbs;
NMFS, Southeast Region, 263 13th Avenue South, St. Petersburg, FL
33701, Attn: Teletha Mincey;
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: Permits Office;
NMFS, Alaska Region, Protected Resources, P.O. Box 22668, 709 West
9th Street, Juneau, AK 99802, Attn: Bridget Mansfield; or
NMFS, Pacific Islands Region, Protected Resources, 1601 Kapiolani
Boulevard, Suite 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 categorization of a fishery in 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
[[Page 73033]]
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 or Stocks Are Included as
Incidentally Killed or Seriously Injured in a Fishery?
The LOF includes a list of marine mammal species or stocks
incidentally killed or seriously injured in each commercial fishery,
based on the level of mortality or serious injury in each fishery
relative to the PBR level for each stock. To determine which species or
stocks are included as incidentally killed or seriously 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 mortality or serious injury incidental to
commercial fishing operations. NMFS also reviews other sources of new
information, including observer data, stranding data, and fisher self-
reports.
In the absence of reliable information on the level of mortality or
serious 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 or a
take reduction plan). NMFS will provide case-specific justification in
the LOF for changes to the list of species or stocks incidentally
killed or seriously 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 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 Web site 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 Web site: https://www.st.nmfs.gov/st4/nop/.
How Do I Find Out if a Specific Fishery Is in Category I, II, or III?
This final rule includes three tables that list all U.S. commercial
fisheries by LOF Category. Table 1 lists all of the 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. 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 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 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.
How Does NMFS Authorize U.S. Vessels To Participate in High Seas
Fisheries?
NMFS issues high seas fishing permits, valid for five years, under
the HSFCA. To fish under a high seas permit, a fisher must also possess
any required permits issued under the Magnuson-Stevens Fishery
Conservation and Management Act (MSA) (with the exception of the South
Pacific Tuna Treaty fisheries, the Pacific Tuna Fisheries (Eastern
Tropical Pacific purse seine vessels) and the South Pacific Albacore
Troll fishery), and any permits issued by NMFS to fish within the
convention area of a Regional Fishery Management Organization. Under
the current permitting system, however, a fisher can obtain a high seas
permit prior to obtaining any necessary MSA permits. Similarly, a
fisher may have a HSFCA permit that was issued prior to changes in
permits issued under the MSA. Therefore, some fishers possess valid
HSFCA permits without the ability to fish under the permit. For this
reason, the number of HSFCA permits displayed in Table 3 of this final
rule is likely higher than the actual fishing effort by U.S. vessels on
the high seas.
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). There are currently seven
U.S.-authorized high seas fisheries: Atlantic Highly Migratory Species
Fisheries, Pacific Highly Migratory Species Fisheries, Western Pacific
Pelagic Fisheries, South Pacific Albacore Troll Fishing, Pacific Tuna
Fisheries, South Pacific Tuna Fisheries, and Antarctic Marine Living
Resources. The LOF does not include the ``Pacific (Eastern Tropical)
Tuna Fisheries'' because these fisheries are managed under Title III of
the MMPA, separate from those fisheries subject to the LOF under
section 118. Permits obtained prior to 2004 for
[[Page 73034]]
fisheries that are no longer authorized by the HSFCA, but for which the
5-year permit is still valid, are included on the LOF as
``unspecified.'' The ``unspecified'' fisheries will be removed from the
LOF once those permits have expired, and the permit holder is required
to renew the permit under one of the seven authorized fisheries.
The authorized high seas fisheries are broad in scope and encompass
multiple specific fisheries identified by gear type. Therefore, the
seven U.S.-authorized high seas fisheries, exclusive of the ``Pacific
(Eastern Tropical) Tuna Fisheries,'' are subdivided on the LOF based on
gear type (e.g., trawl, longline, purse seine, gillnet, troll, etc.),
as listed on each fisher's permit application, to provide more detail
on composition of effort within these fisheries.
How Does NMFS Categorize High Seas Fisheries on the LOF?
As discussed in the previous sections of this preamble, commercial
fisheries operating within U.S. waters are categorized on the LOF based
on the level of mortality and serious injury of marine mammal stocks
incidental to commercial fishing as related to the stock's PBR level.
PBR levels are calculated based on the stock's abundance using data
presented in the SARs. Section 117 of the MMPA (16 U.S.C. 1386)
requires NMFS to prepare SARs for marine mammal stocks occurring ``in
waters under the jurisdiction of the United States.'' NMFS does not
develop SARs or calculate PBR levels for marine mammal 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.
For this reason, NMFS categorizes the majority of high seas
fisheries on the LOF as Category II. As discussed previously in this
preamble, Category II is the appropriate category for commercial
fisheries not currently on the LOF (e.g., new fisheries) and for which
NMFS does not have adequate information to indicate the frequency of
incidental mortality and serious injury. Classifying a fishery in
Category II allows NMFS to place observers on vessels in that fishery,
providing NMFS the opportunity to obtain information needed to assess
the frequency of bycatch in that fishery. For fisheries that operate
both within U.S. waters and on the high seas, the high seas component
of the fishery is classified according to the fishery's status in U.S.
waters because it is not a separate fishery, but an extension of the
fishery. Therefore, for a Category I or Category III fishery operating
within U.S. waters, the high seas component would also be classified as
Category I or Category III, accordingly. NMFS will continue to gather
available information on the authorized high seas fisheries and
reclassify fisheries in Table 3, if necessary, as more information
becomes available.
How Does NMFS Determine Which Species or Stocks To Include as
Incidentally Killed or Seriously Injured in a High Seas Fishery?
All serious injury and mortality of marine mammals incidental to
commercial fishing operations, both in U.S. waters and on the high
seas, must be reported to NMFS. High seas fishers are provided with
Marine Mammal Take Reporting Forms to record such incidents. (Very few
marine mammal takes by U.S. vessels participating in high seas
fisheries, however, have been reported on these forms to date.)
Observer programs for fisheries operating within U.S. waters also
collect data on the high seas if the vessel should cross into high seas
waters. Additionally, some fisheries that operate exclusively on the
high seas have formal observer programs that provide data on
interactions. In these cases, the MSA, NEPA, or ESA documents
supporting the authorization of the seven U.S.-authorized high seas
fisheries review observer documented interactions and list the marine
mammal species taken in those fisheries. This information is used to
identify marine mammals killed or injured in these fisheries in Table 3
on the LOF. For other fisheries without observer data, the MSA, NEPA,
and ESA documents supporting the authorization of the seven U.S.-
authorized high seas fisheries present information on marine mammal
interactions from anecdotal and other reports, which do not always
specify the marine mammal species involved in the interactions.
Therefore, marine mammal species killed or injured in the high seas
fisheries without observer data that are listed in Table 3 are
designated as ``undetermined'' until additional information on marine
mammal populations and fishery interactions on the high seas becomes
available.
For high seas fisheries that are extensions of fisheries operating
within U.S. waters, as discussed above, Table 3 lists the same marine
mammal species killed or injured in the high seas components of
fisheries (excluding coastal species that would not be found on the
high seas) as those killed or injured by the component of the fishery
operating within U.S. waters (Tables 1 and 2). NMFS assumes that these
vessels pose the same risk to the species on both sides of the
Exclusive Economic Zone (EEZ) boundary. NMFS will add and delete
species from the LOF as additional information becomes available.
Am I Required To Register Under the MMPA?
Owners of vessels or gear engaging in a Category I or II fishery
are required under the MMPA (16 U.S.C. 1387(c)(2)), as described in 50
CFR 229.4, to register with NMFS and obtain a marine mammal
authorization to lawfully take a marine mammal incidental to commercial
fishing. Owners of vessels or gear engaged in a Category III fishery
are not required to register with NMFS or obtain a marine mammal
authorization.
How Do I Register?
NMFS has integrated the MMPA registration process, 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 NMFS will issue vessel or gear owners an
authorization certificate. Participants in these fisheries are not
required to submit registration or renewal materials directly under the
MMAP. 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,
Northwest, or Alaska regional fisheries will receive their
authorization certificates and/or injury/mortality
[[Page 73035]]
reporting forms via U.S. mail, or with their State or Federal license
at the time of renewal. Vessel or gear owners participating in
Southwest regional fisheries or 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-
9300 x6505 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 Federal permit is required, as well as
fisheries permitted by the states of North Carolina, South Carolina,
Georgia, Florida, Alabama, Mississippi, Louisiana, and Texas may
receive their authorization certificate and/or injury/mortality
reporting form by contacting the Southeast Regional Office at 727-824-
5312 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.
3. Southwest Region vessel or gear owners participating in Category
I or II fisheries listed in the final 2008 LOF (72 FR 66048, published
November 27, 2007) will receive their authorization certificate and/or
injury/mortality reporting form as described above in the integrated
MMPA registration process. A number of California state fisheries are
being re-categorized as Category II fisheries in this final rule, and
NMFS is working with the State of California to streamline the process
of registering vessel or gear owners participating in these fisheries
and issuing authorization certificates, as required under MMPA section
118. Fishermen may contact the Southwest Regional Office at 562-980-
4025 for more information. The Southwest Region plans to fully
integrate all California State Category I and II fisheries for the
2009/2010 fishing season.
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 their authorization certificates 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 animal that ingests fishing gear or any animal
that is released with fishing gear entangling, trailing, or perforating
any part of the body is considered injured, regardless of the presence
of any wound or other evidence of injury, and must be reported. Injury/
mortality reporting forms and instructions for submitting forms to NMFS
can be downloaded from: https://www.nmfs.noaa.gov/pr/pdfs/interactions/mmap_reporting_form.pdf. 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. 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 take reduction plans. 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-
35.
Sources of Information Reviewed for the Final 2009 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 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 2009 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), the final SARs for 2001 (67 FR 10671, March 8, 2002), the final
SARs for 2002 (68 FR 17920, April 14, 2003), the final SARs for 2003
(69 FR 54262, September 8, 2004), the final SARs for 2004 (70 FR 35397,
June 20, 2005), the final SARs for 2005 (71 FR 26340, May 4, 2006), the
final SARs for 2006 (72 FR 12774, March 19, 2007), the final SARs for
2007 (73 FR 21111, April 18, 2008), and the draft SARs for 2008 (73 FR
40299, July 14, 2008). The SARs are available at: https://www.nmfs.noaa.gov/pr/sars/.
Fishery Descriptions
NMFS described each Category I and II fishery on the 2008 LOF in
the final 2008 LOF (72 FR 66048, November 27, 2007). Below, NMFS
describes the fisheries classified as Category I or II fisheries on the
2009 LOF that were not so categorized on the 2008 LOF. Additional
details for Category I and II fisheries operating in U.S. waters are
[[Page 73036]]
included in the SARs, fishery management plans (FMPs), and take
reduction plans (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.
High Seas Atlantic Highly Migratory Species Fisheries
The Atlantic Highly Migratory Species (HMS) high seas fisheries are
virtually the same as fisheries targeting Atlantic HMS within U.S.
waters, but primarily use pelagic longline gear. Atlantic swordfish and
bigeye tuna are the primary target species on the high seas, with
Atlantic yellowfin, albacore and skipjack tunas, and pelagic sharks
also caught and retained for sale. Bluefin tuna are caught incidental
to pelagic longline operations, both on the high seas and within U.S.
waters, and may be retained subject to specific target catch
requirements.
Within U.S. Atlantic waters, HMS commercial fishers use several
gear types. Authorized gear for tuna include rod and reel, handlines,
bandit gear, harpoon, pelagic longline, trap (pound net and fish weir),
and purse seine. Purse seines used to target bluefin tuna must have a
mesh size of less than or equal to 4.5 in (11.4 cm) and at least 24-
count thread throughout the net. Only rod and reel gear may be used to
target billfish and commercial possession of Atlantic billfish is
prohibited. Authorized gear for sharks includes rod and reel, handline,
bandit gear, longline, and gillnet. Gillnets must be less than or equal
to 2.5 km (1.6 mi) in length and must remain attached to the vessel
except during net checks. Authorized gear for swordfish includes
handline, handgear (including buoy gear), and longline for north
Atlantic swordfish, and longline for south Atlantic swordfish. North
Atlantic swordfish incidentally taken in squid trawls may be retained
by federally permitted vessels. The fishery management area for
Atlantic HMS includes U.S. waters and the adjacent high seas.
Atlantic HMS are managed under regulations implementing the
Consolidated Atlantic HMS FMP (2006), under the authority of the MSA
and the Atlantic Tunas Convention Act (ATCA). Regulations issued under
the MSA address the target fish species, as well as bycatch of species
protected by the ESA, MMPA, and Migratory Bird Treaty Act. The MSA
regulations (50 CFR part 635) require vessel owners and operators
targeting Atlantic HMS with longline or gillnet gear to complete
protected species (sea turtles and marine mammals) safe handling,
release, and identification workshops. The regulations also require
shark dealers to complete an Atlantic shark identification workshop.
The high seas components of Atlantic HMS fisheries (Table 3) are
extensions of various Category I, II, and III fisheries operating in
U.S. waters (Table 2). The longline fishery targeting Atlantic HMS in
U.S. waters is the Category I, ``Atlantic Ocean, Caribbean, Gulf of
Mexico large pelagics longline fishery.'' NMFS has issued proposed
regulations to implement the Pelagic Longline Take Reduction Plan
(PLTRP) for this fishery (73 FR 35623, June 24, 2008). The gillnet
fishery targeting Atlantic HMS in U.S. waters is the Category II,
``Southeastern U.S. Atlantic shark gillnet'' fishery. In U.S. waters
only, this fishery is subject to the Bottlenose Dolphin TRP (BDTRP) (50
CFR 229.35), for coastal gillnetting only, and the Atlantic Large Whale
TRP (ALWTRP) (50 CFR 229.32). The purse seine fishery targeting
Atlantic HMS in U.S. waters is the Category III, ``Atlantic tuna purse
seine fishery.''
For more information on the Atlantic HMS fisheries and details on
the management and regulations of these fisheries, please see the
Consolidated Atlantic HMS FMP (https://www.nmfs.noaa.gov/sfa/hms/hmsdocument_files/FMPs.htm) and the regulations for Atlantic HMS
fisheries in 50 CFR part 635.
High Seas Pacific Highly Migratory Species Fisheries
The Pacific HMS high seas fisheries are virtually the same as
fisheries targeting Pacific HMS within U.S. waters. Pacific HMS
fisheries target tunas (North Pacific albacore, yellowfin, bigeye,
skipjack, and bluefin), billfish (striped marlin), sharks (common
thresher, pelagic thresher, bigeye thresher, shortfin mako, and blue),
swordfish, and dorado (i.e., dolphinfish) using several gear types.
Authorized gear include surface hook-and-line (including troll, rod and
reel, handline, albacore jig, and live bait), harpoon (non-mechanical),
drift gillnet (14 in (35.5 cm) stretch mesh or greater), pelagic
longline, and purse seine (including ring, drum, and lampara nets).
Pacific HMS incidentally caught by unauthorized gear may be landed
under certain circumstances. Species prohibited in Pacific HMS
fisheries include any salmon species, great white shark, basking shark,
megamouth shark, and Pacific halibut. The fishery management area for
Pacific HMS covers U.S. waters from the U.S.-Mexico border to the U.S.-
Canada border, and the adjacent high seas.
Pacific HMS are managed under regulations implementing the FMP for
U.S. West Coast Fisheries for HMS, adopted in April 2004. The MSA
regulations (50 CFR part 660, subpart K) address the target fish
species as well as species protected by the ESA and MMPA. The MSA
regulations lay out multiple restrictions for fishing for Pacific HMS
with longline gear. Vessels fishing longline gear may not target HMS
within U.S. waters. Targeting swordfish with shallow set longline gear
or possessing a light stick on board the vessel west of 150[deg] W.
long. and north of the equator is prohibited. From April 1-May 31,
longline gear is prohibited in the area bounded on the south by the
equator, north by 15[deg] N. lat., east by 145[deg] W. long., and west
by 180[deg] long. Longline vessels must have a valid protected species
workshop certificate onboard, along with safe handling and release
tools for sea turtles and seabirds. The use of shallow set longline
gear to target HMS east of 150[deg] W. long. is prohibited under a rule
promulgated through the ESA to protect threatened loggerhead sea
turtles.
Along with the MSA requirements, including area closures for marine
mammal and sea turtle protection, drift gillnet fishing for Pacific HMS
is managed under the MMPA through the Pacific Offshore Cetacean Take
Reduction Plan (POCTRP) (50 CRF 229.31), both in U.S. waters and on the
high seas. The POCTRP regulations require multiple gear modifications
during the May 1-January 31 fishing season, including a requirement
that all extenders (buoy lines) be at least 6 fathoms (36 ft; 10.9 m)
in length, all floatlines be fished at a minimum of 36 ft (10.9 m)
below the surface, and all nets have operational pingers to a water
depth of a least 100 fathoms (600 ft; 182.9 m). Also, after
notification from NMFS, all drift gillnet vessel operators must attend
skipper education workshops before each fishing season.
The high seas components of Pacific HMS fisheries are extensions of
various Category I, II, and III fisheries operating within U.S. waters
(Tables 1 and 2). The drift gillnet fishery targeting Pacific HMS
within U.S. waters, the Category I ``CA/OR thresher shark/swordfish
drift gillnet (>=14 in. mesh) fishery,'' is managed under the POCTRP.
The purse seine fishery targeting Pacific HMS within U.S. waters is the
Category II ``CA tuna purse seine fishery.'' While longline fishing for
Pacific HMS is prohibited within U.S. waters, the LOF includes the
Category II ``CA pelagic longline fishery'' to account for HMS caught
outside U.S. waters, but landed into the U.S. West coast. The troll
[[Page 73037]]
fishery targeting Pacific HMS within U.S. waters is the Category III
``AK North Pacific halibut, AK bottom fish, WA/OR/CA albacore,
groundfish, bottom fish, CA halibut non-salmonid troll fisheries.''
For more information on the Pacific HMS fisheries and details on
the management and regulations of these fisheries, please see the
Pacific HMS FMP (https://www.pcouncil.org/hms/hmsfmp.html#final), the
Pacific HMS FMP Biological Opinion (BiOp) (https://swr.nmfs.noaa.gov/HMS_FMP_Opinion_Final.pdf), and the regulations for Pacific HMS in
50 CFR part 660, subpart K.
High Seas Western Pacific Pelagic Fisheries
The Western Pacific pelagic high seas fisheries are virtually the
same as fisheries targeting Western Pacific pelagic species in U.S.
waters. Western Pacific pelagic fisheries target tunas (albacore,
bigeye, yellowfin, bluefin, and skipjack), billfish (Indo-Pacific blue
marlin, black marlin, striped marlin, shortbill spearfish), sharks
(pelagic thresher, bigeye thresher, common thresher, silky, oceanic
whitetip, blue, shortfin mako, longfin mako, and salmon), swordfish,
sailfish, wahoo, kawakawa, moonfish, pomfret, oilfish, and other tuna
relatives. The main gear types used to fish in the Western Pacific
Pelagic fisheries are pelagic longline, troll, and handline. The
Western Pacific Pelagic fisheries take place in the Western Pacific
Fishery Management Area (including waters shoreward of the EEZ boundary
around American Samoa, Guam, Hawaii, the Northern Mariana Islands,
Midway, Johnston and Palmyra Atolls, Kingman Reef, and Wake, Jarvis,
Baker, and Howland Islands) and the adjacent high seas waters.
Western Pacific Pelagic fisheries are managed under regulations
implementing the FMP for the Pelagic Fisheries of the Western Pacific
Region developed by the Western Pacific Fishery Management Council
(WPFMC). The MSA regulations (50 CFR part 665, subpart C) address
target fish species as well as bycatch of species protected under the
ESA, MMPA, and Migratory Bird Treaty Act. The MSA regulations outline
restrictions on effort, observer coverage requirements, longline
fishing prohibited areas, sea turtle and seabird bycatch mitigation
measures, annual fleetwide limits on interactions with leatherback and
loggerhead sea turtles, and a requirement for owners of longline
vessels to participate in annual protected species workshops. Drift
gillnet fishing in the fishery management area is prohibited, except
where authorized by an experimental fishery permit.
The high seas components of the Western Pacific Pelagic longline
fishery are extensions of the Category I ``HI deep-set (tuna target)
longline/set line fishery'' and the Category II ``HI shallow-set
(swordfish target) longline/set line fishery'' operating within U.S.
waters. All requirements for vessels fishing longline gear in these two
fisheries operating within U.S. waters remain effective in high seas
waters (as described in the above paragraph).
For more information on the Western Pacific Pelagic fisheries and
details on the management and regulations of these fisheries, please
see the Western Pacific Pelagic FMP BiOp (https://www.fpir.noaa.gov/Library/PUBDOCs/), the Western Pacific Pelagic FMP Environmental Impact
Statement (EIS) (https://www.fpir.noaa.gov/Library/PUBDOCs/), and the
regulations for Western Pacific Pelagic fisheries in 50 CFR 665,
subpart C.
High Seas South Pacific Albacore Troll Fisheries
The South Pacific albacore troll high seas fisheries target South
Pacific albacore using mostly longline or troll gear in waters solely
outside of any nation's EEZ. Longline gear, set with 1,000 or more
hooks suspended from a horizontally buoyed mainline several miles long,
accounts for 86 percent of the catch. Trolling vessels (including jigs
or live bait) attach 10-20 fishing lines of various lengths to the
vessel's outriggers on a slow-moving boat (5-6 knots). The total U.S.
catch of South Pacific albacore has accounted for less than 5 percent
of the total international catch in recent years.
U.S. vessels fish in the South Pacific albacore fishery from
November/December-April. Many vessels then participate in the larger
North Pacific albacore fishery from April-October. South Pacific
albacore fishing occurs outside any nation's EEZ in an area bounded by
approximately 110[deg] W. long. and 180[deg] W. long., and by 25[deg]
S. lat. and 45[deg] S. lat. Most U.S. troll vessels depart from the
U.S. West Coast or Hawaii and land catch in American Samoa, Fiji, or
Tahiti.
The South Pacific albacore troll fishery is not managed by
regulations implementing any FMP. The WPFMC and NMFS have concluded
that conservation and management measures for this fishery are not
warranted because the albacore stock in not overfished and there are no
known protected species interactions. Sea turtles and marine mammals do
not prey on the bait species used by these vessels and vessels are
typically slow-moving and would therefore likely be able to avoid a
collision with a large whale. As of 2001, the HSFCA requires U.S.
albacore troll vessel operators to file logbooks with NMFS for fishing
in the South Pacific.
For more information on the South Pacific albacore troll fishery,
please see the 2004 U.S. South Pacific albacore troll fishery
Environmental Assessment (EA) (https://www.fpir.noaa.gov/Library/PUBDOCs/).
High Seas South Pacific Tuna Fisheries
The South Pacific Tuna Treaty (SPTT) manages access of U.S. purse
seine vessels targeting tuna (skipjack and yellowfin) within the EEZs
of 16 Pacific Island Countries in the Western and Central Pacific Ocean
that are party to the Treaty. The SPTT Area includes the waters from
north of 60[deg] S. lat. and east of 90[deg] E. long. subject to the
fishing jurisdiction of Pacific Island parties to the Treaty, and all
waters within rhumb lines connecting multiple geographic coordinates,
and north along the 152[deg] E. long. out to Australia's EEZ border.
The Treaty Area includes portions of waters in the EEZs of most of the
Pacific Island Countries included in the Treaty. The SPTT was intended
to apply only to U.S. purse seine vessels; however, provisions have
been made to accommodate fishing by U.S. albacore tuna troll and U.S.
longline vessels within the Treaty Area. Both a SPTT and a HSFCA permit
are required to fish in SPTT waters.
Under the SPTT, observers are recruited from the Pacific Island
Countries and then trained and deployed by the Forum Fisheries Agency
(FFA) in Honiara in the Solomon Islands. Many of the FFA deployed
observers serve in and have experience from domestic observer programs
active in each observer's respective country. The target observer level
coverage is 20 percent of U.S. purse seine vessels, the full costs of
which are the responsibility of the U.S. purse seine vessel owners.
Observers collect a range of data, including a form for recording
information on interactions with seabirds, sea turtles, marine mammals,
and sharks. Fishery observers undergo training in species
identification for target and bycatch species; however, marine mammal
species identification has only recently been placed as a priority
matter for reporting. Observer data from January 1997-June 2002 show
that 11 sets resulted in interactions with marine mammals. However, the
data indicate only that the animals were ``unidentified whales, marine
mammals,
[[Page 73038]]
or dolphin/porpoise.'' The International Fisheries Division of the NMFS
Pacific Islands Region is working with the FFA observer program to
better train observers in marine mammal identification.
For additional information on the SPTT and details on the
management and regulations of these fisheries, see the South Pacific
Tuna Treaty EA (https://www.fpir.noaa.gov/Library/PUBDOCs/) and the
regulations for the SPTT in 50 CFR 300, subpart D.
High Seas Antarctic Living Marine Resources Fisheries
The Commission for the Conservation of Antarctic Marine Living
Resources (Convention or CCAMLR) conserves and manages Antarctic marine
living resources (AMLR) in waters surrounding Antarctica. The
Convention applies to AMLR in the waters from 60[deg] S. lat. south to
the Antarctic Convergence, with limited exceptions, covering 32.9
million square kilometers. Both an AMLR and a HSFCA permit are required
to fish in CCAMLR waters. There are multiple gear types used to target
multiple species in the Convention Area. Gear types include pelagic and
bottom trawl, trap/pot, gillnet, and longline. Target species include
krill and Antarctic finfish (rockcod species, toothfish species,
icefish species, silverfish, cod, and lanternfish), mollusks, and
crustaceans. CCAMLR Conservation Measures require or recommend several
measures for fisheries in the Convention area. Mandatory measures
include requirements for reporting; operating a Vessel Monitoring
System while in the Convention area; longline gear modifications to
reduce seabird interactions; and mesh sizes restrictions for trawl
gear. Recommendations include seal bycatch mitigation measures, such as
a seal excluder device in trawl fisheries.
CCAMLR has identified two types of scientifically trained observers
to collect information required in CCAMLR-managed fisheries, including
information on entanglements and incidental mortality of seabirds and
marine mammals. The first type of observer is a ``national observer,''
such as a U.S. observer placed on a U.S. vessel by the U.S. government.
The second type of observer is an ``international observer,'' or an
observer operating in accordance with bilateral arrangements between
the nation whose vessel is fishing and the nation providing the
observer. CCAMLR Conservation measures require all fishing vessels in
the Convention area (except vessels fishing for krill) to carry at
least one international observer and, where possible, an additional
observer. The United States requires all of its vessels fishing in the
CCAMLR area, for any target species and with any gear, to carry an
observer. In certain exploratory toothfish fisheries, the vessel must
carry two observers, with at least one being an international observer.
For additional information on the fishing activities in the CCAMLR
region and details on the management and regulations of these
fisheries, see the CCAMLR Programmatic EIS (https://www.nmfs.noaa.gov/sfa/domes_fish/news_of_note.htm#ccamlr), the CCAMLR Schedule of
Conservation Measures in Force (https://www.ccamlr.org), and the
regulations for the harvesting of AMLR in 50 CFR 300, subpart D.
CA Spot Prawn Pot Fishery
The Category II ``CA spot prawn pot fishery'' operates from Central
CA southward to the Mexican border. Strings of 10-50 oblong cylindrical
traps are commonly fished at depths usually greater than 100 fathoms.
This is a limited access fishery managed by the state of CA. A tiered
permit system allows a maximum of 150 or 500 traps to be fished at one
time depending on the fishing history associated with the permit. A
maximum of 300 traps may be located within state waters (inside 3
miles), regardless of the permit tier. North of Point Arguello, the
season is open from August 1-April 30. South of Point Arguello, the
season runs from February 1-October 30.
CA Dungeness Crab Pot Fishery
The Category II ``CA Dungeness crab pot fishery'' operates in the
central and northern coastal waters of CA in depths typically from 10-
40 fathoms. The cylindrical or rectangular pots used in the fishery are
fished singly, or individually, such that each pot has its own buoy;
although, fishing multiple traps connected together (called
``strings'') is allowed in the central region. There is no limit on the
number of traps which may be operated by a fisher at one time. This is
a limited access fishery managed by the state of CA and pursuant to the
Tri-State Committee agreement for Dungeness crab, which also includes
the states of OR and WA. The fishery is divided into two management
areas. The fishing season in the central region (south of the
Mendocino-Sonoma county line) is open November 15-June 30. The fishing
season in the northern region (north of the Mendocino-Sonoma county
line) can open on December 1, but may be delayed by the California
Department of Fish and Game based on the condition of market crabs, and
continues until July 15.
OR Dungeness Crab Pot Fishery
The Category II ``OR Dungeness crab pot fishery'' operates in the
coastal waters of OR in depths typically from 10-40 fathoms. The
cylindrical or rectangular pots used in the fishery are fished singly,
or individually, such that each pot has its own buoy. This is a limited
access fishery managed by the OR Department of Fish and Wildlife and
pursuant to the Tri-State Committee agreement for Dungeness crab, which
also includes the states of CA and WA. A three-tiered pot limitation
system, based on previous landing history, allows a maximum 200, 300,
or 500 single pots to be fished by a fisher at once. The Dungeness crab
season runs from December 1-August 14, although the Oregon Department
of Fish and Wildlife may delay the opening based on the condition of
the market crabs. Additionally, the state may close the season after
the end of May, if catch rates are still high, to protect molting crab.
Logbook reporting of effort and catch data to the state is required.
WA/OR/CA Sablefish Pot Fishery
The Category II ``CA/OR/WA sablefish pot fishery'' operates in
waters past the 100 fathom curve off the West coast of the U.S. In CA,
gear is set outside 150 fathoms, with an average depth of 190 fathoms.
There are two separate trap fisheries, open access and limited entry,
and both have quotas. Open access fishers will usually fish 1 to 8
strings of 3-4 pots, each with a float line and buoy stick. The gear
sometimes soaks for long periods. Fishers in the limited entry fishery
will normally fish 20-30 pot strings. As with most pot gear fished out
in deeper waters, sablefish traps are set in strings of multiple traps.
The fishery operates year round and effort varies from southern CA to
the Canadian border.
This fishery is managed under regulations implementing the West
Coast Groundfish FMP developed by Pacific Fishery Management Council.
Access to the limited entry fishery is granted under a limited entry
permit system, in addition to gear endorsements required by the
individual states. Open access privileges are currently available to
any fisher with the requisite state gear endorsement, but involve much
more restrictive limitations in catch quotas and additional area
closures than the primary limited entry permit. Open access quotas vary
based upon the area being fished. The limited entry fishery
[[Page 73039]]
is open from April 1-October 31, while open access is available year-
round. Limited entry permits are tiered based on the annual cumulative
landings allowed by each permit. Permits are transferable, but the tier
category remains fixed. Up to three limited entry permits may be
stacked on a single vessel.
Comments and Responses
NMFS received 10 comment letters on the proposed 2009 LOF (73 FR
33760, June 13, 2008). Comments were received from the Marine Mammal
Commission, Center for Biological Diversity (CBD), Western Pacific
Regional Fishery Management Council (WPFMC), Mid-Atlantic Fishery
Management Council (MAFMC), North Carolina Division of Marine Fisheries
(NCDMF), Oregon Department of Fish and Wildlife (ODFW), California
Department of Fish and Game (CDFG), Garden State Seafood Association,
Hawaii Longline Association (HLA), and California Wetfish Producers
Association. Comments on issues outside the scope of the LOF were
noted, but are not responded to in this final rule.
General Comments
Comment 1: The Marine Mammal Commission reiterated comments made on
the 2005 through 2008 LOFs recommending that NMFS describe the level of
observer coverage for each fishery as part of the LOF. NMFS indicated
in its response to the comments on the 2008 LOF that it ``feels that it
will be of limited use to include observer coverage data or percentages
in the LOF without also including the confidence associated with
mortality/serious injury estimates generated from the observer data.''
The Commission would welcome inclusion of information on mortality and
serious injury estimates within the LOF, as they recommended in
comments on the 2005 LOF that such information be included. The
Commission continues to believe observer coverage information is
important in itself, particularly for evaluating cases where no marine
mammal interactions are reported. Fisheries without recorded
interactions are not reported in the SARs and, without information on
observer coverage, it is impossible to determine 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.
Response: NMFS continues to feel that the LOF is not the
appropriate venue for reporting this data because it will confuse
rather than clarify if presented without all the associated information
supplied in the SARs. However, NMFS agrees 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 exploring other options for providing
information on observer coverage as it applies to the LOF and will
notify readers of these sources in subsequent LOFs. In addition, NMFS
is preparing to release the National Bycatch Report (NBR). The NBR will
provide a comprehensive summary of regional and national bycatch
estimates, based on observer data and fisher reports, of fish, marine
mammals, sea turtles, and sea birds in U.S. commercial fisheries that
have a Federal nexus. The NBR will include observer coverage
information that can be referenced while reviewing the 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 Resource's 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 2: The CBD noted that the proposed 2009 LOF lists over 40
fisheries that are known to interact with ESA-listed marine mammals.
Only one fishery, the Category I ``CA/OR thresher shark/swordfish drift
gillnet fishery,'' has authorization to take ESA-listed marine mammals.
Each of these other fisheries is therefore operating in violation of
both the ESA and MMPA. 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: CBD's comment refers to how NMFS authorizes takes of ESA-
listed marine mammals incidental to commercial fishing. The MMPA
requires fishers 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 fisher 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/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 or
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 in the process of making these determinations in various
fisheries on the LOF.
Comment 3: The CBD noted that the proposed 2009 LOF includes a
table of fisheries subject to take reduction teams (TRT). This is very
useful. However, numerous Category I and II fisheries not yet subject
to TRTs also meet the statutory criteria for convening such teams. All
Category I and II fisheries not yet subject to TRTs which interact with
strategic stocks must have TRTs promptly convened. The Hawaii pelagic
longline fishery should be the highest priority for such a team as take
continues to exceed PBR for false killer whales.
Response: Please see comment/response 6 in the final 2008 LOF (72
FR 66048, November 27, 2007). 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 or stocks whose level
of incidental mortality and serious injury exceeds PBR, those with a
small population size, and those which are declining most rapidly,
pursuant to MMPA section 118(f)(3).
Comment 4: The CBD stated concerns regarding groups of
``fisheries'' that NMFS has excluded from the LOF. In the final rule
implementing section 118 of the MMPA (60 FR 45086, August 20,
[[Page 73040]]
1995), NMFS concluded that tribal fisheries were exempt from the
permitting requirements the MMPA. In light of the subsequent holding of
the Ninth Circuit in Anderson v. Evans, 371 F.3d 475 (9th Cir. 2002)
finding that the MMPA applies to the Makah application to the gray
whale hunt, the CBD believes that NMFS' 1995 conclusion exempting
tribal fisheries from the LOF and the Section 118 authorization process
is no longer valid. The 2009 LOF should be amended to include tribal
fisheries.
Response: NMFS will consider this comment during the development of
future proposed LOFs.
Comment 5: The CBD does not believe aquaculture facilities are
properly considered commercial fishing operations eligible for the take
authorization contained in MMPA section 118. These facilities and
activities, to the degree they interact with marine mammals, should be
subject to the take prohibitions and permitting regimes contained in
MMPA section 101.
Response: 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
``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.''
Comment 6: The WPFMC continues to be concerned that no recreational
fishing activities are assessed under the LOF, although recreational
fisheries may have a much greater impact on marine mammal stocks than
their commercial counterparts. This seems a rather arbitrary
application of the MMPA to marine fisheries.
Response: NMFS agrees there are documented cases of incidental
injury or death of marine mammals in recreational fishing gear.
However, MMPA section 118 governs the ``Taking of Marine Mammals
Incidental to Commercial Fishing Operations.'' Specifically, section
118(c)(1)(A) directs NMFS to ``publish * * * list of commercial
fisheries'' that interact with marine mammals.
Comments on High Seas Fisheries
Comment 7: The CBD supported NMFS' decision to include high seas
fisheries on the LOF, but they have concerns with how NMFS is
implementing the process. NMFS treats fisheries that have both a high
seas and within-EEZ component as two separate fisheries for LOF
purposes. CBD believes this raises 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),
therefore resulting in an underestimation of the true environmental
effect, and LOF classification of what is more properly considered the
same fishery. For example, if the total take from a fishery operating
both in and outside the EEZ is 60 percent of PBR, the fishery should be
a Category I. However, if the fishery is split into two components and
take is evenly apportioned, the total take from each fishery is only 30
percent of PBR, and therefore a Category II. NMFS must clarify how it
will apportion take so as to not create this problem.
Response: Although the high seas components of fisheries that
operate both within U.S. waters and on the high seas are listed in a
separate table in the LOF, they are not considered separate fisheries
from their associated components operating in U.S. waters. Instead,
NMFS considers these fisheries as the same fishery that has extended
beyond the 200 nmi boundary of the EEZ. Because of the organization and
format of Tables 1 and 2 in the LOF, and because high seas fisheries
have additional management (permit) requirements, it is necessary to
list them on a separate table on the LOF (Table 3). NMFS clarifies
which fisheries in Table 3 are extensions of fisheries operating in
U.S. waters by placing a ``*'' after the fishery name. NMFS will