Magnuson-Stevens Act Provisions; Fisheries off West Coast States; Pacific Coast Groundfish Fishery; Biennial Specifications and Management Measures for the 2013 Tribal and Non-Tribal Fisheries for Pacific Whiting, 26526-26539 [2013-10806]
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Federal Register / Vol. 78, No. 88 / Tuesday, May 7, 2013 / Rules and Regulations
in South Carolina and Georgia were near
zero in 2011, representing a negligible
proportion of the total bluefish landings
along the Atlantic Coast. Therefore, this
analysis assumed that no vessel activity
for these two states took place in 2011.
In recent years, approximately 2,000
party/charter vessels may have been
active in the bluefish fishery and/or
have caught bluefish.
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Description of Projected Reporting,
Recordkeeping, and Other Compliance
Requirements
No additional reporting,
recordkeeping, or other compliance
requirements are included in this final
rule.
Description of the Steps Taken To
Minimize Economic Impact on Small
Entities
Specification of commercial quota,
recreational harvest levels, and
possession limits is constrained by the
conservation objectives of the FMP,
under the authority of the MagnusonStevens Act. The 2013 commercial
quota contained in this final rule is 12
percent lower than the 2012 quota, but
significantly higher than actual 2012
bluefish landings. All affected states
will receive decreases in their
individual commercial quota allocation
in comparison to their respective 2012
individual state allocations. However,
the magnitude of the increase varies
depending on the state’s relative percent
share in the total commercial quota, as
specified in the FMP. The 2014
commercial quota contained in this final
rule is 4 percent lower than the 2013
quota.
The 2013 and 2014 RHL contained in
this final rule is approximately 19
percent lower than the RHL in 2012.
The 2013 and 2014 RHL is the same as
the total estimated recreational bluefish
harvest for 2013 and 2014, and therefore
it does not constrain recreational
bluefish harvest below a level that the
fishery is anticipated to achieve. The
possession limit for bluefish will remain
at 15 fish per person, so there should be
no impact on demand for party/charter
vessel fishing and, therefore, no impact
on revenues earned by party/charter
vessels. No negative economic impacts
on the recreational fishery are
anticipated.
The impacts on revenues associated
with the proposed RSA quota were
analyzed and are expected to be
minimal. Assuming that the full RSA
quota 715,819 lb (325 mt) for 2013 and
703,385 lb (319 mt) for 2014 is landed
and sold to support the proposed
research projects, then all of the
participants in the fishery would benefit
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from the improved fisheries data
yielded from each project.
Small Entity Compliance Guide
Section 212 of the Small Business
Regulatory Enforcement Fairness Act of
1996 states that, for each rule or group
of related rules for which an agency is
required to prepare a FRFA, the agency
shall publish one or more guides to
assist small entities in complying with
the rule, and shall designate such
publications as ‘‘small entity
compliance guides.’’ The agency shall
explain the actions a small entity is
required to take to comply with a rule
or group of rules. As part of this
rulemaking process, a small entity
compliance guide will be sent to all
holders of Federal permits issued for the
Atlantic bluefish fishery.
In addition, copies of this final rule
and guide (i.e., permit holder letter) are
available upon request, and posted on
the Northeast Regional Office’s Web site
at www.nero.noaa.gov.
Authority: 16 U.S.C. 1801 et seq.
Dated: May 2, 2013.
Alan D. Risenhoover,
Director, Office of Sustainable Fisheries,
performing the functions and duties of the
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
[FR Doc. 2013–10805 Filed 5–6–13; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 660
[Docket No. 130114034–3422–02]
RIN 0648–BC93
Magnuson-Stevens Act Provisions;
Fisheries off West Coast States;
Pacific Coast Groundfish Fishery;
Biennial Specifications and
Management Measures for the 2013
Tribal and Non-Tribal Fisheries for
Pacific Whiting
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
SUMMARY: NMFS issues this final rule
for the 2013 Pacific whiting fishery
under the authority of the Pacific Coast
Groundfish Fishery Management Plan
(FMP), the Magnuson Stevens Fishery
Conservation and Management Act
(Magnuson-Stevens Act), and the Pacific
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Whiting Act of 2006. This final rule
establishes the tribal allocation of
63,205 metric tons of Pacific whiting for
2013, and final allocations of Pacific
whiting to the non-tribal fishery for
2013.
DATES: Effective May 7, 2013.
FOR FURTHER INFORMATION CONTACT:
Kevin C. Duffy (Northwest Region,
NMFS), phone: 206–526–4743, fax: 206–
526–6736 and email:
kevin.duffy@noaa.gov.
SUPPLEMENTARY INFORMATION:
Electronic Access
This final rule is accessible via the
Internet at the Office of the Federal
Register Web site at https://
www.federalregister.gov. Background
information and documents are
available at the NMFS Northwest Region
Web site at https://www.nwr.noaa.gov/
fisheries/management/whiting/
pacific_whiting.html and at the Pacific
Fishery Management Council’s Web site
at https://www.pcouncil.org/.
Copies of the final environmental
impact statement (FEIS) for the 2013–
2014 Groundfish Specifications and
Management Measures are available
from Donald McIsaac, Executive
Director, Pacific Fishery Management
Council (Council), 7700 NE Ambassador
Place, Portland, OR 97220, phone: 503–
820–2280.
Background
This rule announces the Total
Allowable Catch (TAC) for whiting,
expressed in metric tons (mt). This is
the second year that the TAC for Pacific
whiting is being determined under the
terms of Agreement with Canada on
Pacific Hake/Whiting (the Agreement)
and the Pacific Whiting Act of 2006 (the
Whiting Act), 16 U.S.C. 7001–7010. The
Agreement and the Act establish
bilateral bodies to implement the terms
of the Agreement, each with various
responsibilities, including: The Joint
Management Committee (JMC), which is
the decision-making body; the Joint
Technical Committee (JTC), which
conducts the stock assessment; the
Scientific Review Group (SRG), which
reviews the stock assessment; and the
Advisory Panel (AP), which provides
stakeholder input to the JMC (The
Agreement, Art. II–IV; 16 U.S.C. 7001–
7005). The Agreement establishes a
default harvest policy (F–40 percent
with a 40/10 adjustment) and allocates
73.88 percent of the TAC to the United
States and 26.12 percent of the TAC to
Canada. The bilateral JMC is primarily
responsible for developing a TAC
recommendation to the Parties (United
States and Canada). The Secretary of
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Commerce, in consultation with the
Secretary of State, has the authority to
accept or reject this recommendation.
The Joint Technical Committee (JTC)
met three times over the last six months
to prepare the 2013 stock assessment for
Pacific hake (whiting). The assessment
presents a single base-case model using
nine years of an acoustic survey biomass
index as well as catches to estimate the
scale of the current hake stock. The
2012 acoustic-trawl survey result was a
relative biomass 1,380,000 mt, an
increase of 2.5 times the 2011 survey
biomass of 521,000 mt, which is the
lowest in the time series. The agecomposition data from the aggregated
fisheries (1975–2012) and the acoustic
survey contribute to the assessment
model’s ability to resolve strong and
weak cohorts. The survey and the
fishery were dominated by age 2 (63.7
percent survey; 34.6 percent fishery)
and 4 (16.1 percent survey; 34.5
percent) year old fish from the 2010 and
2008 year classes, with differences due
to the different selectivity of young fish
to the survey vs. the fishery. Both
sources indicate a strong 2008 cohort in
the 2011 and 2012 data (age 4 hake), and
a strong 2010 cohort in the 2012 data
(age 2 hake), which may partially
explain the recent increase in the survey
index.
The median estimated female biomass
is 1,503,000 mt at the beginning of 2013
and is expected to be stable to
increasing through 2015 due to an
expected very large 2010 year class and
the above average 2008 year class. This
level of estimated spawning biomass has
not been seen since 1993. The 2012
survey verified the strength of the 2008
year class and finds that the 2010 year
class seems even stronger, but there is
uncertainty in the 2010 year class
strength because it has only been
observed once by the survey. Agreement
between the most recent acoustic survey
and commercial fishery age composition
data as well as the most recent acoustic
survey biomass index engenders greater
confidence in the 2013 assessment
estimates than if there was no survey
data from 2012.
Until cohorts are five or six years old,
the model’s ability to resolve cohort
strength is poor. For many of the recent
above average cohorts (2005, 2006, and
2008), the size of the year class was
overestimated when it was age 2,
compared to updated estimates as the
cohort aged and more observations were
available from the fishery and survey.
Given that there is some uncertainty in
the estimate of the 2010 year class, and
that the size of this year class has a
strong effect on a projected 2013 catch,
the JTC developed additional forecast
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decision tables reflecting a low,
medium, and high range of recruitment
for the 2010 year class. Using the more
conservation-minded low-recruitment
state of nature, there is an equal
probability that the spawning stock
biomass in 2014 will be less or greater
than the spawning biomass in 2013 with
a catch between 300,000 and 350,000
mt. There is an equal probability that
the spawning biomass will be below 40
percent of unfished equilibrium
spawning biomass with a 2013 catch
near 400,000 mt.
The JTC provided tables showing the
outcome and probabilities of various
events under different catch alternatives
for 2013. For the base case median
recruitment, the probability that the
spawning stock biomass in 2014
remains above the 2013 level is 50
percent with a catch of 603,000 mt, the
probability that the fishing intensity is
above target in 2013 is 50 percent with
a catch of 626,364 mt, and the
probability that the predicted 2014
catch target is the same as a set value
in 2013 is 50 percent for a set value of
696,000 mt in 2013. There is a less than
12 percent probability that the spawning
stock biomass will drop below 40
percent in 2014 for all catch levels
considered. This information indicates
probabilities at projected catch levels
that were significantly higher than the
TAC levels recommended by the JMC,
reinforcing the conservative nature of
the proposed fishing regime in 2013.
The two cohorts that will likely be
supporting the 2013 fishery will be ages
3 and 5. Cohorts in this age range are
near their peak biomass and potential
maximum contribution to lifetime yield.
Because of this, an argument could be
made to fish the stock harder because
the contribution to the population from
these age classes will start to decline in
future years. However, there is still
considerable risk in fishing them too
hard until the absolute size of these
cohorts is verified, particularly the 2010
year class, which is still very young and
thus not yet well characterized. A
conservative estimate of the 2010 year
class strength (using only the lower 10
percent of the model estimated
recruitment) reduces the strength from a
median estimate of 11.6 billion recruits
(a near record size) to 6.9 billion
recruits, which is near the size of the
1970 and 1999 recruitments.
The Scientific Review Group (SRG)
met in Vancouver, British Columbia, on
February 19–22, 2013, to review the
draft stock assessment document
prepared by the JTC. The SRG endorsed
the assessment and recommended that it
be used for management advice. Along
with the JTC, the SRG recommended
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(for consideration by the JMC) a range
of 336,000—626,000 mt as plausible
harvest levels in 2013. The upper end
would implement the default harvest
policy in the Agreement and would
allow some continued biomass growth
into 2014 if the current assessment
result is accurate. The lower level, using
only the lower 10 percent of the model
estimated recruitment, would still not
exceed the harvest policy even if the
2010 year class is only 51 percent of its
current estimate.
At its March 18–19, 2013 meeting, the
JMC reviewed the advice of the JTC,
SRG, and AP, and agreed on a TAC
recommendation for transmittal to the
Parties. The JMC focused on the
conservative estimate of the 2010 year
class strength (using only the lower 10
percent of the model estimated
recruitment) and the SRG suggested
target catch of 336,200 mt, based
primarily on concerns that this lower
bound may indeed reflect the true state
of nature. This conservative approach
resulted in a TAC recommendation of
336,200 mt, with adjustments upwards
for uncaught Pacific whiting in 2012, as
allowed by the Agreement, for a
coastwide adjusted TAC of 365,112 mt
for 2013. The TAC recommendation is
expected to sustain the offshore hake/
whiting resource in the event that the
2010 year class is not as large as
expected, while still allowing a
substantial increase in TAC compared to
2012.
The recommendation for an adjusted
United States TAC of 269,745 mt for
2013 (73.88 percent of the coastwide
TAC) is consistent with the best
available science, provisions of the
Agreement, and the Whiting Act. The
recommendation was transmitted via
letter to the Parties on March 19, 2013.
NMFS, under delegation of authority
from the Secretary of Commerce,
approved the TAC recommendation of
269,745 mt for U.S. fisheries on April
15, 2013.
Tribal Fishery Allocation
This final rule establishes the tribal
allocation of Pacific whiting for 2013.
NMFS issued a proposed rule for the
allocation and management of the 2013
tribal Pacific whiting fishery on March
5, 2013 (78 FR 14259). This action
finalizes the allocation and management
measures.
Since 1996, NMFS has been allocating
a portion of the U.S. TAC of Pacific
whiting to the tribal fishery using the
process established in 50 CFR
660.50(d)(1). According to the formula
found in that section, the tribal
allocation is subtracted from the total
U.S. Pacific whiting TAC and the
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remainder, less a deduction of 2,500 mt
for research and bycatch in nongroundfish fisheries (for 2013 only), is
allocated to the non-tribal sectors. The
tribal Pacific whiting fishery is managed
separately from the non-tribal whiting
fishery, and is not governed by the
limited entry or open access regulations
or allocations.
The proposed rule described the tribal
allocation as 17.5 percent of the U.S.
TAC plus 16,000 mt, and projected a
range of potential tribal allocations for
2013 based on a range of U.S. TACs over
the last ten years, 2003 through 2012.
This range of TACs is 148,200 mt (2003)
to 290,903 mt (2011). The resulting
range of potential tribal allocations is
41,935 mt to 66,906 mt.
As described earlier in this preamble,
the U.S. TAC for 2013 is 269,745 mt.
Applying the formula at 50 CFR
660.50(d)(1), NMFS calculated that the
tribal allocation implemented by this
final rule is 63,205 mt (17.5 percent of
the U.S. TAC or 47,205 mt, plus 16,000
mt). While the total amount of whiting
to which the Tribes are entitled under
their treaty right has not yet been
determined, and new scientific
information or discussions with the
relevant parties may impact that
decision, the best available scientific
information to date suggests that 63,205
mt (23 percent of the 2013 U.S. TAC) is
within the likely range of potential
treaty right amounts.
As with prior tribal whiting
allocations, this final rule is not
intended to establish any precedent for
future Pacific whiting seasons, or for the
determination of the total amount of
whiting to which the Tribes are entitled
under their treaty right. Rather, this rule
adopts an interim allocation, pending
the determination of the total treaty
amount. That amount will be based on
further development of scientific
information and additional coordination
and discussion with and among the
coastal tribes and States of Washington
and Oregon. The process of determining
that amount, begun in 2008, is
continuing.
Non-Tribal Allocations
This final rule establishes the nontribal allocation for the Pacific whiting
fishery. The non-tribal allocation was
not included in the tribal whiting
proposed rule published on March 5,
2013 (78 FR 14259) for two reasons
related to timing and process. First, a
recommendation on the coastwide TAC
for Pacific whiting for 2013, under the
terms of the Agreement with Canada,
was not available until March 19, 2013.
This recommendation for a U.S. TAC
was approved by NMFS, under
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delegation of authority from the
Secretary of Commerce, on April 15,
2013. Second, the non-tribal allocation
is established after deductions from the
U.S. TAC for the tribal allocation
(63,205 mt) and set asides for research
and incidental catch in non-groundfish
fisheries (2,500 mt). The non-tribal
allocation is therefore being finalized in
this rule.
The 2013 fishery harvest guideline
(HG) for Pacific whiting is 204,040 mt.
This amount was determined by
deducting from the total U.S. TAC of
269,745 mt, the 63,205 mt tribal
allocation, along with 2,500 mt for
research catch and bycatch in nongroundfish fisheries. Regulations at 50
CFR 660.55 (f)(2) allocate the fishery HG
among the non-tribal catcher/processor,
mothership, and shorebased sectors of
the Pacific whiting fishery. The catcher/
processor sector is allocated 34 percent
(69,373 mt for 2013), the mothership
sector is allocated 24 percent (48,970 mt
for 2013), and the shorebased sector is
allocated 42 percent (85,697 mt for
2013). The fishery south of 42° N. lat.
may not take more than 4,284 mt (5
percent of the shorebased allocation)
prior to the start of the primary Pacific
whiting season north of 42° N. lat.
The 2013 allocations of Pacific Ocean
perch, canary rockfish, darkblotched
rockfish, and widow rockfish to the
whiting fishery were published in a
final rule on January 3, 2013 (78 FR
580). The allocations to the Pacific
whiting fishery for these species are
described in the footnotes to Table 1.b
To Part 660, Subpart C–2013.
Comments and Responses
On March 5, 2013, NMFS issued a
proposed rule for the allocation and
management of the 2013 tribal Pacific
whiting fishery. The comment period on
the proposed rule closed on April 4,
2013. During the comment period,
NMFS received two letters of comment.
The U.S. Department of Interior
submitted a letter of ‘‘no comment’’
associated with their review of the
proposed rule.
A letter was received from a
commercial fishing organization. In
their letter, they state that given past
performance in the tribal fishery, the
lack of demonstrable fishery operations
from the Quileute tribe, and the
potential economic harm to the nontribal fishery, the proposed tribal
whiting set aside is too high. They state
that the proposed tribal whiting set
aside for 2013 is not justified by past
fishery performance, and fails in
striking an appropriate balance of the
treaty rights of the tribes against the
Agency’s obligation to achieve optimum
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yield. They suggest that NMFS:
Establish a realistic 2013 tribal whiting
set aside that is bolstered by fishery
plans from each tribe; and aptly and
effectively exercise its reapportionment
authority.
Response: In determining the tribal
allocation, NMFS must ensure that the
tribes have the opportunity to exercise
their treaty right, which is ‘‘other
applicable law’’ under the MagnusonStevens Act. As noted above, the
amount requested by the tribes appears
to be within the amount to which they
are entitled by treaty, as suggested by
the best available science. Although the
allocation to the tribal fishery in 2013 is
a higher allocation amount than 2012
(63,205 mt versus 48,556 mt), the
percent of the TAC allocated to the
tribes in 2013 represents approximately
23 percent of the U.S. TAC, versus 26
percent of the U.S. TAC in 2012.
As the commenter has noted, the
reapportionment process is available to
NMFS to address the situation in which
the tribes are unable to use their full
allocation. NMFS will monitor both the
tribal and non-tribal fishery during the
season, and will remain in contact with
tribal representatives in order to
determine, to the extent practicable, the
likely harvest levels in the tribal fishery.
If circumstances supporting
reapportionment under NMFS’
regulations arise, NMFS will be
prepared to expeditiously reapportion
Pacific whiting from the tribal to the
non-tribal sector, in order to manage the
fishery in a manner consistent with both
the implementation of the tribal treaty
right and the Magnuson Stevens Act
requirements.
Classification
The final Pacific whiting
specifications and management
measures for 2013 are issued under the
authority of the Magnuson-Stevens
Fishery Conservation and Management
Act (MSA), and the Pacific Whiting Act
of 2006, and are in accordance with 50
CFR part 660, subparts C through G, the
regulations implementing the Pacific
Coast Groundfish Fishery Management
Plan (PCGFMP). NMFS has determined
that this rule is consistent with the
national standards of the MagnusonStevens Act and other applicable laws.
NMFS, in making the final
determination, took into account the
data, views, and comments received
during the comment period.
NMFS has determined that the tribal
whiting fishery, conducted off the coast
of the State of Washington, is consistent,
to the maximum extent practicable, with
the approved coastal zone management
program of the States of Washington and
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Oregon. NMFS has also determined that
the Pacific whiting fishery, both tribal
and non-tribal, is consistent, to the
maximum extent practicable, with
approved coastal zone management
programs for the States of Washington
and Oregon. The State of Washington
submitted a letter of concurrence on
February 25, 2013. The State of Oregon
did not respond and consistency is
inferred.
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Administrative Procedure Act
Pursuant to 5 U.S.C. 553(b)(B), the
NMFS Assistant Administrator finds
good cause to waive prior public notice
and comment and delay in effectiveness
the 2013 annual harvest specifications
for Pacific whiting, as delaying this rule
would be contrary to the public interest.
The annual harvest specifications for
Pacific whiting must be implemented by
the start of the main primary Pacific
whiting season, which begins on May
15, 2013, or the primary whiting season
will effectively remain closed.
Every year, NMFS conducts a Pacific
whiting stock assessment in which U.S.
and Canadian scientists cooperate. The
2013 stock assessment for Pacific
whiting was prepared in early 2013, as
the new 2012 data—including updated
total catch, length and age data from the
U.S. and Canadian fisheries, and
biomass indices from the Joint U.S.Canadian acoustic/midwater trawl
surveys—were not available until
January, 2013. Because of this late
availability of the most recent data for
the assessment, and the need for time to
conduct the treaty process for
determining the TAC using the most
recent assessment, it would not be
possible to allow for notice and
comment before the start of the primary
Pacific whiting season on May 15.
A delay in implementing the Pacific
whiting harvest specifications to allow
for notice and comment would be
contrary to the public interest because it
would require either a shorter primary
whiting season or development of a
TAC without the most recent data. A
shorter season could prevent the tribal
and non-tribal fisheries from attaining
their 2013 allocations, which would
result in unnecessary short-term adverse
economic effects for the Pacific whiting
fishing vessels and the associated
fishing communities. A TAC
determined without the most recent
data could fail to account for significant
fluctuations in the biomass of this
relatively short-lived species. To
prevent these adverse effects and to
allow the Pacific whiting season to
commence, it is in the public interest to
waive prior notice and comment.
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In addition, pursuant to 5 U.S.C.
553(d)(3), the NMFS Assistant
Administrator finds good cause to waive
the 30-day delay in effectiveness.
Waiving the 30-day delay in
effectiveness will not have a negative
impact on any entities, as there are no
new compliance requirements or other
burdens placed on the fishing
community with this rule. Failure to
make this final rule effective at the start
of the fishing year will undermine the
intent of the rule, which is to promote
the optimal utilization and conservation
of Pacific whiting. It would also serve
the best interests of the public because
it will allow for the longest possible
Pacific whiting fishing season and
therefore the best possible economic
outcome for those whose livelihoods
depend on this fishery. Because the 30day delay in effectiveness would
potentially cause significant financial
harm without providing any
corresponding benefits, this final rule is
made effective May 7, 2013.
The preamble to the proposed rule
and this final rule serve as the small
entity compliance guide required by
Section 212 of the Small Business
Regulatory Enforcement Fairness Act of
1996. This action does not require any
additional compliance from small
entities that is not described in the
preamble. Copies of this final rule are
available from NMFS at the following
Web site: https://www.nwr.noaa.gov/
fisheries/management/whiting/
pacific_whiting.html.
Rulemaking must comply with
Executive Order (EO) 12866 and the
Regulatory Flexibility Act (RFA). The
Office of Management and Budget has
determined that this final rule is not
significant for purposes of Executive
Order 12866.
The NMFS Economic Guidelines that
describe the RFA and EO 12866 can be
found at https://www.nmfs.noaa.gov/sfa/
domes_fish/EconomicGuidelines.pdf
The RFA can be found at https://
www.archives.gov/federal-register/laws/
regulatory-flexibility/
Executive Order 12866 can be found
at https://www.plainlanguage.gov/
populartopics/regulations/eo12866.pdf
When an agency proposes regulations,
the RFA requires the agency to prepare
and make available for public comment
an Initial Regulatory Flexibility Act
(IRFA) document that describes the
impact on small businesses, non-profit
enterprises, local governments, and
other small entities. The IRFA is to aid
the agency in considering all reasonable
regulatory alternatives that would
minimize the economic impact on
affected small entities. After the public
comment period, the agency prepares a
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Final Regulatory Flexibility Analysis
(FRFA) that takes into consideration any
new information and public comments.
This FRFA incorporates the IRFA, a
summary of the significant issues raised
by the public comments, NMFS’
responses to those comments, and a
summary of the analyses completed to
support the action. NMFS published the
proposed rule on March 5, 2013 78 FR
14259, with a comment period through
April 4, 2013. An IRFA was prepared
and summarized in the Classification
section of the preamble to the proposed
rule. The description of this action, its
purpose, and its legal basis are
described in the preamble to the
proposed rule and are not repeated here.
The FRFA describes the impacts on
small entities, which are defined in the
IRFA for this action and not repeated
here. Analytical requirements for the
FRFA are described in Regulatory
Flexibility Act, section 304(a)(1)
through (5), and summarized below.
The FRFA must contain: (1) A succinct
statement of the need for, and objectives
of, the rule; (2) A summary of the
significant issues raised by the public
comments in response to the initial
regulatory flexibility analysis, a
summary of the assessment of the
agency of such issues, and a statement
of any changes made in the proposed
rule as a result of such comments; (3) A
description and an estimate of the
number of small entities to which the
rule will apply, or an explanation of
why no such estimate is available; (4) A
description of the projected reporting,
recordkeeping and other compliance
requirements of the rule, including an
estimate of the classes of small entities
which will be subject to the requirement
and the type of professional skills
necessary for preparation of the report
or record; and (5) A description of the
steps the agency has taken to minimize
the significant economic impact on
small entities consistent with the stated
objectives of applicable statutes,
including a statement of the factual,
policy, and legal reasons for selecting
the alternative adopted in the final rule
and why each one of the other
significant alternatives to the rule
considered by the agency which affect
the impact on small entities was
rejected.
This rule establishes the 2013 harvest
specifications for Pacific whiting and
the allocation of Pacific whiting for the
tribal whiting fishery. This rule
establishes the initial 2013 Pacific
whiting allocations for the tribal fishery
and the non-tribal sectors (catcher/
processor, mothership, and shoreside),
and the amount of Pacific whiting set
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aside for research and incidental catch
in other fisheries.
In 2012, the total estimated catch of
whiting by tribal and non-tribal
fishermen was 162,000 mt, or 87 percent
of the U.S. TAC (186,037 mt). There was
a late fall reapportionment of 28,000 mt
of Pacific whiting from the tribal to nontribal sectors. The tribal harvest was less
than 1,000 mt, approximately 3 percent
of the final tribal allocation of 20,556
mt. In total, non-tribal sectors harvested
97 percent of the final non-tribal
allocation of 163,381 mt. This rule
increases the U.S. TAC for 2013 to
269,745 mt, and the tribal allocation
will increase to 63,205 mt. After setting
aside 2,500 mt for research catch and
bycatch in non-groundfish fisheries, the
overall non-tribal allocation for 2013 is
204,040 mt. The non-tribal allocation is
28 percent higher than the 2012 nontribal catch. In 2012, total Pacific
whiting ex-vessel revenues earned by
tribal and non-tribal fisheries reached
about $50 million. If the 2013 TAC is
entirely harvested, projected ex-vessel
revenues would reach $83 million,
based on 2012 ex-vessel prices. (Note
that ex-vessel revenues do not take into
account wholesale or export revenues or
the costs of harvesting and processing
whiting into a finished product.)
There were no significant issues
raised by the public comments in
response to the IRFA. However, there
was one comment that referred to small
entities. Noting that the highest annual
tribal catch has been 34,500 mt, one
association representing large fishing
companies commented that the
proposed tribal allocation is too high.
They suggested that NMFS should be
more effective in reapportioning tribal
whiting to minimize the amount of
whiting stranded, as the reapportioning
process allows unharvested tribal
allocations to be fished by non-tribal
fleets, benefitting both large and small
businesses. The association also
suggested that pre-season plans be
required from the tribes. A detailed
response to these comments is included
in the comment and response section of
this final rule.
This rule establishes a tribal
allocation of 63,205 mt. This allocation
is based on NMFS consultations with
the tribes upon which tribes discuss
their plans with NMFS. This allocation
amount is within the long-term tribal
treaty right to harvest. Applicable law
requires NMFS to provide the tribes
with the opportunity to harvest their
treaty right. Should reapportionment in
late fall be warranted, after discussions
with the tribes, NMFS will determine
the appropriate amount of fish to
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provide to the non-tribal fleets in
accordance with applicable law.
It should be also noted that under
Agreement with Canada on Pacific
Hake/Whiting, as described in 77 FR
28501 (May 15, 2012), unharvested fish
are not necessarily ‘‘stranded.’’ If at the
end of the year, there are unharvested
allocations, there are provisions for an
amount of these fish to be carried over
into the next year’s allocation process.
‘‘If, in any year, a Party’s catch is less
than its individual TAC, an amount
equal to the shortfall shall be added to
its individual TAC in the following
year, unless otherwise recommended by
the JMC. Adjustments under this subparagraph shall in no case exceed 15
percent of a Party’s unadjusted
individual TAC for the year in which
the shortfall occurred.’’ Such an
adjustment was made for the 2013
fishery under the Agreement: This
adjustment resulted in 7,552 mt being
added to the Canadian share, for an
adjusted Canadian TAC of 95,367 mt,
and 21,360 mt being added to the
United States share, for an adjusted
United States TAC of 269,745 mt. This
results in a coastwide adjusted TAC of
365,112 mt for 2013.
Under the RFA, the term ‘‘small
entities’’ includes small businesses,
small organizations, and small
governmental jurisdictions. The Small
Business Administration (SBA) has
established size criteria for all major
industry sectors in the United States,
including fish harvesting and fish
processing businesses. A business
involved in fish harvesting is a small
business if it is independently owned
and operated and not dominant in its
field of operation (including its
affiliates) and if it has combined annual
receipts not in excess of $4.0 million for
all its affiliated operations worldwide. A
seafood processor is a small business if
it is independently owned and operated,
not dominant in its field of operation,
and employs 500 or fewer persons on a
full time, part-time, temporary, or other
basis, at all its affiliated operations
worldwide. A business involved in both
the harvesting and processing of seafood
products is a small business if it meets
the $4.0 million criterion for fish
harvesting operations. A wholesale
business servicing the fishing industry
is a small business if it employs 100 or
fewer persons on a full time, part time,
temporary, or other basis, at all its
affiliated operations worldwide. For
marinas and charter/party boats, a small
business is one with annual receipts not
in excess of $7.0 million. The RFA
defines small organizations as any
nonprofit enterprise that is
independently owned and operated and
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is not dominant in its field. The RFA
defines small governmental
jurisdictions as governments of cities,
counties, towns, townships, villages,
school districts, or special districts with
populations of less than 50,000.
This final rule affects how whiting is
allocated to the following sectors/
programs: Tribal, Shorebased Individual
Fishing Quota (IFQ) Program—Trawl
Fishery, Mothership Coop (MS)
Program—Whiting At-sea Trawl
Fishery, and Catcher-Processor (C/P)
Coop Program—Whiting At-sea Trawl
Fishery. The amount of whiting
allocated to these sectors is based on the
U.S. TAC. From the U.S. TAC, small
amounts of whiting that account for
research catch and for bycatch in other
fisheries are deducted. The amount of
the tribal allocation is also deducted
directly from the TAC prior to
allocations to the non-tribal sectors. The
remainder is the commercial harvest
guideline. This guideline is then
allocated among the other three sectors
as follows: 34 percent for the C/P Coop
Program; 24 percent for the MS Coop
Program; and 42 percent for the
Shorebased IFQ Program.
The shorebased IFQ fishery is
managed with individual fishing quotas
for most groundfish species, including
whiting. Annually, quota pounds (QP)
are allocated from the shorebased sector
allocation based on the individual quota
shares (QS) of each QS owner. (QP is
expressed as a weight and QS is
expressed as a percent of the shorebased
allocation for a given species or species
group.). Quota pounds (QP) may be
transferred from a QS account to a
vessel account or from one vessel
account to another vessel account.
Vessel accounts are used to track how
QP is harvested as QP is to cover catch
(landings and discards) by limited entry
trawl vessels of all IFQ species/species
groups. Shorebased IFQ catch must be
landed at authorized first receiver sites.
The IFQ whiting quota shares (QS) were
allocated to a mixture of limited entry
permit holders and shorebased
processors. One non-profit organization
received quota share based on the
ownership of multiple limited entry
permits. The Mothership (MS) coop
sector can consist of one or more coops
and a non-coop subsector. For a MS
coop to participate in the Pacific
whiting fishery, it must be composed of
MS catcher-vessel (MSCV) endorsed
limited entry permit owners. Each
permitted MS coop is authorized to
harvest a quantity of Pacific whiting
based on the sum of the catch history
assignments for each member’s MS/
Catcher Vessel (MSCV) endorsed permit
identified in the NMFS accepted coop
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agreement for a given calendar year.
Each MS/CV endorsed permit has an
allocation of Pacific whiting catch based
on its catch history in the fishery. The
catch history assignment (CHA) is
expressed as a percentage of Pacific
whiting of the total MS sector
allocation. Currently the MS sector is
composed of only a single coop. The
Catcher/Processor (C/P) coop program is
a limited access program that applies to
vessels in the C/P sector of the Pacific
whiting at-sea trawl fishery and is a
single voluntary coop. Unlike the MS
coop regulations where multiple coops
can be formed around the catch history
assignments of each coop’s member’s
endorsed permit, the single C/P coop
receives the total Pacific whiting
allocation for the C/P sector. Only C/P
endorsed limited entry permits can
participate in this coop. Currently
(February 2013), the Shorebased IFQ
Program is composed of 138 QS
permits/accounts, 142 vessel accounts,
and 50 first receivers. The MS coop
fishery is currently composed of a single
coop, with six mothership processor
permits, and 36 MS/CV endorsed
permits with one permit having two
catch history assignments endorsed to
it. The C/P coop is composed of 10
catcher-processor permits owned by
three companies. There are four tribes
that can participate in the tribal whiting
fishery. The current tribal fleet is
composed of 5 trawlers that either
deliver to a shoreside plant or to a
contracted mothership.
These regulations directly affect IFQ
Quota share holders who determine
which vessel accounts receive QP,
holders of MS/CV endorsed permits
who determine how many coops will
participate in the fishery and how much
fish each coop is to receive, and the CP
coop which is made up of three
companies that own the CP permits. As
part of the permit application processes
for the non-tribal fisheries, based on a
review of the SBA size criteria,
applicants are asked if they considered
themselves a ‘‘small’’ business and to
provide detailed ownership
information. Although there are three
non-tribal sectors, many companies
participate in two or more of these
sectors. All MS/CV participants are
involved in the shorebased IFQ sector
while two of the three CP companies
also participate in both the shorebased
IFQ sector and in the MS sector. Many
companies own several QS accounts.
After accounting for cross participation,
multiple QS account holders, and for
affiliation through ownership, there are
100 non-tribal entities directly affected
by these regulations, 82 of which are
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considered to be ‘‘small’’ businesses.
These regulations also directly affect
tribal whiting fisheries. Based on
groundfish ex-vessel revenues and on
tribal enrollments (the population size)
of each tribe, the four tribes and their
fleets are considered ‘‘small’’ entities.
There are no recordkeeping
requirements associated with this final
rule.
This final rule directly regulates what
entities can harvest whiting. This rule
allocates fish between tribal harvesters
(harvest vessels are small entities, tribes
are small jurisdictions) and to non-tribal
harvesters (a mixture of small and large
businesses). Tribal fisheries are a
mixture of activities that are similar to
the activities that non-tribal fisheries
undertake. Tribal harvests are delivered
to both shoreside plants and
motherships for processing. These
processing facilities also process fish
harvested by non-tribal fisheries.
The alternatives to the 2013 interim
tribal allocation implemented by this
rule are the ‘‘No-Action’’ and the
‘‘Proposed Action (or preferred
alternative).’’ The preferred alternative,
based on discussions with the tribes, is
for NMFS to allocate between 28
percent and 23 percent of the U.S. total
allowable catch for 2013. NMFS did not
consider a broader range of alternatives
to the proposed allocation. The tribal
allocation is based primarily on the
requests of the tribes. These requests
reflect the level of participation in the
fishery that will allow them to exercise
their treaty right to fish for whiting.
Consideration of amounts lower than
the tribal requests is not appropriate in
this instance. As a matter of policy,
NMFS has historically supported the
harvest levels requested by the tribes.
Based on the information available to
NMFS, the tribal request is within their
tribal treaty rights, and the participating
tribe has on occasion shown an ability
to harvest the amount of whiting
requested. A higher allocation would,
arguably, also be within the scope of the
treaty right. However, a higher
allocation would unnecessarily limit the
non-tribal fishery.
A no-action alternative was
considered, but the regulatory
framework provides for a tribal
allocation on an annual basis only.
Therefore, no action would result in no
allocation of Pacific whiting to the tribal
sector in 2013, which would be
inconsistent with NMFS’ responsibility
to manage the fishery consistent with
the tribes’ treaty rights. Given that there
are tribal requests for allocations in
2013, this alternative was rejected.
There are no significant alternatives to
the rule that accomplish the stated
PO 00000
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26531
objectives of applicable statutes and the
treaties with the affected tribes that
minimize any of the significant
economic impact of the proposed rule
on small entities. NMFS believes this
final rule will not adversely affect small
entities. Sector allocations are higher
than sector catches in 2012, so this rule
will be beneficial to both large and
small entities.
No Federal rules have been identified
that duplicate, overlap, or conflict with
this action.
NMFS issued Biological Opinions
under the ESA on August 10, 1990,
November 26, 1991, August 28, 1992,
September 27, 1993, May 14, 1996, and
December 15, 1999 pertaining to the
effects of the Pacific Coast groundfish
FMP fisheries on Chinook salmon
(Puget Sound, Snake River spring/
summer, Snake River fall, upper
Columbia River spring, lower Columbia
River, upper Willamette River,
Sacramento River winter, Central Valley
spring, California coastal), coho salmon
(Central California coastal, southern
Oregon/northern California coastal),
chum salmon (Hood Canal summer,
Columbia River), sockeye salmon (Snake
River, Ozette Lake), and steelhead
(upper, middle and lower Columbia
River, Snake River Basin, upper
Willamette River, central California
coast, California Central Valley, south/
central California, northern California,
southern California). These biological
opinions have concluded that
implementation of the FMP for the
Pacific Coast groundfish fishery was not
expected to jeopardize the continued
existence of any endangered or
threatened species under the
jurisdiction of NMFS, or result in the
destruction or adverse modification of
critical habitat.
NMFS issued a Supplemental
Biological Opinion on March 11, 2006
concluding that neither the higher
observed bycatch of Chinook in the
2005 whiting fishery nor new data
regarding salmon bycatch in the
groundfish bottom trawl fishery
required a reconsideration of its prior
‘‘no jeopardy’’ conclusion. NMFS also
reaffirmed its prior determination that
implementation of the Groundfish
PCGFMP is not likely to jeopardize the
continued existence of any of the
affected ESUs. Lower Columbia River
coho (70 FR 37160, June 28, 2005) and
Oregon Coastal coho (73 FR 7816,
February 11, 2008) were recently
relisted as threatened under the ESA.
The 1999 biological opinion concluded
that the bycatch of salmonids in the
Pacific whiting fishery were almost
entirely Chinook salmon, with little or
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no bycatch of coho, chum, sockeye, and
steelhead.
On December 7, 2012, NMFS
completed a biological opinion
concluding that the groundfish fishery
is not likely to jeopardize non-salmonid
marine species including listed
eulachon, green sturgeon, humpback
whales, Steller sea lions, and
leatherback sea turtles. The opinion also
concludes that the fishery is not likely
to adversely modify critical habitat for
green sturgeon and leatherback sea
turtles. An analysis included in the
same document as the opinion
concludes that the fishery is not likely
to adversely affect green sea turtles,
olive ridley sea turtles, loggerhead sea
turtles, sei whales, North Pacific right
whales, blue whales, fin whales, sperm
whales, Southern Resident killer
whales, Guadalupe fur seals, or the
critical habitat for Steller sea lions.
As Steller sea lions and humpback
whales are also protected under the
Marine Mammal Protection Act
(MMPA), incidental take of these
species from the groundfish fishery
must be addressed under MMPA section
101(a)(5)(E). On February 27, 2012,
NMFS published notice that the
incidental taking of Steller sea lions in
the West Coast groundfish fisheries is
addressed in NMFS’ December 29, 2010
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Negligible Impact Determination and
this fishery has been added to the list of
fisheries authorized to take Steller sea
lions (77 FR 11493). NMFS is currently
developing MMPA authorization for the
incidental take of humpback whales in
the fishery.
On November 21, 2012, the U.S. Fish
and Wildlife Service (FWS) issued a
biological opinion concluding that the
groundfish fishery will not jeopardize
the continued existence of the shorttailed albatross. The FWS also
concurred that the fishery is not likely
to adversely affect the marbled murrelet,
California least tern, southern sea otter,
bull trout, nor bull trout critical habitat.
Pursuant to Executive Order 13175,
this final rule was developed after
meaningful consultation and
collaboration with tribal officials from
the area covered by the FMP. Consistent
with the Magnuson-Stevens Act at 16
U.S.C. 1852(b)(5), one of the voting
members of the Pacific Council is a
representative of an Indian tribe with
federally recognized fishing rights from
the area of the Council’s jurisdiction. In
addition, NMFS has coordinated
specifically with the tribes interested in
the whiting fishery regarding the issues
addressed by this rule.
List of Subjects in 50 CFR Part 660
Fisheries, Fishing, Indian Fisheries.
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Dated: May 2, 2013.
Alan D. Risenhoover,
Director, Office of Sustainable Fisheries,
performing the functions and duties of the
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
For the reasons set out in the
preamble, 50 CFR part 660 is amended
as follows:
PART 660—FISHERIES OFF WEST
COAST STATES
1. The authority citation for part 660
continues to read as follows:
■
Authority: 16 U.S.C. 1801 et seq. and 16
U.S.C. 773 et seq.
2. In § 660.50, paragraph (f)(4) is
revised to read as follows:
■
§ 660.50 Pacific Coast treaty Indian
fisheries.
*
*
*
*
*
(f) * * *
(4) Pacific whiting. The tribal
allocation for 2013 is 63,205 mt.
*
*
*
*
*
3. Table 1a, to part 660, subpart C, is
revised to read as follows:
■
BILLING CODE 3510–22–P
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Table lao To Part 660, Subpart C- 2013, Specifications of OFL, ABC,
ACT and Fishery Harvest guidelines (weights in metric tons) .
Species
Arrowtooth flounder
Area
Coastwide
cl
dl el
Black
Bocaccio
Cabezon
il
49
170
47
163
47
163
47
163
126
120
120
118
752
1,768
719
1,690
116
1,690
98.5
1,466
11
541
92,955
9
517
Coastwide
N of 40° 10' N. lat.
ql
7,129
88,865
6,815
3,334
1,334
2,902
3,036
1,111
2,774
3,391
2,825
110
94
S of 40° 10' N. lat.
Coastwide
rl
ILongspine thornyhead
sl
Minor nearshore rockfish north tl
Minor shelf rockfish north
ul
N of
S of
N of
N of
lat.
lat.
lat.
lat.
2.9
296 .2
23,410
6,815
6,712
3,036
1,111
2,000
2,758
1,102
1,928
2,009
1,963
356
94
353
94
1,920
968
903
1,381
1,005
1,160
990
1,098
990
1,910
1,617
714
668.0
681
6,832
618
4,717
597
4,540
10,060
6,982
618
4, 717 1
4,884
Coastwide
N of 40° 10' N. lat.
3,200
844
2,221
807
1,600
150
1,191
133.5
Coastwide
626,364
Coastwide
2,711
ddl
2,592
204,040
ddl
2,592 2,358.0
N of 36° N. lat.
6,621
6,045
4,012
lc
1,439
1,434
48
N of 40°10' N. lat.
wi
yl
Minor slope rockfish south
2,183
1,518
1,164
Coastwide
Minor nearshore rockfish south
Minor shelf rockfish south
xl
S of 40°10' N. lat.
S of 40°10' N. lat.
S of 40°10' N. lat.
zl
Other flatfish
34°27' N.
34°27' N.
40°10' N.
40°10' N.
3
317
25,000
Coastwide
vi
Minor slope rockfish north
Other fish
1,000
311.6
Coastwide
Coastwide
01
Longnose skate
397
1,000
320
ml
Darkblotched rockfish
Dover sole nl
pi
411
1,108
845
Coastwide
S of 40°10' N. lat.
S of 40°10' N. lat.
11
English sole
411
1,159
884
46°16' to 42° N. lat.
S of 42° N. lat.
S of 34°27' N. lat.
kl
Chilipepper
430
S of 46°16' N. lat.
S of 40°10' N. lat.
fl
gl hi
ILingcod
Fishery
HG bl
4,070
ABC
ACL al
6,157
6,157
N of 46°16' N. lat.
California scorpionfish
Canary rockfish jl
Cowcod
OFL
7,391
ACL,
aal
Pacific cod bbl
Pacific ocean perch (POP)
eel
Pacific whiting ddl
Petrale sole eel
4,682
t;ee TaDle
Sablefish ffl
Shortbelly
ggl
S of 36° N. lat.
Coastwide
hhl
Shortspine thornyhead
N of 34°27' N. lat.
iii
6,950
5,789
50
1,540
1,481
355
1,598
2,230
1,684
1,610
397
1,610
1,825
1,520
1,520
1,513
widow 111
Yelloweye rockfish
Coastwide
Coastwide
4,841
51
4,598
43
1,500
18
1,411
12.2
N of 40°10' N. lat.
4,579
4,378
4,378
3,677
Splitnose
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2,333
Starry flounder kk/
S of 34°27' N. lat.
S of 40°10' N. lat.
Coastwide
Federal Register / Vol. 78, No. 88 / Tuesday, May 7, 2013 / Rules and Regulations
a/ ACLs, ACTs and HGs are specified as total catch values.
b/ Fishery harvest guideline means the harvest guideline or quota after subtracting from the ACL or ACT Pacific
Coast treaty Indian tribes allocations or projected catch, projected research catch, deductions for fishing mortality in
non-groundfish fisheries, and deductions for EFPs.
c/ Arrowtooth flounder. The stock was last assessed in 2007 and was estimated to be at 79 percent of its unfished
biomass in 2007. The OFL of7,391 mt is based on the 2007 assessment with an F30%FMSY proxy. The ABC of6,157
mt is a 17 percent reduction from the OFL (cr=0.721P*=0.40) as it's a category 2 stock. Because the stock is above
B 2s %, the ACL is set equal to the ABC. 2,087.39 mt is deducted from the ACL for the Tribal fishery (2,041 mt), the
incidental open access fishery (30 mt), and research catch (16.39 mt), resulting in a fishery HG of 4,070 mt.
d/ Black rockfish north (Washington). A stock assessment was prepared for black rockfish north of 45°46' N. lat.
(Cape Falcon, Oregon) in 2007. The biomass in the north was estimated to be at 53 percent of its unfished biomass
in 2007. The OFL from the assessed area is based on the 2007 assessment with a harvest rate proxy of Fso%. The
resulting OFL for the area north of 46°16 N. lat. is 430 mt and is 97 percent of the OFL from the assessed area,
based on the area distribution of historical catch. The ABC of 411 mt for the north is a 4 percent reduction from the
OFL (a=0.361P*=0.45) as it's a category 1 stock. The ACL was set equal to the ABC, since the stock is above B 4o%.
14 mt is deducted from the ACL for the Tribal fishery, resulting in a fishery HG of397 mt.
e/ Black rockfish south (Oregon and California). A stock assessment was prepared for black rockfish south of 45°46
N. lat. (Cape Falcon, Oregon) to Central California in 2007. The biomass in the south was estimated to be at 70
percent of its unfished biomass in 2007. The OFL from the assessed area is based on the 2007 assessment with a
harvest rate proxy of F SO% plus 3 percent of the OFL from the stock assessment prepared for black rockfish north of
45°46' N. lat. The resulting OFL for the area south of 46°16 N. lat. is 1,159 mt. The ABC of 1,108 mt is a 4 percent
reduction from the OFL (a=0.361P*=0.45) as it's a category 1 stock. The 2013 and 2014 ACL is 1,000 mt, which
maintains the constant catch strategy designed to keep the stock biomass above B4o %. There are no deductions from
the ACL, thus the fishery HG is equal to the ACL. The black rockfish ACL in the area south of 46°16' N. lat.
(Columbia River), is subdivided with separate HGs being set for the waters off Oregon (580 mt/58 percent) and for
the waters off California (420 mt/42 percent).
fI Bocaccio. A bocaccio stock assessment update was prepared in 2011 for the bocaccio stock between the U.S.Mexico border and Cape Blanco. The stock is managed with stock-specific harvest specifications south of 40°10' N.
lat. and within the minor shelf rockfish complex north of 40°10' N. lat. Historical catch distribution of
approximately 6 percent was used to apportion the assessed stock to the area north of 40°10' N. lat. The bocaccio
stock was estimated to be at 26 percent of its unfished biomass in 2011. The OFL of884 mt is based on the 2011
stock assessment STAT model with an F MSY proxy of Fso%. The ABC of 845 mt is a 4 percent reduction from the
OFL (cr=0.361P*=0.45) as it's a category 1 stock. The 320 mt ACL is based on a rebuilding plan with a target year
to rebuild of2022 and an SPR harvest rate of77.7 percent. 8.4 mt is deducted from the ACL for the incidental open
access fishery (0.7 mt), EFP catch (6.0 mt) and research catch (1.7 mt), resulting in a fishery HG of311.6 mt. The
California recreational fishery has an HG of 163.5.
g! Cabezon (Oregon). A cabezon stock assessment was prepared in 2009. The cabezon biomass in waters off Oregon
was estimated to be at 52 percent of its unfished biomass in 2009. The OFL of 49 mt was calculated using an FMSY
proxy ofF 4s %. The ABC of 47 mt was based on a 4 percent reduction from the OFL (a=0.361P*=0.45) as it's a
category 1 species. Because the stock is above B4o %, the ACL is set equal to the ABC. No deductions are made from
the ACL, so the fishery HG is equal to the ACL at 47 mt. Cabezon in waters off Oregon were removed from the
"other fish" complex in 2011.
hi Cabezon (California). A cabezon stock assessment was prepared in 2009. The cabezon biomass in waters off
California was estimated to be at 48 percent of its unfished biomass in 2009. The OFL of 170 mt was calculated
using an FMSY proxy ofF 4s %. The ABC of 163 mt was based on a 4 percent reduction from the OFL
(cr=0.361P*=0.45) as it's a category 1 stock. Because the stock is above B 4o%, the ACL is set equal to the ABC. No
deductions are made from the ACL, so the fishery HG is equal to the ACL at 163 mt.
i/ California scorpionfish was assessed in 2005 and was estimated to be at 80 percent of its unfished biomass in
2005. The OFL of 126 mt is based on the 2005 assessment with a harvest rate proxy ofF so%. The ABC of 120 mt is
a 4 percent reduction from the OFL (a=0.36/P*=0.45) as it's a category 1 stock. Because the stock is above B4o%,
the ACL is set equal to the ABC. 2 mt is deducted from the ACL for the incidental open access fishery, resulting in a
fishery HG of 118 mt.
j/ Canary rockfish. A canary rockfish stock assessment update was prepared in 2011 and the stock was estimated to
be at 24 percent of its unfished biomass coastwide in 2011. The coastwide OFL of 752 mt is based on the new
assessment with an FMSY proxy ofF so%. The ABC of719 mt is a 4 percent reduction from the OFL
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(cr=0.361P*=0.45) as it's a category 1 stock. The ACL of 116 mt is based on a rebuilding plan with a target year to
rebuild of2030 and a SPR harvest rate of88.7 percent. 17.5 mt is deducted from the ACL for the Tribal fishery (9.5
mt), the incidental open access fishery (2 mt), EFP catch (1.5 mt) and research catch (4.5 mt) resulting in a fishery
HG of98.52 mt. Recreational HGs are being specified as follows: Washington recreational 3.1; Oregon recreational
10.8 mt; and California recreational 22.4 mt.
k/ Chilipepper. The coastwide chilipepper stock was assessed in 2007 and estimated to be at 70 percent of its
unfished biomass coastwide in 2006. Chilipepper are managed with stock-specific harvest specifications south of
40°10 N. lat. and within the minor shelf rockfish complex north of 40°10' N. lat. Projected OFLs are stratified north
and south of 40°10' N. latitude based on the average 1998-2008 assessed area catch, which is 93 percent for the area
south of 40°10' N. latitude and 7 percent for the area north of 40°10' N. latitude. South of 40°10' N. lat., the OFL of
1,768 mt is based on the 2007 assessment with an FMSY proxy ofF50%. The ABC of 1,690 mt is a 4 percent reduction
from the OFL (cr=0.361P*=0.45) as it's a category 1 stock. Because the unfished biomass is estimated to be above 40
percent of the unfished biomass, the ACL was set equal to the ABC. 224 mt is deducted from the ACL for the
incidental open access fishery (5 mt), EFP fishing (210 mt), and research catch (9 mt), resulting in a fishery HG of
1,466 mt.
11 Cowcod. A stock assessment update prepared in 2009 estimated the stock to be 5 percent of its unfished biomass
in 2009. The OFLs for the Monterey and Conception areas were summed to derive the south of 40°10' N. lat. OFL
of 11 mt. The ABC for the area south of 40°10' N. lat. is 9 mt. The assessed portion of the stock in the Conception
Area was considered category 2, with a Conception Area contribution to the ABC of 5 mt, which is a 17 percent
reduction from the OFL (cr=O. 721P*=0.40). The unassessed portion of the stock in the Monterey area was considered
a category 3 stock, with a contribution to the ABC of3 mt, which is a 31 percent reduction from the OFL
(cr= 1.441P*=0.40). A single ACL of 3 mt is being set for both areas combined. The ACL of 3 mt is based on a
rebuilding plan with a target year to rebuild of2068 and an SPR rate of82.7 percent. 0.1 mt is deducted from the
ACL for the amount anticipated to be taken during research activity (0.1 mt) and EFP catch (0.03 mt) which results
in a fishery HG of2.9 mt.
mI Darkblotched rockfish. A stock assessment update was prepared in 2011, and the stock was estimated to be at
30.2 percent of its unfished biomass in 2011. The OFL is projected to be 541 mt and is based on the 2011 stock
assessment with an FMSY proxy ofF 50%. The ABC of517 mt is a 4 percent reduction from the OFL
(cr=0.361P*=0.45) as it's a category 1 stock. The ACL of 317 mt is based on a rebuilding plan with a target year to
rebuild of 2025 and an SPR harvest rate of 64.9 percent. 20.8 mt is deducted from the ACL for the Tribal fishery
(0.1 mt), the incidental open access fishery (18.4 mt), EFP catch (0.2 mt) and research catch (2.1 mt), resulting in a
fishery HG of296.2 mt.
nJ Dover sole. A 2011 Dover sole assessment estimated the stock to be at 83.7 percent of its unfished biomass in
2011. The OFL of92,955 mt is based on the results of the 2011 stock assessment with an FMSY proxy ofF 30%. The
ABC of 88,865 mt is a 4 percent reduction from the OFL (cr=0.361P*=0.45) as it's a category 1 stock. Because the
stock is above B 25 % coastwide, the ACL could be set equal to the ABC. However, the ACL of25,000 mt is set at a
level below the ABC and higher than the maximum historical landed catch. 1,590 mt is deducted from the ACL for
the Tribal fishery (1,497 mt), the incidental open access fishery (55 mt) and research catch (38 mt), resulting in a
fishery HG of23,410 mt.
01 English sole. A stock assessment update was prepared in 2007. The stock was estimated to be at 116 percent of its
unfished biomass in 2007. The OFL of7,129 mt is based on the results of the 2007 assessment update with an FMSY
proxy ofF 30%. The ABC of6,815 mt is a 4 percent reduction from the OFL (cr=0.361P*=0.45) as it's a category 1
stock. Because the stock is above B25 %, the ACL was set equal to the ABC. 103 mt is deducted from the ACL for the
Tribal fishery (91 mt), the incidental open access fishery (7 mt) and research catch (5 mt), resulting in a fishery HG
of6,712 mt.
pi Lingcod north. A lingcod stock assessment was prepared in 2009. The lingcod biomass off Washington and
Oregon was estimated to be at 62 percent of its unfished biomass in 2009. The OFL of3,334 mt was calculated
using an FMSY proxy ofF 45 %. The ABC of3,036 mt was based on a 4 percent reduction from the OFL
(cr=0.361P*=0.45) for the area north of 42° N. lat. as it's a category 1 stock, and a 17 percent reduction from the
OFL (cr=0.721P*=0.40) for the area between 42° N. lat. and 40 0 10'N.lat. as it's a category 2 stock. The ACL was
set equal to the ABC. 277.67 mt is deducted from the ACL for the Tribal fishery (250 mt), the incidental open
access fishery (16 mt) and research catch (11.67 mt), resulting in a fishery HG of2,758 mt.
q/ Lingcod south. A lingcod stock assessment was prepared in 2009. The lingcod biomass off California was
estimated to be at 74 percent of its unfished biomass in 2009. The OFL of 1,334 mt was calculated using an FMSY
proxy ofF 45 %. The ABC of 1,111 mt was based on a 17 percent reduction from the OFL (cr=0.72IP*=0.40) as it's a
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category 2 stock. The ACL was set equal to the ABC. 9 mt is deducted from the ACL for the incidental open access
fishery (7 mt) and EFP fishing (2 mt), resulting in a fishery HG of 1,102 mt.
rl Longnose skate. A stock assessment was prepared in 2007 and the stock was estimated to be at 66 percent of its
unfished biomass. The OFL of 2,902 mt is based on the 2007 stock assessment with an FMSY proxy ofF 4s %. The
ABC of 2,774 mt is a 4 percent reduction from the OFL (2010
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zl "Other fish" is composed entirely of groundfish FMP species that are neither rockfish (family Scorpaenidae) nor
flatfish, and most of these species are unassessed, with the exception of spiny dogfish, which was assessed in 2011
and is a category 2 stock. The OFL of 6,832 mt is the sum of the OFL contributions for the component species
within the complex. The OFL contribution for spiny dogfish is projected from the 2011 assessment using an F 4S %
FMSY proxy harvest rate. The ABC of 4,717 mt is calculated by applying a p* of 0.40 and a sigma of 1.44 to the
OFLs calculated for the category 3 stocks (i.e., all stocks other than spiny dogfish) and a P* of 0.30 and a sigma of
0.72 to the OFL calculated for spiny dogfish. The resulting ABC for the complex is the summed contribution of the
ABCs calculated for the component stocks. The ACL is set equal to the ABC. 177 mt is deducted from the ACL for
the Tribal fishery (112 mt), the incidental open access fishery (50 mt), EFP catch (3 mt) and research catch (12 mt),
resulting in an "other fish" fishery HG of 4,540 mt.
aa/ "Other flatfish" are the unassessed flatfish species that do not have individual OFLs/ABCs/ACLs and include
butter sole, curlfin sole, flathead sole, Pacific sand dab, rex sole, rock sole, and sand sole. The other flatfish OFL of
10,060 mt is based on the sum of the OFL contributions of the component stocks. The ABC of 6,982 mt is a 31
percent reduction from the OFL (a= 1.441P*=0.40) as the complex is composed of category 3 stocks. The ACL of
4,884 mt is the 2011 and 2012 ACL carried forward as there have been no significant changes in the status or
management of stocks within the complex. 202 mt is deducted from the ACL for the Tribal fishery (60 mt), the
incidental open access fishery (125 mt), and research catch (17 mt), resulting in a fishery HG of 4,682 mt.
bbl Pacific cod. The 3,200 mt OFL is based on the maximum level of historic landings. The ABC of2,221 mt is a 31
percent reduction from the OFL (a=1.441P*=0.40) as it's a category 3 stock. The 1,600 mt ACL is the OFL reduced
by 50 percent as a precautionary adjustment. 409.04 mt is deducted from the ACL for the Tribal fishery (400 mt),
research fishing (7.04 mt), and the incidental open access fishery (2.0 mt), resulting in a fishery HG of 1,191 mt.
ccl Pacific Ocean Perch (POP). A POP stock assessment was prepared in 2011 and the stock was estimated to be at
19.1 percent of its unfished biomass in 2011. The OFL of 844 mt for the area north of 40°10' N. lat. is based on the
2011 stock assessment with an Fso% FMSY proxy. The ABC of807 mt is a 4 percent reduction from the OFL
(a=0.361P*=0.45) as it's a category 1 stock. The ACL of 150 mt is based on a rebuilding plan with a target year to
rebuild of 2051 and an SPR harvest rate of 86.4 percent. 16.5 mt is deducted from the ACL for the Tribal fishery
(10.9 mt), open access fishery (0.4 mt) and research catch (5.2 mt), resulting in a fishery HG of 133.5 mt.
dd/ Pacific whiting. The most recent stock assessment was prepared in January 2013. The 2013 Fishery Harvest
Guideline (Fishery HG) is calculated as follows. u.s. TAC of269,745 mt minus 63,205 mt for the Tribal allocation
minus 2,500 mt for catch in research activities and as non-groundfish bycatch, resulting in a fishery harvest
guideline of204,040 mt. The TAC for Pacific whiting is established under the provisions of the Pacific
Hake/whiting Agreement with Canada and the Pacific Whiting Act of2006, 16 U.S.C. 7001-7010, and the
international exception applies. Therefore, no ABC or ACL values are provided for Pacific whiting. The 2013 OFL
of 626,364 mt is based on the 2013 assessment with an F40%FMSY proxy.
eel Petrale sole. A petrale sole stock assessment was prepared for 2011. In 2011 the petrale sole stock was estimated
to be at 18 percent of its unfished biomass. The OFL of 2,711 mt is based on the 2011 assessment with an F 30% FMSY
proxy. The ABC of2,592 mt is a 4 percent reduction from the OFL (a=0.361P*=0.45) as it's a category 1 stock. The
ACL is set equal to the ABC. 234 mt is deducted from the ACL for the Tribal fishery (220 mt), the incidental open
access fishery (2.4 mt), and research catch (11.6 mt), resulting in a fishery HG of 2,358 mt.
ff! Sablefish north. A coastwide sablefish stock assessment was prepared in 2011. The coastwide sablefish biomass
was estimated to be at 33 percent of its unfished biomass in 2011. The coastwide OFL of 6,621 mt is based on the
2011 stock assessment with an FMSY proxy ofF4s %. The coastwide ABC of 6,045 mt is an 8.7 percent reduction from
the OFL (0-=0.361P*=0.40). The 40-10 harvest policy was applied to the ABC to derive a coastwide ACL value.
Then the ACL value was apportioned, north and south of 36° N. lat., using the average of annual swept area biomass
(2003-2010) from the NMFS NWFSC trawl survey, between the northern and southern areas with 73.6 percent
going to the area north of 36° N. lat. and 26.4 percent going to the area south of 36° N. lat. The northern ACL is
4,012 mt and is reduced by 401 mt for the tribal allocation (10 percent of the ACL north of36° N. lat.). The 401 mt
Tribal allocation is reduced by 1.5 percent to account for discard mortality. Detailed sablefish allocations are shown
in Table 1c.
gg! Sablefish south. The ACL for the area south of 36° N. lat. is 1,439 mt (26.4 percent of the calculated coastwide
ACL value). 5 mt is deducted from the ACL for the incidental open access fishery (2 mt) and research catch (3 mt),
resulting in a fishery HG of 1,434 mt.
hhl Shortbelly rockfish. A non-quantitative assessment was conducted in 2007. The spawning stock biomass of
shortbelly rockfish was estimated at 67 percent of its unfished biomass in 2005. The OFL of 6,950 mt was
recommended for the stock in 2013 with an ABC of 5,789 mt (0-=0.72 with a p* of 0.40). The 50 mt ACL is slightly
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higher than recent landings and is in recognition of the stock's importance as a forage species in the California
Current ecosystem. 2 mt is deducted from the ACL for research catch, resulting in a fishery HG of 48 mt.
iii Shortspine thornyhead. A coastwide stock assessment was conducted in 2005 and the stock was estimated to be at
63 percent of its unfished biomass in 2005. A coastwide OFL of2,333 mt is based on the 2005 stock assessment
with an F 50% FMSY proxy. The coastwide ABC of2,230 mt is a 4 percent reduction from the OFL (cr=0.361P*=0.45)
as it's a category 1 stock. For the portion of the stock that is north of34°27' N. lat., the ACL is 1,540 mt. The
northern ACL is 66 percent ofthe coastwide OFL for the portion ofthe biomass found north of 34°27' N. lat. 59.22
mt is deducted from the ACL for the Tribal fishery (50 mt), the incidental open access fishery (2 mt), and research
catch (7.22 mt) resulting in a fishery HG of 1,481 mt for the area north of 34°27' N. lat. For that portion of the stock
south of 34°27' N. lat., the ACL is 397 mt which is 34 percent of the coastwide OFL for the portion of the biomass
found south of 34°27' N. lat. reduced by 50 percent as a precautionary adjustment. 42 mt is deducted from the ACL
for the incidental open access fishery (41 mt), and research catch (1 mt), resulting in a fishery HG of355 mt for the
area south of34°27' N. lat.
jj/ Splitnose rockfish. A coastwide assessment was prepared in 2009 that estimated the stock to be at 66 percent of
its unfished biomass in 2009. Splitnose in the north is managed under the minor slope rockfish complex and with
species-specific harvest specifications south of 40°10' N. lat. The OFLs were apportioned north and south based on
the average 1916-2008 assessed area catch resulting in 64.2 percent stock-specific OFL south of 40°10' N. lat, and
35.8 percent for the contribution of splitnose rockfish to the northern minor slope rockfish complex OFL. South of
40°10 N. lat., the OFL of 1,684 mt is based on the 2009 assessment with an FMSY proxy ofF 50%. The ABC of 1,610
mt is a 4 percent reduction from the OFL (cr=0.361P*=0.45) as it's a category 1 stock. Because the unfished biomass
is estimated to be above 40 percent of the unfished biomass, the ACL is set equal to the ABC. 12 mt is deducted
from the ACL for research catch (9 mt) and EFP catch (3 mt), resulting in a fishery HG of 1,598 mt.
kk/ Starry Flounder. The stock was assessed in 2005 and was estimated to be above 40 percent of its unfished
biomass in 2005. For 2013, the coastwide OFL of 1,825 mt is based on the 2005 assessment with an FMSY proxy of
F3o%. The ABC of 1,520 mt is a 17 percent reduction from the OFL (cr=0.721P*=0.40) as it's a category 2 stock.
Because the stock is above B25 %, the ACL was set equal to the ABC. 7 mt is deducted from the ACL for the Tribal
fishery (2 mt)and the incidental open access fishery (5 mt), resulting in a fishery HG of 1,513 mt.
IV Widow rockfish. The stock was assessed in 2011 and was estimated to be at 51.1 percent of its unfished biomass
in 2011. The OFL of 4,841 mt is based on the 2011 stock assessment with an F 50% FMSY proxy. The ABC of 4,598
mt is a 5 percent reduction from the OFL (cr=0.411P*=0.45). A unique sigma of 0.41 was calculated for widow
rockfish since the estimated variance in estimated biomass was greater than the 0.36 used as a proxy for other
category 1 stocks. A constant catch strategy will be used with an ACL of 1,500 mt. 89.2 mt is deducted from the
ACL for the Tribal fishery (60 mt), the incidental open access fishery (89.2 mt), EFP catch (18 mt) and research
catch (7.9 mt), resulting in a fishery HG of 1,411 mt.
mm/ Yelloweye rockfish. A stock assessment update was prepared in 2011. The stock was estimated to be at 21.3
percent of its unfished biomass in 2011. The 51 mt coastwide OFL was derived from the base model in the new
stock assessment with an FMSY proxy ofF50%. The ABC of 43 mt is a 17 percent reduction from the OFL
(cr=0.721P*=0.40) as it's a category 2 stock. The 18 mt ACL is based on a rebuilding plan with a target year to
rebuild of 2074 and an SPR harvest rate of76.0 percent. 5.82 mt is deducted from the ACL for the Tribal fishery
(2.3 mt), the incidental open access fishery (0.2 mt), EFP catch (0.02 mt) and research catch (3.3 mt) resulting in a
fishery HG of 12.2 mt. Recreational HGs are being established: Washington, 2.9; Oregon, 2.6 mt; and California,
3.4 mt.
nn! Yellowtail rockfish. A yellowtail rockfish stock assessment update was last prepared in 2005 for the area north
of 40°10' N. latitude to the U.S-Canadian border. Yellowtail rockfish was estimated to be at 55 percent of its
unfished biomass in 2005. The OFL of 4,579 mt is based on the 2005 stock assessment with the FMSY proxy ofF50 %.
The ABC of 4,378 mt is a 4 percent reduction from the OFL (cr=0.361P*=0.45) as it's a category 1 stock. The ACL
was set equal to the ABC, because the stock is above B4o %. 701.49 mt is deducted from the ACL for the Tribal
fishery (677 mt), the incidental open access fishery (3 mt), EFP catch (10 mt) and research catch (11.49 mt),
resulting in a fishery HG of3,677 mt.
*
*
*
§ 660.140
*
4. In § 660.140, paragraph (d)(1)(ii)(D)
is revised to read as follows:
■
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26539
SHOREBASED TRAWL ALLOCATIONS
IFQ Species
Management area
Arrowtooth flounder ........................................................................................
BOCACCIO ....................................................................................................
CANARY ROCKFISH ....................................................................................
Chilipepper .....................................................................................................
COWCOD ......................................................................................................
DARKBLOTCHED ROCKFISH ......................................................................
Dover sole ......................................................................................................
English sole ....................................................................................................
Lingcod ...........................................................................................................
Lingcod ...........................................................................................................
Longspine thornyhead ...................................................................................
Minor shelf rockfish complex .........................................................................
Minor shelf rockfish complex .........................................................................
Minor slope rockfish complex ........................................................................
Minor slope rockfish complex ........................................................................
Other flatfish complex ....................................................................................
Pacific cod ......................................................................................................
PACIFIC OCEAN PERCH .............................................................................
Pacific Whiting ...............................................................................................
PETRALE SOLE ............................................................................................
Sablefish ........................................................................................................
Sablefish ........................................................................................................
Shortspine thornyhead ...................................................................................
Shortspine thornyhead ...................................................................................
Splitnose rockfish ...........................................................................................
Starry flounder ...............................................................................................
Widow rockfish ...............................................................................................
YELLOWEYE ROCKFISH .............................................................................
Yellowtail rockfish ..........................................................................................
*
*
*
*
2013 Shorebased
trawl allocation
(mt)
South of 40°10′ N. lat.
South of 40°10′ N. lat.
South of 40°10′ N. lat.
North of 40°10′ N. lat.
South of 40°10′ N. lat.
North of 34°27′ N. lat.
North of 40°10′ N. lat.
South of 40°10′ N. lat.
North of 40°10′ N. lat.
South of 40°10′ N. lat.
North of 40°10′ N. lat.
North of 36° N. lat.
South of 36° N. lat.
North of 34°27′ N. lat.
South of 34°27′ N. lat.
South of 40°10′ N. lat.
North of 40°10′ N. lat.
3,846.13
74.90
39.90
1,099.50
1.00
266.70
22,234.50
6,365.03
1,222.57
494.41
1,859.85
508.00
81.00
776.93
376.11
4,189.61
1,125.29
109.43
85,697
2,318.00
1,828.00
602.28
1,385.35
50.00
1,518.10
751.50
993.83
1.00
2,635.33
*
[FR Doc. 2013–10806 Filed 5–6–13; 8:45 am]
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2014 Shorebased
trawl allocation
(mt)
3,467.08
79.00
41.10
1,067.25
1.00
278.41
22,234.50
5,255.59
1,151.68
472.88
1,811.40
508.00
81.00
776.93
378.63
4,189.61
1,125.29
112.28
................................
2,378.00
1,988.00
653.10
1,371.12
50.00
1,575.10
755.50
993.83
1.00
2,638.85
Agencies
[Federal Register Volume 78, Number 88 (Tuesday, May 7, 2013)]
[Rules and Regulations]
[Pages 26526-26539]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2013-10806]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 660
[Docket No. 130114034-3422-02]
RIN 0648-BC93
Magnuson-Stevens Act Provisions; Fisheries off West Coast States;
Pacific Coast Groundfish Fishery; Biennial Specifications and
Management Measures for the 2013 Tribal and Non-Tribal Fisheries for
Pacific Whiting
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS issues this final rule for the 2013 Pacific whiting
fishery under the authority of the Pacific Coast Groundfish Fishery
Management Plan (FMP), the Magnuson Stevens Fishery Conservation and
Management Act (Magnuson-Stevens Act), and the Pacific Whiting Act of
2006. This final rule establishes the tribal allocation of 63,205
metric tons of Pacific whiting for 2013, and final allocations of
Pacific whiting to the non-tribal fishery for 2013.
DATES: Effective May 7, 2013.
FOR FURTHER INFORMATION CONTACT: Kevin C. Duffy (Northwest Region,
NMFS), phone: 206-526-4743, fax: 206-526-6736 and email:
kevin.duffy@noaa.gov.
SUPPLEMENTARY INFORMATION:
Electronic Access
This final rule is accessible via the Internet at the Office of the
Federal Register Web site at https://www.federalregister.gov.
Background information and documents are available at the NMFS
Northwest Region Web site at https://www.nwr.noaa.gov/fisheries/management/whiting/pacific_whiting.html and at the Pacific Fishery
Management Council's Web site at https://www.pcouncil.org/.
Copies of the final environmental impact statement (FEIS) for the
2013-2014 Groundfish Specifications and Management Measures are
available from Donald McIsaac, Executive Director, Pacific Fishery
Management Council (Council), 7700 NE Ambassador Place, Portland, OR
97220, phone: 503-820-2280.
Background
This rule announces the Total Allowable Catch (TAC) for whiting,
expressed in metric tons (mt). This is the second year that the TAC for
Pacific whiting is being determined under the terms of Agreement with
Canada on Pacific Hake/Whiting (the Agreement) and the Pacific Whiting
Act of 2006 (the Whiting Act), 16 U.S.C. 7001-7010. The Agreement and
the Act establish bilateral bodies to implement the terms of the
Agreement, each with various responsibilities, including: The Joint
Management Committee (JMC), which is the decision-making body; the
Joint Technical Committee (JTC), which conducts the stock assessment;
the Scientific Review Group (SRG), which reviews the stock assessment;
and the Advisory Panel (AP), which provides stakeholder input to the
JMC (The Agreement, Art. II-IV; 16 U.S.C. 7001-7005). The Agreement
establishes a default harvest policy (F-40 percent with a 40/10
adjustment) and allocates 73.88 percent of the TAC to the United States
and 26.12 percent of the TAC to Canada. The bilateral JMC is primarily
responsible for developing a TAC recommendation to the Parties (United
States and Canada). The Secretary of
[[Page 26527]]
Commerce, in consultation with the Secretary of State, has the
authority to accept or reject this recommendation.
The Joint Technical Committee (JTC) met three times over the last
six months to prepare the 2013 stock assessment for Pacific hake
(whiting). The assessment presents a single base-case model using nine
years of an acoustic survey biomass index as well as catches to
estimate the scale of the current hake stock. The 2012 acoustic-trawl
survey result was a relative biomass 1,380,000 mt, an increase of 2.5
times the 2011 survey biomass of 521,000 mt, which is the lowest in the
time series. The age-composition data from the aggregated fisheries
(1975-2012) and the acoustic survey contribute to the assessment
model's ability to resolve strong and weak cohorts. The survey and the
fishery were dominated by age 2 (63.7 percent survey; 34.6 percent
fishery) and 4 (16.1 percent survey; 34.5 percent) year old fish from
the 2010 and 2008 year classes, with differences due to the different
selectivity of young fish to the survey vs. the fishery. Both sources
indicate a strong 2008 cohort in the 2011 and 2012 data (age 4 hake),
and a strong 2010 cohort in the 2012 data (age 2 hake), which may
partially explain the recent increase in the survey index.
The median estimated female biomass is 1,503,000 mt at the
beginning of 2013 and is expected to be stable to increasing through
2015 due to an expected very large 2010 year class and the above
average 2008 year class. This level of estimated spawning biomass has
not been seen since 1993. The 2012 survey verified the strength of the
2008 year class and finds that the 2010 year class seems even stronger,
but there is uncertainty in the 2010 year class strength because it has
only been observed once by the survey. Agreement between the most
recent acoustic survey and commercial fishery age composition data as
well as the most recent acoustic survey biomass index engenders greater
confidence in the 2013 assessment estimates than if there was no survey
data from 2012.
Until cohorts are five or six years old, the model's ability to
resolve cohort strength is poor. For many of the recent above average
cohorts (2005, 2006, and 2008), the size of the year class was
overestimated when it was age 2, compared to updated estimates as the
cohort aged and more observations were available from the fishery and
survey. Given that there is some uncertainty in the estimate of the
2010 year class, and that the size of this year class has a strong
effect on a projected 2013 catch, the JTC developed additional forecast
decision tables reflecting a low, medium, and high range of recruitment
for the 2010 year class. Using the more conservation-minded low-
recruitment state of nature, there is an equal probability that the
spawning stock biomass in 2014 will be less or greater than the
spawning biomass in 2013 with a catch between 300,000 and 350,000 mt.
There is an equal probability that the spawning biomass will be below
40 percent of unfished equilibrium spawning biomass with a 2013 catch
near 400,000 mt.
The JTC provided tables showing the outcome and probabilities of
various events under different catch alternatives for 2013. For the
base case median recruitment, the probability that the spawning stock
biomass in 2014 remains above the 2013 level is 50 percent with a catch
of 603,000 mt, the probability that the fishing intensity is above
target in 2013 is 50 percent with a catch of 626,364 mt, and the
probability that the predicted 2014 catch target is the same as a set
value in 2013 is 50 percent for a set value of 696,000 mt in 2013.
There is a less than 12 percent probability that the spawning stock
biomass will drop below 40 percent in 2014 for all catch levels
considered. This information indicates probabilities at projected catch
levels that were significantly higher than the TAC levels recommended
by the JMC, reinforcing the conservative nature of the proposed fishing
regime in 2013.
The two cohorts that will likely be supporting the 2013 fishery
will be ages 3 and 5. Cohorts in this age range are near their peak
biomass and potential maximum contribution to lifetime yield. Because
of this, an argument could be made to fish the stock harder because the
contribution to the population from these age classes will start to
decline in future years. However, there is still considerable risk in
fishing them too hard until the absolute size of these cohorts is
verified, particularly the 2010 year class, which is still very young
and thus not yet well characterized. A conservative estimate of the
2010 year class strength (using only the lower 10 percent of the model
estimated recruitment) reduces the strength from a median estimate of
11.6 billion recruits (a near record size) to 6.9 billion recruits,
which is near the size of the 1970 and 1999 recruitments.
The Scientific Review Group (SRG) met in Vancouver, British
Columbia, on February 19-22, 2013, to review the draft stock assessment
document prepared by the JTC. The SRG endorsed the assessment and
recommended that it be used for management advice. Along with the JTC,
the SRG recommended (for consideration by the JMC) a range of 336,000--
626,000 mt as plausible harvest levels in 2013. The upper end would
implement the default harvest policy in the Agreement and would allow
some continued biomass growth into 2014 if the current assessment
result is accurate. The lower level, using only the lower 10 percent of
the model estimated recruitment, would still not exceed the harvest
policy even if the 2010 year class is only 51 percent of its current
estimate.
At its March 18-19, 2013 meeting, the JMC reviewed the advice of
the JTC, SRG, and AP, and agreed on a TAC recommendation for
transmittal to the Parties. The JMC focused on the conservative
estimate of the 2010 year class strength (using only the lower 10
percent of the model estimated recruitment) and the SRG suggested
target catch of 336,200 mt, based primarily on concerns that this lower
bound may indeed reflect the true state of nature. This conservative
approach resulted in a TAC recommendation of 336,200 mt, with
adjustments upwards for uncaught Pacific whiting in 2012, as allowed by
the Agreement, for a coastwide adjusted TAC of 365,112 mt for 2013. The
TAC recommendation is expected to sustain the offshore hake/whiting
resource in the event that the 2010 year class is not as large as
expected, while still allowing a substantial increase in TAC compared
to 2012.
The recommendation for an adjusted United States TAC of 269,745 mt
for 2013 (73.88 percent of the coastwide TAC) is consistent with the
best available science, provisions of the Agreement, and the Whiting
Act. The recommendation was transmitted via letter to the Parties on
March 19, 2013. NMFS, under delegation of authority from the Secretary
of Commerce, approved the TAC recommendation of 269,745 mt for U.S.
fisheries on April 15, 2013.
Tribal Fishery Allocation
This final rule establishes the tribal allocation of Pacific
whiting for 2013. NMFS issued a proposed rule for the allocation and
management of the 2013 tribal Pacific whiting fishery on March 5, 2013
(78 FR 14259). This action finalizes the allocation and management
measures.
Since 1996, NMFS has been allocating a portion of the U.S. TAC of
Pacific whiting to the tribal fishery using the process established in
50 CFR 660.50(d)(1). According to the formula found in that section,
the tribal allocation is subtracted from the total U.S. Pacific whiting
TAC and the
[[Page 26528]]
remainder, less a deduction of 2,500 mt for research and bycatch in
non-groundfish fisheries (for 2013 only), is allocated to the non-
tribal sectors. The tribal Pacific whiting fishery is managed
separately from the non-tribal whiting fishery, and is not governed by
the limited entry or open access regulations or allocations.
The proposed rule described the tribal allocation as 17.5 percent
of the U.S. TAC plus 16,000 mt, and projected a range of potential
tribal allocations for 2013 based on a range of U.S. TACs over the last
ten years, 2003 through 2012. This range of TACs is 148,200 mt (2003)
to 290,903 mt (2011). The resulting range of potential tribal
allocations is 41,935 mt to 66,906 mt.
As described earlier in this preamble, the U.S. TAC for 2013 is
269,745 mt. Applying the formula at 50 CFR 660.50(d)(1), NMFS
calculated that the tribal allocation implemented by this final rule is
63,205 mt (17.5 percent of the U.S. TAC or 47,205 mt, plus 16,000 mt).
While the total amount of whiting to which the Tribes are entitled
under their treaty right has not yet been determined, and new
scientific information or discussions with the relevant parties may
impact that decision, the best available scientific information to date
suggests that 63,205 mt (23 percent of the 2013 U.S. TAC) is within the
likely range of potential treaty right amounts.
As with prior tribal whiting allocations, this final rule is not
intended to establish any precedent for future Pacific whiting seasons,
or for the determination of the total amount of whiting to which the
Tribes are entitled under their treaty right. Rather, this rule adopts
an interim allocation, pending the determination of the total treaty
amount. That amount will be based on further development of scientific
information and additional coordination and discussion with and among
the coastal tribes and States of Washington and Oregon. The process of
determining that amount, begun in 2008, is continuing.
Non-Tribal Allocations
This final rule establishes the non-tribal allocation for the
Pacific whiting fishery. The non-tribal allocation was not included in
the tribal whiting proposed rule published on March 5, 2013 (78 FR
14259) for two reasons related to timing and process. First, a
recommendation on the coastwide TAC for Pacific whiting for 2013, under
the terms of the Agreement with Canada, was not available until March
19, 2013. This recommendation for a U.S. TAC was approved by NMFS,
under delegation of authority from the Secretary of Commerce, on April
15, 2013. Second, the non-tribal allocation is established after
deductions from the U.S. TAC for the tribal allocation (63,205 mt) and
set asides for research and incidental catch in non-groundfish
fisheries (2,500 mt). The non-tribal allocation is therefore being
finalized in this rule.
The 2013 fishery harvest guideline (HG) for Pacific whiting is
204,040 mt. This amount was determined by deducting from the total U.S.
TAC of 269,745 mt, the 63,205 mt tribal allocation, along with 2,500 mt
for research catch and bycatch in non-groundfish fisheries. Regulations
at 50 CFR 660.55 (f)(2) allocate the fishery HG among the non-tribal
catcher/processor, mothership, and shorebased sectors of the Pacific
whiting fishery. The catcher/processor sector is allocated 34 percent
(69,373 mt for 2013), the mothership sector is allocated 24 percent
(48,970 mt for 2013), and the shorebased sector is allocated 42 percent
(85,697 mt for 2013). The fishery south of 42[deg] N. lat. may not take
more than 4,284 mt (5 percent of the shorebased allocation) prior to
the start of the primary Pacific whiting season north of 42[deg] N.
lat.
The 2013 allocations of Pacific Ocean perch, canary rockfish,
darkblotched rockfish, and widow rockfish to the whiting fishery were
published in a final rule on January 3, 2013 (78 FR 580). The
allocations to the Pacific whiting fishery for these species are
described in the footnotes to Table 1.b To Part 660, Subpart C-2013.
Comments and Responses
On March 5, 2013, NMFS issued a proposed rule for the allocation
and management of the 2013 tribal Pacific whiting fishery. The comment
period on the proposed rule closed on April 4, 2013. During the comment
period, NMFS received two letters of comment. The U.S. Department of
Interior submitted a letter of ``no comment'' associated with their
review of the proposed rule.
A letter was received from a commercial fishing organization. In
their letter, they state that given past performance in the tribal
fishery, the lack of demonstrable fishery operations from the Quileute
tribe, and the potential economic harm to the non-tribal fishery, the
proposed tribal whiting set aside is too high. They state that the
proposed tribal whiting set aside for 2013 is not justified by past
fishery performance, and fails in striking an appropriate balance of
the treaty rights of the tribes against the Agency's obligation to
achieve optimum yield. They suggest that NMFS: Establish a realistic
2013 tribal whiting set aside that is bolstered by fishery plans from
each tribe; and aptly and effectively exercise its reapportionment
authority.
Response: In determining the tribal allocation, NMFS must ensure
that the tribes have the opportunity to exercise their treaty right,
which is ``other applicable law'' under the Magnuson-Stevens Act. As
noted above, the amount requested by the tribes appears to be within
the amount to which they are entitled by treaty, as suggested by the
best available science. Although the allocation to the tribal fishery
in 2013 is a higher allocation amount than 2012 (63,205 mt versus
48,556 mt), the percent of the TAC allocated to the tribes in 2013
represents approximately 23 percent of the U.S. TAC, versus 26 percent
of the U.S. TAC in 2012.
As the commenter has noted, the reapportionment process is
available to NMFS to address the situation in which the tribes are
unable to use their full allocation. NMFS will monitor both the tribal
and non-tribal fishery during the season, and will remain in contact
with tribal representatives in order to determine, to the extent
practicable, the likely harvest levels in the tribal fishery. If
circumstances supporting reapportionment under NMFS' regulations arise,
NMFS will be prepared to expeditiously reapportion Pacific whiting from
the tribal to the non-tribal sector, in order to manage the fishery in
a manner consistent with both the implementation of the tribal treaty
right and the Magnuson Stevens Act requirements.
Classification
The final Pacific whiting specifications and management measures
for 2013 are issued under the authority of the Magnuson-Stevens Fishery
Conservation and Management Act (MSA), and the Pacific Whiting Act of
2006, and are in accordance with 50 CFR part 660, subparts C through G,
the regulations implementing the Pacific Coast Groundfish Fishery
Management Plan (PCGFMP). NMFS has determined that this rule is
consistent with the national standards of the Magnuson-Stevens Act and
other applicable laws. NMFS, in making the final determination, took
into account the data, views, and comments received during the comment
period.
NMFS has determined that the tribal whiting fishery, conducted off
the coast of the State of Washington, is consistent, to the maximum
extent practicable, with the approved coastal zone management program
of the States of Washington and
[[Page 26529]]
Oregon. NMFS has also determined that the Pacific whiting fishery, both
tribal and non-tribal, is consistent, to the maximum extent
practicable, with approved coastal zone management programs for the
States of Washington and Oregon. The State of Washington submitted a
letter of concurrence on February 25, 2013. The State of Oregon did not
respond and consistency is inferred.
Administrative Procedure Act
Pursuant to 5 U.S.C. 553(b)(B), the NMFS Assistant Administrator
finds good cause to waive prior public notice and comment and delay in
effectiveness the 2013 annual harvest specifications for Pacific
whiting, as delaying this rule would be contrary to the public
interest. The annual harvest specifications for Pacific whiting must be
implemented by the start of the main primary Pacific whiting season,
which begins on May 15, 2013, or the primary whiting season will
effectively remain closed.
Every year, NMFS conducts a Pacific whiting stock assessment in
which U.S. and Canadian scientists cooperate. The 2013 stock assessment
for Pacific whiting was prepared in early 2013, as the new 2012 data--
including updated total catch, length and age data from the U.S. and
Canadian fisheries, and biomass indices from the Joint U.S.-Canadian
acoustic/midwater trawl surveys--were not available until January,
2013. Because of this late availability of the most recent data for the
assessment, and the need for time to conduct the treaty process for
determining the TAC using the most recent assessment, it would not be
possible to allow for notice and comment before the start of the
primary Pacific whiting season on May 15.
A delay in implementing the Pacific whiting harvest specifications
to allow for notice and comment would be contrary to the public
interest because it would require either a shorter primary whiting
season or development of a TAC without the most recent data. A shorter
season could prevent the tribal and non-tribal fisheries from attaining
their 2013 allocations, which would result in unnecessary short-term
adverse economic effects for the Pacific whiting fishing vessels and
the associated fishing communities. A TAC determined without the most
recent data could fail to account for significant fluctuations in the
biomass of this relatively short-lived species. To prevent these
adverse effects and to allow the Pacific whiting season to commence, it
is in the public interest to waive prior notice and comment.
In addition, pursuant to 5 U.S.C. 553(d)(3), the NMFS Assistant
Administrator finds good cause to waive the 30-day delay in
effectiveness. Waiving the 30-day delay in effectiveness will not have
a negative impact on any entities, as there are no new compliance
requirements or other burdens placed on the fishing community with this
rule. Failure to make this final rule effective at the start of the
fishing year will undermine the intent of the rule, which is to promote
the optimal utilization and conservation of Pacific whiting. It would
also serve the best interests of the public because it will allow for
the longest possible Pacific whiting fishing season and therefore the
best possible economic outcome for those whose livelihoods depend on
this fishery. Because the 30-day delay in effectiveness would
potentially cause significant financial harm without providing any
corresponding benefits, this final rule is made effective May 7, 2013.
The preamble to the proposed rule and this final rule serve as the
small entity compliance guide required by Section 212 of the Small
Business Regulatory Enforcement Fairness Act of 1996. This action does
not require any additional compliance from small entities that is not
described in the preamble. Copies of this final rule are available from
NMFS at the following Web site: https://www.nwr.noaa.gov/fisheries/management/whiting/pacific_whiting.html.
Rulemaking must comply with Executive Order (EO) 12866 and the
Regulatory Flexibility Act (RFA). The Office of Management and Budget
has determined that this final rule is not significant for purposes of
Executive Order 12866.
The NMFS Economic Guidelines that describe the RFA and EO 12866 can
be found at https://www.nmfs.noaa.gov/sfa/domes_fish/EconomicGuidelines.pdf
The RFA can be found at https://www.archives.gov/federal-register/laws/regulatory-flexibility/
Executive Order 12866 can be found at https://www.plainlanguage.gov/populartopics/regulations/eo12866.pdf
When an agency proposes regulations, the RFA requires the agency to
prepare and make available for public comment an Initial Regulatory
Flexibility Act (IRFA) document that describes the impact on small
businesses, non-profit enterprises, local governments, and other small
entities. The IRFA is to aid the agency in considering all reasonable
regulatory alternatives that would minimize the economic impact on
affected small entities. After the public comment period, the agency
prepares a Final Regulatory Flexibility Analysis (FRFA) that takes into
consideration any new information and public comments. This FRFA
incorporates the IRFA, a summary of the significant issues raised by
the public comments, NMFS' responses to those comments, and a summary
of the analyses completed to support the action. NMFS published the
proposed rule on March 5, 2013 78 FR 14259, with a comment period
through April 4, 2013. An IRFA was prepared and summarized in the
Classification section of the preamble to the proposed rule. The
description of this action, its purpose, and its legal basis are
described in the preamble to the proposed rule and are not repeated
here. The FRFA describes the impacts on small entities, which are
defined in the IRFA for this action and not repeated here. Analytical
requirements for the FRFA are described in Regulatory Flexibility Act,
section 304(a)(1) through (5), and summarized below. The FRFA must
contain: (1) A succinct statement of the need for, and objectives of,
the rule; (2) A summary of the significant issues raised by the public
comments in response to the initial regulatory flexibility analysis, a
summary of the assessment of the agency of such issues, and a statement
of any changes made in the proposed rule as a result of such comments;
(3) A description and an estimate of the number of small entities to
which the rule will apply, or an explanation of why no such estimate is
available; (4) A description of the projected reporting, recordkeeping
and other compliance requirements of the rule, including an estimate of
the classes of small entities which will be subject to the requirement
and the type of professional skills necessary for preparation of the
report or record; and (5) A description of the steps the agency has
taken to minimize the significant economic impact on small entities
consistent with the stated objectives of applicable statutes, including
a statement of the factual, policy, and legal reasons for selecting the
alternative adopted in the final rule and why each one of the other
significant alternatives to the rule considered by the agency which
affect the impact on small entities was rejected.
This rule establishes the 2013 harvest specifications for Pacific
whiting and the allocation of Pacific whiting for the tribal whiting
fishery. This rule establishes the initial 2013 Pacific whiting
allocations for the tribal fishery and the non-tribal sectors (catcher/
processor, mothership, and shoreside), and the amount of Pacific
whiting set
[[Page 26530]]
aside for research and incidental catch in other fisheries.
In 2012, the total estimated catch of whiting by tribal and non-
tribal fishermen was 162,000 mt, or 87 percent of the U.S. TAC (186,037
mt). There was a late fall reapportionment of 28,000 mt of Pacific
whiting from the tribal to non-tribal sectors. The tribal harvest was
less than 1,000 mt, approximately 3 percent of the final tribal
allocation of 20,556 mt. In total, non-tribal sectors harvested 97
percent of the final non-tribal allocation of 163,381 mt. This rule
increases the U.S. TAC for 2013 to 269,745 mt, and the tribal
allocation will increase to 63,205 mt. After setting aside 2,500 mt for
research catch and bycatch in non-groundfish fisheries, the overall
non-tribal allocation for 2013 is 204,040 mt. The non-tribal allocation
is 28 percent higher than the 2012 non-tribal catch. In 2012, total
Pacific whiting ex-vessel revenues earned by tribal and non-tribal
fisheries reached about $50 million. If the 2013 TAC is entirely
harvested, projected ex-vessel revenues would reach $83 million, based
on 2012 ex-vessel prices. (Note that ex-vessel revenues do not take
into account wholesale or export revenues or the costs of harvesting
and processing whiting into a finished product.)
There were no significant issues raised by the public comments in
response to the IRFA. However, there was one comment that referred to
small entities. Noting that the highest annual tribal catch has been
34,500 mt, one association representing large fishing companies
commented that the proposed tribal allocation is too high. They
suggested that NMFS should be more effective in reapportioning tribal
whiting to minimize the amount of whiting stranded, as the
reapportioning process allows unharvested tribal allocations to be
fished by non-tribal fleets, benefitting both large and small
businesses. The association also suggested that pre-season plans be
required from the tribes. A detailed response to these comments is
included in the comment and response section of this final rule.
This rule establishes a tribal allocation of 63,205 mt. This
allocation is based on NMFS consultations with the tribes upon which
tribes discuss their plans with NMFS. This allocation amount is within
the long-term tribal treaty right to harvest. Applicable law requires
NMFS to provide the tribes with the opportunity to harvest their treaty
right. Should reapportionment in late fall be warranted, after
discussions with the tribes, NMFS will determine the appropriate amount
of fish to provide to the non-tribal fleets in accordance with
applicable law.
It should be also noted that under Agreement with Canada on Pacific
Hake/Whiting, as described in 77 FR 28501 (May 15, 2012), unharvested
fish are not necessarily ``stranded.'' If at the end of the year, there
are unharvested allocations, there are provisions for an amount of
these fish to be carried over into the next year's allocation process.
``If, in any year, a Party's catch is less than its individual TAC, an
amount equal to the shortfall shall be added to its individual TAC in
the following year, unless otherwise recommended by the JMC.
Adjustments under this sub-paragraph shall in no case exceed 15 percent
of a Party's unadjusted individual TAC for the year in which the
shortfall occurred.'' Such an adjustment was made for the 2013 fishery
under the Agreement: This adjustment resulted in 7,552 mt being added
to the Canadian share, for an adjusted Canadian TAC of 95,367 mt, and
21,360 mt being added to the United States share, for an adjusted
United States TAC of 269,745 mt. This results in a coastwide adjusted
TAC of 365,112 mt for 2013.
Under the RFA, the term ``small entities'' includes small
businesses, small organizations, and small governmental jurisdictions.
The Small Business Administration (SBA) has established size criteria
for all major industry sectors in the United States, including fish
harvesting and fish processing businesses. A business involved in fish
harvesting is a small business if it is independently owned and
operated and not dominant in its field of operation (including its
affiliates) and if it has combined annual receipts not in excess of
$4.0 million for all its affiliated operations worldwide. A seafood
processor is a small business if it is independently owned and
operated, not dominant in its field of operation, and employs 500 or
fewer persons on a full time, part-time, temporary, or other basis, at
all its affiliated operations worldwide. A business involved in both
the harvesting and processing of seafood products is a small business
if it meets the $4.0 million criterion for fish harvesting operations.
A wholesale business servicing the fishing industry is a small business
if it employs 100 or fewer persons on a full time, part time,
temporary, or other basis, at all its affiliated operations worldwide.
For marinas and charter/party boats, a small business is one with
annual receipts not in excess of $7.0 million. The RFA defines small
organizations as any nonprofit enterprise that is independently owned
and operated and is not dominant in its field. The RFA defines small
governmental jurisdictions as governments of cities, counties, towns,
townships, villages, school districts, or special districts with
populations of less than 50,000.
This final rule affects how whiting is allocated to the following
sectors/programs: Tribal, Shorebased Individual Fishing Quota (IFQ)
Program--Trawl Fishery, Mothership Coop (MS) Program--Whiting At-sea
Trawl Fishery, and Catcher-Processor (C/P) Coop Program--Whiting At-sea
Trawl Fishery. The amount of whiting allocated to these sectors is
based on the U.S. TAC. From the U.S. TAC, small amounts of whiting that
account for research catch and for bycatch in other fisheries are
deducted. The amount of the tribal allocation is also deducted directly
from the TAC prior to allocations to the non-tribal sectors. The
remainder is the commercial harvest guideline. This guideline is then
allocated among the other three sectors as follows: 34 percent for the
C/P Coop Program; 24 percent for the MS Coop Program; and 42 percent
for the Shorebased IFQ Program.
The shorebased IFQ fishery is managed with individual fishing
quotas for most groundfish species, including whiting. Annually, quota
pounds (QP) are allocated from the shorebased sector allocation based
on the individual quota shares (QS) of each QS owner. (QP is expressed
as a weight and QS is expressed as a percent of the shorebased
allocation for a given species or species group.). Quota pounds (QP)
may be transferred from a QS account to a vessel account or from one
vessel account to another vessel account. Vessel accounts are used to
track how QP is harvested as QP is to cover catch (landings and
discards) by limited entry trawl vessels of all IFQ species/species
groups. Shorebased IFQ catch must be landed at authorized first
receiver sites. The IFQ whiting quota shares (QS) were allocated to a
mixture of limited entry permit holders and shorebased processors. One
non-profit organization received quota share based on the ownership of
multiple limited entry permits. The Mothership (MS) coop sector can
consist of one or more coops and a non-coop subsector. For a MS coop to
participate in the Pacific whiting fishery, it must be composed of MS
catcher-vessel (MSCV) endorsed limited entry permit owners. Each
permitted MS coop is authorized to harvest a quantity of Pacific
whiting based on the sum of the catch history assignments for each
member's MS/Catcher Vessel (MSCV) endorsed permit identified in the
NMFS accepted coop
[[Page 26531]]
agreement for a given calendar year. Each MS/CV endorsed permit has an
allocation of Pacific whiting catch based on its catch history in the
fishery. The catch history assignment (CHA) is expressed as a
percentage of Pacific whiting of the total MS sector allocation.
Currently the MS sector is composed of only a single coop. The Catcher/
Processor (C/P) coop program is a limited access program that applies
to vessels in the C/P sector of the Pacific whiting at-sea trawl
fishery and is a single voluntary coop. Unlike the MS coop regulations
where multiple coops can be formed around the catch history assignments
of each coop's member's endorsed permit, the single C/P coop receives
the total Pacific whiting allocation for the C/P sector. Only C/P
endorsed limited entry permits can participate in this coop. Currently
(February 2013), the Shorebased IFQ Program is composed of 138 QS
permits/accounts, 142 vessel accounts, and 50 first receivers. The MS
coop fishery is currently composed of a single coop, with six
mothership processor permits, and 36 MS/CV endorsed permits with one
permit having two catch history assignments endorsed to it. The C/P
coop is composed of 10 catcher-processor permits owned by three
companies. There are four tribes that can participate in the tribal
whiting fishery. The current tribal fleet is composed of 5 trawlers
that either deliver to a shoreside plant or to a contracted mothership.
These regulations directly affect IFQ Quota share holders who
determine which vessel accounts receive QP, holders of MS/CV endorsed
permits who determine how many coops will participate in the fishery
and how much fish each coop is to receive, and the CP coop which is
made up of three companies that own the CP permits. As part of the
permit application processes for the non-tribal fisheries, based on a
review of the SBA size criteria, applicants are asked if they
considered themselves a ``small'' business and to provide detailed
ownership information. Although there are three non-tribal sectors,
many companies participate in two or more of these sectors. All MS/CV
participants are involved in the shorebased IFQ sector while two of the
three CP companies also participate in both the shorebased IFQ sector
and in the MS sector. Many companies own several QS accounts. After
accounting for cross participation, multiple QS account holders, and
for affiliation through ownership, there are 100 non-tribal entities
directly affected by these regulations, 82 of which are considered to
be ``small'' businesses. These regulations also directly affect tribal
whiting fisheries. Based on groundfish ex-vessel revenues and on tribal
enrollments (the population size) of each tribe, the four tribes and
their fleets are considered ``small'' entities.
There are no recordkeeping requirements associated with this final
rule.
This final rule directly regulates what entities can harvest
whiting. This rule allocates fish between tribal harvesters (harvest
vessels are small entities, tribes are small jurisdictions) and to non-
tribal harvesters (a mixture of small and large businesses). Tribal
fisheries are a mixture of activities that are similar to the
activities that non-tribal fisheries undertake. Tribal harvests are
delivered to both shoreside plants and motherships for processing.
These processing facilities also process fish harvested by non-tribal
fisheries.
The alternatives to the 2013 interim tribal allocation implemented
by this rule are the ``No-Action'' and the ``Proposed Action (or
preferred alternative).'' The preferred alternative, based on
discussions with the tribes, is for NMFS to allocate between 28 percent
and 23 percent of the U.S. total allowable catch for 2013. NMFS did not
consider a broader range of alternatives to the proposed allocation.
The tribal allocation is based primarily on the requests of the tribes.
These requests reflect the level of participation in the fishery that
will allow them to exercise their treaty right to fish for whiting.
Consideration of amounts lower than the tribal requests is not
appropriate in this instance. As a matter of policy, NMFS has
historically supported the harvest levels requested by the tribes.
Based on the information available to NMFS, the tribal request is
within their tribal treaty rights, and the participating tribe has on
occasion shown an ability to harvest the amount of whiting requested. A
higher allocation would, arguably, also be within the scope of the
treaty right. However, a higher allocation would unnecessarily limit
the non-tribal fishery.
A no-action alternative was considered, but the regulatory
framework provides for a tribal allocation on an annual basis only.
Therefore, no action would result in no allocation of Pacific whiting
to the tribal sector in 2013, which would be inconsistent with NMFS'
responsibility to manage the fishery consistent with the tribes' treaty
rights. Given that there are tribal requests for allocations in 2013,
this alternative was rejected.
There are no significant alternatives to the rule that accomplish
the stated objectives of applicable statutes and the treaties with the
affected tribes that minimize any of the significant economic impact of
the proposed rule on small entities. NMFS believes this final rule will
not adversely affect small entities. Sector allocations are higher than
sector catches in 2012, so this rule will be beneficial to both large
and small entities.
No Federal rules have been identified that duplicate, overlap, or
conflict with this action.
NMFS issued Biological Opinions under the ESA on August 10, 1990,
November 26, 1991, August 28, 1992, September 27, 1993, May 14, 1996,
and December 15, 1999 pertaining to the effects of the Pacific Coast
groundfish FMP fisheries on Chinook salmon (Puget Sound, Snake River
spring/summer, Snake River fall, upper Columbia River spring, lower
Columbia River, upper Willamette River, Sacramento River winter,
Central Valley spring, California coastal), coho salmon (Central
California coastal, southern Oregon/northern California coastal), chum
salmon (Hood Canal summer, Columbia River), sockeye salmon (Snake
River, Ozette Lake), and steelhead (upper, middle and lower Columbia
River, Snake River Basin, upper Willamette River, central California
coast, California Central Valley, south/central California, northern
California, southern California). These biological opinions have
concluded that implementation of the FMP for the Pacific Coast
groundfish fishery was not expected to jeopardize the continued
existence of any endangered or threatened species under the
jurisdiction of NMFS, or result in the destruction or adverse
modification of critical habitat.
NMFS issued a Supplemental Biological Opinion on March 11, 2006
concluding that neither the higher observed bycatch of Chinook in the
2005 whiting fishery nor new data regarding salmon bycatch in the
groundfish bottom trawl fishery required a reconsideration of its prior
``no jeopardy'' conclusion. NMFS also reaffirmed its prior
determination that implementation of the Groundfish PCGFMP is not
likely to jeopardize the continued existence of any of the affected
ESUs. Lower Columbia River coho (70 FR 37160, June 28, 2005) and Oregon
Coastal coho (73 FR 7816, February 11, 2008) were recently relisted as
threatened under the ESA. The 1999 biological opinion concluded that
the bycatch of salmonids in the Pacific whiting fishery were almost
entirely Chinook salmon, with little or
[[Page 26532]]
no bycatch of coho, chum, sockeye, and steelhead.
On December 7, 2012, NMFS completed a biological opinion concluding
that the groundfish fishery is not likely to jeopardize non-salmonid
marine species including listed eulachon, green sturgeon, humpback
whales, Steller sea lions, and leatherback sea turtles. The opinion
also concludes that the fishery is not likely to adversely modify
critical habitat for green sturgeon and leatherback sea turtles. An
analysis included in the same document as the opinion concludes that
the fishery is not likely to adversely affect green sea turtles, olive
ridley sea turtles, loggerhead sea turtles, sei whales, North Pacific
right whales, blue whales, fin whales, sperm whales, Southern Resident
killer whales, Guadalupe fur seals, or the critical habitat for Steller
sea lions.
As Steller sea lions and humpback whales are also protected under
the Marine Mammal Protection Act (MMPA), incidental take of these
species from the groundfish fishery must be addressed under MMPA
section 101(a)(5)(E). On February 27, 2012, NMFS published notice that
the incidental taking of Steller sea lions in the West Coast groundfish
fisheries is addressed in NMFS' December 29, 2010 Negligible Impact
Determination and this fishery has been added to the list of fisheries
authorized to take Steller sea lions (77 FR 11493). NMFS is currently
developing MMPA authorization for the incidental take of humpback
whales in the fishery.
On November 21, 2012, the U.S. Fish and Wildlife Service (FWS)
issued a biological opinion concluding that the groundfish fishery will
not jeopardize the continued existence of the short-tailed albatross.
The FWS also concurred that the fishery is not likely to adversely
affect the marbled murrelet, California least tern, southern sea otter,
bull trout, nor bull trout critical habitat.
Pursuant to Executive Order 13175, this final rule was developed
after meaningful consultation and collaboration with tribal officials
from the area covered by the FMP. Consistent with the Magnuson-Stevens
Act at 16 U.S.C. 1852(b)(5), one of the voting members of the Pacific
Council is a representative of an Indian tribe with federally
recognized fishing rights from the area of the Council's jurisdiction.
In addition, NMFS has coordinated specifically with the tribes
interested in the whiting fishery regarding the issues addressed by
this rule.
List of Subjects in 50 CFR Part 660
Fisheries, Fishing, Indian Fisheries.
Dated: May 2, 2013.
Alan D. Risenhoover,
Director, Office of Sustainable Fisheries, performing the functions and
duties of the Deputy Assistant Administrator for Regulatory Programs,
National Marine Fisheries Service.
For the reasons set out in the preamble, 50 CFR part 660 is amended
as follows:
PART 660--FISHERIES OFF WEST COAST STATES
0
1. The authority citation for part 660 continues to read as follows:
Authority: 16 U.S.C. 1801 et seq. and 16 U.S.C. 773 et seq.
0
2. In Sec. 660.50, paragraph (f)(4) is revised to read as follows:
Sec. 660.50 Pacific Coast treaty Indian fisheries.
* * * * *
(f) * * *
(4) Pacific whiting. The tribal allocation for 2013 is 63,205 mt.
* * * * *
0
3. Table 1a, to part 660, subpart C, is revised to read as follows:
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[GRAPHIC] [TIFF OMITTED] TR07MY13.000
[[Page 26534]]
[GRAPHIC] [TIFF OMITTED] TR07MY13.001
[[Page 26535]]
[GRAPHIC] [TIFF OMITTED] TR07MY13.002
[[Page 26536]]
[GRAPHIC] [TIFF OMITTED] TR07MY13.003
[[Page 26537]]
[GRAPHIC] [TIFF OMITTED] TR07MY13.004
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[GRAPHIC] [TIFF OMITTED] TR07MY13.005
* * * * *
0
4. In Sec. 660.140, paragraph (d)(1)(ii)(D) is revised to read as
follows:
Sec. 660.140 Shorebased IFQ Program.
* * * * *
(d) * * *
(1) * * *
(ii) * * *
(D) For the trawl fishery, NMFS will issue QP based on the
following shorebased trawl allocations:
[[Page 26539]]
Shorebased Trawl Allocations
----------------------------------------------------------------------------------------------------------------
2013 Shorebased 2014 Shorebased
IFQ Species Management area trawl allocation trawl allocation
(mt) (mt)
----------------------------------------------------------------------------------------------------------------
Arrowtooth flounder................ ................................... 3,846.13 3,467.08
BOCACCIO........................... South of 40[deg]10' N. lat. 74.90 79.00
CANARY ROCKFISH.................... ................................... 39.90 41.10
Chilipepper........................ South of 40[deg]10' N. lat. 1,099.50 1,067.25
COWCOD............................. South of 40[deg]10' N. lat. 1.00 1.00
DARKBLOTCHED ROCKFISH.............. ................................... 266.70 278.41
Dover sole......................... ................................... 22,234.50 22,234.50
English sole....................... ................................... 6,365.03 5,255.59
Lingcod............................ North of 40[deg]10' N. lat. 1,222.57 1,151.68
Lingcod............................ South of 40[deg]10' N. lat. 494.41 472.88
Longspine thornyhead............... North of 34[deg]27' N. lat. 1,859.85 1,811.40
Minor shelf rockfish complex....... North of 40[deg]10' N. lat. 508.00 508.00
Minor shelf rockfish complex....... South of 40[deg]10' N. lat. 81.00 81.00
Minor slope rockfish complex....... North of 40[deg]10' N. lat. 776.93 776.93
Minor slope rockfish complex....... South of 40[deg]10' N. lat. 376.11 378.63
Other flatfish complex............. ................................... 4,189.61 4,189.61
Pacific cod........................ ................................... 1,125.29 1,125.29
PACIFIC OCEAN PERCH................ North of 40[deg]10' N. lat. 109.43 112.28
Pacific Whiting.................... ................................... 85,697 ..................
PETRALE SOLE....................... ................................... 2,318.00 2,378.00
Sablefish.......................... North of 36[deg] N. lat. 1,828.00 1,988.00
Sablefish.......................... South of 36[deg] N. lat. 602.28 653.10
Shortspine thornyhead.............. North of 34[deg]27' N. lat. 1,385.35 1,371.12
Shortspine thornyhead.............. South of 34[deg]27' N. lat. 50.00 50.00
Splitnose rockfish................. South of 40[deg]10' N. lat. 1,518.10 1,575.10
Starry flounder.................... ................................... 751.50 755.50
Widow rockfish..................... ................................... 993.83 993.83
YELLOWEYE ROCKFISH................. ................................... 1.00 1.00
Yellowtail rockfish................ North of 40[deg]10' N. lat. 2,635.33 2,638.85
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* * * * *
[FR Doc. 2013-10806 Filed 5-6-13; 8:45 am]
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