Magnuson-Stevens Fishery Conservation and Management Act Provisions; Fisheries of the Northeastern United States; Northeast Multispecies Fishery; Framework Adjustment 47, 26104-26128 [2012-10526]
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Federal Register / Vol. 77, No. 85 / Wednesday, May 2, 2012 / Rules and Regulations
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 120109034–2171–01]
RIN 0648–BB62
Magnuson-Stevens Fishery
Conservation and Management Act
Provisions; Fisheries of the
Northeastern United States; Northeast
Multispecies Fishery; Framework
Adjustment 47
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
NMFS approves Framework
Adjustment 47 (Framework 47) to the
Northeast (NE) Multispecies Fishery
Management Plan (FMP) and
implements the approved measures. The
New England Fishery Management
Council (Council) developed and
adopted Framework 47 based on the
biennial review process established in
the NE Multispecies FMP to develop
annual catch limits (ACLs) and revise
management measures necessary to
rebuild overfished groundfish stocks
and achieve the goals and objectives of
the FMP. This action also implements
management measures and revises
existing regulations that are not
included in Framework 47, including
common pool management measures for
fishing year (FY) 2012, modification of
the Ruhle trawl definition, and
clarification of the regulations for
charter/party and recreational
groundfish vessels fishing in groundfish
closed areas. This action is intended to
prevent overfishing, rebuild overfished
stocks, achieve optimum yield, and
ensure that management measures are
based on the best available scientific
information at the time Framework 47
was submitted.
DATES: Effective May 1, 2012.
ADDRESSES: Copies of Framework 47,
the draft environmental assessment
(EA), its Regulatory Impact Review
(RIR), and the draft Initial Regulatory
Flexibility Act (IRFA) analysis prepared
by the Council are available from Paul
J. Howard, Executive Director, New
England Fishery Management Council,
50 Water Street, Mill 2, Newburyport,
MA 01950. A supplemental analysis
was included with the draft IRFA
prepared by the Council in the preamble
to the proposed rule for this action. The
Final Regulatory Flexibility Act (FRFA)
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SUMMARY:
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analysis consists of the IRFA, public
comments and responses, and the
summary of impacts and alternatives
contained in the Classification section
of this final rule and Framework 47. The
Framework 47 EA/RIR/FRFA is also
accessible via the Internet at https://
www.nefmc.org/nemulti/ or
https://www.nero.noaa.gov.
FOR FURTHER INFORMATION CONTACT:
Sarah Heil, Fishery Policy Analyst,
phone: 978–281–9257, fax: 978–281–
9135.
SUPPLEMENTARY INFORMATION:
Background
The NE Multispecies FMP specifies
management measures for 16 species in
Federal waters off the New England and
Mid-Atlantic coasts, including both
large-mesh and small-mesh species.
Small-mesh species include silver hake
(whiting), red hake, offshore hake, and
ocean pout, and large-mesh species
include Atlantic cod, haddock,
yellowtail flounder, pollock, American
plaice, witch flounder, white hake,
windowpane flounder, Atlantic halibut,
winter flounder, redfish, and Atlantic
wolffish. Large-mesh species, which are
referred to as ‘‘regulated species,’’ are
divided into 19 fish stocks, and along
with ocean pout, comprise the
groundfish complex.
Amendment 16 to the NE
Multispecies FMP (Amendment 16)
established a process for setting
acceptable biological catches (ABCs)
and ACLs for regulated species and
ocean pout, as well as for distributing
the available catch among the various
components of the groundfish fishery.
Amendment 16 also established
accountability measures (AMs) for the
20 groundfish stocks in order to prevent
overfishing of these stocks and correct
or mitigate any overages of the ACLs.
Framework 47 is part of the process
established in the FMP to set ABCs and
ACLs and to revise management
measures necessary to achieve the goals
and objectives of the FMP. The Council
developed Framework 47 to respond to
recent stock assessments and updated
stock information, as well as to revise
management measures after the fishery
has operated for more than 1 year under
ACLs and AMs. NMFS published a
proposed rule to approve Framework 47
and implement its measures on March
27, 2012 (77 FR 18176), and accepted
public comments through April 11,
2012. NMFS proposed additional
measures not included in Framework 47
to modify the Ruhle trawl definition,
clarify regulations for charter/party
vessels fishing in groundfish closed
areas, modify the conversion rate used
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to estimate the live weight of fillets and
parts of fish landed for home
consumption, and implement
management measures for the common
pool fishery for FY 2012.
Approved Measures
This section summarizes the
Framework 47 measures, all of which
have been approved, and the measures
being implemented by NMFS under the
authority of section 305(d) of the
Magnuson-Stevens Fishery
Conservation and Management Act
(Magnuson-Stevens Act), which allows
the Secretary of Commerce to
implement regulations necessary to
ensure that fishery management plans or
amendments are carried out consistent
with the Magnuson-Steven Act. The
measures implemented under this
authority are necessary to implement
changes to the Atlantic Sea Scallop FMP
proposed by the Council in Framework
47, and to change regulations that are
not part of Framework 47, but that are
necessary to clarify existing regulations
and achieve the objective of the FMP.
This final rule modifies the Rhule trawl
definition and clarifies the regulations
for charter/party vessels fishing in the
groundfish closed areas. This action
does not change the conversion rate for
home consumption landings, which
NMFS had originally proposed, for
reasons discussed below. This final rule
also implements management measures
for the common pool fishery for FY
2012 that are not included in
Framework 47, but that are
implemented by the Regional
Administrator (RA) under authority
provided by the FMP.
1. Status Determination Criteria for
Winter Flounder and Gulf of Maine Cod
New assessments were conducted for
Gulf of Maine (GOM), Georges Bank
(GB), and Southern New England/MidAtlantic (SNE/MA) winter flounder in
June 2011, and a new assessment for
GOM cod was completed in December
2011. Based on the results from the
52nd Stock Assessment Workshop
(SAW) completed in June 2011, GB
winter flounder is no longer
experiencing overfishing, and the stock
is no longer overfished. SNE/MA winter
flounder is still overfished, but
overfishing is no longer occurring for
this stock. In addition, the overfishing
status is no longer unknown for GOM
winter flounder, and overfishing is not
occurring. However, the overfished
status for GOM winter flounder is still
unknown. The results of the 53rd SAW
completed in December 2011 indicate
that overfishing is occurring for GOM
cod, and the stock is overfished.
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This final rule updates the status
determination criteria for the three
winter flounder stocks and GOM cod to
incorporate the results of the recent
stock assessments into the FMP. These
changes are based on the best scientific
information available. The revised
biomass targets for GB and SNE/MA
winter flounder is spawning stock
biomass at maximum sustainable yield
(SSBMSY), and the maximum fishing
mortality rate (F) threshold is FMSY. The
revised maximum F threshold for GOM
winter flounder is F at 40 percent of the
maximum spawning potential (F40%MSP).
The biomass target for this stock is still
undefined. For GOM cod, the biomass
target is unchanged from GARM III and
is SSB at 40 percent MSP (SSB40%MSP).
The maximum F threshold proxy is also
unchanged from GARM III and is
F40%MSP. Table 1 lists the revised status
determination criteria, and the
numerical estimates of these criteria are
shown in Table 2.
TABLE 1—STATUS DETERMINATION CRITERIA FOR WINTER FLOUNDER STOCKS AND GOM COD
Maximum fishing
mortality threshold
Stock
Biomass target
Minimum biomass threshold
GOM winter flounder .....................
GB winter flounder .........................
SNE/MA winter flounder ................
GOM cod .......................................
Undefined .....................................
SSBMSY .........................................
SSBMSY .........................................
SSB40%MSP ....................................
Undefined .....................................
1⁄2 SSB
MSY ....................................
1⁄2 SSB
MSY ....................................
1⁄2 SSB
40%MSP ...............................
F40%MSP.
FMSY.
FMSY.
F40%MSP.
TABLE 2—NUMERICAL ESTIMATES OF THE STATUS DETERMINATION CRITERIA FOR WINTER FLOUNDER STOCKS AND GOM
COD
Maximum fishing mortality
threshold
Stock
Biomass target
(mt)
GOM winter flounder ...................................................
GB winter flounder ......................................................
SNE/MA winter flounder ..............................................
GOM cod .....................................................................
0.31
0.42
0.29
0.20
Undefined.
3,700.
11,728.
10,392.
Undefined ....................................................................
10,100 .........................................................................
43,661 .........................................................................
61,218 .........................................................................
2. Rebuilding Program for GB Yellowtail
Flounder
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MSY
(mt)
GB yellowtail flounder is jointly
managed with Canada under the U.S./
Canada Resource Sharing
Understanding (Understanding).
Framework Adjustment 45 to the NE
Multispecies FMP (Framework 45)
revised the GB yellowtail flounder
rebuilding program in 2011, based on
the best available scientific information,
to rebuild the stock by 2016 with a 50percent probability of success. This
revision extended the rebuilding
program to the maximum 10-year
rebuilding period allowed by the
Magnuson-Stevens Act in order to
maximize the amount of GB yellowtail
flounder that could be caught while the
stock rebuilds.
Under the International Fisheries
Agreement Clarification Act (IFACA)
enacted into law on January 4, 2011, the
Council and NMFS have flexibility in
establishing rebuilding programs for
stocks that are jointly managed with
Canada under the Understanding.
IFACA allows the Council and NMFS to
consider decisions made under the
Understanding as management
measures under an international
agreement in order to provide an
exception to the Magnuson-Stevens
Act’s maximum 10-year rebuilding
period requirement.
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Each year, pursuant to the
Understanding, the Transboundary
Management Guidance Committee
(TMGC) meets to consider the scientific
advice of the Transboundary Resources
Assessment Committee and to make
decisions regarding total allowable
catch (TAC) recommendations for the
upcoming year for each stock managed
under the Understanding. The TMGC
adopts harvest strategies to guide its
annual TAC recommendations. The
TMGC’s harvest strategy for GB
yellowtail flounder is to maintain a low
to neutral risk of exceeding the fishing
mortality limit reference (Fref) of 0.25. At
its September 2011 meeting, the TMGC
reaffirmed its harvest strategy for GB
yellowtail flounder to maintain a low to
neutral risk of exceeding the fishing
mortality limit reference (Fref) of 0.25.
Based on that harvest strategy, the
TMGC developed its 2012 TAC
recommendation for GB yellowtail
flounder and forwarded the
recommendation to the Council for
approval (See Item 5 for more
information on the 2012 TMGC TAC
recommendations).
Given the provisions of IFACA, and
that the TMGC decisions regarding a GB
yellowtail flounder harvest strategy and
annual TAC are considered management
measures under an international
agreement, NFMS interprets the
Magnuson-Stevens Act to allow the
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rebuilding program for GB yellowtail
flounder to exceed 10 years. Therefore,
this action revises the rebuilding
strategy for GB yellowtail flounder. The
revised rebuilding strategy would
rebuild the stock by 2032 with at least
a 50-percent probability of success. This
rebuilding strategy is based on an F of
0.21 and would extend 26 years beyond
the rebuilding program start date (2006).
The rebuilding time period is as short as
possible, taking into account the
Understanding and decisions made
under it, and the needs of the fishing
communities, and will provide more
flexibility for negotiating annual catches
with Canada.
3. Overfishing Levels and Acceptable
Biological Catches
The overfishing level (OFL) for each
stock in the NE Multispecies FMP is
calculated using the estimated stock size
and FMSY (i.e., the fishing mortality rate
that, if applied over the long term,
would result in maximum sustainable
yield). The Council’s Scientific and
Statistical Committee (SSC)
recommends ABCs for each stock that
are lower than the OFLs to account for
scientific uncertainty. The ABCs are
calculated using the estimated stock size
for a particular year and are based on
the catch associated with 75 percent of
FMSY or the F required to rebuild a stock
within its rebuilding time period
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(Frebuild), whichever is lower. For SNE/
MA winter flounder, the ABC is
calculated using the F expected to result
from management measures that are
designed to achieve an F as close to zero
as practicable. For some stocks, the
Canadian share of an ABC, or the
expected Canadian catch, is deducted
from the ABC. The U.S. ABC is the
amount available to the U.S. fishery
after accounting for Canadian catch.
As part of the biennial review process
for the NE Multispecies FMP, the
Council adopts OFLs and ABCs for 3
years at a time. Although it is expected
that the Council will adopt new catch
levels every 2 years, specifying catch
levels for a third year ensures there are
default catch limits in place in the event
that a management action is delayed.
Framework 44 specified OFLps and
ABCs for each stock for FYs 2010–2012
based on the best scientific information
available, and Framework 45 revised the
OFLs and ABCs for five stocks for FYs
2011–2012 based on updated stock
information. Although Framework 44
and Framework 45 specified catch
levels for all stocks through FY 2012,
Framework 47 was developed to set
catch levels for FYs 2012–2014 and
revise the OFLs and ABCs previously
adopted for FY 2012 based on updated
stock information.
This action sets the OFLs and ABCs
for nine stocks (GB, GOM, and SNE/MA
winter flounder, pollock, northern and
southern windowpane flounder, ocean
pout, Atlantic halibut, and Atlantic
wolffish) for FYs 2012–2014 that are
assessed with an index-based stock
assessment or that have had a recent
stock assessment completed. This action
also sets the OFL and ABC for FYs
2012–2013 only for GB yellowtail
flounder based on updated stock
information. Table 3 lists the OFLs and
ABCs for these stocks.
For nine other stocks (GB cod, GB
haddock, GOM haddock, SNE/MA
yellowtail flounder, CC/GOM yellowtail
flounder, American plaice, witch
flounder, redfish, and white hake), this
action adopts the OFLs and ABCs for FY
2012 only, that were previously
specified in Framework 44 or
Framework 45 (Table 3). OFLs and
ABCs are only being set for FY 2012
based on advice from the SSC. At the
time the Council was developing
Framework 47, these stocks were last
assessed at the 3rd Groundfish
Assessment Review Meeting (GARM III)
in 2008. The SSC determined that
projections from the GARM III
assessment were not a reliable basis for
providing catch advice for these stocks
for all three fishing years from 2012–
2014. As a result, the SSC recommended
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that the Council specify ABCs for FY
2012 only based on the ABCs that were
previously adopted in Framework 44 or
Framework 45. Consistent with the SSC
recommendations, the Council adopted
the FY 2012 ABCs previously set by
Framework 44 and Framework 45 in
Framework 47. The Council also
requested that the Northeast Fisheries
Science Center complete assessment
updates for the stocks last assessed at
GARM III in order to set catch limits for
FYs 2013–2014 for these stocks. The
Council made this request with the
understanding that these catch limits
would be implemented through a
subsequent framework that the Council
is already developing.
The Council finalized and submitted
Framework 47 to NMFS on February 7,
2012. The stock assessment updates to
be used for setting FYs 2013–2014 catch
limits were not completed until
February 13–17, 2012, and the final
report for the updates was not published
until March 14, 2012. As the Council
and the SSC understood while
developing Framework 47, these
updated assessments were never
intended to be incorporated into
Framework 47 for the nine stocks for FY
2012 because they would not be
available in time for the Council and the
SSC to consider them for
implementation by the start of FY 2012.
Therefore, Framework 47 adopted the
OFLs and ABCs for FY 2012 for these
nine stocks based on the best scientific
information available at the time the
Council took final action on Framework
47.
The updated assessments for five
stocks (GB cod, GOM haddock, CC/
GOM yellowtail flounder, American
plaice, and witch flounder), indicate
that the FY 2012 ABCs adopted in
Framework 47 are significantly higher
than those suggested by the assessment
updates. For the remaining eight stocks
that were updated in early 2012, the FY
2012 ABCs adopted in Framework 47
are virtually the same, or somewhat
lower, than those suggested by the
assessment updates. Because the stock
assessment updates suggest that ABCs
might be different than those adopted in
Framework 47 for some stocks, and may
be significantly lower for the five stocks
specified above, one commenter
recommended that NMFS disapprove
the OFLs and ABCs for these stocks
because they are not consistent with
National Standard 2, which requires
actions to be consistent with best
scientific information available. This
comment is briefly discussed below to
explain NMFS’ decision to approve the
FY 2012 OFLs and ABCs despite the
comment received on this measure.
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The National Standard 2 guidelines
(50 CFR 600.315) require that each FMP
(and by extension amendment and
framework) take into account the best
scientific information available at the
time, or preparation, of an action. The
guidelines recognize that new
information often becomes available
between the initial drafting of an FMP
and its submission to NMFS for final
review. The guidelines state that this
new information should be incorporated
into the action, if practicable; but it is
unnecessary for the Council to re-start
the FMP process based on this
information, unless it indicates that
drastic changes have occurred in the
fishery that might require revision of the
management objectives or measures.
This is not a situation in which the
Council received information that
‘‘drastic changes’’ have occurred in the
fishery prior to submission of the action
to NMFS. Instead, as was fully
understood in developing Framework
47, the assessment updates would not
be completed until after the Council
took final action on Framework 47 and
submitted it to NMFS for review. As a
result, there was no practicable way to
incorporate this information into
Framework 47 without reinitiating the
Council process and delaying the action
far beyond the start of FY 2012, which
begins on May 1, 2012, and is when the
ABCs need to be in place. Therefore,
NMFS has determined that it is
appropriate for the Council to set the
OFLs and ABCs in this action based on
the best scientific information available
at the time the Council took final action
and submitted Framework 47 to NMFS
for approval. The appropriate response
to the new information that became
available after submission of Framework
47 is for the Council to consider
whether to initiate a new framework or
amendment, or to request an emergency
or interim Secretarial action, to revise
the existing measures or catch limits
adopted in this action.
Consistent with the National Standard
2 guidelines, this determination
recognizes the need for some certainty
as to what information the Council may
rely on in taking its final action, and
what information NMFS will use to
evaluate the approvability of a Council
action. Without such certainty, there
would be a lack of predictability and
confidence in Council actions, which
must be developed well in advance of
their implementation due to the time it
takes to prepare appropriate analyses
and documents for submission to NMFS
for final review. A lack of certainty
about what information will be used to
review a Council action could also
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seriously undermine the Council
process because neither the Council, nor
the public, would have confidence that
their efforts would not be meaningless.
Thus, new scientific information that
becomes available after the Council has
submitted its final action to NMFS for
review should not, based on National
Standard 2, be used retroactively to
undo recommended actions that had the
benefit of the full Council process.
NMFS also considered the practical
effect of disapproving the OFLs and
ABCs specified in this action.
Approving catch limits for these stocks,
whose assessments were updated in
early 2012, actually results in slightly
lower fishing mortality than if they were
disapproved and the default measures
specified by Framework 44 and
Framework 45 went into place. The
default catch limits for FY 2012 for the
five stocks mentioned earlier (GB cod,
GOM haddock, CC/GOM yellowtail
flounder, American plaice, and witch
flounder) are identical to those specified
in this action, except for GB cod, which
is 5 percent higher. For the remaining
stocks, the default measures are
essentially identical or higher than
those adopted in Framework 47.
Therefore, disapproving the FY 2012
ABCs in Framework 47 would result in
almost identical catch limits as those
previously specified, but a higher catch
limit for GB cod, which could increase
overfishing of this stock while the
Council develops its next management
action to incorporate the new scientific
information available.
Approving these catch limits, as
explained above, does not reduce the
importance of acting on the new
information as soon as possible in a new
action, but rather emphasizes the
importance of analyzing and
considering this information through
the full Council process. Consistent
with the SSC guidance and the
Council’s understanding during the
development of Framework 47, the
Council has already started developing
a management action that will
incorporate the assessment update
information and adopt catch limits for
the pertinent stocks for FYs 2013–2014.
The Council is scheduled to receive and
discuss the results of the assessment
updates at its April 25, 2012, meeting.
A new stock assessment for SNE/MA
yellowtail flounder is also scheduled for
June 2012, and the results of this stock
assessment will be incorporated into the
same Council action to set OFLs and
ABCs for the stock for FYs 2013–2014.
The Council may also use updated
information for other stocks to revise the
FYs 2013–2014 OFLs and ABCs
specified in this action. The Council
intends to complete this management
action by May 1, 2013, to set catch
limits for FYs 2013–2014. NMFS has
notified the Council that the updated
assessment information must be
incorporated as soon as possible, but no
later than May 1, 2013. NMFS
recommends that, at its June meeting,
the Council identify how and when this
information will be incorporated and
how that process would affect any
existing or planned management
measures.
Framework 47, as approved by the
Council on November 16, 2011, initially
proposed to set specifications for GOM
cod for FYs 2012–2014 based on the
most recent stock assessment,
completed in December 2011. The
results of that assessment indicate that
the stock is overfished and overfishing
is occurring, and that GOM cod cannot
rebuild by its rebuilding end date (2014)
even in the absence of all fishing
mortality. Given the final results of the
GOM cod assessment, and that
rebuilding cannot be achieved within
the rebuilding period, NMFS concluded
that the NE Multispecies FMP is not
26107
making adequate progress toward
ending overfishing and rebuilding GOM
cod. In a letter dated January 26, 2012,
NMFS notified the Council of this
determination and that the Council
must implement a plan by May 1, 2013,
to immediately end overfishing for GOM
cod. The Council was also notified that
it has up to 2 years to address GOM cod
rebuilding. In addition, NMFS indicated
that the Magnuson-Stevens Act provides
some flexibility for NMFS to only
reduce overfishing, rather than end it
immediately, during FY 2012 while the
Council develops measures to address
GOM cod.
At its January 25, 2012, meeting, the
Council’s SSC met to discuss the GOM
cod stock assessment. At the request of
the Council, the SSC did not
recommend ABCs for GOM cod for FYs
2012–2014. Instead, the SSC reviewed
the stock assessment and identified
issues that may warrant a closer
examination and that may influence the
interpretation of the assessment results.
Subsequently, at its February 1, 2012,
meeting, the Council did not adopt
ABCs for GOM cod for Framework 47.
The Council requested that NMFS
implement an interim action for FY
2012 to reduce overfishing on GOM cod
while the Council responds to the new
GOM cod stock assessment and
develops measures for FY 2013 that will
immediately end overfishing. In
response to the Council’s request, NMFS
published an interim action on April 3,
2012, to set catch levels for GOM cod for
FY 2012 (77 FR 19944). Therefore,
although this action does not include
OFLs and ABCs for GOM cod for FYs
2012–2014, it is not deficient regarding
GOM cod because of the interim action.
The SSC will meet in the future to
recommend ABCs for FYs 2013–2014
for GOM cod, and the Council intends
to adopt these ABCs in a future
management action.
TABLE 3—FYS 2012–2014 OFLS AND ABCS (MT)
OFL
U.S. ABC
Stock
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2012
GB cod .....................................................................................................
GB haddock .............................................................................................
GOM haddock ..........................................................................................
GB yellowtail flounder ..............................................................................
SNE/MA yellowtail flounder .....................................................................
Cape Cod (CC)/GOM yellowtail flounder ................................................
American plaice .......................................................................................
Witch flounder ..........................................................................................
GB winter flounder ...................................................................................
GOM winter flounder ................................................................................
SNE/MA winter flounder ..........................................................................
Redfish .....................................................................................................
White hake ...............................................................................................
Pollock ......................................................................................................
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7,311
51,150
1,296
1,691
3,166
1,508
4,727
2,141
4,839
1,458
2,336
12,036
5,306
19,887
Sfmt 4700
2013
2014
................
................
................
1,691
................
................
................
................
4,819
1,458
2,637
................
................
20,060
................
................
................
................
................
................
................
................
4,626
1,458
3,471
................
................
20,554
E:\FR\FM\02MYR3.SGM
2012
02MYR3
5,103
30,726
1,013
564
1,003
1,159
3,632
1,639
3,753
1,078
626
9,224
3,638
15,400
2013
2014
................
................
................
564
................
................
................
................
3,750
1,078
697
................
................
15,600
................
................
................
................
................
................
................
................
3,598
1,078
912
................
................
16,000
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TABLE 3—FYS 2012–2014 OFLS AND ABCS (MT)—Continued
OFL
U.S. ABC
Stock
2012
Northern windowpane flounder ................................................................
Southern windowpane flounder ...............................................................
Ocean pout ..............................................................................................
Atlantic halibut ..........................................................................................
Atlantic wolffish ........................................................................................
4. Annual Catch Limits
Unless otherwise noted below, the
U.S. ABC for each stock (for each fishing
year) is divided into the following
fishery components to account for all
sources of fishing mortality: State waters
(portion of ABC expected to be caught
from state waters outside Federal
management); other sub-components
(expected catch by non-groundfish
fisheries); scallop fishery; mid-water
trawl fishery; commercial groundfish
fishery; and recreational groundfish
fishery. Currently, the scallop fishery
only receives an allocation for GB and
SNE/MA yellowtail flounder, the midwater trawl fishery only receives an
allocation for GB and GOM haddock,
and the recreational groundfish fishery
only receives an allocation for GOM cod
and haddock. Once the ABC is divided,
sub-annual catch limits (sub-ACLs) and
ACL sub-components are set by
reducing the amount of the ABC
distributed to each component of the
fishery to account for management
uncertainty. Management uncertainty is
the likelihood that management
measures will result in a level of catch
greater than expected. For each stock,
management uncertainty is estimated
using the following criteria:
Enforceability, monitoring adequacy,
precision of management tools, latent
effort, and catch of groundfish in non-
230
515
342
143
92
2013
2014
230
515
342
143
92
groundfish fisheries. Appendix III of the
Framework 47 EA provides a detailed
description of the process used to
estimate management uncertainty and
calculate ACLs for this action (see
ADDRESSES).
The total ACL is the sum of all of the
sub-ACLs and ACL sub-components,
and is the catch limit for a particular
year after accounting for both scientific
and management uncertainty. Landings
and discards from all fisheries
(commercial and recreational
groundfish fishery, state waters, and
non-groundfish fisheries) are counted
against the catch limit for each stock.
Components of the fishery that are
allocated a sub-ACL for a particular
stock are subject to AMs if the catch
limit is exceeded. ACL sub-components
represent the expected catch by
components of the fishery that are not
subject to AMs (e.g., state waters).
This final rule sets ACLs for each
groundfish stock except GOM cod (see
Item 3 of this preamble), based on the
ABCs set by this action. The ACLs for
FYs 2012–2014 are listed in Table 4
through Table 7. For stocks allocated to
sectors, the commercial groundfish subACL is further divided into the nonsector (common pool) sub-ACL and the
sector sub-ACL, based on the total
vessel enrollment in all sectors and the
cumulative Potential Sector
2012
230
515
342
143
92
2013
173
386
256
85
83
173
386
256
85
83
2014
173
386
256
85
83
Contributions associated with those
sectors. The distribution of the
groundfish sub-ACL between the
common pool and sectors shown in
Tables 5 through Table 7 are based on
preliminary FY 2012 sector rosters
submitted to NMFS as of December 1,
2011, including any PSC updates or
corrections that have been made since
the proposed rule for this action was
published. This distribution differs from
the common pool and sector sub-ACLs
included in the Framework 47 EA,
which were based on FY 2011 sector
rosters, and do not reflect updated
rosters submitted to NMFS for FY 2012.
FY 2012 sector rosters will not be
finalized until May 1, 2012, because
owners of individual permits signed up
to participate in sectors have until the
end of the 2011 fishing year, or April 30,
2012, to drop out of a sector and fish in
the common pool for FY 2012. NMFS
also extended the deadline to join a
sector for FY 2012 through April 30,
2012, to provide common pool vessels
the opportunity to join a sector due to
the potential impacts of the FY 2012
GOM cod catch limits. The sector subACLs listed in the tables below may
change due to changes in the sector
rosters. If necessary, updated sector subACLs will be published in a future
adjustment rule to reflect the final FY
2012 sector rosters as of May 1, 2012.
TABLE 4—FY 2012 ALLOCATIONS TO THE RECREATIONAL GROUNDFISH FISHERY, SCALLOP FISHERY, AND MID-WATER
TRAWL FISHERY (MT)
Fishery
Stock
GOM Cod ......................................
n/a ..................................................
GOM Haddock.
259.
Scallop Fishery ........................................................................................
SNE/MA Yellowtail Flounder .........
126 .................................................
GB Yellowtail Flounder.
307.5.
Midwater Trawl Fishery ...........................................................................
mstockstill on DSK4VPTVN1PROD with RULES3
Recreational Groundfish Fishery .............................................................
GB Haddock ..................................
286 .................................................
GOM Haddock.
9.
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26109
TABLE 5—FY 2012 TOTAL ACLS, SUB-ACLS, AND ACL SUB-COMPONENTS (MT, LIVE WEIGHT)
Stock
Total ACL
GB cod .....................................................
GB haddock .............................................
GOM haddock ..........................................
GB yellowtail flounder ..............................
SNE/MA yellowtail flounder .....................
CC/GOM yellowtail flounder ....................
American plaice .......................................
Witch flounder ..........................................
GB winter flounder ...................................
GOM winter flounder ................................
SNE/MA winter flounder ..........................
Redfish .....................................................
White hake ...............................................
Pollock ......................................................
Northern windowpane flounder ................
Southern windowpane flounder ...............
Ocean pout ..............................................
Atlantic halibut ..........................................
Atlantic wolffish ........................................
4,861
29,260
958
547.8
936
1,104
3,459
1,563
3,575
1,040
603
8,786
3,465
14,736
163
381
240
83
77
Preliminary
sector
sub-ACL
Groundfish
sub-ACL
4,605
27,438
912
217.7
760
1,046
3,278
1,448
3,387
715
303
8,325
3,283
12,612
129
72
214
36
73
Preliminary
common
pool
sub-ACL
4,523
27,306
648
214.6
592
1,019
3,221
1,424
3,365
691
na
8,291
3,256
12,530
na
na
na
na
na
82
132
5
3.1
168
27
57
24
22
24
303
34
27
82
129
72
214
36
73
State waters
subcomponent
51
307
15
0.0
10
35
36
49
0
272
175
92
73
754
2
39
3
43
1
Other
subcomponent
204
1,229
22
22.6
40
23
145
66
188
54
125
369
109
1,370
33
270
23
4
3
TABLE 6—FY 2013 TOTAL ACLS, SUB-ACLS, AND ACL SUB-COMPONENTS (MT, LIVE WEIGHT)
Stock
Total ACL
GB yellowtail flounder ..............................
GB winter flounder ...................................
GOM winter flounder ................................
SNE/MA winter flounder ..........................
Pollock ......................................................
Northern windowpane flounder ................
Southern windowpane flounder ...............
Ocean pout ..............................................
Atlantic halibut ..........................................
Atlantic wolffish ........................................
547.8
3,572
1,040
672
14,927
163
381
240
83
77
Preliminary
sector
sub-ACL
Groundfish
sub-ACL
217.7
3,384
715
337
12,791
129
72
214
36
73
Preliminary
common
Pool
sub-ACL
214.6
3,362
690
na
12,707
na
na
na
na
na
3.1
22
25
337
83
129
72
214
36
73
State waters
sub-component
0.0
0
272
195
756
2
39
3
43
1
Other
sub-component
22.6
188
54
139
1,380
33
270
23
4
3
TABLE 7—FY 2014 TOTAL ACLS, SUB-ACLS, AND ACL SUB-COMPONENTS (MT, LIVE WEIGHT)
Stock
Total ACL
GB winter flounder ...................................
GOM winter flounder ................................
SNE/MA winter flounder ..........................
Pollock ......................................................
Northern windowpane flounder ................
Southern windowpane flounder ...............
Ocean pout ..............................................
Atlantic halibut ..........................................
Atlantic wolffish ........................................
3,427
1,040
879
15,308
163
381
240
83
77
mstockstill on DSK4VPTVN1PROD with RULES3
5. U.S./Canada Total Allowable Catches
Eastern GB cod, eastern GB haddock,
and GB yellowtail flounder are managed
jointly with Canada through the U.S./
Canada Resource Sharing
Understanding. Each year the TMGC,
which is made up of representatives
from Canada and the U.S., negotiates a
shared TAC for each stock based on the
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sector
sub-ACL
Groundfish
sub-ACL
3,247
715
441
13,148
129
72
214
36
73
3,226
690
0
13,062
0
0
0
0
0
most recent stock information and the
TMGC harvest strategy. The TMGC’s
harvest strategy for setting catch levels
is to maintain a low to neutral (less than
50-percent) risk of exceeding the fishing
mortality limit reference (Fref = 0.18,
0.26, and 0.25 for cod, haddock, and
yellowtail flounder, respectively). When
stock conditions are poor, fishing
mortality should be further reduced to
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Preliminary
common
pool
sub-ACL
21
25
441
86
129
72
214
36
73
State waters
subcomponent
0
272
255
760
2
39
3
43
1
Other
subcomponent
180
54
182
1,400
33
270
23
4
3
promote rebuilding. The shared TACs
are allocated between the U.S. and
Canada based on a formula that
considers historical catch percentages
and the current resource distribution
based on trawl surveys. The U.S./
Canada Management Area comprises the
entire stock area for GB yellowtail
flounder; therefore, the U.S. TAC for
this stock is also the U.S. ABC.
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Federal Register / Vol. 77, No. 85 / Wednesday, May 2, 2012 / Rules and Regulations
In September 2011, the TMGC
recommended 2012 shared TACs for
eastern GB cod, eastern GB haddock,
and GB yellowtail flounder. The TMGC
recommended a shared TAC of 675 mt
for eastern GB cod, 16,000 mt for eastern
GB haddock, and 900 mt for GB
yellowtail flounder. However, at its
September 2011 meeting, the Council’s
SSC recommended an ABC of 1,150 mt
for GB yellowtail flounder, which was
higher than the TMGC recommendation.
On September 28, 2011, the Council
reviewed the recommendations of the
TMGC and the SSC, and approved the
TMGC recommendations for eastern GB
cod and eastern GB haddock. The
Council also approved an ABC of up to
1,150 mt for GB yellowtail flounder,
consistent with the SSC’s
recommendation. The TMGC met by
conference call in October 2011 to
reconsider its 2012 recommendation for
GB yellowtail flounder since the ABC
approved by the Council was higher
than the shared TAC initially negotiated
by the TMGC. At this meeting, the
TMGC recommended a shared TAC of
1,150 mt for GB yellowtail flounder for
2012.
The 2012 U.S./Canada TACs and the
percentage shared for each country are
listed in Table 8. For 2012, the annual
percentage shares for each country are
based on a 10-percent weighting of
historical catches and a 90-percent
weighting of the current resource
distribution. Any overages of the eastern
GB cod, eastern GB haddock, or GB
yellowtail flounder U.S. TACs will be
deducted from the U.S. TAC in the
following fishing year. If FY 2011 catch
information indicates that the U.S.
fishery exceeded its TAC for any of the
shared stocks, NMFS will reduce the FY
2012 U.S. TAC for that stock in a future
management action.
TABLE 8—2012 U.S. CANADA TACS (MT, LIVE WEIGHT) AND PERCENTAGE SHARES
Eastern GB
cod
TAC
Eastern GB
haddock
GB
yellowtail
flounder
675
162 (24%)
513 (76%)
16,000
6,880 (43%)
9,120 (57%)
1,150
564 (49%)
586 (51%)
Total Shared TAC ....................................................................................................................................
U.S. TAC ..................................................................................................................................................
Canada TAC ............................................................................................................................................
6. Incidental Catch Total Allowable
Catches and Allocations to Special
Management Programs
Incidental catch TACs are specified
for certain stocks of concern (i.e., stocks
that are overfished or subject to
overfishing) for common pool vessels
fishing in the special management
programs (i.e., special access programs
(SAPs) and the Regular B Days-At-Sea
(DAS) Program), in order to limit the
catch of these stocks under each
program. Table 9 shows the percentage
of the common pool sub-ACL allocated
to the special management programs
and the FYs 2012–2014 Incidental Catch
TACs for each stock. Any catch on a trip
that ends on a Category B DAS (either
Regular or Reserve B DAS) is attributed
to the Incidental Catch TAC for the
pertinent stock. Catch on a trip that
starts under a Category B DAS and then
flips to a Category A DAS is counted
against the common pool sub-ACL.
The Incidental Catch TAC is further
divided among each special
management program based on the
percentages listed in Table 10. Table 11
lists the FYs 2012–2014 Incidental
Catch TACs for each special
management program. The FY 2012
sector rosters will not be finalized until
May 1, 2012, for the reasons mentioned
earlier in this preamble. Therefore, the
common pool sub-ACL may change due
to changes to the FY 2012 sector rosters.
Updated incidental catch TACs will be
published in a future adjustment rule, if
necessary, based on the final sector
rosters as of May 1, 2012.
TABLE 9—COMMON POOL INCIDENTAL CATCH TACS FOR FYS 2012–2014 (MT, LIVE WEIGHT)
Percentage of
common pool
sub-ACL
Stock
GB cod .............................................................................................................
GB yellowtail flounder ......................................................................................
SNE/MA yellowtail flounder .............................................................................
CC/GOM yellowtail flounder ............................................................................
Plaice ...............................................................................................................
Witch flounder ..................................................................................................
GB winter flounder ...........................................................................................
SNE/MA winter flounder ..................................................................................
White hake .......................................................................................................
2012
2
2
1
1
5
5
2
1
2
2013
1.6
0.1
1.7
0.3
2.9
1.4
0.4
3.0
0.9
2014
n/a
n/a
n/a
n/a
n/a
n/a
0.4
3.4
n/a
n/a
n/a
n/a
n/a
n/a
n/a
0.4
4.4
n/a
mstockstill on DSK4VPTVN1PROD with RULES3
TABLE 10—PERCENTAGE OF INCIDENTAL CATCH TACS DISTRIBUTED TO EACH SPECIAL MANAGEMENT PROGRAM
Regular B
DAS
program
Stock
GB cod .....................................................................................................................................................
GB yellowtail flounder ..............................................................................................................................
SNE/MA yellowtail flounder .....................................................................................................................
CC/GOM yellowtail flounder ....................................................................................................................
Plaice .......................................................................................................................................................
Witch flounder ..........................................................................................................................................
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50
50
100
100
100
100
02MYR3
Closed Area
I hook gear
haddock
SAP
16
n/a
n/a
n/a
n/a
n/a
Eastern
U.S./CA
haddock
SAP
34
50
n/a
n/a
n/a
n/a
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Federal Register / Vol. 77, No. 85 / Wednesday, May 2, 2012 / Rules and Regulations
TABLE 10—PERCENTAGE OF INCIDENTAL CATCH TACS DISTRIBUTED TO EACH SPECIAL MANAGEMENT PROGRAM—
Continued
Closed Area
I hook gear
haddock
SAP
Regular B
DAS
program
Stock
GB winter flounder ...................................................................................................................................
SNE/MA winter flounder ..........................................................................................................................
White hake ...............................................................................................................................................
50
100
100
Eastern
U.S./CA
haddock
SAP
n/a
n/a
n/a
50
n/a
n/a
TABLE 11—INCIDENTAL CATCH TACS FOR EACH SPECIAL MANAGEMENT PROGRAM FOR FY 2012–2014 (MT, LIVE
WEIGHT)
Regular B DAS
program
Stock
Closed Area I hook
gear haddock SAP
Eastern U.S./Canada
haddock SAP
2012
GB cod ...............................................................................................
GB yellowtail flounder ........................................................................
SNE/MA yellowtail flounder ...............................................................
CC/GOM yellowtail flounder ..............................................................
Plaice .................................................................................................
Witch flounder ....................................................................................
GB winter flounder .............................................................................
SNE/MA winter flounder ....................................................................
White hake .........................................................................................
7. Common Pool Trimester Total
Allowable Catches
Beginning in FY 2012, the common
pool sub-ACL for each stock (except for
SNE/MA winter flounder, windowpane
flounder, ocean pout, Atlantic wolffish,
and Atlantic halibut) will be divided
into trimester TACs. Table 12 shows the
percentage of the common pool subACL that is allocated to each trimester
for each stock. Once NMFS projects that
90 percent of the trimester TAC is
caught for a stock, the trimester TAC
area for that stock will be closed for the
remainder of the trimester. The area
closure will apply to all common pool
vessels fishing with gear capable of
2013
2014
2012
2013
2014
2012
2013
2014
0.8
0.03
1.7
0.3
2.9
1.2
0.2
3.0
0.5
n/a
n/a
n/a
n/a
n/a
n/a
0.2
3.4
n/a
n/a
n/a
n/a
n/a
n/a
n/a
0.2
4.4
n/a
0.3
n/a
n/a
n/a
n/a
n/a
n/a
n/a
n/a
0.0
n/a
n/a
n/a
n/a
n/a
n/a
n/a
n/a
0.0
n/a
n/a
n/a
n/a
n/a
n/a
n/a
n/a
0.5
0.03
n/a
n/a
n/a
n/a
0.2
n/a
n/a
0.0
n/a
n/a
n/a
n/a
n/a
0.2
n/a
n/a
0.0
n/a
n/a
n/a
n/a
n/a
0.2
n/a
n/a
catching the pertinent stock. The
trimester TAC areas for each stock, as
well as the applicable gear types, are
defined at § 648.82(n)(2). Any uncaught
portion of the trimester TAC in
Trimester 1 or Trimester 2 will be
carried forward to the next trimester
(e.g., any remaining portion of the
Trimester 1 TAC will be added to the
Trimester 2 TAC). Overages of the
trimester TAC in Trimester 1 or
Trimester 2 will be deducted from the
Trimester 3 TAC, and any overage of the
total sub-ACL will be deducted from the
following fishing year’s common pool
sub-ACL for that stock. Uncaught
portions of the Trimester 3 TAC will not
be carried over into the following
fishing year.
Table 13 lists the common pool
trimester TACs for FYs 2012–2014
based on the ACLs and sub-ACLs set in
this action (see Item 4 of this preamble).
As described earlier, vessels have until
April 30, 2012, to drop out of a sector,
and common pool vessels may join a
sector through April 30, 2012. If the
final sub-ACLs included in this rule
change as a result of changes to FY 2012
sector rosters, the trimester TACs will
also change. NMFS will update the
common pool trimester TACs in an
adjustment rule in early May 2012, if
necessary.
TABLE 12—PERCENTAGE OF COMMON POOL SUB-ACL DISTRIBUTED TO EACH TRIMESTER
Percentage of common pool sub-ACL
Stock
mstockstill on DSK4VPTVN1PROD with RULES3
Trimester 1
Trimester 2
Trimester 3
25
27
27
27
19
21
35
24
27
8
37
25
38
28
37
36
33
26
30
37
35
36
31
24
38
31
31
35
38
37
40
47
52
42
30
40
42
69
25
44
31
37
GB cod .....................................................................................................................................................
GOM cod .................................................................................................................................................
GB haddock .............................................................................................................................................
GOM haddock ..........................................................................................................................................
GB yellowtail flounder ..............................................................................................................................
SNE/MA yellowtail flounder .....................................................................................................................
CC/GOM yellowtail flounder ....................................................................................................................
American plaice .......................................................................................................................................
Witch flounder ..........................................................................................................................................
GB Winter flounder ..................................................................................................................................
GOM Winter flounder ...............................................................................................................................
Redfish .....................................................................................................................................................
White hake ...............................................................................................................................................
Pollock .....................................................................................................................................................
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Federal Register / Vol. 77, No. 85 / Wednesday, May 2, 2012 / Rules and Regulations
TABLE 13—FY 2012–2014 COMMON POOL TRIMESTER TACS
2012
2013
2014
Stock
Tri 1
GB cod .............................................................................
GB haddock .....................................................................
GOM haddock ..................................................................
GB yellowtail flounder ......................................................
SNE/MA yellowtail flounder ..............................................
CC/GOM yellowtail flounder .............................................
American plaice ................................................................
Witch flounder ..................................................................
GB winter flounder ...........................................................
GOM winter flounder ........................................................
Redfish .............................................................................
White hake .......................................................................
Pollock ..............................................................................
Tri 2
20.5
35.6
1.3
0.6
35.3
9.5
13.7
6.4
1.8
8.9
8.6
10.1
23.0
30.3
43.5
1.2
0.9
62.2
9.5
20.5
7.3
5.3
9.1
10.6
8.2
28.8
Tri 3
Tri 1
31.1
52.7
2.3
1.6
70.6
8.1
22.8
9.9
15.2
6.0
15.0
8.2
30.5
n/a
n/a
n/a
0.6
n/a
n/a
n/a
n/a
1.8
9.1
n/a
n/a
23.4
Tri 2
n/a
n/a
n/a
0.9
n/a
n/a
n/a
n/a
5.3
9.3
n/a
n/a
29.2
Tri 3
n/a
n/a
n/a
1.6
n/a
n/a
n/a
n/a
15.2
6.1
n/a
n/a
30.9
Tri 1
n/a
n/a
n/a
n/a
n/a
n/a
n/a
n/a
1.7
9.1
n/a
n/a
24.0
Tri 2
n/a
n/a
n/a
n/a
n/a
n/a
n/a
n/a
5.1
9.3
n/a
n/a
30.0
Tri 3
n/a
n/a
n/a
n/a
n/a
n/a
n/a
n/a
14.6
6.1
n/a
n/a
31.7
* Tri 1 = Trimester 1; Tri 2 = Trimester 2; Tri 3 = Trimester 3.
8. Common Pool Restricted Gear Areas
This action removes the common pool
Western GB Multispecies Restricted
Gear Area (RGA) and the SNE
Multispecies RGA. These RGAs were
implemented by Amendment 16
beginning in FY 2010 to help meet the
mortality objectives for the common
pool fishery, and primarily reduce the
catch of flatfish species by common
pool vessels. There are sufficient fishing
mortality controls for common pool
vessels to keep catch within the
common pool catch limits. Therefore,
the Western GB and SNE Multispecies
RGAs are no longer needed to control
fishing mortality for the common pool
fishery. NMFS expects that removing
the Western GB and SNE Multispecies
RGAs will facilitate fishing for common
pool vessels without risk of exceeding
the common pool catch limits. In
addition, removing these common pool
RGAs will simplify the regulations and
avoid confusion with new restricted
gear areas included in this action as an
AM for common pool and sector vessels
(see Item 9 of this preamble).
mstockstill on DSK4VPTVN1PROD with RULES3
9. Accountability Measures
AMs are required to prevent
overfishing and ensure accountability in
the fishery. Proactive AMs are intended
to prevent ACLs from being exceeded,
and reactive AMs are meant to correct
or mitigate overages if they occur.
Amendment 16 implemented AMs for
all of the groundfish stocks. Upon
approving Amendment 16, however,
NMFS notified the Council that it was
concerned that the AMs developed for
stocks not allocated to sectors lacked
sector-specific AMs. NMFS
recommended that the Council develop
appropriate AMs for these stocks in a
future action. As a result, Framework 47
intended to revise the AMs for these
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stocks for common pool and sector
vessels.
During the development of
Framework 47, there was ongoing
litigation on Amendment 16. Oceana, an
environmental organization, challenged
Amendment 16 partially because it
lacked sector-specific AMs for stocks
not allocated to sectors. On December
20, 2011, the U.S. District Court for the
District of Columbia upheld most of
Amendment 16, but found that the
Amendment’s lack of reactive AMs for
those stocks not allocated to sectors
(SNE/MA winter flounder, northern
windowpane flounder, southern
windowpane flounder, ocean pout,
Atlantic halibut, and Atlantic wolffish)
violated the Magnuson-Stevens Act. The
court remanded this single issue to
NMFS and the Council for further
action. The Council developed the
Framework 47 AMs before the Court
decided the case, however, and,
therefore, did not specifically address
this remand in Framework 47. When it
proposed Framework 47, NMFS asked
for specific comments about the
adequacy of sector specific AMs in light
of the court’s decision and remand.
Ocean Pout and Windowpane
Flounder, and Atlantic Halibut
This action adopts reactive AMs for
ocean pout, both stocks of windowpane
flounder, and Atlantic halibut for sector
and common pool vessels that would be
triggered if the total ACL is exceeded.
NMFS will evaluate total catch of each
stock in the year following the pertinent
fishing year (Year 2), and if the total
ACL for the fishing year (Year 1) is
exceeded, the AM will be implemented
in the next fishing year (Year 3). For
example, if the total ACL for ocean pout
is exceeded in FY 2012, NMFS will
implement the applicable AM for ocean
pout in FY 2014.
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The Council decided to implement
these AMs in Year 3 out of its concern
that final catch information, including
final discard estimates, needed to
evaluate total catch in the fishery would
not be available in time to implement
until Year 3.
To determine if the total ACL is
exceeded for any of these stocks, NMFS
will include catch by the groundfish
fishery as well as catch by subcomponents of the fishery (e.g., state
waters and non-groundfish fisheries).
Since these AMs are meant to restrict
catch by common pool and sector
vessels, sectors cannot be exempt from
these AM provisions. Adopting these
AMs removes the trimester TAC
provision for common pool vessels,
which was the previous AM
implemented by Amendment 16 for
these stocks that would have become
effective in FY 2012. Prior to
Framework 47, the AMs for these stocks
only applied to common pool vessels,
and did not include measures to restrict
catch by sector vessels should an ACL
be exceeded.
Currently, a sub-ACL is only allocated
to the common pool fishery for these
stocks and catch by common pool and
sector vessels is counted against the
common pool sub-ACL. If a sub-ACL is
specified in the future for other
fisheries, and AMs are developed for
these fisheries, the AMs for the
groundfish fishery or any other fisheries
would only be triggered if both the total
ACL for the stock and the fishery’s subACL are exceeded, including the
fishery’s share of any overage caused by
the other sub-components.
If the total ACL for Atlantic halibut is
exceeded in Year 1, landing of Atlantic
halibut will be prohibited by common
pool and sector vessels in Year 3. If the
total ACL is exceeded for ocean pout,
northern windowpane flounder, or
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southern windowpane flounder in year
1, gear restrictions will apply in the AM
areas developed for each stock for both
sector and common pool vessels in Year
3. For all three stocks, trawl vessels will
be required to use selective trawl gear.
Approved gears include the haddock
separator trawl, the Ruhle trawl (see
Item 14 for description of Ruhle trawl
that includes the mid-sized eliminator
(or Ruhle) trawl in the definition of this
gear type), the rope trawl, and any other
gears authorized by the Council in a
management action or approved for use
consistent with the process defined at
§ 648.85(b)(6). There are no restrictions
on longline or gillnet gear because these
gear types comprise a small amount of
the total catch for these stocks. If the
amount of the total ACL overage is
between the management uncertainty
buffer and up to 20 percent, the small
AM area will be triggered for the
pertinent stock. Currently, the
management uncertainty buffer is 5
percent; however, this buffer could be
modified in the future. If the ACL is
exceeded by 21 percent or more, the
large AM area will be triggered. The
applicable GB AM area will be
implemented if the total ACL for
northern windowpane is exceeded, and
the applicable SNE AM area will be
implemented if the total ACL for
southern windowpane is exceeded. Both
the GB and SNE AM areas will be
implemented if the total ACL for ocean
pout is exceeded. Sectors may not be
exempted from these AM provisions.
Currently, common pool and sector
vessels have a one-fish landing limit for
Atlantic halibut. Because commercial
groundfish vessels can only land one
Atlantic halibut per trip, and generally
do not target this stock, a zero
possession limit, by itself, even if
implemented sooner than Year 3, will
not likely create a sufficient incentive
for vessels to avoid catching this stock
should the total ACL be exceeded.
Therefore, NMFS finds that the reactive
AM for this stock adopted in this action
is not adequate, by itself, in light of
court’s remand described above. NMFS
recommends that the Council consider
area closures or gear-restricted areas,
similar to those adopted for
windowpane flounder and ocean pout,
as a reactive AM for Atlantic halibut.
NMFS requests that the Council take
action to ensure that necessary revisions
to the reactive AM for Atlantic halibut
are developed and implemented as soon
as possible, and that significant progress
be made on this issue by its November
2012 meeting. NMFS also requests that
the Council consider whether these
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measures could be applied retroactively
to FY 2012.
NMFS is approving the reactive AM
for Atlantic halibut because, should the
total ACL be exceeded, it will provide
some benefit to the fishery as a
conservation measure, where currently
there is none, and will alleviate
perceived inequity between sector and
common pool vessels. The AM for this
stock adopted in Amendment 16, which
would go into place if NMFS
disapproved the Framework 47 a.m.,
only applies to common pool vessels.
Common pool and sector catch would
count against the common pool subACL, and if the sub-ACL were exceeded,
the common pool sub-ACL would be
reduced by the amount of the overage in
the subsequent fishing year. In FY 2010,
sector vessels caught 92 percent of the
total commercial catch for Atlantic
halibut, and, based on preliminary catch
information, sector vessels have caught
more than 95 percent of the total
commercial catch for Atlantic halibut in
FY 2011. Therefore, although NMFS
does not find the reactive AM for this
stock adopted in this action adequate by
itself, in light of court’s remand
described above, approving this reactive
AM as a conservation measure provides
some meaningful benefit until a new, or
additional, reactive AM can be
developed.
With respect to the delayed
implementation of these reactive AMs to
Year 3, NMFS recommends that these
AMs be implemented as soon as
possible after the overage occurs, when
catch data, including final discard
information, reliably show an overage of
the catch limit, and not be bound by an
AM that only allows implementation in
Year 3. The Council recommended a
Year 3 implementation because of
concerns that final catch data for these
stocks, which include catch from state
waters and non-groundfish fisheries and
discard estimates, could not be reliably
available in time to trigger the AM in
Year 2, or earlier. As monitoring
improves, and discard estimates are
more readily available for all
components of the fishery, NMFS
anticipates that these reactive AMs can,
and should, be implemented more
quickly.
SNE/MA Winter Flounder and Atlantic
Wolffish
Amendment 16 prohibited possession
of SNE/MA winter flounder and
Atlantic wolffish by commercial vessels.
This action adopts the current zero
possession as a proactive AM for SNE/
MA winter flounder and Atlantic
wolffish for commercial vessels. Based
on FY 2010 catch information and
partial FY 2011 catch information, the
Council concluded, before the decision
in the Amendment 16 lawsuit described
above, that prohibiting possession
appears to have kept catch of these
stocks well below mortality targets, and
that such preventive measures satisfy
the AM requirements of the MagnusonStevens Act. However, although zero
possession may be a sufficient proactive
AM for these stocks, the MagnusonStevens Act requires reactive AMs.
NMFS recommends that the Council
consider area closures or gear-restricted
areas, similar to those adopted for
windowpane flounder and ocean pout,
as a reactive AM for SNE/MA winter
flounder and Atlantic wolffish. NMFS
requests that the Council take action to
ensure reactive AMs for SNE/MA winter
flounder and Atlantic wolffish are
developed and implemented as soon as
possible, and that significant progress be
made on this issue by its November
2012 meeting. NMFS also requests that
the Council consider whether these
measures could be applied retroactively
to FY 2012.
Although zero possession does not
meet the requirement for a reactive AM
for these stocks, NMFS approves these
measures because it removes a potential
inequity for common pool vessels.
Adopting zero possession for SNE/MA
winter flounder and Atlantic wolffish,
as prescribed by Framework 47,
removes the trimester TAC provision for
these stocks for common pool vessels
established by Amendment 16. Under
the default Amendment 16 measures, if
the overall sub-ACL for these stocks is
exceeded in a year, the common pool’s
sub-ACL is reduced by the amount of
the overage. This AM only applies to the
common pool, even if sector vessels
cause the overage. Because common
pool vessels generally take less than 10
percent of the total commercial catch of
these two stocks, there is a potential
inequity in only applying the AM to the
common pool vessels. Until the Council
is able to develop reactive AMs for these
two stocks, the zero possession
proactive AM will avoid
disproportionately penalizing common
pool vessels for catch by sector vessels,
and will continue to benefit the fishery
by keeping catch within allowable
levels.
10. Removal of Cap on Yellowtail
Flounder Catch in Scallop Access Areas
In 2004, Framework 39 to the NE
Multispecies FMP and Framework 16 to
the Atlantic Sea Scallop FMP
implemented a cap on the amount of
yellowtail flounder that could be caught
in the Nantucket Lightship, Closed Area
I, and Closed Area II Sea Scallop Access
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Areas. This measure was implemented
before ACL and AM provisions were
added to the NE Multispecies and
Atlantic Sea Scallop FMPs to ensure
that yellowtail flounder catches did not
exceed the target TACs for yellowtail
flounder or exceed the U.S TAC for GB
yellowtail flounder. This action removes
the 10-percent access area cap for the
Nantucket Lightship, Closed Area I, and
Closed Area II Sea Scallop Access
Areas. The scallop fishery is still subject
to its GB and SNE/MA yellowtail
flounder sub-ACLs, but there is no limit
on how much of the sub-ACLs can be
caught in the scallop access areas. The
yellowtail flounder sub-ACLs limit the
amount of yellowtail flounder that can
be caught by the scallop fishery, so a
catch cap for the access areas in no
longer necessary to meet fishing
mortality objectives.
11. Implementation of Scallop Fishery
Accountability Measure
Each year a portion of the GB and
SNE/MA yellowtail flounder ABC is
allocated to the scallop fishery as a subACL. If the scallop fishery exceeds its
sub-ACL for either of these stocks, the
statistical areas with high catch rates of
yellowtail flounder are closed to limited
access scallop vessels. The duration of
the closure depends on the magnitude
of the overage. Framework 23 to the
Atlantic Sea Scallop FMP (Framework
23) set the yellowtail flounder seasonal
closure AM schedule for scallop vessels
to ensure that the closures would occur
during the months with the highest
yellowtail flounder catch rates.
This action modifies when the AM for
the scallop fishery is triggered. The
scallop fishery AM will be triggered if:
(1) The scallop fishery exceeds it subACL for any groundfish stock, and the
total ACL for that stock is also exceeded;
or (2) the scallop fishery exceeds its subACL by 50 percent or more for any
groundfish stock, even if the total ACL
for that stock is not exceeded. If the
scallop fishery AM is triggered, the
corresponding scallop seasonal closure
will be implemented according to the
seasonal closure AM schedule.
Currently, the scallop fishery is only
allocated a sub-ACL for GB and SNE/
MA yellowtail flounder; however, this
measure applies to the scallop fishery
AM for any additional groundfish stock
that is allocated to the scallop fishery in
a future action. This measure is applied
retroactively to the 2011 scallop fishing
year.
Given the differences in the scallop
and groundfish fishing years, complete
catch information for GB and SNE/MA
yellowtail flounder will not be available
until sometime after April 30 (the end
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of the groundfish fishing year). In
addition, inseason catch information is
not available for groundfish ACL subcomponents, such as state waters catch.
As a result, when evaluating the total
catch of GB and SNE/MA yellowtail
flounder for the purposes of triggering
the scallop fishery AM, NMFS will
primarily rely on partial catch
information to project total fishing year
catch of these two stocks from state
waters and non-groundfish fisheries.
NMFS will also use partial fishing year
data to estimate GB and SNE/MA
yellowtail flounder catch by the
commercial groundfish fishery and will
project catch of these two stocks by
groundfish vessels for the remainder of
the groundfish fishing year. NMFS will
add the maximum carryover available to
the groundfish fishery to the estimate of
total catch when evaluating whether the
total ACL has been exceeded for a
groundfish stock for the purposes of
triggering the scallop fishery AM.
This measure is expected to allow
more flexibility in the fishery. The
yellowtail flounder allocation to the
scallop fishery is based on an estimated
catch of yellowtail flounder with the
projected scallop harvest for the fishing
year. There is uncertainty in the
projected yellowtail flounder catch in
the scallop fishery, and this measure
will help account for that uncertainty
without compromising the mortality
objectives for GB and SNE/MA
yellowtail flounder. In addition,
triggering the AM when the scallop
fishery exceeds its allocation by
50 percent or more will still ensure
accountability in the fishery. The
Council did not specifically include
how to reference this measure in the
scallop regulations in Framework 47;
therefore, NMFS adopts these references
under its authority in section 305(d) of
the Magnuson-Stevens Act.
12. Inseason Re-Estimation of Scallop
Fishery GB Yellowtail Flounder SubACL
The allocation of the GB yellowtail
flounder sub-ACL to the scallop fishery
is based on an estimate of the expected
GB yellowtail flounder catch in the
scallop fishery. Because there is
uncertainty in the initial estimates of
projected GB yellowtail flounder catch,
it is possible that the initial allocation
to the scallop fishery will be too low,
which could cause the scallop sub-ACL
to be exceeded, or that the initial
allocation to the scallop fishery will be
too high, which could reduce GB
yellowtail flounder yield. This measure
creates a mechanism to re-estimate the
expected GB yellowtail flounder catch
by the scallop fishery by January 15 of
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each fishing year. If the re-estimate of
projected GB yellowtail flounder
indicates that the scallop fishery will
catch less than 90 percent of its subACL, NMFS may reduce the scallop
fishery sub-ACL to the amount expected
to be caught, and increase the
groundfish fishery sub-ACL for GB
yellowtail flounder up to the difference
between the original estimate and the
revised estimate. Any increase to the
groundfish fishery sub-ACL will be
distributed to sectors and the common
pool. NMFS will not make any changes
to the GB yellowtail flounder sub-ACL
for the scallop fishery if the revised
estimate indicates that the scallop
fishery will catch 90 percent or more of
its sub-ACL. Consistent with the
Administrative Procedure Act, NMFS
will notify the public of any changes to
the GB yellowtail flounder sub-ACLs.
This measure is expected to prevent any
loss of GB yellowtail flounder yield that
may occur if the initial catch estimate of
this stock by the scallop fishery is too
high. Re-estimating the expected GB
yellowtail flounder catch by the scallop
fishery mid-season will allow additional
GB yellowtail flounder yield by the
commercial groundfish fishery, and will
help achieve optimum yield for this
stock.
Due to uncertainty associated with the
revised estimate of expected GB
yellowtail flounder catch, NMFS has the
authority to adjust the size of the change
made to the sub-ACLs for the scallop
and groundfish fisheries. Based on the
amount of the uncertainty, NMFS could
revise the sub-ACLs by any amount
between the initial estimate of expected
GB yellowtail flounder catch by the
scallop fishery and the revised estimate.
Implementation of this measure may be
delayed until data are sufficient for
NMFS to project GB yellowtail flounder
catch and re-estimate the GB yellowtail
flounder sub-ACL for the scallop fishery
mid-season. Consideration of
uncertainty and delay in
implementation of this measure will
avoid errors in re-estimating the GB
yellowtail flounder sub-ACLs if the
projected scallop fishery catch is
underestimated. Errors in the reestimation of the scallop fishery subACL could cause the scallop fishery to
exceed its sub-ACL if projected catch is
underestimated, which may trigger the
scallop fishery AM. In addition, if the
groundfish fishery catches the
additional GB yellowtail flounder
allocated mid-fishing year, the U.S. TAC
for GB yellowtail flounder could be
exceeded.
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13. Annual Measures for FY 2012 Under
Regional Administrator Authority
The FMP authorizes the RA to
implement certain types of management
measures for the common pool fishery,
the U.S./Canada Management Area, and
Special Management Programs on an
annual basis, or as needed. This rule
includes management measures for FY
2012 that are being implemented under
RA authority. These measures are not
part of Framework 47, and were not
specifically proposed by the Council,
but are included in this final rule
because they relate to Framework 47
measures (i.e., ACLs). The RA may
modify these measures if current
information indicates changes are
necessary. Any adjustments to these
measures will be implemented through
an inseason action consistent with the
Administrative Procedure Act.
Table 14 lists the initial FY 2012 trip
limits for common pool vessels. These
FY 2012 trip limits take into
consideration changes to the FY 2012
common pool sub-ACLs and sector
rosters, trimester TACs for FY 2012,
catch rates of each stock during FY
2011, bycatch, the potential for
differential DAS counting in FY 2012,
public comments received on the
26115
proposed FY 2012 trip limits, and other
available information. This action does
not change the default cod trip limit for
vessels with a limited access Handgear
A permit (300 lb (136.1. kg) per trip), an
open access Handgear B permit (75 lb
(34.0 kg) per trip), or a limited access
Small Vessel Category permit (300 lb
(136.1 kg) of cod, haddock, and
yellowtail flounder combined).
NMFS will monitor common pool
catch using dealer-reported landings,
VMS catch reports, and other available
information, and if necessary, will
adjust the common pool management
measures.
TABLE 14—INITIAL FY 2012 COMMON POOL TRIP LIMITS
Stock
Initial FY 2012 trip limits
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GOM cod ..................................................................................................
GB cod ......................................................................................................
GOM haddock ..........................................................................................
GB haddock ..............................................................................................
GOM winter flounder ................................................................................
GB winter flounder ....................................................................................
CC/GOM yellowtail flounder .....................................................................
GB yellowtail flounder ...............................................................................
SNE/MA yellowtail flounder ......................................................................
American plaice ........................................................................................
Pollock ......................................................................................................
Witch flounder ...........................................................................................
White hake ................................................................................................
Redfish ......................................................................................................
The FMP also provides the RA the
authority to allocate the total number of
trips into the Closed Area II Yellowtail
Flounder/Haddock SAP based on
several criteria, including the GB
yellowtail flounder TAC and the
amount of GB yellowtail flounder
caught outside of the SAP. In 2005,
Framework 40B (June 1, 2005; 70 FR
31323) implemented a provision that no
trips should be allocated to the Closed
Area II Yellowtail Flounder/Haddock
SAP if the available GB yellowtail
flounder catch is insufficient to support
at least 150 trips with a 15,000-lb
(6,804-kg) trip limit (i.e., 150 trips of
15,000 lb (6,804 kg)/trip, or 2,250,000 lb
(1,020,600 kg)). This calculation
accounts for the projected catch from
the area outside the SAP. Based on the
groundfish sub-ACL of 479,946 lb
(217,700 kg), there is insufficient GB
yellowtail flounder to allocate any trips
to the SAP, even if the projected catch
from outside the SAP area is zero.
Therefore, this action allocates zero
trips to the Closed Area II Yellowtail
Flounder/Haddock SAP for FY 2012.
Vessels can still fish in this SAP in FY
2012 using a haddock separator trawl, a
Ruhle trawl, or hook gear. Vessels are
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650 lb (294.8 kg) per DAS, up to 2,000 lb (907.2 kg) per trip.
2,000 lb (907.2 kg) per DAS, up to 20,000 lb (9,072 kg) per trip.
1,000 lb (453.6 kg) per trip.
10,000 lb (4,535.9 kg) per trip.
250 lb (113.4 kg) per trip.
1,000 lb (453.6 kg) per trip.
500 lb (226.8 kg) per DAS, up to 2,000 lb (907.2 kg) per trip.
500 lb (226.8 kg) per trip.
1,500 lb (680.4 kg), up to 4,500 (2,041.1 kg) per trip.
unrestricted.
unrestricted.
250 lb (113.4 kg) per trip.
1,500 lb (680.4 kg) per trip.
unrestricted.
not allowed to fish in this SAP using
flounder nets.
14. Mid-Size Ruhle Trawl
This action modifies the definition of
the Ruhle Trawl to include the smaller
dimensions of the mid-size Eliminator
trawl and only include the primary
design features of the net design. The
following modifications are being made:
Replace the minimum fishing circle
requirement with a more concise and
enforceable measure using the
minimum number of meshes at the wide
end of the first bottom belly; adjust the
mesh configuration in the forward part
of the net and the minimum kite area
requirements to that of the mid-size
Eliminator; and remove the sweep
configuration requirements. The sweep
requirements have been removed from
the definition because this component
of the gear is largely based on bottom
composition and preference, and is not
the primary bycatch reduction device.
The primary bycatch reduction device
for this gear type is the large meshes
located in the forward part of the net.
The minimum mesh sizes and minimum
kite area are reduced to enable the midsize Eliminator to meet the Ruhle trawl
definition.
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The Council requested that NMFS
implement a smaller-scale version of the
Ruhle trawl (i.e., the mid-size
Eliminator Trawl) that should be: (1)
Available for use by both sector and
non-sector vessels in the Eastern U.S./
Canada Haddock SAP and Regular B
DAS Program; and (2) assigned a
separate gear code but should not be
assigned a separate stratum for the
purpose of discard information.
Expanding this definition will increase
fishing opportunity for smaller vessels
by allowing them to utilize this smallerscale trawl, and therefore, have access to
the Haddock SAP, as well as the B DAS
program. In addition, vessels will be
able to operate under the Ruhle trawl
gear code, which will result in reduced
discard rates for certain species,
particularly depleted stocks that may
have constraining catch limits.
Vessels fishing in the Regular B DAS
Program or the Haddock SAP must use
approved trawl gear that has been
determined to reduce the catch of NE
multispecies stocks of concern. The RA
may approve additional gears for use in
the Regular B DAS Program and the
Eastern U.S./Canada Haddock SAP if a
gear meets gear performance standards
defined at § 648.85(b)(6)(iv)(J)(2). These
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gear performance standards were
developed to allow the harvest of
healthy stocks (e.g., GB haddock) while
avoiding the capture of stocks of
concern (e.g., GB cod and GB yellowtail
flounder). The full-size Eliminator trawl
(i.e., Ruhle trawl) was tested in 2006.
This experiment demonstrated that it
effectively harvested the target species
haddock while reducing catches of cod
and other stocks of concern. In response
to a Council’s request, NMFS, approved
the Ruhle trawl for use in the B DAS
Program and Haddock SAP on July 14,
2008 (73 FR 40186). The current
definition of the Ruhle trawl is specific
to the experimental net, which was
designed for relatively large vessels. The
University of Rhode Island (URI)
conducted a follow-on study that tested
two smaller versions of the Ruhle trawl
that could be used by smaller vessels
(small-size Eliminator trawl and midsize Eliminator trawl) to determine if
the catch performance of the smaller
trawls is similar to that of the full-size
trawl. Following a successful peer
review in 2010, the Council determined
that the mid-size Eliminator trawl
effectively meets the pertinent gear
performance standards and requested
that NMFS approve the use of the midsize Eliminator trawl by sector and nonsector vessels in the B DAS Program and
Haddock SAP.
Vessels participating in the NE
multispecies common pool and sector
management programs are subject to
catch limits, which include discarded
catch. Vessel Trip Report (VTR) gear
codes, in conjunction with stock area
fished and sector, are used to establish
discard strata for each NE multispecies
stock to ensure these catch limits are not
exceeded. Each discard stratum has a
particular discard rate associated with
each NE multispecies stock based on of
Northeast Fisheries Observer Program
(NEFOP) and at-sea-monitor (ASM)
data. There are currently three
commonly used VTR trawl gear codes
for groundfish: Bottom fish; haddock
separator; and Ruhle trawl. Because the
haddock separator trawl and the Ruhle
trawl were designed to fish more
selectively than a regular bottom fish
trawl, trips using these two gear types
generally have reduced catch for certain
stocks of NE multispecies, particularly
flatfish and cod, resulting in a lower
discard rate for these species. Due to the
similar catch performance
characteristics of the mid-size
Eliminator and Ruhle trawl, data from
both gear types will be pooled for the
purpose of assigning discard rates and
establishing discard strata.
The Council also requested that
NMFS create a new VTR gear code for
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the mid-size Eliminator Trawl to
monitor the catch performance of this
net design in the fishery. However,
creating a new gear code would not
achieve the Council’s objective. A midsize Eliminator trawl can range in size
from the experimental net up to the size
of the Ruhle trawl. As a result, a vessel
may correctly choose the mid-size
Eliminator Trawl VTR gear code, but the
net size could vary considerably from
the experimental net size. This would
prevent using the VTR gear code to
monitor how the experiment net
performs when adopted in the fishery.
Instead, NMFS will use foot-rope length
and discard data obtained by trips that
are accompanied by a NEFOP assigned
observer or ASM. Data from observed or
monitored vessels that are using a midsize Eliminator with a sweep that is
comparable to the experimental net
sweep of 33m (109 ft) will be used to
evaluate how the experimental gear is
performing in practice.
at a 1:1 rate against the common pool
and sector sub-ACLs. This was not
accurate. Beginning in FY 2012, all
fillets and parts of fish landed for home
consumption will be multiplied by 3 for
quota monitoring purposes. All catch by
sector and common pool vessels,
including fillets retained by crew for
home consumption, count against a
sector’s ACE for that stock or the
common pool sub-ACL for that stock.
The 3:1 counting method is consistent
with the FMP requirement that all catch
by sector and common pool vessels be
accounted for, and is also consistent
with the 3:1 counting method
implemented by the Council in
Framework 27. The 3:1 counting rate for
fillets and parts of fish will also
continue to be used to determine
compliance with possession limits for
common pool vessels.
15. Monitoring of Fillets, Fish Parts, and
Fish Landed for At-Home Consumption
In the proposed rule for this action,
NMFS proposed to replace the 3:1
counting method with new speciesspecific conversion factors for the
purposes of counting fillets and fishparts landed for at-home consumption
against the pertinent ACLs. However,
based on public comments received on
this proposed measure, and additional
analysis performed, NMFS concluded
that the 3:1 counting method is the most
accurate for counting fillets and fish
parts landed for at-home consumption
against ACLs, and that any changes to
this conversion factor should go through
the Council.
Framework Adjustment 27 to the NE
Multispecies FMP (Framework 27)
implemented a counting rate of 3:1 for
the purposes of ensuring compliance
with days-at-sea possession limits. This
counting rate was implemented prior to
implementation of ACLs and AMs in the
FMP. When Amendment 16 was
implemented in 2010, the 3:1 counting
rate was not extended for quota
monitoring purposes to ensure that all
catch by common pool and sector
vessels is counted and attributed to the
appropriate sub-ACL. Therefore, on July
19, 2011, NMFS published an interim
final rule correcting the counting
method for fillets and parts of fish
landed for home consumption (76 FR
42577). The interim final rule applied
the 3:1 counting rate to all fillets and
parts of fish landed for home
consumption by sector and common
pool vessels.
For FY 2010 and FY 2011, fish landed
for at-home consumption were counted
Framework Adjustment 33 to the NE
Multispecies FMP (Framework 33)
allowed charter/party and recreational
vessels to fish in the GOM Rolling
Closure Areas, the Western GOM
Closure Area, Cashes Ledge Closure
Area, and the Nantucket Lightship
Closed Area, provided the vessel is
issued a letter of authorization (LOA)
from the Regional Administrator.
Framework 33 prohibited vessels issued
this LOA from selling any fish, except
for species that are not managed by the
New England Fishery Management
Council (NEFMC) or the Mid-Atlantic
Fishery Management Council (MAFMC).
When NMFS implemented this action,
the regulations only provided an
exception to the sale of tuna for charter/
party vessels issued this LOA. This
exception was inconsistent with the
Council’s intent. In addition to tuna,
striped bass and lobster, among other
species, are not managed by the NEFMC
or the MAFMC, and therefore, should be
precluded from the prohibition of sale.
This action clarifies the regulations that
charter/party vessels issued a LOA to
fish in the GOM Rolling Closure Areas,
the Western GOM Closure Area, Cashes
Ledge Closure Area, and the Nantucket
Lightship Closed Area are only
prohibited from selling fishing species
managed by the NEFMC or the MAFMC.
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16. Charter/Party Vessel Closed Area
Letter of Authorization
Comments and Responses on Measures
Proposed in the Framework 47 Proposed
Rule
NMFS received nine comments
during the comment period on the
Framework 47 proposed rule from six
individuals, one industry group, the
Council, and Oceana.
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Acceptable Biological Catches and
Annual Catch Limits
Comment 1: Oceana commented that
NMFS should disapprove the catch
limits in Framework 47 because they are
not based on the best scientific
information available and, therefore,
violate National Standard 2. Oceana
stated that the stock assessment updates
completed in early 2012 should be the
basis for setting catch limits in
Framework 47, and that NMFS should
disapprove the ABCs for the 13 stocks
whose assessments were updated in
2012. Oceana also stated that NMFS
should take emergency or interim action
to revise catch limits for FY 2012.
Response: National Standard 2
guidelines (50 CFR 600.315) require that
each FMP (and by extension
amendment and framework) must take
into account the best scientific
information available at the time, or
preparation, of an action. The guidelines
recognize that new information often
becomes available between the initial
drafting of an FMP and its submission
to NMFS for final review. The
guidelines state that this new
information should be incorporated into
the action, if practicable; but it is
unnecessary for the Council to start the
FMP process over again, unless the
information indicates that drastic
changes have occurred in the fishery
that might require revision of the
management objectives or measures.
This is not a situation in which the
Council received information that
‘‘drastic changes’’ have occurred in the
fishery prior to submission of the action
to NMFS. Instead, as was fully
understood in the development of
Framework 47, the assessment updates
were not completed until after the
Council took final action on Framework
47 and submitted it to NMFS for review.
As a result, there was no practicable
way to incorporate this information into
Framework 47 without reinitiating the
Council process and delaying the action
far beyond the start of FY 2012, which
begins on May 1, 2012, and is when the
ABCs need to be in place. Therefore,
NMFS has determined that it is
appropriate for the Council to set the
OFLs and ABCs in this action based on
the best scientific information available
at the time the Council took final action
and submitted Framework 47 to NMFS
for approval. The appropriate response
to the new information that became
available after submission to NMFS is
for the Council to consider whether to
initiate a new framework or
amendment, or to request an emergency
or interim Secretarial action, to revise
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the existing measures or catch limits
adopted in this action.
Consistent with the National Standard
2 guidelines, this determination
recognizes the need for some certainty
as to what scientific information the
Council may rely on in taking its final
action, and what information NMFS
will use to evaluate the approvability of
a Council action. Without such
certainty, there would be a lack of
predictability and confidence in Council
actions, which must be developed well
in advance of their implementation due
to the time it takes to prepare
appropriate analyses and documents for
submission to NMFS for final review.
Uncertainty about what information will
be used to review a Council action
could also seriously undermine the
Council process, because neither the
Council, nor the public, would be
confident their efforts would not be
meaningless. Thus, new scientific
information that becomes available after
the Council has submitted its final
action to NMFS for review should not,
based on National Standard 2, be used
retroactively to undo recommended
actions that had the benefit of the full
Council process.
NMFS also considered the practical
effect of disapproving the OFLs and
ABCs specified in this action.
Approving the catch limits for these
stocks, whose assessments were
updated in early 2012, actually results
in slightly less fishing mortality than if
they were disapproved and the default
measures specified by Framework 44
and Framework 45 went into place. The
default catch limits for FY 2012 for the
five stocks mentioned earlier (GB cod,
GOM haddock, CC/GOM yellowtail
flounder, American plaice, and witch
flounder) are identical to those specified
in this action, except for GB cod, which
is 5 percent higher. For the remaining
stocks, the default measures are
essentially identical or higher than
those adopted in Framework 47.
Therefore, disapproving the FY 2012
ABCs in Framework 47 would result in
the same catch limits as those
previously specified, and a higher catch
limit for GB cod, which could increase
overfishing on this stock while the
Council develops its next management
action to incorporate the new scientific
information available.
Approving these catch limits, as
explained above, does not reduce the
importance of acting on the new
information as soon as possible in a new
action, but rather emphasizes the
importance of analyzing and
considering this information through
the full Council process. Consistent
with the SSC guidance and the
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Council’s understanding during the
development of Framework 47, the
Council has already started developing
a management action to incorporate the
assessment update information and
adopt catch limits for the pertinent
stocks for FYs 2013–2014. A new stock
assessment is also scheduled for SNE/
MA yellowtail flounder in June 2012,
and the results of this stock assessment
will be incorporated into the same
Council action to set OFLs and ABCs for
the stock for FYs 2013–2014. The
Council may also use updated
information for other stocks to revise the
FYs 2013–2014 OFLs and ABCs
specified in this action. The Council
intends to complete this management
action by May 1, 2013, to set catch
limits for FYs 2013–2014.
Oceana’s comment recommending
emergency action is outside the scope of
this action and is considered to be an
independent request for NMFS to take
action addressing the updated stock
assessment information. As explained
above, this new information should
preferably be considered through the
full Council process, and NMFS has
charged the Council to address this new
information as soon as possible. At the
time of this rulemaking, the Council has
not yet had the opportunity to review
and discuss the results of the
assessment updates. NMFS believes this
information is best incorporated through
the Council process, and is waiting on
a response from the Council to
Framework 47 and the assessment
updates. The Council is scheduled to
receive and discuss the results of the
assessment updates at its April 25, 2012,
meeting. NMFS has notified the Council
that the updated assessment information
must be incorporated as soon as
possible, but no later than May 1, 2013.
NMFS recommends that, at its June
meeting, the Council identify how and
when this information will be
incorporated and how that process
would affect any existing or planned
management measures.
Accountability Measures
Comment 1: The Council commented
that the use of zero possession has been
effective at keeping catches within
allowable levels for pertinent stocks.
The Council commented that adopting
zero possession as a proactive AM for
SNE/MA winter flounder and Atlantic
wolffish, and as a reactive AM for
Atlantic halibut, is the Council’s
preferred method for ensuring catch
levels are not exceeded while also
giving industry the greatest possible
opportunity to target healthy stocks.
Oceana commented that the use of zero
possession as an AM is not adequate for
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SNE/MA winter flounder, Atlantic
wolffish, or Atlantic halibut.
Response: NMFS agrees that zero
possession for SNE/MA winter flounder
and Atlantic wolffish appears to have
effectively kept catches within
allowable levels. In FY 2010, total catch
of these two stocks was well below the
total ACL, and based on preliminary
catch information, it appears that total
catches will also be below the total ACL
in FY 2011. However, as discussed in
Item 9 of this preamble, although zero
possession may be a sufficient proactive
AM for these two stocks, effective
reactive AMs remain necessary, and
must be developed as soon as possible
as a step in the ongoing process to
ensure compliance with the with the
Court remand. If zero possession
continues to be an effective proactive
AM, the reactive AM will likely not be
triggered. However, should the
proactive AM fail, and an overage of the
total ACL occurs, a reactive AM will
ensure this overage is mitigated, and
prevent repeated overages of the ACL.
For Atlantic halibut, a zero possession
reactive AM, while a step in the right
direction, by itself, is not adequate in
light of the court’s remand. Because
commercial groundfish vessels can only
land one halibut per trip, and generally
do not target halibut, a zero possession
limit will not likely create a sufficient
incentive for vessels to avoid catching
this stock should an ACL be exceeded.
NMFS recommends that the Council
consider area closures or gear-restricted
areas, similar to those adopted for
windowpane flounder and ocean pout,
as a reactive AM for these stocks. NMFS
requests that the Council take action to
ensure that effective reactive AMs are
developed and implemented as soon as
possible, and that significant progress be
made on this issue by its November
2012 meeting. NMFS also requests that
the Council consider whether these
measures could be applied retroactively
to FY 2012.
While NMFS recognizes that the AMs
approved in this action do not satisfy
the court remand, zero possession as a
proactive AM for SNE/MA winter
flounder, and as a reactive AM for
Atlantic halibut, will still provide some
benefit to prevent catch from exceeding
the ACLs for these stocks, and will
reduce a potential inequity between
common pool and sector vessels. The
initial AMs implemented by
Amendment 16 for these stocks only
applied to common pool vessels. Catch
by common pool and sector vessels
counted against the common pool subACL. Based on preliminary FY 2011
catch information, sector vessels have
caught more than 95 percent of the total
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commercial catch for SNE/ME winter
flounder, Atlantic wolffish, and Atlantic
halibut. Disapproving the Framework 47
AMs for these stocks would result in the
same default management measures for
SNE/MA winter flounder and Atlantic
wolffish (zero possession), no reactive
AM for Atlantic halibut, and would
disproportionately penalize common
pool vessels. Therefore, NMFS has
approved zero possession as a proactive
AM for SNE/MA winter flounder and
Atlantic wolffish, but recognizes that
reactive AMs are required for these
stocks and must be developed as soon
as possible. In addition, NMFS approves
the reactive AM for Atlantic halibut
because it will provide some
conservation benefit while the Council
develops a more effective reactive AM
for this stock. Approving these AMs will
also ensure the common pool vessels are
not disproportionately penalized for any
overages that may occur.
Comment 2: Oceana disagreed that an
AM should be implemented 2 years
after the fishing year in which the
overage occurred, and stated that this
measure is inconsistent with the
National Standard 1 guidelines. Oceana
suggests that inseason AMs are not
impossible and that preliminary data is
used for inseason management in other
fisheries.
Response: The Council adopted AMs
for windowpane flounder, ocean pout,
and Atlantic halibut that would be
implemented in Year 3 because
evaluating total catch includes catch of
these stocks in state waters and nongroundfish fisheries. The Council felt
that final catch data, including final
discard estimates, would not be reliably
available in time to implement these
AMs earlier than Year 3. Indeed, catch
information, including discard
estimates, are not readily available
inseason for these components of the
fishery. While we are approving this
measure because it provides a reactive
AM for these stocks should an ACL be
exceeded, where no AM currently
exists, NMFS recommends that the
Council reconsider the timing of these
AMs. NMFS recommends to the Council
that AMs should be implemented as
soon as possible, rather than 2 years
after an overage occurs, when catch
data, including final discard
information, show an overage of the
catch limit. As monitoring improves,
and discard estimates are more readily
available for all components of the
fishery, NMFS anticipates that these
reactive AMs can, and should, be
implemented more quickly.
Annual Measures for FY 2012 Under
Regional Administrator Authority
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Comment 1: One commenter favored
an 800 lb per day-at-sea (DAS) trip limit
for GOM cod. The commenter stated
that this trip limit would make each trip
more profitable and would allow hiring
one crew member, as opposed to fishing
alone.
Response: NMFS proposed a trip limit
range for GOM cod of 500 lb-800 lb per
DAS. NMFS is implementing an initial
FY 2012 trip limit for GOM cod of 650
lb per DAS. NMFS believes this trip
limit will allow a more profitable trip
than the 500 lb DAS limit in FY 2011.
A 650-lb trip limit will likely preserve
the GOM cod trimester TAC throughout
each trimester and prevent premature
closure of the trimester TAC area. If
necessary, NMFS will modify trip limits
inseason to prevent under harvest or
overharvest of the trimester TACs, or the
common pool sub-ACLs.
Comment 2: One commenter stated
that the common pool fishery does not
need the trimester TAC AM because trip
limits effectively control fishing
mortality during the fishing year and
requested that NMFS not implement the
trimester TAC AM for the common pool
fishery. This commenter also stated that
the trimester TAC AM for white hake
should not apply to vessels fishing with
longline or hook gear. Another
commenter stated that the distribution
of the common pool sub-ACL to the
trimesters should be revisited.
Response: The trimester TAC AM
provision was adopted in Amendment
16 in 2010, and is not part of
Framework 47. Accordingly, this
measure was not proposed in this
action. Because this measure was not
part of Framework 47, these comments
are irrelevant to, and outside the scope
of, the measures approved in this final
rule.
To provide some background,
however, FY 2012 will be the first
fishing year that this AM is effective for
the common pool fishery. The trimester
TAC AM serves as a reactive AM that is
triggered if an overage of the common
pool catch limit occurs. Sector-specific
reactive AMs are required for every
groundfish stock. The trimester TAC
AM is only one type of reactive AM that
the Council may use, and the Council
could develop a different AM for the
common pool fishery if it chooses.
However, any changes to the trimester
TAC AM must be developed through the
full Council process in another action,
and cannot be addressed in this rule. If
trip limits continue to be an effective
proactive AM that keep common pool
catch within allowable levels, the
trimester TAC AM will likely not be
triggered. However, if inseason
management measures fail to keep catch
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within allowable levels, the trimester
TAC AM will ensure overfishing does
not occur and mitigate any overages.
When the trimester TAC AM was
developed, the area closures for each
stock were applied to any gear types
capable of catching that stock. In
addition, the distribution of the
common pool sub-ACL was based on
the distribution of landings and the
influence of management measures on
landings patterns. NMFS does not have
the authority to modify the applicable
gear types for the white hake trimester
TAC AM or the distribution of the
common pool sub-ACL. Any
modifications to these measures must be
made through the Council process.
NMFS recommends that the
commenters raise this issue to the
Council for possible inclusion in a
future management action.
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Mid-Size Ruhle Trawl
Comment 1: Two individuals
commented that they strongly support
the proposed revision to the Ruhle trawl
definition because it will provide
smaller vessels with increased fishing
opportunities. One commenter
suggested that eliminating the
requirement for a minimum kite area (as
opposed to the proposed minimum kite
area of 19.3 sq. ft (1.8 sq. m)) would
allow more flexibility.
Response: NMFS believes that the
minimum kite size is necessary because
it will help ensure that the catch
performance of the mid-size Ruhle trawl
will be more consistent and comparable
with the catch performance of the
experimental net. The large meshes
greatly reduce catch of flounders and
cod; however, the experimental net
effectively caught other fish, such as
haddock, as a result of the relatively
high profile of the net. The high profile
of the net is due, in part, to the lift
provided by the kites. A minimum kite
size will also minimize the catch
performance differences between kites
and headrope floats. Therefore, NMFS
retained the minimum kite size
requirement.
Monitoring of Fillets, Fish Parts, and
Fish Landed for At-Home Consumption
Comment 1: One individual
commented that landing fish for home
consumption should be prohibited, and
that all catch should be counted against
the appropriate catch limit.
Response: ACLs and AMs for the
groundfish fishery were implemented
by Amendment 16 in FY 2010. Allowing
home consumption of some fish has
been a long-standing provision and was
not proposed for elimination. Therefore,
this comment is outside the scope of
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this action. In any event, landings and
discards from all fisheries are counted
against the catch limit for each stock,
including landings by commercial
groundfish vessels for home
consumption. The proposed rule was
intended only to address the
appropriateness of the conversion factor
for determining the live weight of fillets
and parts of fish landed for home
consumption. As discussed in the
response to the next comment, NMFS
decided not to implement a new
conversion factor for fish parts landed
for home consumption.
Comment 2: One individual and the
Council commented that the proposed
species-specific conversion factors for
home consumption are nearly identical
to the conversional factors used for
dressed fish, which could underestimate
the amount of fish landed for home
consumption.
Response: NMFS agrees that the
proposed species-species conversion
factors are similar to the conversion
factors used for dressed fish. Based on
additional analysis, NMFS is not
implementing the proposed speciesspecific conversion factors. Beginning in
FY 2012, all fillets and parts of fish
landed for home consumption will be
multiplied by 3 and attributed to the
appropriate sector ACE or common pool
sub-ACL. Any change to the conversion
factor should be considered by Council
first.
Changes From the Proposed Rule
NMFS has made three changes from
the proposed rule. After further review,
the coordinates for several AM areas are
revised to correct errors contained in the
proposed rule. In addition, the
regulations are further revised to reflect
the removal of the trimester TAC for the
common pool fishery for those stocks
whose AMs were revised in this action.
NMFS is not implementing speciesspecific conversion factors in place of
the 3:1 counting rate for home
consumption landings, as was proposed
in the proposed rule for this action.
Classification
Pursuant to section 304(b)(1)(A) of the
Magnuson-Stevens Act, the NMFS
Assistant Administrator determined that
Framework 47 is necessary for the
conservation and management of the NE
multispecies fishery and that it is
consistent with the Magnuson-Stevens
Act, and other applicable law.
Under 5 U.S.C. 553(d)(1), the
Assistant Administrator for Fisheries
finds good cause to waive the 30-day
delayed effectiveness of this action. The
effective date of this action affects a
parallel rulemaking approving sector
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operations plans for the start of FY 2012
on May 1, 2012. In addition, the
effective date of this action affects the
scallop fishery AM for FY 2011.
Therefore, these actions must be in
effect at the beginning of FY 2012 to
fully capture the environmental and
economic benefits of Framework 47
measures as well as the FY 2012 sector
operations plans. Due to unforeseen
circumstances related to FY 2012 catch
levels for GOM cod, the Council’s
submission of Framework 47 to NMFS
was delayed until February 2012. Due to
this constraint, this rulemaking could
not be completed further in advance of
May 1, 2012. Therefore, in order to have
this action effective at the beginning of
FY 2012, it is necessary to waive the 30day delayed effectiveness of this rule.
The waiver of the 30-day delayed
effectiveness for this final rule is in the
public interest because it is necessary to
implement a number of measures by the
start of FY 2012 that would benefit the
NE multispecies fishery and the Atlantic
sea scallop fishery. This action sets
catch levels for FY 2012–2014 for most
groundfish stocks, adopts U.S./Canada
TACs for FY 2012, removes restricted
gear areas for common pool vessels, and
alleviates the scallop fishery AM trigger
to allow the scallop fishery to catch
more yellowtail flounder. This rule also
includes measures controlling fishing
effort by common pool vessels to help
prevent the premature or overharvest of
the common pool trimester TACs and
sub-ACLs during FY 2012. Waiving the
30-day delayed effectiveness of this
final rule will ensure that the
appropriate catch levels are
implemented at the start of FY 2012.
Waiver of delayed effectiveness will
also ensure that common pool vessels
will benefit from the removal of
restricted gear areas as soon as possible.
This measure will also modify when the
scallop fishery AM is triggered to allow
the scallop fishery to catch more
yellowtail flounder before an AM is
triggered. This measure is being applied
retroactively to FY 2011, and a waiver
of the delayed effectiveness will prevent
a premature trigger of the scallop fishery
AM.
Failure to waive the 30-day delayed
effectiveness would result in the default
FY 2012 ABCs, which could be lower or
higher than those adopted in this final
rule. This could prevent vessels from
maximizing the benefit from increased
catch limits or result in catch limits that
are too high based on the best scientific
information available. Failure to waive
the 30-day delayed effectiveness of this
action could also result in no TACs
being specified for U.S./Canada stocks.
Without an allocation for Eastern GB
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cod or haddock, sector vessels would be
unable to fish in the Eastern U.S./
Canada Area. Failure to waive delayed
effectiveness will delay the removal of
the GB or SNE/MA Multispecies
Restricted Gear Areas, which would
unnecessarily burden common pool
vessels and reduce their economic
efficiency. Failure to delay could also
result in prematurely triggering the
scallop fishery AM pending final FY
2011 catch information. Thus, delaying
implementation of this final rule would
result in short-term adverse economic
impacts to groundfish and scallop
vessels and associated fishing
communities. In addition, delaying
implementation of this final rule could
increase the risk of excessive catch by
common pool vessels, and exceeding a
trimester TAC or sub-ACL, if the FY
2012 trip limits included in this rule are
not in place at the start of FY 2012.
Therefore, a 30-day delay in the
effectiveness of this rule is
impracticable and contrary to the public
interest.
This final rule has been determined to
be not significant for purposes of
Executive Order 12866.
This final rule does not contain
policies with federalism or ‘‘takings’’
implications, as those terms are defined
in E.O. 13132 and E.O. 12630,
respectively.
An FRFA was prepared for this
action, as required by section 604 of the
Regulatory Flexibility Act (RFA). The
FRFA, which includes the summary in
this rule and the analyses contained in
Framework 47 and its accompanying
EA/RIR/FRFA, describes the economic
impact the measures adopted in
Framework 47 would have on small
entities. A description of this action and
its objectives and the legal basis for this
action are contained in Framework 47
and in the preamble to the proposed
rule as well as this final rule; it is not
repeated here. All of the documents that
constitute the FRFA are available from
NMFS (see ADDRESSES). This FRFA
analyzes expected impacts of the
measures in Framework 47, including
setting GOM cod specifications based on
the new GOM cod assessment. As
explained in the preamble, however, the
Council did not adopt ABCs for GOM
cod in Framework 47. Therefore, the
following summary also includes
expected impacts of this action in the
absence of GOM cod specifications.
No issues were raised by public
comments in response to the IRFA or
with respect to the economic impacts of
this action. As a result, no changes were
made from the proposed rule.
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Description and Estimate of the Number
of Small Entities to Which the Final
Rule Will Apply
FY 2010, which is the last full fishing
year for which data are available, was
used as the baseline period in this
analysis to estimate the impacts of this
action on regulated small entities. The
measures implemented by this action
would primarily affect commercial
groundfish vessels (in a sector or in the
common pool) and commercial Atlantic
sea scallop vessels. The primary
economic impact of the action is
associated with the specification of
ACLs and sub-ACLs. The Small
Business Administration considers a
commercial fishing operation a small
entity if it has annual sales of less than
$4 million (see North American
Industry Classification System code
114111). Multiple vessels may be owned
by a single owner, and contrary to the
IRFA prepared for Framework 47, data
tracking ownership recently became
available to determine affiliated entities.
However, this FRFA does not analyze
the expected impacts of this action
using ownership groups (i.e., ownership
of multiple vessels by one owner).
Therefore, for the purposes of analysis,
each permitted vessel is treated as a
single entity, except for vessels
participating in the sector program, as
described below.
In the IRFA prepared for Framework
47, as explained in Section 8.11.2 of
Framework 47, sectors were used as the
regulated entity for the first time to
estimate impacts of this action. Sectors
were used as the entity for analysis, in
part, because each vessel’s Potential
Sector Contribution only becomes
fishable quota if the vessel is a member
of a sector. Since sectors are allocated
Annual Catch Entitlement (ACE), based
on the cumulative Potential Sector
Contribution of each individual sector
member, sectors as an affiliated entity
provides a useful approach for
analyzing the impacts of Framework 47.
This approach differs from the approach
used to prepare the IRFA for the
proposed rule to implement the 2012
sector operations plans and allocate
ACE to sectors, as well as other previous
groundfish actions. In the past,
individual vessels, not sectors, were
used as the regulated entity to estimate
impacts of measures on vessels
participating in the sector program.
NMFS determined that deeming a sector
as the regulated entity, for the purposes
of analysis under the RFA, is a useful
alternative to analyzing individual
vessels for Framework 47. NMFS
believes this analysis should also be
completed using the individual vessels
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as the regulated entity to provide
continuity with the RFA analyses of
previous actions. Therefore, a
supplemental analysis was prepared
using individual vessels as the regulated
entity to analyze the impacts of
Framework 47. This supplemental
analysis, which is described below,
along with the Framework 47 analysis,
gives the public the best description of
impacts of Framework 47.
The entities affected by this action
would include 7 large and 10 small
regulated entities participating in the
sector program, and 342 small regulated
entities in the common pool. If
individual vessels are considered
regulated entities for the sector program,
this action would affect 740 small
regulated entities enrolled in the sector
program.
If sectors are considered regulated
entities for the purposes of estimating
this rule’s impacts, this rule would
affect 7 large and 10 small regulated
entities participating in the sector
program in FY 2010. Mean gross sales
of fish for the 7 large entities was $13.7
million, and approximately $2 million
for the 10 small entities. Under this
action, 3 large entities would fall below
the threshold of $4 million in sales,
which would result in 4 large and 13
small regulated entities. NMFS
estimates this action will result in mean
gross sales for the large regulated
entities of $9.5 million, which is a 30percent reduction from the baseline
period. Mean gross sales for the small
regulated entities is estimated at $0.7
million, which is a 62-percent reduction
from the baseline period.
There were 343 commercial
groundfish vessels in the common pool
that had at least $1 in gross sales from
fish during FY 2010. All of these were
small regulated entities with mean gross
sales of $156,000. Of this amount,
NMFS estimates that gross sales from
groundfish would be approximately
$2,600 per vessel, or less than 2 percent
of the mean gross sales. Although this
action may trigger common pool AMs,
which would limit opportunities to fish
for groundfish, the impact on small
regulated entities would likely be
insignificant.
If individual vessels are considered
the regulated entities for the purposes of
this FRFA, this action would affect
substantially more small entities. During
FY 2010, for example, 740 vessels
enrolled in the sector program, and 607
remained in the common pool. During
the baseline period, 446 sector vessels
and 343 common pool vessels generated
gross sales from any species. Of those
vessels, 305 sector vessels and 145
common pool vessels generated gross
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Federal Register / Vol. 77, No. 85 / Wednesday, May 2, 2012 / Rules and Regulations
sales from groundfish species. No
individual vessel generated gross sales
in excess of $4 million. Therefore, using
individual vessels as the regulated
entity, all regulated entities are
considered small, and there are no
disproportional impacts between small
and large entities. Mean gross sales of
fish for vessels enrolled in the sector
program were $299.9K, and $138.1K for
common pool vessels. This action is
expected to reduce mean gross sales of
fish by 33 percent for sector vessels to
$200.1K. Mean gross sales for common
pool vessels are expected to decline to
$132.6K, which is less than a 5-percent
decline.
Potentially affected entities in the
scallop fishery would include 347
limited access scallop vessels and 730
general category scallop vessels. All
individual vessels in the sea scallop
fishery are considered small business
entities under the Small Business
Administration criteria. Mean gross
sales for limited access scallop vessels
are approximately $1 million, and are
approximately $80,000 for general
category scallop vessels. The statistical
areas with the highest catch rates of GB
yellowtail flounder are 562 and 525. If
this action caused one or both of these
areas to close beginning on March 1,
2013, fishing effort by scallop vessels
would be displaced to other locations,
primarily the Mid-Atlantic region. Since
more than 75 percent of revenues from
the Atlantic sea scallop fishery come
from statistical areas south of Georges
Bank, the impact of closing statistical
areas 562 or 525 is difficult to
anticipate. In addition, during FY 2010,
less than 1 percent of total revenues in
the scallop fishery came from the
statistical areas potentially affected by
this action. There were no access area
trips taken in the scallop fishery during
this time. Opening portions of statistical
area 562 to access area trips could
increase the probability of triggering an
AM for the scallop fishery, and could
increase the potential for adverse
regulatory impacts to lost access area
trips or displaced fishing effort.
However, the effect on profitability is
likely to be minimal, and because all
participating vessels are deemed to be
small regulated entities, there are no
disproportional impacts.
The primary impact of this action is
associated with setting ACLs, which
includes specification of sub-ACLs of
GB and GOM haddock to the Atlantic
herring fishery. Because this action
decreases the ABCs for GB and GOM
haddock, Atlantic herring vessels are
potentially affected by this action. In
calendar year 2010, 90 vessels were
issued a limited access herring permit
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Jkt 226001
and two vessels exceeded $4 million in
sales. Approximately 17 percent of the
haddock ABCs were landed in FY 2010,
and similar utilization of the available
quota is expected under this action.
Therefore, vessels participating in the
Atlantic herring fishery are not expected
to be affected by this action.
Of the affected entities under this
action, only groundfish sectors and
vessels are anticipated to be adversely
affected. Due to conservation needs, this
action would reduce short-term profits
for regulated small entities relative to
the baseline period. Regulated small
sector entities are estimated to be more
adversely impacted by this action than
large sector entities. Gross sales for
small sector entities would be reduced
by 63 percent, and gross sales for large
entities would be reduced by 30
percent. These are short-term impacts.
In addition, reductions in fishing
opportunities for some stocks are
necessary to ensure rebuilding. The
ability to lease quota between sectors
and consolidate quota within sectors
will help mitigate the adverse effect on
profitability. In addition, exemptions
included in the 2012 sector rule are
expected to mitigate adverse economic
impacts. However, using sectors as the
regulated entities, this action is likely to
have a significant impact on regulated
small sector entities under the
disproportionality criteria. This analysis
was based in part on anticipated
decreases in the GOM cod catch limits
for FYs 2012–2014 that were initially
proposed as part of this action.
However, Framework 47 no longer sets
the GOM cod catch limits for FY 2012–
2014, as explained in the preamble, and,
therefore, the expected impacts of this
action on regulated small entities are
likely to be less.
Description of Steps the Agency Has
Taken To Minimize the Economic
Impact on Small Entities Consistent
With the Stated Objectives of Applicable
Statues
During the development of
Framework 47, NMFS and the Council
considered ways to reduce the
regulatory burden on, and provide
flexibility for, the regulated entities in
this action. Proposed actions and
alternatives are described in detail in
Framework 47, which includes an EA,
RIR, and IRFA (available at ADDRESSES).
The measures implemented by this final
rule minimize the long-term economic
impacts on small entities to the extent
practicable. Reasonable alternatives are
limited because of the legal
requirements to implement effective
conservation measures which
necessarily may result in negative
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26121
impacts that cannot be effectively
mitigated. Moreover, the limited
number of alternatives available for this
action must be evaluated in the context
of an ever-changing fishery management
plan that has considered numerous
alternatives over the years.
Overall, this rule minimizes adverse
long-term impacts by ensuring that
management measures and catch limits
result in sustainable fishing mortality
rates promote stock rebuilding, and as a
result, maximize yield. The measures
implemented by this final rule also
provide additional flexibility for fishing
operations in the short-term. This final
rule implements several measures that
enable small entities to offset some
portion of the estimated economic
impacts. These measures include:
extending the rebuilding period for GB
yellowtail flounder; removing the
Western GB and SNE Multispecies
RGAs for common pool vessels; reestimation of the GB yellowtail flounder
sub-ACL for the scallop fishery;
eliminating the cap on yellowtail
flounder catch in the Nantucket, Closed
Area I, and Closed Area II Sea Scallop
Access Areas; and revising the scallop
fishery AM trigger.
Revisions to the status determination
criteria for the three winter flounder
stocks and GOM cod primarily affect
setting the OFLs, ABCs, and ACLs for
these stocks based on these criteria.
Over the long-term, the revised status
determination criteria limit the potential
harvest from the fishery. The MSY
values are higher for GB and SNE/MA
winter flounder than the previous MSY
values which would result in greater
potential revenues over the long-term.
This action also extends the rebuilding
period for GB yellowtail flounder,
which allows for greater yellowtail
flounder catches and result in larger
revenues for groundfish and scallop
vessels than if the rebuilding program
was not extended beyond 2016.
Adopting the U.S./Canada TACs for FY
2012 would have short-term positive
economic impacts if no U.S. TACs were
specified. Reduced revenue due to
decreases in Eastern GB cod and GB
yellowtail flounder TACs could be
mitigated if vessels are able to maximize
Eastern GB haddock catch.
Removing the Western GB
Multispecies and SNE Multispecies
RGAs for common pool vessels could
increase revenues for common pool
vessels compared to revenues if this
action was not implemented. Removing
these RGAs will likely increase common
pool landings of some stocks, increase
efficiency for common pool vessels, and
may reduce costs for common pool
vessels because vessel operators would
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Federal Register / Vol. 77, No. 85 / Wednesday, May 2, 2012 / Rules and Regulations
not be required to purchase selective
gear to fish in these areas. The economic
impacts of the AMs adopted in this
action could be mitigated by using
selective gear or fishing in other areas,
and will be addressed in a future
rulemaking implementing the AMs, if
necessary. Given the relatively small
size of the AM areas, additional trip
costs for fishing in other areas are likely
negligible.
Eliminating the 10-percent yellowtail
flounder access area caps for the scallop
fishery will reduce the incentive for
derby fishing, and will likely positively
impact on the scallop fishery. In
addition, revising the implementation of
the scallop fishery AM is expected to
mitigate economic impacts that may
occur if the scallop fishery exceeds its
yellowtail flounder allocation. This
measure will prevent the loss of scallop
landings, revenues, and increased
fishing costs compared to impacts of
this measure not being implemented.
This measure will also prevent effort
shifts to less optimal areas by scallop
vessels, as well as effort shifts into
seasons with lower meat weights for
scallops. Inseason re-estimation of the
scallop fishery GB yellowtail flounder
sub-ACL will have positive economic
benefits for the groundfish fishery.
These benefits would only occur in
years when the scallop fishery is not
projected to catch its initial sub-ACL,
and the groundfish sub-ACL is
increased mid-fishing year. When
additional quota is made available to the
groundfish fishery, revenues for the
groundfish fishery will increase if
groundfish vessels are able to catch
additional GB yellowtail flounder.
Modifying the definition of the Ruhle
trawl will provide more flexibility for
the groundfish fishery in the use of
trawl gear that minimizes catch of
stocks of concern. This measure will
provide small vessels with increased
fishing opportunities. The additional
exempted gear option will provide
vessels a choice of the most costeffective means of targeting healthy
stocks.
mstockstill on DSK4VPTVN1PROD with RULES3
Description of the Projected Reporting,
Recordkeeping, and Other Compliance
Requirements
This action contains no new
collection-of-information, reporting, or
recordkeeping requirements. This action
does not duplicate, overlap, or conflict
with any other Federal law.
List of Subjects in 50 CFR Part 648
Fisheries, Fishing, Recordkeeping and
reporting requirements.
VerDate Mar<15>2010
17:10 May 01, 2012
Jkt 226001
Dated: April 26, 2012.
Alan D. Risenhoover,
Acting Deputy Assistant Administrator For
Regulatory Programs, National Marine
Fisheries Service.
For the reasons stated in the
preamble, 50 CFR part 648 is amended
as follows:
PART 648—FISHERIES OF THE
NORTHEASTERN UNITED STATES
1. The authority citation for part 648
continues to read as follows:
■
Authority: 16 U.S.C. 1801 et seq.
2. In § 648.14,
a. Remove and reserve paragraphs
(i)(2)(vi)(B), (i)(2)(vi)(C), and (i)(3)(v)(C);
■ b. Remove paragraph (k)(7)(i)(C)(4);
■ c. Revise paragraph (k)(13)(ii)(B); and
■ d. Add paragraph (k)(20).
The revision and addition read as
follows:
■
■
§ 648.14
Prohibitions.
*
*
*
*
*
(k) * * *
(13) * * *
(ii) * * *
(B) Possess or land per trip more than
the possession or landing limits
specified in § 648.86(a), (b), (c), (e), (g),
(h), (j), (l), (m), (n), and (o);
§ 648.82(b)(5) and (6); § 648.85; or
§ 648.88, if the vessel has been issued a
limited access NE multispecies permit
or open access NE multispecies permit,
as applicable.
*
*
*
*
*
(20) AMs for both stocks of
windowpane flounder and ocean pout.
It is unlawful for any person, including
any owner or operator of a vessel issued
a valid Federal NE multispecies permit
or letter under § 648.4(a)(1)(i), unless
otherwise specified in § 648.17, to fail to
comply with the restrictions on fishing
and gear specified in § 648.90(a)(5)(i)(D).
*
*
*
*
*
■ 5. In § 648.60, paragraphs
(a)(5)(ii)(C)(1) and (3) are removed and
reserved, and paragraph (g)(1) is revised
to read as follows:
§ 648.60 Sea scallop area access program
requirements.
*
*
*
*
*
(g) * * *
(1) An LAGC scallop vessel may only
fish in the scallop access areas specified
in § 648.59(a) through (e), subject to the
seasonal restrictions specified in
§ 648.59(b)(4), (c)(4), and (d)(4), and
subject to the possession limit specified
in § 648.52(a), and provided the vessel
complies with the requirements
specified in paragraphs (a)(1), (a)(2),
(a)(6) through (9), (d), (e), (f), and (g) of
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Fmt 4701
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this section. A vessel issued both a NE
multispecies permit and an LAGC
scallop permit may fish in an approved
SAP under § 648.85 and under
multispecies DAS in the Closed Area I,
Closed Area II, and Nantucket Lightship
Sea Scallop Access Areas specified in
§ 648.59(b) through (d), provided the
vessel complies with the requirements
specified in § 648.59(b)(5)(ii), (c)(5)(ii),
and (d)(5)(ii), and this paragraph (g), but
may not fish for, possess, or land
scallops on such trips.
*
*
*
*
*
■ 6. In § 648.64, paragraph (a)
introductory text and paragraphs (b)(1)
and (c)(1) are revised to read as follows:
§ 648.64 Yellowtail flounder sub-ACLs and
AMs for the scallop fishery.
(a) As specified in § 648.55(d), and
pursuant to the biennial framework
adjustment process specified in
§ 648.90, the scallop fishery shall be
allocated a sub-ACL for the Georges
Bank and Southern New England/MidAtlantic stocks of yellowtail flounder.
Unless otherwise specified in
§ 648.90(a)(4)(iii)(C) of the NE
multispecies regulations, the sub-ACLs
for the 2011 through 2013 fishing years
are as follows:
*
*
*
*
*
(b) * * *
(1) Unless otherwise specified in
§ 648.90(a)(5)(iv) of the NE multispecies
regulations, if the Georges Bank
yellowtail flounder sub-ACL for the
scallop fishery is exceeded, the area
defined by the following coordinates
shall be closed to scallop fishing by
vessels issued a limited access scallop
permit for the period of time specified
in paragraph (b)(2) of this section:
GEORGES BANK YELLOWTAIL CLOSURE
Point
GBYT
GBYT
GBYT
GBYT
GBYT
GBYT
GBYT
GBYT
GBYT
GBYT
GBYT
GBYT
GBYT
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
N. lat.
1 ...
2 ...
3 ...
4 ...
5 ...
6 ...
7 ...
8 ...
9 ...
10
11
12
1 ...
*
41°50′
40°30.75′
40°30′
40°40′
40°40′
40°50′
40°50′
41°00′
41°00′
41°10′
41°10′
41°50′
41°50′
W. long.
66°51.94′
65°44.96′
66°40′
66°40′
66°50′
66°50′
67°00′
67°00′
67°20′
67°20′
67°40′
67°40′
66°51.94′
*
*
*
*
(c) * * *
(1) Unless otherwise specified in
§ 648.90(a)(5)(iv) of the NE multispecies
regulations, if the Southern New
England/Mid-Atlantic yellowtail
flounder sub-ACL for the scallop fishery
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Federal Register / Vol. 77, No. 85 / Wednesday, May 2, 2012 / Rules and Regulations
is exceeded, the area defined by the
following coordinates shall be closed to
scallop fishing by vessels issued a
limited access scallop permit for the
period of time specified in paragraph
(c)(2) of this section:
SOUTHERN NEW ENGLAND YELLOWTAIL
CLOSURE
Point
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
SNEYT
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
AM
N. lat.
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
41°28.4′
41°28.57′
41°20′
41°20′
41°20′
41°18′
41°17.69′
41°14.73′
39°50′
39°50′
39°50′
40°00′
40°00′
40°41.23′
41°00′
41°00′
41°20′
41°21.15′
W. long.
71°10.25′
71°10′
71°10′
70°50′
70°30′
70°15′
70°12.54′
70°00′
70°00′
71°00′
71°40′
71°40′
73°00′
73°00′
71°55′
71°40′
71°40′
71°40′
GOM COD SPAWNING PROTECTION
AREA
Point
CSPA1
CSPA2
CSPA3
CSPA4
CSPA1
*
*
*
*
*
7. In § 648.81:
a. Revise paragraphs (c)(2)(ii)(B),
(f)(2)(iii)(B), and (n); and
■ b. Remove paragraph (o).
The revsions read as follows:
■
■
§ 648.81 NE multispecies closed areas and
measures to protect EFH.
*
(iii) * * *
(B) Fish species managed by the
NEFMC or MAFMC that are harvested
or possessed by the vessel, are not sold
or intended for trade, barter or sale,
regardless of where the fish are caught;
and
*
*
*
*
*
(n) GOM Cod Spawning Protection
Area. (1) Except as specified in
paragraph (n)(2) of this section, from
April through June of each year, no
fishing vessel or person on a fishing
vessel may enter, fish in, or be in; and
no fishing gear capable of catching NE
multispecies may be used on, or be on
board, a vessel in the GOM Cod
Spawning Protection Area, as defined
by straight lines connecting the
following points in the order stated (a
chart depicting this area is available
from the RA upon request):
*
*
*
*
(c) * * *
(2) * * *
(ii) * * *
(B) Fish species managed by the
NEFMC or MAFMC that are harvested
or possessed by the vessel, are not sold
or intended for trade, barter or sale,
regardless of where the fish are caught;
and
*
*
*
*
*
(f) * * *
(2) * * *
...........
...........
...........
...........
...........
N. latitude
42°50.95′
42°47.65′
42°54.91′
42°58.27′
42°50.95′
W. longitude
70°32.22′
70°35.64′
70°41.88′
70°38.64′
70°32.22′
(2) Paragraph (n)(1) of this section
does not apply to persons on a fishing
vessel or fishing vessels:
(i) That have not been issued a NE
multispecies permit and that are fishing
exclusively in state waters;
(ii) That are fishing with or using
exempted gear as defined under this
part, excluding pelagic gillnet gear
capable of catching NE multispecies,
except for vessels fishing with a single
pelagic gillnet not longer than 300 ft
(91.4 m) and not greater than 6 ft (1.83
m) deep, with a maximum mesh size of
3 inches (7.6 cm), provided:
(A) The net is attached to the vessel
and fished in the upper two-thirds of
the water column;
(B) The net is marked with the vessel
owner’s name and vessel identification
number;
(C) There is no retention of regulated
species or ocean pout; and
(D) There is no other gear on board
capable of catching NE multispecies;
(iii) That are fishing as a charter/party
or recreational fishing vessel, provided
that:
(A) With the exception of tuna, fish
harvested or possessed by the vessel are
not sold or intended for trade, barter, or
sale, regardless where the species are
caught;
(B) The vessel has no gear other than
pelagic hook and line gear, as defined in
this part, on board unless that gear is
properly stowed pursuant to § 648.23(b);
and
(C) There is no retention of regulated
species, or ocean pout; and
(iv) That are transiting pursuant to
paragraph (i) of this section.
■ 8. In § 648.82:
■ a. Revise paragraphs (n)(2)(i)(A),
(n)(2)(ii) introductory text, and
(n)(2)(ii)(L) through (N); and
■ b. Remove paragraphs (n)(2)(ii)(O) and
(n)(2)(ii)(P).
The revisions read as follows:
§ 648.82 Effort-control program for NE
multispecies limited access vessels.
*
*
*
*
*
(n) * * *
(2) * * *
(i) Trimester TACs. (A) Trimester TAC
distribution. Any sub-ACLs specified for
common pool vessels pursuant to
§ 648.90(a)(4) shall be apportioned into
trimesters of 4 months in duration,
beginning at the start of the fishing year
(i.e., Trimester 1: May 1–August 31;
Trimester 2: September 1–December 31;
Trimester 3: January 1–April 30), as
follows):
PORTION OF COMMON POOL SUB-ACLS APPORTIONED TO EACH STOCK FOR EACH TRIMESTER
Trimester 1
(percent)
mstockstill on DSK4VPTVN1PROD with RULES3
Stock
Trimester 2
(percent)
Trimester 3
(percent)
27
25
27
27
35
19
21
37
8
27
24
28
25
36
37
26
33
35
30
37
38
24
31
36
35
31
37
38
47
40
30
52
42
25
69
42
40
37
44
GOM cod .................................................................................................................................................
GB cod .....................................................................................................................................................
GOM haddock ..........................................................................................................................................
GB haddock .............................................................................................................................................
CC/GOM yellowtail flounder ....................................................................................................................
GB yellowtail flounder ..............................................................................................................................
SNE/MA yellowtail flounder .....................................................................................................................
GOM winter flounder ...............................................................................................................................
GB winter flounder ...................................................................................................................................
Witch flounder ..........................................................................................................................................
American plaice .......................................................................................................................................
Pollock .....................................................................................................................................................
Redfish .....................................................................................................................................................
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PORTION OF COMMON POOL SUB-ACLS APPORTIONED TO EACH STOCK FOR EACH TRIMESTER—Continued
Trimester 1
(percent)
Stock
Trimester 2
(percent)
Trimester 3
(percent)
38
31
31
White hake ...............................................................................................................................................
*
*
*
*
*
(ii) Stock area closures. If the
Regional Administrator projects that 90
percent of the trimester TACs specified
in paragraph (n)(2)(i) of this section will
be caught based upon available
information, the Regional Administrator
shall close the area where 90 percent of
the catch for each such stock occurred,
according to available VTR data and
other information, to all common pool
vessels using gear capable of catching
such stocks for the remainder of that
trimester, as specified in paragraphs
(n)(2)(ii)(A) through (N) of this section,
in a manner consistent with the
Administrative Procedure Act. For
example, if the Regional Administrator
projects that 90 percent of the CC/GOM
yellowtail flounder Trimester 1 TAC
will be caught, common pool vessels
using trawl and gillnet gear shall be
prohibited from fishing in the CC/GOM
Yellowtail Flounder Closure Area
specified in paragraph (n)(2)(ii)(G) of
this section until the beginning of
Trimester 2 on September 1 of that
fishing year. Based upon all available
information, the Regional Administrator
is authorized to expand or narrow the
areas closed under this paragraph
(n)(2)(ii) in a manner consistent with the
Administrative Procedure Act. If it is
not possible to identify an area where
only 90 percent of the catch occurred,
the Regional Administrator shall close
the smallest area possible where greater
than 90 percent of the catch occurred.
*
*
*
*
*
(L) Redfish Trimester TAC Area. For
the purposes of the trimester TAC AM
closure specified in paragraph (n)(2)(ii)
of this section, the Redfish Trimester
TAC Area shall apply to common pool
vessels using trawl gear within the area
bounded by straight lines connecting
the following points in the order stated:
REDFISH TRIMESTER TAC AREA
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Point
RF1 ................
RF2 ................
RF3 ................
RF4 ................
RF5 ................
RF6 ................
RF7 ................
RF8 ................
RF9 ................
RF10 ..............
VerDate Mar<15>2010
N. latitude
(1)
43°40′
43°40′
43°20′
43°20′
(2)
42°53.1′
(2)
41°20′
41°20′
17:10 May 01, 2012
W. longitude
69°20′
69°20′
69°00′
69°00′
67°40′
67°40′
67°44.4′
67°40′
67°40′
68°10′
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REDFISH TRIMESTER TAC AREA—
Continued
Point
RF11
RF12
RF13
RF14
RF15
RF16
RF17
RF18
RF19
RF20
N. latitude
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
41°10′
41°10′
41°00′
41°00′
41°10′
41°10′
41°20′
41°20′
(4 )
(5 )
W. longitude
68°10′
68°20′
68°20′
69°30′
69°30′
69°50′
69°50′
(3)
70°00′
70°00′
1 Intersection
with ME shoreline.
maritime boundary.
shoreline of Nantucket, MA.
4 North-facing shoreline of Nantucket, MA.
5 South-facing shoreline of Cape Cod, MA.
2 U.S./Canada
3 East-facing
(M) White Hake Trimester TAC Area.
For the purposes of the trimester TAC
AM closure specified in paragraph
(n)(2)(ii) of this section, the White Hake
Trimester TAC Area shall apply to
common pool vessels using trawl gear,
sink gillnet gear, and longline/hook gear
within the area bounded by straight
lines connecting the following points in
the order stated:
TAC Area shall apply to common pool
vessels using trawl gear, sink gillnet
gear, and longline/hook gear within the
area bounded by straight lines
connecting the following points in the
order stated:
POLLOCK TRIMESTER TAC AREA
Point
N. latitude
RF1 ................
RF2 ................
RF3 ................
RF4 ................
RF5 ................
RF6 ................
RF7 ................
RF8 ................
RF9 ................
RF10 ..............
RF11 ..............
RF12 ..............
RF13 ..............
RF14 ..............
RF15 ..............
RF16 ..............
RF17 ..............
RF18 ..............
RF19 ..............
RF20 ..............
(1 )
43°40′
43°40′
43°20′
43°20′
(2 )
42°53.1′
(2 )
41°20′
41°20′
41°10′
41°10′
41°00′
41°00′
41°10′
41°10′
41°20′
41°20′
(4 )
(5 )
W. longitude
69°20′
69°20′
69°00′
69°00′
67°40′
67°40′
67°44.4′
67°40′
67°40′
68°10′
68°10′
68°20′
68°20′
69°30′
69°30′
69°50′
69°50′
(3)
70°00′
70°00′
1 Intersection
with ME shoreline.
maritime boundary.
shoreline of Nantucket, MA.
4 North-facing shoreline of Nantucket, MA.
5 South-facing shoreline of Cape Cod, MA.
WHITE HAKE TRIMESTER TAC AREA
2 U.S./Canada
3 East-facing
Point
N. latitude
(1 )
43°40′
43°40′
43°20′
43°20′
(2 )
42°53.1′
(2 )
41°20′
41°20′
41°10′
41°10′
41°00′
41°00′
41°10′
41°10′
41°20′
41°20′
(4 )
(5 )
RF1 ................
RF2 ................
RF3 ................
RF4 ................
RF5 ................
RF6 ................
RF7 ................
RF8 ................
RF9 ................
RF10 ..............
RF11 ..............
RF12 ..............
RF13 ..............
RF14 ..............
RF15 ..............
RF16 ..............
RF17 ..............
RF18 ..............
RF19 ..............
RF20 ..............
W. longitude
69°20′
69°20′
69°00′
69°00′
67°40′
67°40′
67°44.4′
67°40′
67°40′
68°10′
68°10′
68°20′
68°20′
69°30′
69°30′
69°50′
69°50′
(3)
70°00′
70°00′
1 Intersection
with ME shoreline.
maritime boundary.
3 East-facing shoreline of Nantucket, MA.
4 North-facing shoreline of Nantucket, MA.
5 South-facing shoreline of Cape Cod, MA.
2 U.S./Canada
(N) Pollock Trimester TAC Area. For
the purposes of the trimester TAC AM
closure specified in paragraph (n)(2)(ii)
of this section, the Pollock Trimester
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*
*
*
*
*
9. In § 648.85:
a. Revise paragraphs (b)(5) and
(b)(6)(iv)(J)(3)(i) through (v); and
■ b. Remove paragraphs
(b)(6)(iv)(J)(3)(vi) and (c)(1) through (3).
The revisions read as follows:
■
■
§ 648.85
Special management programs.
*
*
*
*
*
(b) * * *
(5) Incidental Catch TACs. Unless
otherwise specified in this paragraph
(b)(5), Incidental Catch TACs shall be
based upon the portion of the ACL for
a stock specified for the common pool
vessels pursuant to § 648.90(a)(4), and
allocated as described in this paragraph
(b)(5), for each of the following stocks:
GOM cod, GB cod, GB yellowtail
flounder, GB winter flounder, CC/GOM
yellowtail flounder, American plaice,
white hake, SNE/MA yellowtail
flounder, SNE/MA winter flounder, and
witch flounder. Because GB yellowtail
flounder and GB cod are transboundary
stocks, the incidental catch TACs for
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these stocks shall be based upon the
common pool portion of the ACL
available to U.S. vessels. NMFS shall
send letters to limited access NE
multispecies permit holders notifying
them of such TACs.
(i) Stocks other than GB cod, GB
yellowtail flounder, and GB winter
flounder. With the exception of GB cod,
GB yellowtail flounder, and GB winter
flounder, 100 percent of the Incidental
Catch TACs specified in this paragraph
(b)(5) shall be allocated to the Regular
B DAS Program described in paragraph
(b)(6) of this section.
(ii) GB cod. The Incidental Catch TAC
for GB cod specified in this paragraph
(b)(5) shall be subdivided as follows: 50
percent to the Regular B DAS Program
described in paragraph (b)(6) of this
section; 16 percent to the CA I Hook
Gear Haddock SAP described in
paragraph (b)(7) of this section; and 34
percent to the Eastern U.S./Canada
Haddock SAP described in paragraph
(b)(8) of this section.
(6) * * *
(iv) * * *
(J) * * *
(3) * * *
(i) The net must be constructed with
four seams (i.e., a net with a top and
bottom panel and two side panels), and
include at least the following net
sections as depicted in Figure 1 of this
part (this figure is also available from
the Administrator, Northeast Region):
Top jib, bottom jib, jib side panels (× 2),
top wing, bottom wing, wing side panels
(× 2), bunt, square, square side panels (×
2), first top belly, first bottom belly, first
belly side panels (× 2), and second
bottom belly.
(ii) The top and bottom jibs, jib side
panels, top and bottom wings, and wing
side panels, bunt, and first bottom belly
(the first bottom belly and all portions
of the net in front of the first bottom
belly, with the exception of the square
and the square side panels) must be at
least two meshes long in the fore and aft
direction. For these net sections, the
stretched length of any single mesh
must be at least 7.9 ft (240 cm),
measured in a straight line from knot to
knot.
(iii) Mesh size in all other sections
must be consistent with mesh size
requirements specified under § 648.80
and meet the following minimum
specifications: Each mesh in the square,
square side panels, and second bottom
belly must be 31.5 inches (80 cm); each
mesh in the first top belly, and first
belly side panels must be at least 7.9
inches (20 cm); and 6 inches (15.24 cm)
or larger in sections following the first
top belly and second bottom belly
sections, all the way to the codend. The
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mesh size requirements of the top
sections apply to the side panel
sections.
(iv) The trawl must have at least 15
meshes (240 cm each) at the wide end
of the first bottom belly, excluding the
gore.
(v) The trawl must have a single or
multiple kite panels with a total surface
area of at least 19.3 sq. ft. (1.8 sq. m) on
the forward end of the square to help
maximize headrope height, for the
purpose of capturing rising fish. A kite
panel is a flat structure, usually semiflexible, used to modify the shape of
trawl and mesh openings by providing
lift when a trawl is moving through the
water.
*
*
*
*
*
10. In § 648.86, revise paragraph (c) to
read as follows:
■
§ 648.86 NE Multispecies possession
restrictions.
*
*
*
*
*
(c) Atlantic halibut. A vessel issued a
NE multispecies permit under
§ 648.4(a)(1) may land or possess on
board no more than one Atlantic halibut
per trip, provided the vessel complies
with other applicable provisions of this
part, unless otherwise specified in
§ 648.90(a)(5)(i)(D)(2).
*
*
*
*
*
11. In § 648.87, revise paragraph
(c)(2)(i) to read as follows:
■
§ 648.87
Sector allocation.
*
*
*
*
*
(c) * * *
(2) * * *
(i) Regulations that may not be
exempted for sector participants. The
Regional Administrator may not exempt
participants in a sector from the
following Federal fishing regulations:
NE multispecies year-round closure
areas; permitting restrictions (e.g., vessel
upgrades, etc.); gear restrictions
designed to minimize habitat impacts
(e.g., roller gear restrictions, etc.);
reporting requirements; and AMs
specified at § 648.90(a)(5)(i)(D). For the
purposes of this paragraph (c)(2)(i), the
DAS reporting requirements specified at
§ 648.82; the SAP-specific reporting
requirements specified at § 648.85; and
the reporting requirements associated
with a dockside monitoring program
specified in paragraph (b)(5)(i) of this
section are not considered reporting
requirements, and the Regional
Administrator may exempt sector
participants from these requirements as
part of the approval of yearly operations
plans. This list may be modified
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26125
through a framework adjustment, as
specified in § 648.90.
*
*
*
*
*
■ 12. In § 648.89, revise paragraphs
(e)(1) and (e)(3)(ii) to read as follows:
§ 648.89 Recreational and charter/party
vessel restrictions.
*
*
*
*
*
(e) Charter/party vessel restrictions on
fishing in GOM closed areas and the
Nantucket Lightship Closed Area—(1)
GOM Closed Areas. Unless otherwise
specified in this paragraph (e)(1), a
vessel fishing under charter/party
regulations may not fish in the GOM
closed areas specified at § 648.81(d)(1)
through (f)(1) during the time periods
specified in those paragraphs, unless the
vessel has on board a valid letter of
authorization issued by the Regional
Administrator pursuant to
§ 648.81(f)(2)(iii) and paragraph (e)(3) of
this section. The conditions and
restrictions of the letter of authorization
must be complied with for a minimum
of 3 months if the vessel fishes or
intends to fish in the seasonal GOM
closure areas; or for the rest of the
fishing year, beginning with the start of
the participation period of the letter of
authorization, if the vessel fishes or
intends to fish in the year-round GOM
closure areas. A vessel fishing under
charter/party regulations may not fish in
the GOM Cod Spawning Protection Area
specified at § 648.81(n)(1) during the
time period specified in that paragraph,
unless the vessel complies with the
requirements specified at
§ 648.81(n)(2)(iii).
*
*
*
*
*
(3) * * *
(ii) Fish species managed by the
NEFMC or MAFMC that are harvested
or possessed by the vessel, are not sold
or intended for trade, barter or sale,
regardless of where the fish are caught;
*
*
*
*
*
■ 13. In § 648.90, revise paragraph
(a)(4)(iii)(C) and add paragraphs
(a)(5)(i)(D), (a)(5)(i)(E), and (a)(5)(iv) to
read as follows:
§ 648.90 NE multispecies assessment,
framework procedures and specifications,
and flexible area action system.
*
*
*
*
*
(a) * * *
(4) * * *
(iii) * * *
(C) Yellowtail flounder catch by the
Atlantic sea scallop fishery. Yellowtail
flounder catch in the Atlantic sea
scallop fishery, as defined in subpart D,
shall be deducted from the ABC/ACL for
each yellowtail flounder stock pursuant
to the restrictions specified in subpart D
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Federal Register / Vol. 77, No. 85 / Wednesday, May 2, 2012 / Rules and Regulations
of this part and the process to specify
ABCs and ACLs, as described in
paragraph (a)(4) of this section. Unless
otherwise specified in this paragraph
(a)(4)(iii)(C), or subpart D of this part,
the specific value of the subcomponents of the ABC/ACL for each
stock of yellowtail flounder distributed
to the Atlantic sea scallop fishery shall
be specified pursuant to the biennial
adjustment process specified in
paragraph (a)(2) of this section. Based
on information available, NMFS shall
re-estimate the expected scallop fishery
catch of GB yellowtail flounder for the
current fishing year by January 15. If
NMFS determines that the scallop
fishery will catch less than 90 percent
of its GB yellowtail flounder sub-ACL,
the Regional Administrator may reduce
the scallop fishery sub-ACL to the
amount projected to be caught, and
increase the groundfish fishery sub-ACL
by any amount up to the amount
reduced from the scallop fishery subACL. The revised groundfish fishery
sub-ACL shall be distributed to the
common pool and sectors based on the
process specified in paragraph
(a)(4)(E)(1) of this section.
*
*
*
*
*
(5) * * *
(i) * * *
(D) AMs for both stocks of
windowpane flounder, ocean pout, and
Atlantic halibut. At the end of each
fishing year, NMFS shall determine if
the overall ACL for northern
windowpane flounder, southern
windowpane flounder, ocean pout, or
Atlantic halibut was exceeded. If the
overall ACL for any of these stocks is
exceeded, NMFS shall implement the
appropriate AM, as specified in this
paragraph (a)(5)(i)(D), in the second
fishing year after the fishing year in
which the overage occurred, consistent
with the Administrative Procedure Act.
For example, if NMFS determined the
overall ACL for northern windowpane
flounder was exceeded in fishing year
2012, the applicable AM would be
implemented for fishing year 2014.
(1) Windowpane flounder and ocean
pout. If NMFS determines the overall
ACL for either stock of windowpane
flounder or ocean pout is exceeded, as
described in this paragraph
(a)(5)(i)(D)(1), by any amount between
the management uncertainty buffer and
up to 20 percent, the applicable small
AM area for the stock shall be
implemented, as specified in paragraph
(a)(5)(i)(D) of this section. If the overall
ACL is exceeded by 21 percent or more,
the applicable large AM area(s) for the
stock shall be implemented, as specified
in paragraph (a)(5)(i)(D) of this section.
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The AM areas defined below are
bounded by the following coordinates,
connected in the order listed by rhumb
lines, unless otherwise noted. Any
vessel issued a limited access NE
multispecies permit and fishing with
trawl gear in these areas may only use
a haddock separator trawl, as specified
in § 648.85(a)(3)(iii)(A); a Ruhle trawl,
as specified in § 648.85(b)(6)(iv)(J)(3); a
rope separator trawl, as specified in
§ 648.81(n)(3)(i)(A); or any other gear
approved consistent with the process
defined in § 648.85(b)(6). If a sub-ACL
for either stock of windowpane flounder
or ocean pout is allocated to another
fishery, consistent with the process
specified at § 648.90(a)(4), and AMs are
developed for that fishery, the
groundfish fishery AM shall only be
implemented if the sub-ACL allocated to
the groundfish fishery is exceeded (i.e.,
the sector and common pool catch for a
particular stock, including the common
pool’s share of any overage of the
overall ACL caused by excessive catch
by other sub-components of the fishery
pursuant to § 648.90(a)(5) exceeds the
common pool sub-ACL) and the overall
ACL is also exceeded.
NORTHERN WINDOWPANE FLOUNDER
AND OCEAN POUT SMALL AM AREA
Point
NWS1
NWS2
NWS3
NWS4
NWS5
NWS6
NWS1
............
............
............
............
............
............
............
N. latitude
41°10′
41°10′
41°00′
41°00′
40°50′
40°50′
41°10′
W. longitude
67°40′
67°20′
67°20′
67°00′
67°00′
67°40′
67°40′
NORTHERN WINDOWPANE FLOUNDER
AND OCEAN POUT LARGE AM AREA
Point
NWL1
NWL2
NWL3
NWL4
NWL5
NWL6
NWL1
.............
.............
.............
.............
.............
.............
.............
N. latitude
42°10′
42°10′
41°00′
41°00′
40°50′
40°50′
42°10′
W. longitude
67°40′
67°20′
67°20′
67°00′
67°00′
67°40′
67°40′
SOUTHERN WINDOWPANE FLOUNDER
AND OCEAN POUT SMALL AM AREA
Point
SWS1
SWS2
SWS3
SWS4
SWS1
PO 00000
............
............
............
............
............
Frm 00024
N. latitude
41°10′
41°10′
40°50′
40°50′
41°10′
Fmt 4701
W. longitude
71°30′
71°20′
71°20′
71°30′
71°30′
Sfmt 4700
SOUTHERN WINDOWPANE FLOUNDER
AND OCEAN POUT LARGE AM AREA 1
Point
SWL1
SWL2
SWL3
SWL4
SWL5
SWL6
SWL1
.............
.............
.............
.............
.............
.............
.............
N. latitude
41°10′
41°10′
41°00′
41°00′
40°50′
40°50′
41°10′
W. longitude
71°50′
71°10′
71°10′
71°20′
71°20′
71°50′
71°50′
SOUTHERN WINDOWPANE FLOUNDER
AND OCEAN POUT LARGE AM AREA 2
Point
SWL7 .............
SWL8 .............
SWL9 .............
SWL10 ...........
SWL11 ...........
SWL12 ...........
SWL13 ...........
SWL14 ...........
SWL7 .............
N. latitude
(1 )
40°30′
40°30′
40°20′
40°20′
(3 )
(4 )
40°32.6′ (5)
(1 )
W. longitude
73°30′
73°30′
73°50′
73°50′
(2)
73°58.5′
73°58.5′
73°56.4′ (5)
73°30′
1 The southern-most coastline of Long Island, NY at 73°30′ W. longitude.
2 The eastern-most coastline of NJ at 40°20′
N. latitude, then northward along the NJ coastline to point SWL12.
3 The northern-most coastline of NJ at
73°58.5′ W. longitude.
4 The southern-most coastline of Long Island, NY at 73°58.5′ W. longitude.
5 The approximate location of the southwest
corner of the Rockaway Peninsula, Queens,
NY, then eastward along the southern-most
coastline of Long Island, NY (excluding South
Oyster Bay), back to point SWL7.
(2) Atlantic halibut. If NMFS
determines the overall ACL is exceeded
for Atlantic halibut, any vessel issued a
limited access NE multispecies permit,
an open access NE multispecies
Handgear B permit, an open access NE
multispecies Category K permit, or a
limited access monkfish permit and
fishing under the monkfish Category C
or D permit provisions, may not fish for,
possess, or land Atlantic halibut for the
fishing year in which the AM is
implemented as specified in paragraph
(a)(5)(i)(D) of this section.
(E) AMs for SNE/MA winter flounder
and Atlantic wolffish. A vessel issued a
limited access NE multispecies permit,
an open access NE multispecies
Handgear B permit, an open access NE
multispecies charter/party permit, or a
limited access monkfish permit and
fishing under the monkfish Category C
or D permit provisions may not fish for,
possess, or land SNE/MA winter
flounder, as specified in § 648.86(l), as
a proactive AM to prevent the overall
ACL for these stocks from being
exceeded.
*
*
*
*
*
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(iv) AMs if the sub-ACL for the
Atlantic sea scallop fishery is exceeded.
At the end of the scallop fishing year,
NMFS shall evaluate Atlantic sea
scallop fishery catch to determine
whether a scallop fishery sub-ACL has
been exceeded. On January 15, or when
information is available to make an
accurate projection, NMFS will also
determine whether the overall ACL for
each stock allocated to the scallop
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fishery has been exceeded. When
evaluating whether the overall ACL has
been exceeded, NMFS will add the
maximum carryover available to sectors,
as specified at § 648.87(b)(1)(i)(C), to the
estimate of total catch for the pertinent
stock. If catch by scallop vessels exceeds
the pertinent sub-ACL specified in
paragraph (a)(4)(iii)(C) of this section by
50 percent or more, or if scallop catch
exceeds the scallop fishery sub-ACL and
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26127
the overall ACL for that stock is also
exceeded, then the applicable scallop
fishery AM shall take effect, as specified
in § 648.64 of the Atlantic sea scallop
regulations.
*
*
*
*
*
14. In part 648, revise Figure 1 to read
as follows:
■
BILLING CODE 3510–22–P
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[FR Doc. 2012–10526 Filed 5–1–12; 8:45 am]
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BILLING CODE 3510–22–C
Agencies
[Federal Register Volume 77, Number 85 (Wednesday, May 2, 2012)]
[Rules and Regulations]
[Pages 26104-26128]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-10526]
[[Page 26103]]
Vol. 77
Wednesday,
No. 85
May 2, 2012
Part III
Department of Commerce
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National Oceanic and Atmospheric Administration
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50 CFR Part 648
Magnuson-Stevens Fishery Conservation and Management Act Provisions;
Fisheries of the Northeastern United States; Northeast Multispecies
Fishery; Framework Adjustment 47; 2012 Sector Operations Plans and
Contracts, and Allocation of Northeast Multispecies Annual Catch
Entitlements; Final Rules
Federal Register / Vol. 77 , No. 85 / Wednesday, May 2, 2012 / Rules
and Regulations
[[Page 26104]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 648
[Docket No. 120109034-2171-01]
RIN 0648-BB62
Magnuson-Stevens Fishery Conservation and Management Act
Provisions; Fisheries of the Northeastern United States; Northeast
Multispecies Fishery; Framework Adjustment 47
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
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SUMMARY: NMFS approves Framework Adjustment 47 (Framework 47) to the
Northeast (NE) Multispecies Fishery Management Plan (FMP) and
implements the approved measures. The New England Fishery Management
Council (Council) developed and adopted Framework 47 based on the
biennial review process established in the NE Multispecies FMP to
develop annual catch limits (ACLs) and revise management measures
necessary to rebuild overfished groundfish stocks and achieve the goals
and objectives of the FMP. This action also implements management
measures and revises existing regulations that are not included in
Framework 47, including common pool management measures for fishing
year (FY) 2012, modification of the Ruhle trawl definition, and
clarification of the regulations for charter/party and recreational
groundfish vessels fishing in groundfish closed areas. This action is
intended to prevent overfishing, rebuild overfished stocks, achieve
optimum yield, and ensure that management measures are based on the
best available scientific information at the time Framework 47 was
submitted.
DATES: Effective May 1, 2012.
ADDRESSES: Copies of Framework 47, the draft environmental assessment
(EA), its Regulatory Impact Review (RIR), and the draft Initial
Regulatory Flexibility Act (IRFA) analysis prepared by the Council are
available from Paul J. Howard, Executive Director, New England Fishery
Management Council, 50 Water Street, Mill 2, Newburyport, MA 01950. A
supplemental analysis was included with the draft IRFA prepared by the
Council in the preamble to the proposed rule for this action. The Final
Regulatory Flexibility Act (FRFA) analysis consists of the IRFA, public
comments and responses, and the summary of impacts and alternatives
contained in the Classification section of this final rule and
Framework 47. The Framework 47 EA/RIR/FRFA is also accessible via the
Internet at https://www.nefmc.org/nemulti/ or https://www.nero.noaa.gov.
FOR FURTHER INFORMATION CONTACT: Sarah Heil, Fishery Policy Analyst,
phone: 978-281-9257, fax: 978-281-9135.
SUPPLEMENTARY INFORMATION:
Background
The NE Multispecies FMP specifies management measures for 16
species in Federal waters off the New England and Mid-Atlantic coasts,
including both large-mesh and small-mesh species. Small-mesh species
include silver hake (whiting), red hake, offshore hake, and ocean pout,
and large-mesh species include Atlantic cod, haddock, yellowtail
flounder, pollock, American plaice, witch flounder, white hake,
windowpane flounder, Atlantic halibut, winter flounder, redfish, and
Atlantic wolffish. Large-mesh species, which are referred to as
``regulated species,'' are divided into 19 fish stocks, and along with
ocean pout, comprise the groundfish complex.
Amendment 16 to the NE Multispecies FMP (Amendment 16) established
a process for setting acceptable biological catches (ABCs) and ACLs for
regulated species and ocean pout, as well as for distributing the
available catch among the various components of the groundfish fishery.
Amendment 16 also established accountability measures (AMs) for the 20
groundfish stocks in order to prevent overfishing of these stocks and
correct or mitigate any overages of the ACLs. Framework 47 is part of
the process established in the FMP to set ABCs and ACLs and to revise
management measures necessary to achieve the goals and objectives of
the FMP. The Council developed Framework 47 to respond to recent stock
assessments and updated stock information, as well as to revise
management measures after the fishery has operated for more than 1 year
under ACLs and AMs. NMFS published a proposed rule to approve Framework
47 and implement its measures on March 27, 2012 (77 FR 18176), and
accepted public comments through April 11, 2012. NMFS proposed
additional measures not included in Framework 47 to modify the Ruhle
trawl definition, clarify regulations for charter/party vessels fishing
in groundfish closed areas, modify the conversion rate used to estimate
the live weight of fillets and parts of fish landed for home
consumption, and implement management measures for the common pool
fishery for FY 2012.
Approved Measures
This section summarizes the Framework 47 measures, all of which
have been approved, and the measures being implemented by NMFS under
the authority of section 305(d) of the Magnuson-Stevens Fishery
Conservation and Management Act (Magnuson-Stevens Act), which allows
the Secretary of Commerce to implement regulations necessary to ensure
that fishery management plans or amendments are carried out consistent
with the Magnuson-Steven Act. The measures implemented under this
authority are necessary to implement changes to the Atlantic Sea
Scallop FMP proposed by the Council in Framework 47, and to change
regulations that are not part of Framework 47, but that are necessary
to clarify existing regulations and achieve the objective of the FMP.
This final rule modifies the Rhule trawl definition and clarifies the
regulations for charter/party vessels fishing in the groundfish closed
areas. This action does not change the conversion rate for home
consumption landings, which NMFS had originally proposed, for reasons
discussed below. This final rule also implements management measures
for the common pool fishery for FY 2012 that are not included in
Framework 47, but that are implemented by the Regional Administrator
(RA) under authority provided by the FMP.
1. Status Determination Criteria for Winter Flounder and Gulf of Maine
Cod
New assessments were conducted for Gulf of Maine (GOM), Georges
Bank (GB), and Southern New England/Mid-Atlantic (SNE/MA) winter
flounder in June 2011, and a new assessment for GOM cod was completed
in December 2011. Based on the results from the 52nd Stock Assessment
Workshop (SAW) completed in June 2011, GB winter flounder is no longer
experiencing overfishing, and the stock is no longer overfished. SNE/MA
winter flounder is still overfished, but overfishing is no longer
occurring for this stock. In addition, the overfishing status is no
longer unknown for GOM winter flounder, and overfishing is not
occurring. However, the overfished status for GOM winter flounder is
still unknown. The results of the 53rd SAW completed in December 2011
indicate that overfishing is occurring for GOM cod, and the stock is
overfished.
[[Page 26105]]
This final rule updates the status determination criteria for the
three winter flounder stocks and GOM cod to incorporate the results of
the recent stock assessments into the FMP. These changes are based on
the best scientific information available. The revised biomass targets
for GB and SNE/MA winter flounder is spawning stock biomass at maximum
sustainable yield (SSBMSY), and the maximum fishing
mortality rate (F) threshold is FMSY. The revised maximum F
threshold for GOM winter flounder is F at 40 percent of the maximum
spawning potential (F40[percnt]MSP).
The biomass target for this stock is still undefined. For GOM cod, the
biomass target is unchanged from GARM III and is SSB at 40 percent MSP
(SSB40[percnt]MSP). The maximum F
threshold proxy is also unchanged from GARM III and is
F40[percnt]MSP. Table 1 lists the
revised status determination criteria, and the numerical estimates of
these criteria are shown in Table 2.
Table 1--Status Determination Criteria for Winter Flounder Stocks and GOM Cod
----------------------------------------------------------------------------------------------------------------
Minimum biomass Maximum fishing
Stock Biomass target threshold mortality threshold
----------------------------------------------------------------------------------------------------------------
GOM winter flounder.................. Undefined.............. Undefined.............. F40MSP.
GB winter flounder................... SSBMSY................. \1/2\ SSBMSY........... FMSY.
SNE/MA winter flounder............... SSBMSY................. \1/2\ SSBMSY........... FMSY.
GOM cod.............................. SSB40[percnt]MSP....... \1/2\ SSB40[percnt]MSP. F40[percnt]MSP.
----------------------------------------------------------------------------------------------------------------
Table 2--Numerical Estimates of the Status Determination Criteria for Winter Flounder Stocks and GOM Cod
----------------------------------------------------------------------------------------------------------------
Maximum
fishing
Stock Biomass target (mt) mortality MSY (mt)
threshold
----------------------------------------------------------------------------------------------------------------
GOM winter flounder................. Undefined................... 0.31 Undefined.
GB winter flounder.................. 10,100...................... 0.42 3,700.
SNE/MA winter flounder.............. 43,661...................... 0.29 11,728.
GOM cod............................. 61,218...................... 0.20 10,392.
----------------------------------------------------------------------------------------------------------------
2. Rebuilding Program for GB Yellowtail Flounder
GB yellowtail flounder is jointly managed with Canada under the
U.S./Canada Resource Sharing Understanding (Understanding). Framework
Adjustment 45 to the NE Multispecies FMP (Framework 45) revised the GB
yellowtail flounder rebuilding program in 2011, based on the best
available scientific information, to rebuild the stock by 2016 with a
50-percent probability of success. This revision extended the
rebuilding program to the maximum 10-year rebuilding period allowed by
the Magnuson-Stevens Act in order to maximize the amount of GB
yellowtail flounder that could be caught while the stock rebuilds.
Under the International Fisheries Agreement Clarification Act
(IFACA) enacted into law on January 4, 2011, the Council and NMFS have
flexibility in establishing rebuilding programs for stocks that are
jointly managed with Canada under the Understanding. IFACA allows the
Council and NMFS to consider decisions made under the Understanding as
management measures under an international agreement in order to
provide an exception to the Magnuson-Stevens Act's maximum 10-year
rebuilding period requirement.
Each year, pursuant to the Understanding, the Transboundary
Management Guidance Committee (TMGC) meets to consider the scientific
advice of the Transboundary Resources Assessment Committee and to make
decisions regarding total allowable catch (TAC) recommendations for the
upcoming year for each stock managed under the Understanding. The TMGC
adopts harvest strategies to guide its annual TAC recommendations. The
TMGC's harvest strategy for GB yellowtail flounder is to maintain a low
to neutral risk of exceeding the fishing mortality limit reference
(Fref) of 0.25. At its September 2011 meeting, the TMGC
reaffirmed its harvest strategy for GB yellowtail flounder to maintain
a low to neutral risk of exceeding the fishing mortality limit
reference (Fref) of 0.25. Based on that harvest strategy,
the TMGC developed its 2012 TAC recommendation for GB yellowtail
flounder and forwarded the recommendation to the Council for approval
(See Item 5 for more information on the 2012 TMGC TAC recommendations).
Given the provisions of IFACA, and that the TMGC decisions
regarding a GB yellowtail flounder harvest strategy and annual TAC are
considered management measures under an international agreement, NFMS
interprets the Magnuson-Stevens Act to allow the rebuilding program for
GB yellowtail flounder to exceed 10 years. Therefore, this action
revises the rebuilding strategy for GB yellowtail flounder. The revised
rebuilding strategy would rebuild the stock by 2032 with at least a 50-
percent probability of success. This rebuilding strategy is based on an
F of 0.21 and would extend 26 years beyond the rebuilding program start
date (2006). The rebuilding time period is as short as possible, taking
into account the Understanding and decisions made under it, and the
needs of the fishing communities, and will provide more flexibility for
negotiating annual catches with Canada.
3. Overfishing Levels and Acceptable Biological Catches
The overfishing level (OFL) for each stock in the NE Multispecies
FMP is calculated using the estimated stock size and FMSY
(i.e., the fishing mortality rate that, if applied over the long term,
would result in maximum sustainable yield). The Council's Scientific
and Statistical Committee (SSC) recommends ABCs for each stock that are
lower than the OFLs to account for scientific uncertainty. The ABCs are
calculated using the estimated stock size for a particular year and are
based on the catch associated with 75 percent of FMSY or the
F required to rebuild a stock within its rebuilding time period
[[Page 26106]]
(Frebuild), whichever is lower. For SNE/MA winter flounder,
the ABC is calculated using the F expected to result from management
measures that are designed to achieve an F as close to zero as
practicable. For some stocks, the Canadian share of an ABC, or the
expected Canadian catch, is deducted from the ABC. The U.S. ABC is the
amount available to the U.S. fishery after accounting for Canadian
catch.
As part of the biennial review process for the NE Multispecies FMP,
the Council adopts OFLs and ABCs for 3 years at a time. Although it is
expected that the Council will adopt new catch levels every 2 years,
specifying catch levels for a third year ensures there are default
catch limits in place in the event that a management action is delayed.
Framework 44 specified OFLps and ABCs for each stock for FYs 2010-2012
based on the best scientific information available, and Framework 45
revised the OFLs and ABCs for five stocks for FYs 2011-2012 based on
updated stock information. Although Framework 44 and Framework 45
specified catch levels for all stocks through FY 2012, Framework 47 was
developed to set catch levels for FYs 2012-2014 and revise the OFLs and
ABCs previously adopted for FY 2012 based on updated stock information.
This action sets the OFLs and ABCs for nine stocks (GB, GOM, and
SNE/MA winter flounder, pollock, northern and southern windowpane
flounder, ocean pout, Atlantic halibut, and Atlantic wolffish) for FYs
2012-2014 that are assessed with an index-based stock assessment or
that have had a recent stock assessment completed. This action also
sets the OFL and ABC for FYs 2012-2013 only for GB yellowtail flounder
based on updated stock information. Table 3 lists the OFLs and ABCs for
these stocks.
For nine other stocks (GB cod, GB haddock, GOM haddock, SNE/MA
yellowtail flounder, CC/GOM yellowtail flounder, American plaice, witch
flounder, redfish, and white hake), this action adopts the OFLs and
ABCs for FY 2012 only, that were previously specified in Framework 44
or Framework 45 (Table 3). OFLs and ABCs are only being set for FY 2012
based on advice from the SSC. At the time the Council was developing
Framework 47, these stocks were last assessed at the 3rd Groundfish
Assessment Review Meeting (GARM III) in 2008. The SSC determined that
projections from the GARM III assessment were not a reliable basis for
providing catch advice for these stocks for all three fishing years
from 2012-2014. As a result, the SSC recommended that the Council
specify ABCs for FY 2012 only based on the ABCs that were previously
adopted in Framework 44 or Framework 45. Consistent with the SSC
recommendations, the Council adopted the FY 2012 ABCs previously set by
Framework 44 and Framework 45 in Framework 47. The Council also
requested that the Northeast Fisheries Science Center complete
assessment updates for the stocks last assessed at GARM III in order to
set catch limits for FYs 2013-2014 for these stocks. The Council made
this request with the understanding that these catch limits would be
implemented through a subsequent framework that the Council is already
developing.
The Council finalized and submitted Framework 47 to NMFS on
February 7, 2012. The stock assessment updates to be used for setting
FYs 2013-2014 catch limits were not completed until February 13-17,
2012, and the final report for the updates was not published until
March 14, 2012. As the Council and the SSC understood while developing
Framework 47, these updated assessments were never intended to be
incorporated into Framework 47 for the nine stocks for FY 2012 because
they would not be available in time for the Council and the SSC to
consider them for implementation by the start of FY 2012. Therefore,
Framework 47 adopted the OFLs and ABCs for FY 2012 for these nine
stocks based on the best scientific information available at the time
the Council took final action on Framework 47.
The updated assessments for five stocks (GB cod, GOM haddock, CC/
GOM yellowtail flounder, American plaice, and witch flounder), indicate
that the FY 2012 ABCs adopted in Framework 47 are significantly higher
than those suggested by the assessment updates. For the remaining eight
stocks that were updated in early 2012, the FY 2012 ABCs adopted in
Framework 47 are virtually the same, or somewhat lower, than those
suggested by the assessment updates. Because the stock assessment
updates suggest that ABCs might be different than those adopted in
Framework 47 for some stocks, and may be significantly lower for the
five stocks specified above, one commenter recommended that NMFS
disapprove the OFLs and ABCs for these stocks because they are not
consistent with National Standard 2, which requires actions to be
consistent with best scientific information available. This comment is
briefly discussed below to explain NMFS' decision to approve the FY
2012 OFLs and ABCs despite the comment received on this measure.
The National Standard 2 guidelines (50 CFR 600.315) require that
each FMP (and by extension amendment and framework) take into account
the best scientific information available at the time, or preparation,
of an action. The guidelines recognize that new information often
becomes available between the initial drafting of an FMP and its
submission to NMFS for final review. The guidelines state that this new
information should be incorporated into the action, if practicable; but
it is unnecessary for the Council to re-start the FMP process based on
this information, unless it indicates that drastic changes have
occurred in the fishery that might require revision of the management
objectives or measures. This is not a situation in which the Council
received information that ``drastic changes'' have occurred in the
fishery prior to submission of the action to NMFS. Instead, as was
fully understood in developing Framework 47, the assessment updates
would not be completed until after the Council took final action on
Framework 47 and submitted it to NMFS for review. As a result, there
was no practicable way to incorporate this information into Framework
47 without reinitiating the Council process and delaying the action far
beyond the start of FY 2012, which begins on May 1, 2012, and is when
the ABCs need to be in place. Therefore, NMFS has determined that it is
appropriate for the Council to set the OFLs and ABCs in this action
based on the best scientific information available at the time the
Council took final action and submitted Framework 47 to NMFS for
approval. The appropriate response to the new information that became
available after submission of Framework 47 is for the Council to
consider whether to initiate a new framework or amendment, or to
request an emergency or interim Secretarial action, to revise the
existing measures or catch limits adopted in this action.
Consistent with the National Standard 2 guidelines, this
determination recognizes the need for some certainty as to what
information the Council may rely on in taking its final action, and
what information NMFS will use to evaluate the approvability of a
Council action. Without such certainty, there would be a lack of
predictability and confidence in Council actions, which must be
developed well in advance of their implementation due to the time it
takes to prepare appropriate analyses and documents for submission to
NMFS for final review. A lack of certainty about what information will
be used to review a Council action could also
[[Page 26107]]
seriously undermine the Council process because neither the Council,
nor the public, would have confidence that their efforts would not be
meaningless. Thus, new scientific information that becomes available
after the Council has submitted its final action to NMFS for review
should not, based on National Standard 2, be used retroactively to undo
recommended actions that had the benefit of the full Council process.
NMFS also considered the practical effect of disapproving the OFLs
and ABCs specified in this action. Approving catch limits for these
stocks, whose assessments were updated in early 2012, actually results
in slightly lower fishing mortality than if they were disapproved and
the default measures specified by Framework 44 and Framework 45 went
into place. The default catch limits for FY 2012 for the five stocks
mentioned earlier (GB cod, GOM haddock, CC/GOM yellowtail flounder,
American plaice, and witch flounder) are identical to those specified
in this action, except for GB cod, which is 5 percent higher. For the
remaining stocks, the default measures are essentially identical or
higher than those adopted in Framework 47. Therefore, disapproving the
FY 2012 ABCs in Framework 47 would result in almost identical catch
limits as those previously specified, but a higher catch limit for GB
cod, which could increase overfishing of this stock while the Council
develops its next management action to incorporate the new scientific
information available.
Approving these catch limits, as explained above, does not reduce
the importance of acting on the new information as soon as possible in
a new action, but rather emphasizes the importance of analyzing and
considering this information through the full Council process.
Consistent with the SSC guidance and the Council's understanding during
the development of Framework 47, the Council has already started
developing a management action that will incorporate the assessment
update information and adopt catch limits for the pertinent stocks for
FYs 2013-2014. The Council is scheduled to receive and discuss the
results of the assessment updates at its April 25, 2012, meeting. A new
stock assessment for SNE/MA yellowtail flounder is also scheduled for
June 2012, and the results of this stock assessment will be
incorporated into the same Council action to set OFLs and ABCs for the
stock for FYs 2013-2014. The Council may also use updated information
for other stocks to revise the FYs 2013-2014 OFLs and ABCs specified in
this action. The Council intends to complete this management action by
May 1, 2013, to set catch limits for FYs 2013-2014. NMFS has notified
the Council that the updated assessment information must be
incorporated as soon as possible, but no later than May 1, 2013. NMFS
recommends that, at its June meeting, the Council identify how and when
this information will be incorporated and how that process would affect
any existing or planned management measures.
Framework 47, as approved by the Council on November 16, 2011,
initially proposed to set specifications for GOM cod for FYs 2012-2014
based on the most recent stock assessment, completed in December 2011.
The results of that assessment indicate that the stock is overfished
and overfishing is occurring, and that GOM cod cannot rebuild by its
rebuilding end date (2014) even in the absence of all fishing
mortality. Given the final results of the GOM cod assessment, and that
rebuilding cannot be achieved within the rebuilding period, NMFS
concluded that the NE Multispecies FMP is not making adequate progress
toward ending overfishing and rebuilding GOM cod. In a letter dated
January 26, 2012, NMFS notified the Council of this determination and
that the Council must implement a plan by May 1, 2013, to immediately
end overfishing for GOM cod. The Council was also notified that it has
up to 2 years to address GOM cod rebuilding. In addition, NMFS
indicated that the Magnuson-Stevens Act provides some flexibility for
NMFS to only reduce overfishing, rather than end it immediately, during
FY 2012 while the Council develops measures to address GOM cod.
At its January 25, 2012, meeting, the Council's SSC met to discuss
the GOM cod stock assessment. At the request of the Council, the SSC
did not recommend ABCs for GOM cod for FYs 2012-2014. Instead, the SSC
reviewed the stock assessment and identified issues that may warrant a
closer examination and that may influence the interpretation of the
assessment results. Subsequently, at its February 1, 2012, meeting, the
Council did not adopt ABCs for GOM cod for Framework 47. The Council
requested that NMFS implement an interim action for FY 2012 to reduce
overfishing on GOM cod while the Council responds to the new GOM cod
stock assessment and develops measures for FY 2013 that will
immediately end overfishing. In response to the Council's request, NMFS
published an interim action on April 3, 2012, to set catch levels for
GOM cod for FY 2012 (77 FR 19944). Therefore, although this action does
not include OFLs and ABCs for GOM cod for FYs 2012-2014, it is not
deficient regarding GOM cod because of the interim action. The SSC will
meet in the future to recommend ABCs for FYs 2013-2014 for GOM cod, and
the Council intends to adopt these ABCs in a future management action.
Table 3--FYs 2012-2014 OFLs and ABCs (mt)
----------------------------------------------------------------------------------------------------------------
OFL U.S. ABC
Stock -----------------------------------------------------------------
2012 2013 2014 2012 2013 2014
----------------------------------------------------------------------------------------------------------------
GB cod........................................ 7,311 ......... ......... 5,103 ......... .........
GB haddock.................................... 51,150 ......... ......... 30,726 ......... .........
GOM haddock................................... 1,296 ......... ......... 1,013 ......... .........
GB yellowtail flounder........................ 1,691 1,691 ......... 564 564 .........
SNE/MA yellowtail flounder.................... 3,166 ......... ......... 1,003 ......... .........
Cape Cod (CC)/GOM yellowtail flounder......... 1,508 ......... ......... 1,159 ......... .........
American plaice............................... 4,727 ......... ......... 3,632 ......... .........
Witch flounder................................ 2,141 ......... ......... 1,639 ......... .........
GB winter flounder............................ 4,839 4,819 4,626 3,753 3,750 3,598
GOM winter flounder........................... 1,458 1,458 1,458 1,078 1,078 1,078
SNE/MA winter flounder........................ 2,336 2,637 3,471 626 697 912
Redfish....................................... 12,036 ......... ......... 9,224 ......... .........
White hake.................................... 5,306 ......... ......... 3,638 ......... .........
Pollock....................................... 19,887 20,060 20,554 15,400 15,600 16,000
[[Page 26108]]
Northern windowpane flounder.................. 230 230 230 173 173 173
Southern windowpane flounder.................. 515 515 515 386 386 386
Ocean pout.................................... 342 342 342 256 256 256
Atlantic halibut.............................. 143 143 143 85 85 85
Atlantic wolffish............................. 92 92 92 83 83 83
----------------------------------------------------------------------------------------------------------------
4. Annual Catch Limits
Unless otherwise noted below, the U.S. ABC for each stock (for each
fishing year) is divided into the following fishery components to
account for all sources of fishing mortality: State waters (portion of
ABC expected to be caught from state waters outside Federal
management); other sub-components (expected catch by non-groundfish
fisheries); scallop fishery; mid-water trawl fishery; commercial
groundfish fishery; and recreational groundfish fishery. Currently, the
scallop fishery only receives an allocation for GB and SNE/MA
yellowtail flounder, the mid-water trawl fishery only receives an
allocation for GB and GOM haddock, and the recreational groundfish
fishery only receives an allocation for GOM cod and haddock. Once the
ABC is divided, sub-annual catch limits (sub-ACLs) and ACL sub-
components are set by reducing the amount of the ABC distributed to
each component of the fishery to account for management uncertainty.
Management uncertainty is the likelihood that management measures will
result in a level of catch greater than expected. For each stock,
management uncertainty is estimated using the following criteria:
Enforceability, monitoring adequacy, precision of management tools,
latent effort, and catch of groundfish in non-groundfish fisheries.
Appendix III of the Framework 47 EA provides a detailed description of
the process used to estimate management uncertainty and calculate ACLs
for this action (see ADDRESSES).
The total ACL is the sum of all of the sub-ACLs and ACL sub-
components, and is the catch limit for a particular year after
accounting for both scientific and management uncertainty. Landings and
discards from all fisheries (commercial and recreational groundfish
fishery, state waters, and non-groundfish fisheries) are counted
against the catch limit for each stock. Components of the fishery that
are allocated a sub-ACL for a particular stock are subject to AMs if
the catch limit is exceeded. ACL sub-components represent the expected
catch by components of the fishery that are not subject to AMs (e.g.,
state waters).
This final rule sets ACLs for each groundfish stock except GOM cod
(see Item 3 of this preamble), based on the ABCs set by this action.
The ACLs for FYs 2012-2014 are listed in Table 4 through Table 7. For
stocks allocated to sectors, the commercial groundfish sub-ACL is
further divided into the non-sector (common pool) sub-ACL and the
sector sub-ACL, based on the total vessel enrollment in all sectors and
the cumulative Potential Sector Contributions associated with those
sectors. The distribution of the groundfish sub-ACL between the common
pool and sectors shown in Tables 5 through Table 7 are based on
preliminary FY 2012 sector rosters submitted to NMFS as of December 1,
2011, including any PSC updates or corrections that have been made
since the proposed rule for this action was published. This
distribution differs from the common pool and sector sub-ACLs included
in the Framework 47 EA, which were based on FY 2011 sector rosters, and
do not reflect updated rosters submitted to NMFS for FY 2012. FY 2012
sector rosters will not be finalized until May 1, 2012, because owners
of individual permits signed up to participate in sectors have until
the end of the 2011 fishing year, or April 30, 2012, to drop out of a
sector and fish in the common pool for FY 2012. NMFS also extended the
deadline to join a sector for FY 2012 through April 30, 2012, to
provide common pool vessels the opportunity to join a sector due to the
potential impacts of the FY 2012 GOM cod catch limits. The sector sub-
ACLs listed in the tables below may change due to changes in the sector
rosters. If necessary, updated sector sub-ACLs will be published in a
future adjustment rule to reflect the final FY 2012 sector rosters as
of May 1, 2012.
Table 4--FY 2012 Allocations to the Recreational Groundfish Fishery,
Scallop Fishery, and Mid-Water Trawl Fishery (mt)
------------------------------------------------------------------------
------------------------------------------------------------------------
Fishery Stock
------------------------------------------------------------------------
Recreational Groundfish Fishery. GOM Cod........... GOM Haddock.
n/a............... 259.
---------------------------------------
Scallop Fishery................. SNE/MA Yellowtail GB Yellowtail
Flounder. Flounder.
126............... 307.5.
---------------------------------------
Midwater Trawl Fishery.......... GB Haddock........ GOM Haddock.
286............... 9.
------------------------------------------------------------------------
[[Page 26109]]
Table 5--FY 2012 Total ACLs, Sub-ACLs, and ACL Sub-Components (mt, Live Weight)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Preliminary
Stock Total ACL Groundfish sub- Preliminary common pool State waters Other sub-
ACL sector sub-ACL sub-ACL sub- component component
--------------------------------------------------------------------------------------------------------------------------------------------------------
GB cod.................................................. 4,861 4,605 4,523 82 51 204
GB haddock.............................................. 29,260 27,438 27,306 132 307 1,229
GOM haddock............................................. 958 912 648 5 15 22
GB yellowtail flounder.................................. 547.8 217.7 214.6 3.1 0.0 22.6
SNE/MA yellowtail flounder.............................. 936 760 592 168 10 40
CC/GOM yellowtail flounder.............................. 1,104 1,046 1,019 27 35 23
American plaice......................................... 3,459 3,278 3,221 57 36 145
Witch flounder.......................................... 1,563 1,448 1,424 24 49 66
GB winter flounder...................................... 3,575 3,387 3,365 22 0 188
GOM winter flounder..................................... 1,040 715 691 24 272 54
SNE/MA winter flounder.................................. 603 303 na 303 175 125
Redfish................................................. 8,786 8,325 8,291 34 92 369
White hake.............................................. 3,465 3,283 3,256 27 73 109
Pollock................................................. 14,736 12,612 12,530 82 754 1,370
Northern windowpane flounder............................ 163 129 na 129 2 33
Southern windowpane flounder............................ 381 72 na 72 39 270
Ocean pout.............................................. 240 214 na 214 3 23
Atlantic halibut........................................ 83 36 na 36 43 4
Atlantic wolffish....................................... 77 73 na 73 1 3
--------------------------------------------------------------------------------------------------------------------------------------------------------
Table 6--FY 2013 Total ACLs, Sub-ACLs, and ACL Sub-Components (mt, Live Weight)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Preliminary
Stock Total ACL Groundfish sub- Preliminary common Pool State waters Other sub-
ACL sector sub-ACL sub-ACL sub-component component
--------------------------------------------------------------------------------------------------------------------------------------------------------
GB yellowtail flounder.................................. 547.8 217.7 214.6 3.1 0.0 22.6
GB winter flounder...................................... 3,572 3,384 3,362 22 0 188
GOM winter flounder..................................... 1,040 715 690 25 272 54
SNE/MA winter flounder.................................. 672 337 na 337 195 139
Pollock................................................. 14,927 12,791 12,707 83 756 1,380
Northern windowpane flounder............................ 163 129 na 129 2 33
Southern windowpane flounder............................ 381 72 na 72 39 270
Ocean pout.............................................. 240 214 na 214 3 23
Atlantic halibut........................................ 83 36 na 36 43 4
Atlantic wolffish....................................... 77 73 na 73 1 3
--------------------------------------------------------------------------------------------------------------------------------------------------------
Table 7--FY 2014 Total ACLs, Sub-ACLs, and ACL Sub-Components (mt, Live Weight)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Preliminary
Stock Total ACL Groundfish sub- Preliminary common pool State waters Other sub-
ACL sector sub-ACL sub-ACL sub- component component
--------------------------------------------------------------------------------------------------------------------------------------------------------
GB winter flounder...................................... 3,427 3,247 3,226 21 0 180
GOM winter flounder..................................... 1,040 715 690 25 272 54
SNE/MA winter flounder.................................. 879 441 0 441 255 182
Pollock................................................. 15,308 13,148 13,062 86 760 1,400
Northern windowpane flounder............................ 163 129 0 129 2 33
Southern windowpane flounder............................ 381 72 0 72 39 270
Ocean pout.............................................. 240 214 0 214 3 23
Atlantic halibut........................................ 83 36 0 36 43 4
Atlantic wolffish....................................... 77 73 0 73 1 3
--------------------------------------------------------------------------------------------------------------------------------------------------------
5. U.S./Canada Total Allowable Catches
Eastern GB cod, eastern GB haddock, and GB yellowtail flounder are
managed jointly with Canada through the U.S./Canada Resource Sharing
Understanding. Each year the TMGC, which is made up of representatives
from Canada and the U.S., negotiates a shared TAC for each stock based
on the most recent stock information and the TMGC harvest strategy. The
TMGC's harvest strategy for setting catch levels is to maintain a low
to neutral (less than 50-percent) risk of exceeding the fishing
mortality limit reference (Fref = 0.18, 0.26, and 0.25 for
cod, haddock, and yellowtail flounder, respectively). When stock
conditions are poor, fishing mortality should be further reduced to
promote rebuilding. The shared TACs are allocated between the U.S. and
Canada based on a formula that considers historical catch percentages
and the current resource distribution based on trawl surveys. The U.S./
Canada Management Area comprises the entire stock area for GB
yellowtail flounder; therefore, the U.S. TAC for this stock is also the
U.S. ABC.
[[Page 26110]]
In September 2011, the TMGC recommended 2012 shared TACs for
eastern GB cod, eastern GB haddock, and GB yellowtail flounder. The
TMGC recommended a shared TAC of 675 mt for eastern GB cod, 16,000 mt
for eastern GB haddock, and 900 mt for GB yellowtail flounder. However,
at its September 2011 meeting, the Council's SSC recommended an ABC of
1,150 mt for GB yellowtail flounder, which was higher than the TMGC
recommendation. On September 28, 2011, the Council reviewed the
recommendations of the TMGC and the SSC, and approved the TMGC
recommendations for eastern GB cod and eastern GB haddock. The Council
also approved an ABC of up to 1,150 mt for GB yellowtail flounder,
consistent with the SSC's recommendation. The TMGC met by conference
call in October 2011 to reconsider its 2012 recommendation for GB
yellowtail flounder since the ABC approved by the Council was higher
than the shared TAC initially negotiated by the TMGC. At this meeting,
the TMGC recommended a shared TAC of 1,150 mt for GB yellowtail
flounder for 2012.
The 2012 U.S./Canada TACs and the percentage shared for each
country are listed in Table 8. For 2012, the annual percentage shares
for each country are based on a 10-percent weighting of historical
catches and a 90-percent weighting of the current resource
distribution. Any overages of the eastern GB cod, eastern GB haddock,
or GB yellowtail flounder U.S. TACs will be deducted from the U.S. TAC
in the following fishing year. If FY 2011 catch information indicates
that the U.S. fishery exceeded its TAC for any of the shared stocks,
NMFS will reduce the FY 2012 U.S. TAC for that stock in a future
management action.
Table 8--2012 U.S. Canada TACS (mt, Live Weight) and Percentage Shares
------------------------------------------------------------------------
GB
TAC Eastern GB Eastern GB yellowtail
cod haddock flounder
------------------------------------------------------------------------
Total Shared TAC................. 675 16,000 1,150
U.S. TAC......................... 162 (24%) 6,880 (43%) 564 (49%)
Canada TAC....................... 513 (76%) 9,120 (57%) 586 (51%)
------------------------------------------------------------------------
6. Incidental Catch Total Allowable Catches and Allocations to Special
Management Programs
Incidental catch TACs are specified for certain stocks of concern
(i.e., stocks that are overfished or subject to overfishing) for common
pool vessels fishing in the special management programs (i.e., special
access programs (SAPs) and the Regular B Days-At-Sea (DAS) Program), in
order to limit the catch of these stocks under each program. Table 9
shows the percentage of the common pool sub-ACL allocated to the
special management programs and the FYs 2012-2014 Incidental Catch TACs
for each stock. Any catch on a trip that ends on a Category B DAS
(either Regular or Reserve B DAS) is attributed to the Incidental Catch
TAC for the pertinent stock. Catch on a trip that starts under a
Category B DAS and then flips to a Category A DAS is counted against
the common pool sub-ACL.
The Incidental Catch TAC is further divided among each special
management program based on the percentages listed in Table 10. Table
11 lists the FYs 2012-2014 Incidental Catch TACs for each special
management program. The FY 2012 sector rosters will not be finalized
until May 1, 2012, for the reasons mentioned earlier in this preamble.
Therefore, the common pool sub-ACL may change due to changes to the FY
2012 sector rosters. Updated incidental catch TACs will be published in
a future adjustment rule, if necessary, based on the final sector
rosters as of May 1, 2012.
Table 9--Common Pool Incidental Catch TACs for FYs 2012-2014 (mt, Live Weight)
----------------------------------------------------------------------------------------------------------------
Percentage of
Stock common pool 2012 2013 2014
sub-ACL
----------------------------------------------------------------------------------------------------------------
GB cod.......................................... 2 1.6 n/a n/a
GB yellowtail flounder.......................... 2 0.1 n/a n/a
SNE/MA yellowtail flounder...................... 1 1.7 n/a n/a
CC/GOM yellowtail flounder...................... 1 0.3 n/a n/a
Plaice.......................................... 5 2.9 n/a n/a
Witch flounder.................................. 5 1.4 n/a n/a
GB winter flounder.............................. 2 0.4 0.4 0.4
SNE/MA winter flounder.......................... 1 3.0 3.4 4.4
White hake...................................... 2 0.9 n/a n/a
----------------------------------------------------------------------------------------------------------------
Table 10--Percentage of Incidental Catch TACs Distributed to Each
Special Management Program
------------------------------------------------------------------------
Regular B Closed Area Eastern
Stock DAS I hook gear U.S./CA
program haddock SAP haddock SAP
------------------------------------------------------------------------
GB cod........................... 50 16 34
GB yellowtail flounder........... 50 n/a 50
SNE/MA yellowtail flounder....... 100 n/a n/a
CC/GOM yellowtail flounder....... 100 n/a n/a
Plaice........................... 100 n/a n/a
Witch flounder................... 100 n/a n/a
[[Page 26111]]
GB winter flounder............... 50 n/a 50
SNE/MA winter flounder........... 100 n/a n/a
White hake....................... 100 n/a n/a
------------------------------------------------------------------------
Table 11--Incidental Catch TACs for Each Special Management Program for FY 2012-2014 (mt, Live Weight)
----------------------------------------------------------------------------------------------------------------
Regular B DAS program Closed Area I hook Eastern U.S./Canada
------------------------ gear haddock SAP haddock SAP
Stock -----------------------------------------------
2012 2013 2014 2012 2013 2014 2012 2013 2014
----------------------------------------------------------------------------------------------------------------
GB cod.................................. 0.8 n/a n/a 0.3 0.0 0.0 0.5 0.0 0.0
GB yellowtail flounder.................. 0.03 n/a n/a n/a n/a n/a 0.03 n/a n/a
SNE/MA yellowtail flounder.............. 1.7 n/a n/a n/a n/a n/a n/a n/a n/a
CC/GOM yellowtail flounder.............. 0.3 n/a n/a n/a n/a n/a n/a n/a n/a
Plaice.................................. 2.9 n/a n/a n/a n/a n/a n/a n/a n/a
Witch flounder.......................... 1.2 n/a n/a n/a n/a n/a n/a n/a n/a
GB winter flounder...................... 0.2 0.2 0.2 n/a n/a n/a 0.2 0.2 0.2
SNE/MA winter flounder.................. 3.0 3.4 4.4 n/a n/a n/a n/a n/a n/a
White hake.............................. 0.5 n/a n/a n/a n/a n/a n/a n/a n/a
----------------------------------------------------------------------------------------------------------------
7. Common Pool Trimester Total Allowable Catches
Beginning in FY 2012, the common pool sub-ACL for each stock
(except for SNE/MA winter flounder, windowpane flounder, ocean pout,
Atlantic wolffish, and Atlantic halibut) will be divided into trimester
TACs. Table 12 shows the percentage of the common pool sub-ACL that is
allocated to each trimester for each stock. Once NMFS projects that 90
percent of the trimester TAC is caught for a stock, the trimester TAC
area for that stock will be closed for the remainder of the trimester.
The area closure will apply to all common pool vessels fishing with
gear capable of catching the pertinent stock. The trimester TAC areas
for each stock, as well as the applicable gear types, are defined at
Sec. 648.82(n)(2). Any uncaught portion of the trimester TAC in
Trimester 1 or Trimester 2 will be carried forward to the next
trimester (e.g., any remaining portion of the Trimester 1 TAC will be
added to the Trimester 2 TAC). Overages of the trimester TAC in
Trimester 1 or Trimester 2 will be deducted from the Trimester 3 TAC,
and any overage of the total sub-ACL will be deducted from the
following fishing year's common pool sub-ACL for that stock. Uncaught
portions of the Trimester 3 TAC will not be carried over into the
following fishing year.
Table 13 lists the common pool trimester TACs for FYs 2012-2014
based on the ACLs and sub-ACLs set in this action (see Item 4 of this
preamble). As described earlier, vessels have until April 30, 2012, to
drop out of a sector, and common pool vessels may join a sector through
April 30, 2012. If the final sub-ACLs included in this rule change as a
result of changes to FY 2012 sector rosters, the trimester TACs will
also change. NMFS will update the common pool trimester TACs in an
adjustment rule in early May 2012, if necessary.
Table 12--Percentage of Common Pool Sub-ACL Distributed to Each
Trimester
------------------------------------------------------------------------
Percentage of common pool sub-ACL
Stock --------------------------------------
Trimester 1 Trimester 2 Trimester 3
------------------------------------------------------------------------
GB cod........................... 25 37 38
GOM cod.......................... 27 36 37
GB haddock....................... 27 33 40
GOM haddock...................... 27 26 47
GB yellowtail flounder........... 19 30 52
SNE/MA yellowtail flounder....... 21 37 42
CC/GOM yellowtail flounder....... 35 35 30
American plaice.................. 24 36 40
Witch flounder................... 27 31 42
GB Winter flounder............... 8 24 69
GOM Winter flounder.............. 37 38 25
Redfish.......................... 25 31 44
White hake....................... 38 31 31
Pollock.......................... 28 35 37
------------------------------------------------------------------------
[[Page 26112]]
Table 13--FY 2012-2014 Common Pool Trimester TACs
----------------------------------------------------------------------------------------------------------------
2012 2013 2014
Stock --------------------------------------------------------------------------------
Tri 1 Tri 2 Tri 3 Tri 1 Tri 2 Tri 3 Tri 1 Tri 2 Tri 3
----------------------------------------------------------------------------------------------------------------
GB cod......................... 20.5 30.3 31.1 n/a n/a n/a n/a n/a n/a
GB haddock..................... 35.6 43.5 52.7 n/a n/a n/a n/a n/a n/a
GOM haddock.................... 1.3 1.2 2.3 n/a n/a n/a n/a n/a n/a
GB yellowtail flounder......... 0.6 0.9 1.6 0.6 0.9 1.6 n/a n/a n/a
SNE/MA yellowtail flounder..... 35.3 62.2 70.6 n/a n/a n/a n/a n/a n/a
CC/GOM yellowtail flounder..... 9.5 9.5 8.1 n/a n/a n/a n/a n/a n/a
American plaice................ 13.7 20.5 22.8 n/a n/a n/a n/a n/a n/a
Witch flounder................. 6.4 7.3 9.9 n/a n/a n/a n/a n/a n/a
GB winter flounder............. 1.8 5.3 15.2 1.8 5.3 15.2 1.7 5.1 14.6
GOM winter flounder............ 8.9 9.1 6.0 9.1 9.3 6.1 9.1 9.3 6.1
Redfish........................ 8.6 10.6 15.0 n/a n/a n/a n/a n/a n/a
White hake..................... 10.1 8.2 8.2 n/a n/a n/a n/a n/a n/a
Pollock........................ 23.0 28.8 30.5 23.4 29.2 30.9 24.0 30.0 31.7
----------------------------------------------------------------------------------------------------------------
* Tri 1 = Trimester 1; Tri 2 = Trimester 2; Tri 3 = Trimester 3.
8. Common Pool Restricted Gear Areas
This action removes the common pool Western GB Multispecies
Restricted Gear Area (RGA) and the SNE Multispecies RGA. These RGAs
were implemented by Amendment 16 beginning in FY 2010 to help meet the
mortality objectives for the common pool fishery, and primarily reduce
the catch of flatfish species by common pool vessels. There are
sufficient fishing mortality controls for common pool vessels to keep
catch within the common pool catch limits. Therefore, the Western GB
and SNE Multispecies RGAs are no longer needed to control fishing
mortality for the common pool fishery. NMFS expects that removing the
Western GB and SNE Multispecies RGAs will facilitate fishing for common
pool vessels without risk of exceeding the common pool catch limits. In
addition, removing these common pool RGAs will simplify the regulations
and avoid confusion with new restricted gear areas included in this
action as an AM for common pool and sector vessels (see Item 9 of this
preamble).
9. Accountability Measures
AMs are required to prevent overfishing and ensure accountability
in the fishery. Proactive AMs are intended to prevent ACLs from being
exceeded, and reactive AMs are meant to correct or mitigate overages if
they occur. Amendment 16 implemented AMs for all of the groundfish
stocks. Upon approving Amendment 16, however, NMFS notified the Council
that it was concerned that the AMs developed for stocks not allocated
to sectors lacked sector-specific AMs. NMFS recommended that the
Council develop appropriate AMs for these stocks in a future action. As
a result, Framework 47 intended to revise the AMs for these stocks for
common pool and sector vessels.
During the development of Framework 47, there was ongoing
litigation on Amendment 16. Oceana, an environmental organization,
challenged Amendment 16 partially because it lacked sector-specific AMs
for stocks not allocated to sectors. On December 20, 2011, the U.S.
District Court for the District of Columbia upheld most of Amendment
16, but found that the Amendment's lack of reactive AMs for those
stocks not allocated to sectors (SNE/MA winter flounder, northern
windowpane flounder, southern windowpane flounder, ocean pout, Atlantic
halibut, and Atlantic wolffish) violated the Magnuson-Stevens Act. The
court remanded this single issue to NMFS and the Council for further
action. The Council developed the Framework 47 AMs before the Court
decided the case, however, and, therefore, did not specifically address
this remand in Framework 47. When it proposed Framework 47, NMFS asked
for specific comments about the adequacy of sector specific AMs in
light of the court's decision and remand.
Ocean Pout and Windowpane Flounder, and Atlantic Halibut
This action adopts reactive AMs for ocean pout, both stocks of
windowpane flounder, and Atlantic halibut for sector and common pool
vessels that would be triggered if the total ACL is exceeded. NMFS will
evaluate total catch of each stock in the year following the pertinent
fishing year (Year 2), and if the total ACL for the fishing year (Year
1) is exceeded, the AM will be implemented in the next fishing year
(Year 3). For example, if the total ACL for ocean pout is exceeded in
FY 2012, NMFS will implement the applicable AM for ocean pout in FY
2014.
The Council decided to implement these AMs in Year 3 out of its
concern that final catch information, including final discard
estimates, needed to evaluate total catch in the fishery would not be
available in time to implement until Year 3.
To determine if the total ACL is exceeded for any of these stocks,
NMFS will include catch by the groundfish fishery as well as catch by
sub-components of the fishery (e.g., state waters and non-groundfish
fisheries). Since these AMs are meant to restrict catch by common pool
and sector vessels, sectors cannot be exempt from these AM provisions.
Adopting these AMs removes the trimester TAC provision for common pool
vessels, which was the previous AM implemented by Amendment 16 for
these stocks that would have become effective in FY 2012. Prior to
Framework 47, the AMs for these stocks only applied to common pool
vessels, and did not include measures to restrict catch by sector
vessels should an ACL be exceeded.
Currently, a sub-ACL is only allocated to the common pool fishery
for these stocks and catch by common pool and sector vessels is counted
against the common pool sub-ACL. If a sub-ACL is specified in the
future for other fisheries, and AMs are developed for these fisheries,
the AMs for the groundfish fishery or any other fisheries would only be
triggered if both the total ACL for the stock and the fishery's sub-ACL
are exceeded, including the fishery's share of any overage caused by
the other sub-components.
If the total ACL for Atlantic halibut is exceeded in Year 1,
landing of Atlantic halibut will be prohibited by common pool and
sector vessels in Year 3. If the total ACL is exceeded for ocean pout,
northern windowpane flounder, or
[[Page 26113]]
southern windowpane flounder in year 1, gear restrictions will apply in
the AM areas developed for each stock for both sector and common pool
vessels in Year 3. For all three stocks, trawl vessels will be required
to use selective trawl gear. Approved gears include the haddock
separator trawl, the Ruhle trawl (see Item 14 for description of Ruhle
trawl that includes the mid-sized eliminator (or Ruhle) trawl in the
definition of this gear type), the rope trawl, and any other gears
authorized by the Council in a management action or approved for use
consistent with the process defined at Sec. 648.85(b)(6). There are no
restrictions on longline or gillnet gear because these gear types
comprise a small amount of the total catch for these stocks. If the
amount of the total ACL overage is between the management uncertainty
buffer and up to 20 percent, the small AM area will be triggered for
the pertinent stock. Currently, the management uncertainty buffer is 5
percent; however, this buffer could be modified in the future. If the
ACL is exceeded by 21 percent or more, the large AM area will be
triggered. The applicable GB AM area will be implemented if the total
ACL for northern windowpane is exceeded, and the applicable SNE AM area
will be implemented if the total ACL for southern windowpane is
exceeded. Both the GB and SNE AM areas will be implemented if the total
ACL for ocean pout is exceeded. Sectors may not be exempted from these
AM provisions.
Currently, common pool and sector vessels have a one-fish landing
limit for Atlantic halibut. Because commercial groundfish vessels can
only land one Atlantic halibut per trip, and generally do not target
this stock, a zero possession limit, by itself, even if implemented
sooner than Year 3, will not likely create a sufficient incentive for
vessels to avoid catching this stock should the total ACL be exceeded.
Therefore, NMFS finds that the reactive AM for this stock adopted in
this action is not adequate, by itself, in light of court's remand
described above. NMFS recommends that the Council consider area
closures or gear-restricted areas, similar to those adopted for
windowpane flounder and ocean pout, as a reactive AM for Atlantic
halibut. NMFS requests that the Council take action to ensure that
necessary revisions to the reactive AM for Atlantic halibut are
developed and implemented as soon as possible, and that significant
progress be made on this issue by its November 2012 meeting. NMFS also
requests that the Council consider whether these measures could be
applied retroactively to FY 2012.
NMFS is approving the reactive AM for Atlantic halibut because,
should the total ACL be exceeded, it will provide some benefit to the
fishery as a conservation measure, where currently there is none, and
will alleviate perceived inequity between sector and common pool
vessels. The AM for this stock adopted in Amendment 16, which would go
into place if NMFS disapproved the Framework 47 a.m., only applies to
common pool vessels. Common pool and sector catch would count against
the common pool sub-ACL, and if the sub-ACL were exceeded, the common
pool sub-ACL would be reduced by the amount of the overage in the
subsequent fishing year. In FY 2010, sector vessels caught 92 percent
of the total commercial catch for Atlantic halibut, and, based on
preliminary catch information, sector vessels have caught more than 95
percent of the total commercial catch for Atlantic halibut in FY 2011.
Therefore, although NMFS does not find the reactive AM for this stock
adopted in this action adequate by itself, in light of court's remand
described above, approving this reactive AM as a conservation measure
provides some meaningful benefit until a new, or additional, reactive
AM can be developed.
With respect to the delayed implementation of these reactive AMs to
Year 3, NMFS recommends that these AMs be implemented as soon as
possible after the overage occurs, when catch data, including final
discard information, reliably show an overage of the catch limit, and
not be bound by an AM that only allows implementation in Year 3. The
Council recommended a Year 3 implementation because of concerns that
final catch data for these stocks, which include catch from state
waters and non-groundfish fisheries and discard estimates, could not be
reliably available in time to trigger the AM in Year 2, or earlier. As
monitoring improves, and discard estimates are more readily available
for all components of the fishery, NMFS anticipates that these reactive
AMs can, and should, be implemented more quickly.
SNE/MA Winter Flounder and Atlantic Wolffish
Amendment 16 prohibited possession of SNE/MA winter flounder and
Atlantic wolffish by commercial vessels. This action adopts the current
zero possession as a proactive AM for SNE/MA winter flounder and
Atlantic wolffish for commercial vessels. Based on FY 2010 catch
information and partial FY 2011 catch information, the Council
concluded, before the decision in the Amendment 16 lawsuit described
above, that prohibiting possession appears to have kept catch of these
stocks well below mortality targets, and that such preventive measures
satisfy the AM requirements of the Magnuson-Stevens Act. However,
although zero possession may be a sufficient proactive AM for these
stocks, the Magnuson-Stevens Act requires reactive AMs. NMFS recommends
that the Council consider area closures or gear-restricted areas,
similar to those adopted for windowpane flounder and ocean pout, as a
reactive AM for SNE/MA winter flounder and Atlantic wolffish. NMFS
requests that the Council take action to ensure reactive AMs for SNE/MA
winter flounder and Atlantic wolffish are developed and implemented as
soon as possible, and that significant progress be made on this issue
by its November 2012 meeting. NMFS also requests that the Council
consider whether these measures could be applied retroactively to FY
2012.
Although zero possession does not meet the requirement for a
reactive AM for these stocks, NMFS approves these measures because it
removes a potential inequity for common pool vessels. Adopting zero
possession for SNE/MA winter flounder and Atlantic wolffish, as
prescribed by Framework 47, removes the trimester TAC provision for
these stocks for common pool vessels established by Amendment 16. Under
the default Amendment 16 measures, if the overall sub-ACL for these
stocks is exceeded in a year, the common pool's sub-ACL is reduced by
the amount of the overage. This AM only applies to the common pool,
even if sector vessels cause the overage. Because common pool vessels
generally take less than 10 percent of the total commercial catch of
these two stocks, there is a potential inequity in only applying the AM
to the common pool vessels. Until the Council is able to develop
reactive AMs for these two stocks, the zero possession proactive AM
will avoid disproportionately penalizing common pool vessels for catch
by sector vessels, and will continue to benefit the fishery by keeping
catch within allowable levels.
10. Removal of Cap on Yellowtail Flounder Catch in Scallop Access Areas
In 2004, Framework 39 to the NE Multispecies FMP and Framework 16
to the Atlantic Sea Scallop FMP implemented a cap on the amount of
yellowtail flounder that could be caught in the Nantucket Lightship,
Closed Area I, and Closed Area II Sea Scallop Access
[[Page 26114]]
Areas. This measure was implemented before ACL and AM provisions were
added to the NE Multispecies and Atlantic Sea Scallop FMPs to ensure
that yellowtail flounder catches did not exceed the target TACs for
yellowtail flounder or exceed the U.S TAC for GB yellowtail flounder.
This action removes the 10-percent access area cap for the Nantucket
Lightship, Closed Area I, and Closed Area II Sea Scallop Access Areas.
The scallop fishery is still subject to its GB and SNE/MA yellowtail
flounder sub-ACLs, but there is no limit on how much of the sub-ACLs
can be caught in the scallop access areas. The yellowtail flounder sub-
ACLs limit the amount of yellowtail flounder that can be caught by the
scallop fishery, so a catch cap for the access areas in no longer
necessary to meet fishing mortality objectives.
11. Implementation of Scallop Fishery Accountability Measure
Each year a portion of the GB and SNE/MA yellowtail flounder ABC is
allocated to the scallop fishery as a sub-ACL. If the scallop fishery
exceeds its sub-ACL for either of these stocks, the statistical areas
with high catch rates of yellowtail flounder are closed to limited
access scallop vessels. The duration of the closure depends on the
magnitude of the overage. Framework 23 to the Atlantic Sea Scallop FMP
(Framework 23) set the yellowtail flounder seasonal closure AM schedule
for scallop vessels to ensure that the closures would occur during the
months with the highest yellowtail flounder catch rates.
This action modifies when the AM for the scallop fishery is
triggered. The scallop fishery AM will be triggered if: (1) The scallop
fishery exceeds it sub-ACL for any groundfish stock, and the total ACL
for that stock is also exceeded; or (2) the scallop fishery exceeds its
sub-ACL by 50 percent or more for any groundfish stock, even if the
total ACL for that stock is not exceeded. If the scallop fishery AM is
triggered, the corresponding scallop seasonal closure will be
implemented according to the seasonal closure AM schedule. Currently,
the scallop fishery is only allocated a sub-ACL for GB and SNE/MA
yellowtail flounder; however, this measure applies to the scallop
fishery AM for any additional groundfish stock that is allocated to the
scallop fishery in a future action. This measure is applied
retroactively to the 2011 scallop fishing year.
Given the differences in the scallop and groundfish fishing years,
complete catch information for GB and SNE/MA yellowtail flounder will
not be available until sometime after April 30 (the end of the
groundfish fishing year). In addition, inseason catch information is
not available for groundfish ACL sub-components, such as state waters
catch. As a result, when evaluating the total catch of GB and SNE/MA
yellowtail flounder for the purposes of triggering the scallop fishery
AM, NMFS will primarily rely on partial catch information to project
total fishing year catch of these two stocks from state waters and non-
groundfish fisheries. NMFS will also use partial fishing year data to
estimate GB and SNE/MA yellowtail flounder catch by the commercial
groundfish fishery and will project catch of these two stocks by
groundfish vessels for the remainder of the groundfish fishing year.
NMFS will add the maximum carryover available to the groundfish fishery
to the estimate of total catch when evaluating whether the total ACL
has been exceeded for a groundfish stock for the purposes of triggering
the scallop fishery AM.
This measure is expected to allow more flexibility in the fishery.
The yellowtail flounder allocation to the scallop fishery is based on
an estimated catch of yellowtail flounder with the projected scallop
harvest for the fishing year. There is uncertainty in the projected
yellowtail flounder catch in the scallop fishery, and this measure will
help account for that uncertainty without compromising the mortality
objectives for GB and SNE/MA yellowtail flounder. In addition,
triggering the AM when the scallop fishery exceeds its allocation by 50
percent or more will still ensure accountability in the fishery. The
Council did not specifically include how to reference this measure in
the scallop regulations in Framework 47; therefore, NMFS adopts these
references under its authority in section 305(d) of the Magnuson-
Stevens Act.
12. Inseason Re-Estimation of Scallop Fishery GB Yellowtail Flounder
Sub-ACL
The allocation of the GB yellowtail flounder sub-ACL to the scallop
fishery is based on an estimate of the expected GB yellowtail flounder
catch in the scallop fishery. Because there is uncertainty in the
initial estimates of projected GB yellowtail flounder catch, it is
possible that the initial allocation to the scallop fishery will be too
low, which could cause the scallop sub-ACL to be exceeded, or that the
initial allocation to the scallop fishery will be too high, which could
reduce GB yellowtail flounder yield. This measure creates a mechanism
to re-estimate the expected GB yellowtail flounder catch by the scallop
fishery by January 15 of each fishing year. If the re-estimate of
projected GB yellowtail flounder indicates that the scallop fishery
will catch less than 90 percent of its sub-ACL, NMFS may reduce the
scallop fishery sub-ACL to the amount expected to be caught, and
increase the groundfish fishery sub-ACL for GB yellowtail flounder up
to the difference between the original estimate and the revised
estimate. Any increase to the groundfish fishery sub-ACL will be
distributed to sectors and the common pool. NMFS will not make any
changes to the GB yellowtail flounder sub-ACL for the scallop fishery
if the revised estimate indicates that the scallop fishery will catch
90 percent or more of its sub-ACL. Consistent with the Administrative
Procedure Act, NMFS will notify the public of any changes to the GB
yellowtail flounder sub-ACLs. This measure is expected to prevent any
loss of GB yellowtail flounder yield that may occur if the initial
catch estimate of this stock by the scallop fishery is too high. Re-
estimating the expected GB yellowtail flounder catch by the scallop
fishery mid-season will allow additional GB yellowtail flounder yield
by the commercial groundfish fishery, and will help achieve optimum
yield for this stock.
Due to uncertainty associated with the revised estimate of expected
GB yellowtail flounder catch, NMFS has the authority to adjust the size
of the change made to the sub-ACLs for the scallop and groundfish
fisheries. Based on the amount of the uncertainty, NMFS could revise
the sub-ACLs by any amount between the initial estimate of expected GB
yellowtail flounder catch by the scallop fishery and the revised
estimate. Implementation of this measure may be delayed until data are
sufficient for NMFS to project GB yellowtail flounder catch and re-
estimate the GB yellowtail flounder sub-ACL for the scallop fishery
mid-season. Consideration of uncertainty and delay in implementation of
this measure will avoid errors in re-estimating the GB yellowtail
flounder sub-ACLs if the projected scallop fishery catch is
underestimated. Errors in the re-estimation of the scallop fishery sub-
ACL could cause the scallop fishery to exceed its sub-ACL if projected
catch is underestimated, which may trigger the scallop fishery AM. In
addition, if the groundfish fishery catches the additional GB
yellowtail flounder allocated mid-fishing year, the U.S. TAC for GB
yellowtail flounder could be exceeded.
[[Page 26115]]
13. Annual Measures for FY 2012 Under Regional Administrator Authority
The FMP authorizes the RA to implement certain types of management
measures for the common pool fishery, the U.S./Canada Management Area,
and Special Management Programs on an annual basis, or as needed. This
rule includes management measures for FY 2012 that are being
implemented under RA authority. These measures are not part of
Framework 47, and were not specifically proposed by the Council, but
are included in this final rule because they relate to Framework 47
measures (i.e., ACLs). The RA may modify these measures if current
information indicates changes are necessary. Any adjustments to these
measures will be implemented through an inseason action consistent with
the Administrative Procedure Act.
Table 14 lists the initial FY 2012 trip limits for common pool
vessels. These FY 2012 trip limits take into consideration changes to
the FY 2012 common pool sub-ACLs and sector rosters, trimester TACs for
FY 2012, catch rates of each stock during FY 2011, bycatch, the
potential for differential DAS counting in FY 2012, public comments
received on the proposed FY 2012 trip limits, and other available
information. This action does not change the default cod trip limit for
vessels with a limited access Handgear A permit (300 lb (136.1. kg) per
trip), an open access Handgear B permit (75 lb (34.0 kg) per trip), or
a limited access Small Vessel Category permit (300 lb (136.1 kg) of
cod, haddock, and yellowtail flounder combined).
NMFS will monitor common pool catch using dealer-reported landings,
VMS catch reports, and other available information, and if necessary,
will adjust the common pool management measures.
Table 14--Initial FY 2012 Common Pool Trip Limits
------------------------------------------------------------------------
Stock Initial FY 2012 trip limits
------------------------------------------------------------------------
GOM cod................................ 650 lb (294.8 kg) per DAS, up
to 2,000 lb (907.2 kg) per
trip.
GB cod................................. 2,000 lb (907.2 kg) per DAS, up
to 20,000 lb (9,072 kg) per
trip.
GOM haddock............................ 1,000 lb (453.6 kg) per trip.
GB haddock............................. 10,000 lb (4,535.9 kg) per
trip.
GOM winter flounder.................... 250 lb (113.4 kg) per trip.
GB winter flounder..................... 1,000 lb (453.6 kg) per trip.
CC/GOM yellowtail flounder............. 500 lb (226.8 kg) per DAS, up
to 2,000 lb (907.2 kg) per
trip.
GB yellowtail flounder................. 500 lb (226.8 kg) per trip.
SNE/MA yellowtail flounder............. 1,500 lb (680.4 kg), up to
4,500 (2,041.1 kg) per trip.
American plaice........................ unrestricted.
Pollock................................ unrestricted.
Witch flounder......................... 250 lb (113.4 kg) per trip.
White hake............................. 1,500 lb (680.4 kg) per trip.
Redfish................................ unrestricted.
------------------------------------------------------------------------
The FMP also provides the RA the authority to allocate the total
number of trips into the Closed Area II Yellowtail Flounder/Haddock SAP
based on several criteria, including the GB yellowtail flounder TAC and
the amount of GB yellowtail flounder caught outside of the SAP. In
2005, Framework 40B (June 1, 2005; 70 FR 31323) implemented a provision
that no trips should be allocated to the Closed Area II Yellowtail
Flounder/Haddock SAP if the available GB yellowtail flounder catch is
insufficient to support at least 150 trips with a 15,000-lb (6,804-kg)
trip limit (i.e., 150 trips of 15,000 lb (6,804 kg)/trip, or 2,250,000
lb (1,020,600 kg)). This calculation accounts for the projected catch
from the area outside the SAP. Based on the groundfish sub-ACL of
479,946 lb (217,700 kg), there is insufficient GB yellowtail flounder
to allocate any trips to the SAP, even if the projected catch from
outside the SAP area is zero. Therefore, this action allocates zero
trips to the Closed Area II Yellowtail Flounder/Haddock SAP for FY
2012. Vessels can still fish in this SAP in FY 2012 using a haddock
separator trawl, a Ruhle trawl, or hook gear. Vessels are not allowed
to fish in this SAP using flounder nets.
14. Mid-Size Ruhle Trawl
This action modifies the definition of the Ruhle Trawl to include
the smaller dimensions of the mid-size Eliminator trawl and only
include the primary design features of the net design. The following
modifications are being made: Replace the minimum fishing circle
requirement with a more concise and enforceable measure using the
minimum number of meshes at the wide end of the first bottom belly;
adjust the mesh configuration in the forward part of the net and the
minimum kite area requirements to that of the mid-size Eliminator; and
remove the sweep configuration requirements. The sweep requirements
have been removed from the definition because this component of the
gear is largely based on bottom composition and preference, and is not
the primary bycatch reduction device. The primary bycatch reduction
device for this gear type is the large meshes located in the forward
part of the net. The minimum mesh sizes and minimum kite area are
reduced to enable the mid-size Eliminator to meet the Ruhle trawl
definition.
The Council requested that NMFS implement a smaller-scale version
of the Ruhle trawl (i.e., the mid-size Eliminator Trawl) that should
be: (1) Available for use by both sector and non-sector vessels in the
Eastern U.S./Canada Haddock SAP and Regular B DAS Program; and (2)
assigned a separate gear code but should not be assigned a separate
stratum for the purpose of discard information. Expanding this
definition will increase fishing opportunity for smaller vessels by
allowing them to utilize this smaller-scale trawl, and therefore, have
access to the Haddock SAP, as well as the B DAS program. In addition,
vessels will be able to operate under the Ruhle trawl gear code, which
will result in reduced discard rates for certain species, particularly
depleted stocks that may have constraining catch limits.
Vessels fishing in the Regular B DAS Program or the Haddock SAP
must use approved trawl gear that has been determined to reduce the
catch of NE multispecies stocks of concern. The RA may approve
additional gears for use in the Regular B DAS Program and the Eastern
U.S./Canada Haddock SAP if a gear meets gear performance standards
defined at Sec. 648.85(b)(6)(iv)(J)(2). These
[[Page 26116]]
gear performance standards were developed to allow the harvest of
healthy stocks (e.g., GB haddock) while avoiding the capture of stocks
of concern (e.g., GB cod and GB yellowtail flounder). The full-size
Eliminator trawl (i.e., Ruhle trawl) was tested in 2006. This
experiment demonstrated that it effectively harvested the target
species haddock while reducing catches of cod and other stocks of
concern. In response to a Council's request, NMFS, approved the Ruhle
trawl for use in the B DAS Program and Haddock SAP on July 14, 2008 (73
FR 40186). The current definition of the Ruhle trawl is specific to the
experimental net, which was designed for relatively large vessels. The
University of Rhode Island (URI) conducted a follow-on study that
tested two smaller versions of the Ruhle trawl that could be used by
smaller vessels (small-size Eliminator trawl and mid-size Eliminator
trawl) to determine if the catch performance of the smaller trawls is
similar to that of the full-size trawl. Following a successful peer
review in 2010, the Council determined that the mid-size Eliminator
trawl effectively meets the pertinent gear performance standards and
requested that NMFS approve the use of the mid-size Eliminator trawl by
sector and non-sector vessels in the B DAS Program and Haddock SAP.
Vessels participating in the NE multispecies common pool and sector
management programs are subject to catch limits, which include
discarded catch. Vessel Trip Report (VTR) gear codes, in conjunction
with stock area fished and sector, are used to establish discard strata
for each NE multispecies stock to ensure these catch limits are not
exceeded. Each discard stratum has a particular discard rate associated
with each NE multispecies stock based on of Northeast Fisheries
Observer Program (NEFOP) and at-sea-monitor (ASM) data. There are
currently three commonly used VTR trawl gear codes for groundfish:
Bottom fish; haddock separator; and Ruhle trawl. Because the haddock
separator trawl and the Ruhle trawl were designed to fish more
selectively than a regular bottom fish trawl, trips using these two
gear types generally have reduced catch for certain stocks of NE
multispecies, particularly flatfish and cod, resulting in a lower
discard rate for these species. Due to the similar catch performance
characteristics of the mid-size Eliminator and Ruhle trawl, data from
both gear types will be pooled for the purpose of assigning discard
rates and establishing discard strata.
The Council also requested that NMFS create a new VTR gear code for
the mid-size Eliminator Trawl to monitor the catch performance of this
net design in the fishery. However, creating a new gear code would not
achieve the Council's objective. A mid-size Eliminator trawl can range
in size from the experimental net up to the size of the Ruhle trawl. As
a result, a vessel may correctly choose the mid-size Eliminator Trawl
VTR gear code, but the net size could vary considerably from the
experimental net size. This would prevent using the VTR gear code to
monitor how the experiment net performs when adopted in the fishery.
Instead, NMFS will use foot-rope length and discard data obtained by
trips that are accompanied by a NEFOP assigned observer or ASM. Data
from observed or monitored vessels that are using a mid-size Eliminator
with a sweep that is comparable to the experimental net sweep of 33m
(109 ft) will be used to evaluate how the experimental gear is
performing in practice.
15. Monitoring of Fillets, Fish Parts, and Fish Landed for At-Home
Consumption
In the proposed rule for this action, NMFS proposed to replace the
3:1 counting method with new species-specific conversion factors for
the purposes of counting fillets and fish-parts landed for at-home
consumption against the pertinent ACLs. However, based on public
comments received on this proposed measure, and additional analysis
performed, NMFS concluded that the 3:1 counting method is the most
accurate for counting fillets and fish parts landed for at-home
consumption against ACLs, and that any changes to this conversion
factor should go through the Council.
Framework Adjustment 27 to the NE Multispecies FMP (Framework 27)
implemented a counting rate of 3:1 for the purposes of ensuring
compliance with days-at-sea possession limits. This counting rate was
implemented prior to implementation of ACLs and AMs in the FMP. When
Amendment 16 was implemented in 2010, the 3:1 counting rate was not
extended for quota monitoring purposes to ensure that all catch by
common pool and sector vessels is counted and attributed to the
appropriate sub-ACL. Therefore, on July 19, 2011, NMFS published an
interim final rule correcting the counting method for fillets and parts
of fish landed for home consumption (76 FR 42577). The interim final
rule applied the 3:1 counting rate to all fillets and parts of fish
landed for home consumption by sector and common pool vessels.
For FY 2010 and FY 2011, fish landed for at-home consumption were
counted at a 1:1 rate against the common pool and sector sub-ACLs. This
was not accurate. Beginning in FY 2012, all fillets and parts of fish
landed for home consumption will be multiplied by 3 for quota
monitoring purposes. All catch by sector and common pool vessels,
including fillets retained by crew for home consumption, count against
a sector's ACE for that stock or the common pool sub-ACL for that
stock. The 3:1 counting method is consistent with the FMP requirement
that all catch by sector and common pool vessels be accounted for, and
is also consistent with the 3:1 counting method implemented by the
Council in Framework 27. The 3:1 counting rate for fillets and parts of
fish will also continue to be used to determine compliance with
possession limits for common pool vessels.
16. Charter/Party Vessel Closed Area Letter of Authorization
Framework Adjustment 33 to the NE Multispecies FMP (Framework 33)
allowed charter/party and recreational vessels to fish in the GOM
Rolling Closure Areas, the Western GOM Closure Area, Cashes Ledge
Closure Area, and the Nantucket Lightship Closed Area, provided the
vessel is issued a letter of authorization (LOA) from the Regional
Administrator. Framework 33 prohibited vessels issued this LOA from
selling any fish, except for species that are not managed by the New
England Fishery Management Council (NEFMC) or the Mid-Atlantic Fishery
Management Council (MAFMC). When NMFS implemented this action, the
regulations only provided an exception to the sale of tuna for charter/
party vessels issued this LOA. This exception was inconsistent with the
Council's intent. In addition to tuna, striped bass and lobster, among
other species, are not managed by the NEFMC or the MAFMC, and
therefore, should be precluded from the prohibition of sale. This
action clarifies the regulations that charter/party vessels issued a
LOA to fish in the GOM Rolling Closure Areas, the Western GOM Closure
Area, Cashes Ledge Closure Area, and the Nantucket Lightship Closed
Area are only prohibited from selling fishing species managed by the
NEFMC or the MAFMC.
Comments and Responses on Measures Proposed in the Framework 47
Proposed Rule
NMFS received nine comments during the comment period on the
Framework 47 proposed rule from six individuals, one industry group,
the Council, and Oceana.
[[Page 26117]]
Acceptable Biological Catches and Annual Catch Limits
Comment 1: Oceana commented that NMFS should disapprove the catch
limits in Framework 47 because they are not based on the best
scientific information available and, therefore, violate National
Standard 2. Oceana stated that the stock assessment updates completed
in early 2012 should be the basis for setting catch limits in Framework
47, and that NMFS should disapprove the ABCs for the 13 stocks whose
assessments were updated in 2012. Oceana also stated that NMFS should
take emergency or interim action to revise catch limits for FY 2012.
Response: National Standard 2 guidelines (50 CFR 600.315) require
that each FMP (and by extension amendment and framework) must take into
account the best scientific information available at the time, or
preparation, of an action. The guidelines recognize that new
information often becomes available between the initial drafting of an
FMP and its submission to NMFS for final review. The guidelines state
that this new information should be incorporated into the action, if
practicable; but it is unnecessary for the Council to start the FMP
process over again, unless the information indicates that drastic
changes have occurred in the fishery that might require revision of the
management objectives or measures. This is not a situation in which the
Council received information that ``drastic changes'' have occurred in
the fishery prior to submission of the action to NMFS. Instead, as was
fully understood in the development of Framework 47, the assessment
updates were not completed until after the Council took final action on
Framework 47 and submitted it to NMFS for review. As a result, there
was no practicable way to incorporate this information into Framework
47 without reinitiating the Council process and delaying the action far
beyond the start of FY 2012, which begins on May 1, 2012, and is when
the ABCs need to be in place. Therefore, NMFS has determined that it is
appropriate for the Council to set the OFLs and ABCs in this action
based on the best scientific information available at the time the
Council took final action and submitted Framework 47 to NMFS for
approval. The appropriate response to the new information that became
available after submission to NMFS is for the Council to consider
whether to initiate a new framework or amendment, or to request an
emergency or interim Secretarial action, to revise the existing
measures or catch limits adopted in this action.
Consistent with the National Standard 2 guidelines, this
determination recognizes the need for some certainty as to what
scientific information the Council may rely on in taking its final
action, and what information NMFS will use to evaluate the
approvability of a Council action. Without such certainty, there would
be a lack of predictability and confidence in Council actions, which
must be developed well in advance of their implementation due to the
time it takes to prepare appropriate analyses and documents for
submission to NMFS for final review. Uncertainty about what information
will be used to review a Council action could also seriously undermine
the Council process, because neither the Council, nor the public, would
be confident their efforts would not be meaningless. Thus, new
scientific information that becomes available after the Council has
submitted its final action to NMFS for review should not, based on
National Standard 2, be used retroactively to undo recommended actions
that had the benefit of the full Council process.
NMFS also considered the practical effect of disapproving the OFLs
and ABCs specified in this action. Approving the catch limits for these
stocks, whose assessments were updated in early 2012, actually results
in slightly less fishing mortality than if they were disapproved and
the default measures specified by Framework 44 and Framework 45 went
into place. The default catch limits for FY 2012 for the five stocks
mentioned earlier (GB cod, GOM haddock, CC/GOM yellowtail flounder,
American plaice, and witch flounder) are identical to those specified
in this action, except for GB cod, which is 5 percent higher. For the
remaining stocks, the default measures are essentially identical or
higher than those adopted in Framework 47. Therefore, disapproving the
FY 2012 ABCs in Framework 47 would result in the same catch limits as
those previously specified, and a higher catch limit for GB cod, which
could increase overfishing on this stock while the Council develops its
next management action to incorporate the new scientific information
available.
Approving these catch limits, as explained above, does not reduce
the importance of acting on the new information as soon as possible in
a new action, but rather emphasizes the importance of analyzing and
considering this information through the full Council process.
Consistent with the SSC guidance and the Council's understanding during
the development of Framework 47, the Council has already started
developing a management action to incorporate the assessment update
information and adopt catch limits for the pertinent stocks for FYs
2013-2014. A new stock assessment is also scheduled for SNE/MA
yellowtail flounder in June 2012, and the results of this stock
assessment will be incorporated into the same Council action to set
OFLs and ABCs for the stock for FYs 2013-2014. The Council may also use
updated information for other stocks to revise the FYs 2013-2014 OFLs
and ABCs specified in this action. The Council intends to complete this
management action by May 1, 2013, to set catch limits for FYs 2013-
2014.
Oceana's comment recommending emergency action is outside the scope
of this action and is considered to be an independent request for NMFS
to take action addressing the updated stock assessment information. As
explained above, this new information should preferably be considered
through the full Council process, and NMFS has charged the Council to
address this new information as soon as possible. At the time of this
rulemaking, the Council has not yet had the opportunity to review and
discuss the results of the assessment updates. NMFS believes this
information is best incorporated through the Council process, and is
waiting on a response from the Council to Framework 47 and the
assessment updates. The Council is scheduled to receive and discuss the
results of the assessment updates at its April 25, 2012, meeting. NMFS
has notified the Council that the updated assessment information must
be incorporated as soon as possible, but no later than May 1, 2013.
NMFS recommends that, at its June meeting, the Council identify how and
when this information will be incorporated and how that process would
affect any existing or planned management measures.
Accountability Measures
Comment 1: The Council commented that the use of zero possession
has been effective at keeping catches within allowable levels for
pertinent stocks. The Council commented that adopting zero possession
as a proactive AM for SNE/MA winter flounder and Atlantic wolffish, and
as a reactive AM for Atlantic halibut, is the Council's preferred
method for ensuring catch levels are not exceeded while also giving
industry the greatest possible opportunity to target healthy stocks.
Oceana commented that the use of zero possession as an AM is not
adequate for
[[Page 26118]]
SNE/MA winter flounder, Atlantic wolffish, or Atlantic halibut.
Response: NMFS agrees that zero possession for SNE/MA winter
flounder and Atlantic wolffish appears to have effectively kept catches
within allowable levels. In FY 2010, total catch of these two stocks
was well below the total ACL, and based on preliminary catch
information, it appears that total catches will also be below the total
ACL in FY 2011. However, as discussed in Item 9 of this preamble,
although zero possession may be a sufficient proactive AM for these two
stocks, effective reactive AMs remain necessary, and must be developed
as soon as possible as a step in the ongoing process to ensure
compliance with the with the Court remand. If zero possession continues
to be an effective proactive AM, the reactive AM will likely not be
triggered. However, should the proactive AM fail, and an overage of the
total ACL occurs, a reactive AM will ensure this overage is mitigated,
and prevent repeated overages of the ACL. For Atlantic halibut, a zero
possession reactive AM, while a step in the right direction, by itself,
is not adequate in light of the court's remand. Because commercial
groundfish vessels can only land one halibut per trip, and generally do
not target halibut, a zero possession limit will not likely create a
sufficient incentive for vessels to avoid catching this stock should an
ACL be exceeded. NMFS recommends that the Council consider area
closures or gear-restricted areas, similar to those adopted for
windowpane flounder and ocean pout, as a reactive AM for these stocks.
NMFS requests that the Council take action to ensure that effective
reactive AMs are developed and implemented as soon as possible, and
that significant progress be made on this issue by its November 2012
meeting. NMFS also requests that the Council consider whether these
measures could be applied retroactively to FY 2012.
While NMFS recognizes that the AMs approved in this action do not
satisfy the court remand, zero possession as a proactive AM for SNE/MA
winter flounder, and as a reactive AM for Atlantic halibut, will still
provide some benefit to prevent catch from exceeding the ACLs for these
stocks, and will reduce a potential inequity between common pool and
sector vessels. The initial AMs implemented by Amendment 16 for these
stocks only applied to common pool vessels. Catch by common pool and
sector vessels counted against the common pool sub-ACL. Based on
preliminary FY 2011 catch information, sector vessels have caught more
than 95 percent of the total commercial catch for SNE/ME winter
flounder, Atlantic wolffish, and Atlantic halibut. Disapproving the
Framework 47 AMs for these stocks would result in the same default
management measures for SNE/MA winter flounder and Atlantic wolffish
(zero possession), no reactive AM for Atlantic halibut, and would
disproportionately penalize common pool vessels. Therefore, NMFS has
approved zero possession as a proactive AM for SNE/MA winter flounder
and Atlantic wolffish, but recognizes that reactive AMs are required
for these stocks and must be developed as soon as possible. In
addition, NMFS approves the reactive AM for Atlantic halibut because it
will provide some conservation benefit while the Council develops a
more effective reactive AM for this stock. Approving these AMs will
also ensure the common pool vessels are not disproportionately
penalized for any overages that may occur.
Comment 2: Oceana disagreed that an AM should be implemented 2
years after the fishing year in which the overage occurred, and stated
that this measure is inconsistent with the National Standard 1
guidelines. Oceana suggests that inseason AMs are not impossible and
that preliminary data is used for inseason management in other
fisheries.
Response: The Council adopted AMs for windowpane flounder, ocean
pout, and Atlantic halibut that would be implemented in Year 3 because
evaluating total catch includes catch of these stocks in state waters
and non-groundfish fisheries. The Council felt that final catch data,
including final discard estimates, would not be reliably available in
time to implement these AMs earlier than Year 3. Indeed, catch
information, including discard estimates, are not readily available
inseason for these components of the fishery. While we are approving
this measure because it provides a reactive AM for these stocks should
an ACL be exceeded, where no AM currently exists, NMFS recommends that
the Council reconsider the timing of these AMs. NMFS recommends to the
Council that AMs should be implemented as soon as possible, rather than
2 years after an overage occurs, when catch data, including final
discard information, show an overage of the catch limit. As monitoring
improves, and discard estimates are more readily available for all
components of the fishery, NMFS anticipates that these reactive AMs
can, and should, be implemented more quickly.
Annual Measures for FY 2012 Under Regional Administrator Authority
Comment 1: One commenter favored an 800 lb per day-at-sea (DAS)
trip limit for GOM cod. The commenter stated that this trip limit would
make each trip more profitable and would allow hiring one crew member,
as opposed to fishing alone.
Response: NMFS proposed a trip limit range for GOM cod of 500 lb-
800 lb per DAS. NMFS is implementing an initial FY 2012 trip limit for
GOM cod of 650 lb per DAS. NMFS believes this trip limit will allow a
more profitable trip than the 500 lb DAS limit in FY 2011. A 650-lb
trip limit will likely preserve the GOM cod trimester TAC throughout
each trimester and prevent premature closure of the trimester TAC area.
If necessary, NMFS will modify trip limits inseason to prevent under
harvest or overharvest of the trimester TACs, or the common pool sub-
ACLs.
Comment 2: One commenter stated that the common pool fishery does
not need the trimester TAC AM because trip limits effectively control
fishing mortality during the fishing year and requested that NMFS not
implement the trimester TAC AM for the common pool fishery. This
commenter also stated that the trimester TAC AM for white hake should
not apply to vessels fishing with longline or hook gear. Another
commenter stated that the distribution of the common pool sub-ACL to
the trimesters should be revisited.
Response: The trimester TAC AM provision was adopted in Amendment
16 in 2010, and is not part of Framework 47. Accordingly, this measure
was not proposed in this action. Because this measure was not part of
Framework 47, these comments are irrelevant to, and outside the scope
of, the measures approved in this final rule.
To provide some background, however, FY 2012 will be the first
fishing year that this AM is effective for the common pool fishery. The
trimester TAC AM serves as a reactive AM that is triggered if an
overage of the common pool catch limit occurs. Sector-specific reactive
AMs are required for every groundfish stock. The trimester TAC AM is
only one type of reactive AM that the Council may use, and the Council
could develop a different AM for the common pool fishery if it chooses.
However, any changes to the trimester TAC AM must be developed through
the full Council process in another action, and cannot be addressed in
this rule. If trip limits continue to be an effective proactive AM that
keep common pool catch within allowable levels, the trimester TAC AM
will likely not be triggered. However, if inseason management measures
fail to keep catch
[[Page 26119]]
within allowable levels, the trimester TAC AM will ensure overfishing
does not occur and mitigate any overages.
When the trimester TAC AM was developed, the area closures for each
stock were applied to any gear types capable of catching that stock. In
addition, the distribution of the common pool sub-ACL was based on the
distribution of landings and the influence of management measures on
landings patterns. NMFS does not have the authority to modify the
applicable gear types for the white hake trimester TAC AM or the
distribution of the common pool sub-ACL. Any modifications to these
measures must be made through the Council process. NMFS recommends that
the commenters raise this issue to the Council for possible inclusion
in a future management action.
Mid-Size Ruhle Trawl
Comment 1: Two individuals commented that they strongly support the
proposed revision to the Ruhle trawl definition because it will provide
smaller vessels with increased fishing opportunities. One commenter
suggested that eliminating the requirement for a minimum kite area (as
opposed to the proposed minimum kite area of 19.3 sq. ft (1.8 sq. m))
would allow more flexibility.
Response: NMFS believes that the minimum kite size is necessary
because it will help ensure that the catch performance of the mid-size
Ruhle trawl will be more consistent and comparable with the catch
performance of the experimental net. The large meshes greatly reduce
catch of flounders and cod; however, the experimental net effectively
caught other fish, such as haddock, as a result of the relatively high
profile of the net. The high profile of the net is due, in part, to the
lift provided by the kites. A minimum kite size will also minimize the
catch performance differences between kites and headrope floats.
Therefore, NMFS retained the minimum kite size requirement.
Monitoring of Fillets, Fish Parts, and Fish Landed for At-Home
Consumption
Comment 1: One individual commented that landing fish for home
consumption should be prohibited, and that all catch should be counted
against the appropriate catch limit.
Response: ACLs and AMs for the groundfish fishery were implemented
by Amendment 16 in FY 2010. Allowing home consumption of some fish has
been a long-standing provision and was not proposed for elimination.
Therefore, this comment is outside the scope of this action. In any
event, landings and discards from all fisheries are counted against the
catch limit for each stock, including landings by commercial groundfish
vessels for home consumption. The proposed rule was intended only to
address the appropriateness of the conversion factor for determining
the live weight of fillets and parts of fish landed for home
consumption. As discussed in the response to the next comment, NMFS
decided not to implement a new conversion factor for fish parts landed
for home consumption.
Comment 2: One individual and the Council commented that the
proposed species-specific conversion factors for home consumption are
nearly identical to the conversional factors used for dressed fish,
which could underestimate the amount of fish landed for home
consumption.
Response: NMFS agrees that the proposed species-species conversion
factors are similar to the conversion factors used for dressed fish.
Based on additional analysis, NMFS is not implementing the proposed
species-specific conversion factors. Beginning in FY 2012, all fillets
and parts of fish landed for home consumption will be multiplied by 3
and attributed to the appropriate sector ACE or common pool sub-ACL.
Any change to the conversion factor should be considered by Council
first.
Changes From the Proposed Rule
NMFS has made three changes from the proposed rule. After further
review, the coordinates for several AM areas are revised to correct
errors contained in the proposed rule. In addition, the regulations are
further revised to reflect the removal of the trimester TAC for the
common pool fishery for those stocks whose AMs were revised in this
action. NMFS is not implementing species-specific conversion factors in
place of the 3:1 counting rate for home consumption landings, as was
proposed in the proposed rule for this action.
Classification
Pursuant to section 304(b)(1)(A) of the Magnuson-Stevens Act, the
NMFS Assistant Administrator determined that Framework 47 is necessary
for the conservation and management of the NE multispecies fishery and
that it is consistent with the Magnuson-Stevens Act, and other
applicable law.
Under 5 U.S.C. 553(d)(1), the Assistant Administrator for Fisheries
finds good cause to waive the 30-day delayed effectiveness of this
action. The effective date of this action affects a parallel rulemaking
approving sector operations plans for the start of FY 2012 on May 1,
2012. In addition, the effective date of this action affects the
scallop fishery AM for FY 2011. Therefore, these actions must be in
effect at the beginning of FY 2012 to fully capture the environmental
and economic benefits of Framework 47 measures as well as the FY 2012
sector operations plans. Due to unforeseen circumstances related to FY
2012 catch levels for GOM cod, the Council's submission of Framework 47
to NMFS was delayed until February 2012. Due to this constraint, this
rulemaking could not be completed further in advance of May 1, 2012.
Therefore, in order to have this action effective at the beginning of
FY 2012, it is necessary to waive the 30-day delayed effectiveness of
this rule.
The waiver of the 30-day delayed effectiveness for this final rule
is in the public interest because it is necessary to implement a number
of measures by the start of FY 2012 that would benefit the NE
multispecies fishery and the Atlantic sea scallop fishery. This action
sets catch levels for FY 2012-2014 for most groundfish stocks, adopts
U.S./Canada TACs for FY 2012, removes restricted gear areas for common
pool vessels, and alleviates the scallop fishery AM trigger to allow
the scallop fishery to catch more yellowtail flounder. This rule also
includes measures controlling fishing effort by common pool vessels to
help prevent the premature or overharvest of the common pool trimester
TACs and sub-ACLs during FY 2012. Waiving the 30-day delayed
effectiveness of this final rule will ensure that the appropriate catch
levels are implemented at the start of FY 2012. Waiver of delayed
effectiveness will also ensure that common pool vessels will benefit
from the removal of restricted gear areas as soon as possible. This
measure will also modify when the scallop fishery AM is triggered to
allow the scallop fishery to catch more yellowtail flounder before an
AM is triggered. This measure is being applied retroactively to FY
2011, and a waiver of the delayed effectiveness will prevent a
premature trigger of the scallop fishery AM.
Failure to waive the 30-day delayed effectiveness would result in
the default FY 2012 ABCs, which could be lower or higher than those
adopted in this final rule. This could prevent vessels from maximizing
the benefit from increased catch limits or result in catch limits that
are too high based on the best scientific information available.
Failure to waive the 30-day delayed effectiveness of this action could
also result in no TACs being specified for U.S./Canada stocks. Without
an allocation for Eastern GB
[[Page 26120]]
cod or haddock, sector vessels would be unable to fish in the Eastern
U.S./Canada Area. Failure to waive delayed effectiveness will delay the
removal of the GB or SNE/MA Multispecies Restricted Gear Areas, which
would unnecessarily burden common pool vessels and reduce their
economic efficiency. Failure to delay could also result in prematurely
triggering the scallop fishery AM pending final FY 2011 catch
information. Thus, delaying implementation of this final rule would
result in short-term adverse economic impacts to groundfish and scallop
vessels and associated fishing communities. In addition, delaying
implementation of this final rule could increase the risk of excessive
catch by common pool vessels, and exceeding a trimester TAC or sub-ACL,
if the FY 2012 trip limits included in this rule are not in place at
the start of FY 2012. Therefore, a 30-day delay in the effectiveness of
this rule is impracticable and contrary to the public interest.
This final rule has been determined to be not significant for
purposes of Executive Order 12866.
This final rule does not contain policies with federalism or
``takings'' implications, as those terms are defined in E.O. 13132 and
E.O. 12630, respectively.
An FRFA was prepared for this action, as required by section 604 of
the Regulatory Flexibility Act (RFA). The FRFA, which includes the
summary in this rule and the analyses contained in Framework 47 and its
accompanying EA/RIR/FRFA, describes the economic impact the measures
adopted in Framework 47 would have on small entities. A description of
this action and its objectives and the legal basis for this action are
contained in Framework 47 and in the preamble to the proposed rule as
well as this final rule; it is not repeated here. All of the documents
that constitute the FRFA are available from NMFS (see ADDRESSES). This
FRFA analyzes expected impacts of the measures in Framework 47,
including setting GOM cod specifications based on the new GOM cod
assessment. As explained in the preamble, however, the Council did not
adopt ABCs for GOM cod in Framework 47. Therefore, the following
summary also includes expected impacts of this action in the absence of
GOM cod specifications.
No issues were raised by public comments in response to the IRFA or
with respect to the economic impacts of this action. As a result, no
changes were made from the proposed rule.
Description and Estimate of the Number of Small Entities to Which the
Final Rule Will Apply
FY 2010, which is the last full fishing year for which data are
available, was used as the baseline period in this analysis to estimate
the impacts of this action on regulated small entities. The measures
implemented by this action would primarily affect commercial groundfish
vessels (in a sector or in the common pool) and commercial Atlantic sea
scallop vessels. The primary economic impact of the action is
associated with the specification of ACLs and sub-ACLs. The Small
Business Administration considers a commercial fishing operation a
small entity if it has annual sales of less than $4 million (see North
American Industry Classification System code 114111). Multiple vessels
may be owned by a single owner, and contrary to the IRFA prepared for
Framework 47, data tracking ownership recently became available to
determine affiliated entities. However, this FRFA does not analyze the
expected impacts of this action using ownership groups (i.e., ownership
of multiple vessels by one owner). Therefore, for the purposes of
analysis, each permitted vessel is treated as a single entity, except
for vessels participating in the sector program, as described below.
In the IRFA prepared for Framework 47, as explained in Section
8.11.2 of Framework 47, sectors were used as the regulated entity for
the first time to estimate impacts of this action. Sectors were used as
the entity for analysis, in part, because each vessel's Potential
Sector Contribution only becomes fishable quota if the vessel is a
member of a sector. Since sectors are allocated Annual Catch
Entitlement (ACE), based on the cumulative Potential Sector
Contribution of each individual sector member, sectors as an affiliated
entity provides a useful approach for analyzing the impacts of
Framework 47. This approach differs from the approach used to prepare
the IRFA for the proposed rule to implement the 2012 sector operations
plans and allocate ACE to sectors, as well as other previous groundfish
actions. In the past, individual vessels, not sectors, were used as the
regulated entity to estimate impacts of measures on vessels
participating in the sector program. NMFS determined that deeming a
sector as the regulated entity, for the purposes of analysis under the
RFA, is a useful alternative to analyzing individual vessels for
Framework 47. NMFS believes this analysis should also be completed
using the individual vessels as the regulated entity to provide
continuity with the RFA analyses of previous actions. Therefore, a
supplemental analysis was prepared using individual vessels as the
regulated entity to analyze the impacts of Framework 47. This
supplemental analysis, which is described below, along with the
Framework 47 analysis, gives the public the best description of impacts
of Framework 47.
The entities affected by this action would include 7 large and 10
small regulated entities participating in the sector program, and 342
small regulated entities in the common pool. If individual vessels are
considered regulated entities for the sector program, this action would
affect 740 small regulated entities enrolled in the sector program.
If sectors are considered regulated entities for the purposes of
estimating this rule's impacts, this rule would affect 7 large and 10
small regulated entities participating in the sector program in FY
2010. Mean gross sales of fish for the 7 large entities was $13.7
million, and approximately $2 million for the 10 small entities. Under
this action, 3 large entities would fall below the threshold of $4
million in sales, which would result in 4 large and 13 small regulated
entities. NMFS estimates this action will result in mean gross sales
for the large regulated entities of $9.5 million, which is a 30-percent
reduction from the baseline period. Mean gross sales for the small
regulated entities is estimated at $0.7 million, which is a 62-percent
reduction from the baseline period.
There were 343 commercial groundfish vessels in the common pool
that had at least $1 in gross sales from fish during FY 2010. All of
these were small regulated entities with mean gross sales of $156,000.
Of this amount, NMFS estimates that gross sales from groundfish would
be approximately $2,600 per vessel, or less than 2 percent of the mean
gross sales. Although this action may trigger common pool AMs, which
would limit opportunities to fish for groundfish, the impact on small
regulated entities would likely be insignificant.
If individual vessels are considered the regulated entities for the
purposes of this FRFA, this action would affect substantially more
small entities. During FY 2010, for example, 740 vessels enrolled in
the sector program, and 607 remained in the common pool. During the
baseline period, 446 sector vessels and 343 common pool vessels
generated gross sales from any species. Of those vessels, 305 sector
vessels and 145 common pool vessels generated gross
[[Page 26121]]
sales from groundfish species. No individual vessel generated gross
sales in excess of $4 million. Therefore, using individual vessels as
the regulated entity, all regulated entities are considered small, and
there are no disproportional impacts between small and large entities.
Mean gross sales of fish for vessels enrolled in the sector program
were $299.9K, and $138.1K for common pool vessels. This action is
expected to reduce mean gross sales of fish by 33 percent for sector
vessels to $200.1K. Mean gross sales for common pool vessels are
expected to decline to $132.6K, which is less than a 5-percent decline.
Potentially affected entities in the scallop fishery would include
347 limited access scallop vessels and 730 general category scallop
vessels. All individual vessels in the sea scallop fishery are
considered small business entities under the Small Business
Administration criteria. Mean gross sales for limited access scallop
vessels are approximately $1 million, and are approximately $80,000 for
general category scallop vessels. The statistical areas with the
highest catch rates of GB yellowtail flounder are 562 and 525. If this
action caused one or both of these areas to close beginning on March 1,
2013, fishing effort by scallop vessels would be displaced to other
locations, primarily the Mid-Atlantic region. Since more than 75
percent of revenues from the Atlantic sea scallop fishery come from
statistical areas south of Georges Bank, the impact of closing
statistical areas 562 or 525 is difficult to anticipate. In addition,
during FY 2010, less than 1 percent of total revenues in the scallop
fishery came from the statistical areas potentially affected by this
action. There were no access area trips taken in the scallop fishery
during this time. Opening portions of statistical area 562 to access
area trips could increase the probability of triggering an AM for the
scallop fishery, and could increase the potential for adverse
regulatory impacts to lost access area trips or displaced fishing
effort. However, the effect on profitability is likely to be minimal,
and because all participating vessels are deemed to be small regulated
entities, there are no disproportional impacts.
The primary impact of this action is associated with setting ACLs,
which includes specification of sub-ACLs of GB and GOM haddock to the
Atlantic herring fishery. Because this action decreases the ABCs for GB
and GOM haddock, Atlantic herring vessels are potentially affected by
this action. In calendar year 2010, 90 vessels were issued a limited
access herring permit and two vessels exceeded $4 million in sales.
Approximately 17 percent of the haddock ABCs were landed in FY 2010,
and similar utilization of the available quota is expected under this
action. Therefore, vessels participating in the Atlantic herring
fishery are not expected to be affected by this action.
Of the affected entities under this action, only groundfish sectors
and vessels are anticipated to be adversely affected. Due to
conservation needs, this action would reduce short-term profits for
regulated small entities relative to the baseline period. Regulated
small sector entities are estimated to be more adversely impacted by
this action than large sector entities. Gross sales for small sector
entities would be reduced by 63 percent, and gross sales for large
entities would be reduced by 30 percent. These are short-term impacts.
In addition, reductions in fishing opportunities for some stocks are
necessary to ensure rebuilding. The ability to lease quota between
sectors and consolidate quota within sectors will help mitigate the
adverse effect on profitability. In addition, exemptions included in
the 2012 sector rule are expected to mitigate adverse economic impacts.
However, using sectors as the regulated entities, this action is likely
to have a significant impact on regulated small sector entities under
the disproportionality criteria. This analysis was based in part on
anticipated decreases in the GOM cod catch limits for FYs 2012-2014
that were initially proposed as part of this action. However, Framework
47 no longer sets the GOM cod catch limits for FY 2012-2014, as
explained in the preamble, and, therefore, the expected impacts of this
action on regulated small entities are likely to be less.
Description of Steps the Agency Has Taken To Minimize the Economic
Impact on Small Entities Consistent With the Stated Objectives of
Applicable Statues
During the development of Framework 47, NMFS and the Council
considered ways to reduce the regulatory burden on, and provide
flexibility for, the regulated entities in this action. Proposed
actions and alternatives are described in detail in Framework 47, which
includes an EA, RIR, and IRFA (available at ADDRESSES). The measures
implemented by this final rule minimize the long-term economic impacts
on small entities to the extent practicable. Reasonable alternatives
are limited because of the legal requirements to implement effective
conservation measures which necessarily may result in negative impacts
that cannot be effectively mitigated. Moreover, the limited number of
alternatives available for this action must be evaluated in the context
of an ever-changing fishery management plan that has considered
numerous alternatives over the years.
Overall, this rule minimizes adverse long-term impacts by ensuring
that management measures and catch limits result in sustainable fishing
mortality rates promote stock rebuilding, and as a result, maximize
yield. The measures implemented by this final rule also provide
additional flexibility for fishing operations in the short-term. This
final rule implements several measures that enable small entities to
offset some portion of the estimated economic impacts. These measures
include: extending the rebuilding period for GB yellowtail flounder;
removing the Western GB and SNE Multispecies RGAs for common pool
vessels; re-estimation of the GB yellowtail flounder sub-ACL for the
scallop fishery; eliminating the cap on yellowtail flounder catch in
the Nantucket, Closed Area I, and Closed Area II Sea Scallop Access
Areas; and revising the scallop fishery AM trigger.
Revisions to the status determination criteria for the three winter
flounder stocks and GOM cod primarily affect setting the OFLs, ABCs,
and ACLs for these stocks based on these criteria. Over the long-term,
the revised status determination criteria limit the potential harvest
from the fishery. The MSY values are higher for GB and SNE/MA winter
flounder than the previous MSY values which would result in greater
potential revenues over the long-term. This action also extends the
rebuilding period for GB yellowtail flounder, which allows for greater
yellowtail flounder catches and result in larger revenues for
groundfish and scallop vessels than if the rebuilding program was not
extended beyond 2016. Adopting the U.S./Canada TACs for FY 2012 would
have short-term positive economic impacts if no U.S. TACs were
specified. Reduced revenue due to decreases in Eastern GB cod and GB
yellowtail flounder TACs could be mitigated if vessels are able to
maximize Eastern GB haddock catch.
Removing the Western GB Multispecies and SNE Multispecies RGAs for
common pool vessels could increase revenues for common pool vessels
compared to revenues if this action was not implemented. Removing these
RGAs will likely increase common pool landings of some stocks, increase
efficiency for common pool vessels, and may reduce costs for common
pool vessels because vessel operators would
[[Page 26122]]
not be required to purchase selective gear to fish in these areas. The
economic impacts of the AMs adopted in this action could be mitigated
by using selective gear or fishing in other areas, and will be
addressed in a future rulemaking implementing the AMs, if necessary.
Given the relatively small size of the AM areas, additional trip costs
for fishing in other areas are likely negligible.
Eliminating the 10-percent yellowtail flounder access area caps for
the scallop fishery will reduce the incentive for derby fishing, and
will likely positively impact on the scallop fishery. In addition,
revising the implementation of the scallop fishery AM is expected to
mitigate economic impacts that may occur if the scallop fishery exceeds
its yellowtail flounder allocation. This measure will prevent the loss
of scallop landings, revenues, and increased fishing costs compared to
impacts of this measure not being implemented. This measure will also
prevent effort shifts to less optimal areas by scallop vessels, as well
as effort shifts into seasons with lower meat weights for scallops.
Inseason re-estimation of the scallop fishery GB yellowtail flounder
sub-ACL will have positive economic benefits for the groundfish
fishery. These benefits would only occur in years when the scallop
fishery is not projected to catch its initial sub-ACL, and the
groundfish sub-ACL is increased mid-fishing year. When additional quota
is made available to the groundfish fishery, revenues for the
groundfish fishery will increase if groundfish vessels are able to
catch additional GB yellowtail flounder.
Modifying the definition of the Ruhle trawl will provide more
flexibility for the groundfish fishery in the use of trawl gear that
minimizes catch of stocks of concern. This measure will provide small
vessels with increased fishing opportunities. The additional exempted
gear option will provide vessels a choice of the most cost-effective
means of targeting healthy stocks.
Description of the Projected Reporting, Recordkeeping, and Other
Compliance Requirements
This action contains no new collection-of-information, reporting,
or recordkeeping requirements. This action does not duplicate, overlap,
or conflict with any other Federal law.
List of Subjects in 50 CFR Part 648
Fisheries, Fishing, Recordkeeping and reporting requirements.
Dated: April 26, 2012.
Alan D. Risenhoover,
Acting Deputy Assistant Administrator For Regulatory Programs, National
Marine Fisheries Service.
For the reasons stated in the preamble, 50 CFR part 648 is amended
as follows:
PART 648--FISHERIES OF THE NORTHEASTERN UNITED STATES
0
1. The authority citation for part 648 continues to read as follows:
Authority: 16 U.S.C. 1801 et seq.
0
2. In Sec. 648.14,
0
a. Remove and reserve paragraphs (i)(2)(vi)(B), (i)(2)(vi)(C), and
(i)(3)(v)(C);
0
b. Remove paragraph (k)(7)(i)(C)(4);
0
c. Revise paragraph (k)(13)(ii)(B); and
0
d. Add paragraph (k)(20).
The revision and addition read as follows:
Sec. 648.14 Prohibitions.
* * * * *
(k) * * *
(13) * * *
(ii) * * *
(B) Possess or land per trip more than the possession or landing
limits specified in Sec. 648.86(a), (b), (c), (e), (g), (h), (j), (l),
(m), (n), and (o); Sec. 648.82(b)(5) and (6); Sec. 648.85; or Sec.
648.88, if the vessel has been issued a limited access NE multispecies
permit or open access NE multispecies permit, as applicable.
* * * * *
(20) AMs for both stocks of windowpane flounder and ocean pout. It
is unlawful for any person, including any owner or operator of a vessel
issued a valid Federal NE multispecies permit or letter under Sec.
648.4(a)(1)(i), unless otherwise specified in Sec. 648.17, to fail to
comply with the restrictions on fishing and gear specified in Sec.
648.90(a)(5)(i)(D).
* * * * *
0
5. In Sec. 648.60, paragraphs (a)(5)(ii)(C)(1) and (3) are removed and
reserved, and paragraph (g)(1) is revised to read as follows:
Sec. 648.60 Sea scallop area access program requirements.
* * * * *
(g) * * *
(1) An LAGC scallop vessel may only fish in the scallop access
areas specified in Sec. 648.59(a) through (e), subject to the seasonal
restrictions specified in Sec. 648.59(b)(4), (c)(4), and (d)(4), and
subject to the possession limit specified in Sec. 648.52(a), and
provided the vessel complies with the requirements specified in
paragraphs (a)(1), (a)(2), (a)(6) through (9), (d), (e), (f), and (g)
of this section. A vessel issued both a NE multispecies permit and an
LAGC scallop permit may fish in an approved SAP under Sec. 648.85 and
under multispecies DAS in the Closed Area I, Closed Area II, and
Nantucket Lightship Sea Scallop Access Areas specified in Sec.
648.59(b) through (d), provided the vessel complies with the
requirements specified in Sec. 648.59(b)(5)(ii), (c)(5)(ii), and
(d)(5)(ii), and this paragraph (g), but may not fish for, possess, or
land scallops on such trips.
* * * * *
0
6. In Sec. 648.64, paragraph (a) introductory text and paragraphs
(b)(1) and (c)(1) are revised to read as follows:
Sec. 648.64 Yellowtail flounder sub-ACLs and AMs for the scallop
fishery.
(a) As specified in Sec. 648.55(d), and pursuant to the biennial
framework adjustment process specified in Sec. 648.90, the scallop
fishery shall be allocated a sub-ACL for the Georges Bank and Southern
New England/Mid-Atlantic stocks of yellowtail flounder. Unless
otherwise specified in Sec. 648.90(a)(4)(iii)(C) of the NE
multispecies regulations, the sub-ACLs for the 2011 through 2013
fishing years are as follows:
* * * * *
(b) * * *
(1) Unless otherwise specified in Sec. 648.90(a)(5)(iv) of the NE
multispecies regulations, if the Georges Bank yellowtail flounder sub-
ACL for the scallop fishery is exceeded, the area defined by the
following coordinates shall be closed to scallop fishing by vessels
issued a limited access scallop permit for the period of time specified
in paragraph (b)(2) of this section:
Georges Bank Yellowtail Closure
------------------------------------------------------------------------
Point N. lat. W. long.
------------------------------------------------------------------------
GBYT AM 1...................... 41[deg]50' 66[deg]51.94'
GBYT AM 2...................... 40[deg]30.75' 65[deg]44.96'
GBYT AM 3...................... 40[deg]30' 66[deg]40'
GBYT AM 4...................... 40[deg]40' 66[deg]40'
GBYT AM 5...................... 40[deg]40' 66[deg]50'
GBYT AM 6...................... 40[deg]50' 66[deg]50'
GBYT AM 7...................... 40[deg]50' 67[deg]00'
GBYT AM 8...................... 41[deg]00' 67[deg]00'
GBYT AM 9...................... 41[deg]00' 67[deg]20'
GBYT AM 10..................... 41[deg]10' 67[deg]20'
GBYT AM 11..................... 41[deg]10' 67[deg]40'
GBYT AM 12..................... 41[deg]50' 67[deg]40'
GBYT AM 1...................... 41[deg]50' 66[deg]51.94'
------------------------------------------------------------------------
* * * * *
(c) * * *
(1) Unless otherwise specified in Sec. 648.90(a)(5)(iv) of the NE
multispecies regulations, if the Southern New England/Mid-Atlantic
yellowtail flounder sub-ACL for the scallop fishery
[[Page 26123]]
is exceeded, the area defined by the following coordinates shall be
closed to scallop fishing by vessels issued a limited access scallop
permit for the period of time specified in paragraph (c)(2) of this
section:
Southern New England Yellowtail Closure
------------------------------------------------------------------------
Point N. lat. W. long.
------------------------------------------------------------------------
SNEYT AM 1..................... 41[deg]28.4' 71[deg]10.25'
SNEYT AM 2..................... 41[deg]28.57' 71[deg]10'
SNEYT AM 3..................... 41[deg]20' 71[deg]10'
SNEYT AM 4..................... 41[deg]20' 70[deg]50'
SNEYT AM 5..................... 41[deg]20' 70[deg]30'
SNEYT AM 6..................... 41[deg]18' 70[deg]15'
SNEYT AM 7..................... 41[deg]17.69' 70[deg]12.54'
SNEYT AM 8..................... 41[deg]14.73' 70[deg]00'
SNEYT AM 9..................... 39[deg]50' 70[deg]00'
SNEYT AM 10.................... 39[deg]50' 71[deg]00'
SNEYT AM 11.................... 39[deg]50' 71[deg]40'
SNEYT AM 12.................... 40[deg]00' 71[deg]40'
SNEYT AM 13.................... 40[deg]00' 73[deg]00'
SNEYT AM 14.................... 40[deg]41.23' 73[deg]00'
SNEYT AM 15.................... 41[deg]00' 71[deg]55'
SNEYT AM 16.................... 41[deg]00' 71[deg]40'
SNEYT AM 17.................... 41[deg]20' 71[deg]40'
SNEYT AM 18.................... 41[deg]21.15' 71[deg]40'
------------------------------------------------------------------------
* * * * *
0
7. In Sec. 648.81:
0
a. Revise paragraphs (c)(2)(ii)(B), (f)(2)(iii)(B), and (n); and
0
b. Remove paragraph (o).
The revsions read as follows:
Sec. 648.81 NE multispecies closed areas and measures to protect EFH.
* * * * *
(c) * * *
(2) * * *
(ii) * * *
(B) Fish species managed by the NEFMC or MAFMC that are harvested
or possessed by the vessel, are not sold or intended for trade, barter
or sale, regardless of where the fish are caught; and
* * * * *
(f) * * *
(2) * * *
(iii) * * *
(B) Fish species managed by the NEFMC or MAFMC that are harvested
or possessed by the vessel, are not sold or intended for trade, barter
or sale, regardless of where the fish are caught; and
* * * * *
(n) GOM Cod Spawning Protection Area. (1) Except as specified in
paragraph (n)(2) of this section, from April through June of each year,
no fishing vessel or person on a fishing vessel may enter, fish in, or
be in; and no fishing gear capable of catching NE multispecies may be
used on, or be on board, a vessel in the GOM Cod Spawning Protection
Area, as defined by straight lines connecting the following points in
the order stated (a chart depicting this area is available from the RA
upon request):
GOM Cod Spawning Protection Area
------------------------------------------------------------------------
Point N. latitude W. longitude
------------------------------------------------------------------------
CSPA1.......................... 42[deg]50.95' 70[deg]32.22'
CSPA2.......................... 42[deg]47.65' 70[deg]35.64'
CSPA3.......................... 42[deg]54.91' 70[deg]41.88'
CSPA4.......................... 42[deg]58.27' 70[deg]38.64'
CSPA1.......................... 42[deg]50.95' 70[deg]32.22'
------------------------------------------------------------------------
(2) Paragraph (n)(1) of this section does not apply to persons on
a fishing vessel or fishing vessels:
(i) That have not been issued a NE multispecies permit and that are
fishing exclusively in state waters;
(ii) That are fishing with or using exempted gear as defined under
this part, excluding pelagic gillnet gear capable of catching NE
multispecies, except for vessels fishing with a single pelagic gillnet
not longer than 300 ft (91.4 m) and not greater than 6 ft (1.83 m)
deep, with a maximum mesh size of 3 inches (7.6 cm), provided:
(A) The net is attached to the vessel and fished in the upper two-
thirds of the water column;
(B) The net is marked with the vessel owner's name and vessel
identification number;
(C) There is no retention of regulated species or ocean pout; and
(D) There is no other gear on board capable of catching NE
multispecies;
(iii) That are fishing as a charter/party or recreational fishing
vessel, provided that:
(A) With the exception of tuna, fish harvested or possessed by the
vessel are not sold or intended for trade, barter, or sale, regardless
where the species are caught;
(B) The vessel has no gear other than pelagic hook and line gear,
as defined in this part, on board unless that gear is properly stowed
pursuant to Sec. 648.23(b); and
(C) There is no retention of regulated species, or ocean pout; and
(iv) That are transiting pursuant to paragraph (i) of this section.
0
8. In Sec. 648.82:
0
a. Revise paragraphs (n)(2)(i)(A), (n)(2)(ii) introductory text, and
(n)(2)(ii)(L) through (N); and
0
b. Remove paragraphs (n)(2)(ii)(O) and (n)(2)(ii)(P).
The revisions read as follows:
Sec. 648.82 Effort-control program for NE multispecies limited access
vessels.
* * * * *
(n) * * *
(2) * * *
(i) Trimester TACs. (A) Trimester TAC distribution. Any sub-ACLs
specified for common pool vessels pursuant to Sec. 648.90(a)(4) shall
be apportioned into trimesters of 4 months in duration, beginning at
the start of the fishing year (i.e., Trimester 1: May 1-August 31;
Trimester 2: September 1-December 31; Trimester 3: January 1-April 30),
as follows):
Portion of Common Pool Sub-ACLs Apportioned to Each Stock for Each
Trimester
------------------------------------------------------------------------
Trimester 1 Trimester 2 Trimester 3
Stock (percent) (percent) (percent)
------------------------------------------------------------------------
GOM cod.......................... 27 36 37
GB cod........................... 25 37 38
GOM haddock...................... 27 26 47
GB haddock....................... 27 33 40
CC/GOM yellowtail flounder....... 35 35 30
GB yellowtail flounder........... 19 30 52
SNE/MA yellowtail flounder....... 21 37 42
GOM winter flounder.............. 37 38 25
GB winter flounder............... 8 24 69
Witch flounder................... 27 31 42
American plaice.................. 24 36 40
Pollock.......................... 28 35 37
Redfish.......................... 25 31 44
[[Page 26124]]
White hake....................... 38 31 31
------------------------------------------------------------------------
* * * * *
(ii) Stock area closures. If the Regional Administrator projects
that 90 percent of the trimester TACs specified in paragraph (n)(2)(i)
of this section will be caught based upon available information, the
Regional Administrator shall close the area where 90 percent of the
catch for each such stock occurred, according to available VTR data and
other information, to all common pool vessels using gear capable of
catching such stocks for the remainder of that trimester, as specified
in paragraphs (n)(2)(ii)(A) through (N) of this section, in a manner
consistent with the Administrative Procedure Act. For example, if the
Regional Administrator projects that 90 percent of the CC/GOM
yellowtail flounder Trimester 1 TAC will be caught, common pool vessels
using trawl and gillnet gear shall be prohibited from fishing in the
CC/GOM Yellowtail Flounder Closure Area specified in paragraph
(n)(2)(ii)(G) of this section until the beginning of Trimester 2 on
September 1 of that fishing year. Based upon all available information,
the Regional Administrator is authorized to expand or narrow the areas
closed under this paragraph (n)(2)(ii) in a manner consistent with the
Administrative Procedure Act. If it is not possible to identify an area
where only 90 percent of the catch occurred, the Regional Administrator
shall close the smallest area possible where greater than 90 percent of
the catch occurred.
* * * * *
(L) Redfish Trimester TAC Area. For the purposes of the trimester
TAC AM closure specified in paragraph (n)(2)(ii) of this section, the
Redfish Trimester TAC Area shall apply to common pool vessels using
trawl gear within the area bounded by straight lines connecting the
following points in the order stated:
Redfish Trimester TAC Area
------------------------------------------------------------------------
Point N. latitude W. longitude
------------------------------------------------------------------------
RF1............................ (\1\) 69[deg]20'
RF2............................ 43[deg]40' 69[deg]20'
RF3............................ 43[deg]40' 69[deg]00'
RF4............................ 43[deg]20' 69[deg]00'
RF5............................ 43[deg]20' 67[deg]40'
RF6............................ (\2\) 67[deg]40'
RF7............................ 42[deg]53.1' 67[deg]44.4'
RF8............................ (\2\) 67[deg]40'
RF9............................ 41[deg]20' 67[deg]40'
RF10........................... 41[deg]20' 68[deg]10'
RF11........................... 41[deg]10' 68[deg]10'
RF12........................... 41[deg]10' 68[deg]20'
RF13........................... 41[deg]00' 68[deg]20'
RF14........................... 41[deg]00' 69[deg]30'
RF15........................... 41[deg]10' 69[deg]30'
RF16........................... 41[deg]10' 69[deg]50'
RF17........................... 41[deg]20' 69[deg]50'
RF18........................... 41[deg]20' (\3\)
RF19........................... (\4\) 70[deg]00'
RF20........................... (\5\) 70[deg]00'
------------------------------------------------------------------------
\1\ Intersection with ME shoreline.
\2\ U.S./Canada maritime boundary.
\3\ East-facing shoreline of Nantucket, MA.
\4\ North-facing shoreline of Nantucket, MA.
\5\ South-facing shoreline of Cape Cod, MA.
(M) White Hake Trimester TAC Area. For the purposes of the
trimester TAC AM closure specified in paragraph (n)(2)(ii) of this
section, the White Hake Trimester TAC Area shall apply to common pool
vessels using trawl gear, sink gillnet gear, and longline/hook gear
within the area bounded by straight lines connecting the following
points in the order stated:
White Hake Trimester TAC Area
------------------------------------------------------------------------
Point N. latitude W. longitude
------------------------------------------------------------------------
RF1............................ (\1\) 69[deg]20'
RF2............................ 43[deg]40' 69[deg]20'
RF3............................ 43[deg]40' 69[deg]00'
RF4............................ 43[deg]20' 69[deg]00'
RF5............................ 43[deg]20' 67[deg]40'
RF6............................ (\2\) 67[deg]40'
RF7............................ 42[deg]53.1' 67[deg]44.4'
RF8............................ (\2\) 67[deg]40'
RF9............................ 41[deg]20' 67[deg]40'
RF10........................... 41[deg]20' 68[deg]10'
RF11........................... 41[deg]10' 68[deg]10'
RF12........................... 41[deg]10' 68[deg]20'
RF13........................... 41[deg]00' 68[deg]20'
RF14........................... 41[deg]00' 69[deg]30'
RF15........................... 41[deg]10' 69[deg]30'
RF16........................... 41[deg]10' 69[deg]50'
RF17........................... 41[deg]20' 69[deg]50'
RF18........................... 41[deg]20' (\3\)
RF19........................... (\4\) 70[deg]00'
RF20........................... (\5\) 70[deg]00'
------------------------------------------------------------------------
\1\ Intersection with ME shoreline.
\2\ U.S./Canada maritime boundary.
\3\ East-facing shoreline of Nantucket, MA.
\4\ North-facing shoreline of Nantucket, MA.
\5\ South-facing shoreline of Cape Cod, MA.
(N) Pollock Trimester TAC Area. For the purposes of the trimester
TAC AM closure specified in paragraph (n)(2)(ii) of this section, the
Pollock Trimester TAC Area shall apply to common pool vessels using
trawl gear, sink gillnet gear, and longline/hook gear within the area
bounded by straight lines connecting the following points in the order
stated:
Pollock Trimester TAC Area
------------------------------------------------------------------------
Point N. latitude W. longitude
------------------------------------------------------------------------
RF1............................ (\1\) 69[deg]20'
RF2............................ 43[deg]40' 69[deg]20'
RF3............................ 43[deg]40' 69[deg]00'
RF4............................ 43[deg]20' 69[deg]00'
RF5............................ 43[deg]20' 67[deg]40'
RF6............................ (\2\) 67[deg]40'
RF7............................ 42[deg]53.1' 67[deg]44.4'
RF8............................ (\2\) 67[deg]40'
RF9............................ 41[deg]20' 67[deg]40'
RF10........................... 41[deg]20' 68[deg]10'
RF11........................... 41[deg]10' 68[deg]10'
RF12........................... 41[deg]10' 68[deg]20'
RF13........................... 41[deg]00' 68[deg]20'
RF14........................... 41[deg]00' 69[deg]30'
RF15........................... 41[deg]10' 69[deg]30'
RF16........................... 41[deg]10' 69[deg]50'
RF17........................... 41[deg]20' 69[deg]50'
RF18........................... 41[deg]20' (\3\)
RF19........................... (\4\) 70[deg]00'
RF20........................... (\5\) 70[deg]00'
------------------------------------------------------------------------
\1\ Intersection with ME shoreline.
\2\ U.S./Canada maritime boundary.
\3\ East-facing shoreline of Nantucket, MA.
\4\ North-facing shoreline of Nantucket, MA.
\5\ South-facing shoreline of Cape Cod, MA.
* * * * *
0
9. In Sec. 648.85:
0
a. Revise paragraphs (b)(5) and (b)(6)(iv)(J)(3)(i) through (v); and
0
b. Remove paragraphs (b)(6)(iv)(J)(3)(vi) and (c)(1) through (3).
The revisions read as follows:
Sec. 648.85 Special management programs.
* * * * *
(b) * * *
(5) Incidental Catch TACs. Unless otherwise specified in this
paragraph (b)(5), Incidental Catch TACs shall be based upon the portion
of the ACL for a stock specified for the common pool vessels pursuant
to Sec. 648.90(a)(4), and allocated as described in this paragraph
(b)(5), for each of the following stocks: GOM cod, GB cod, GB
yellowtail flounder, GB winter flounder, CC/GOM yellowtail flounder,
American plaice, white hake, SNE/MA yellowtail flounder, SNE/MA winter
flounder, and witch flounder. Because GB yellowtail flounder and GB cod
are transboundary stocks, the incidental catch TACs for
[[Page 26125]]
these stocks shall be based upon the common pool portion of the ACL
available to U.S. vessels. NMFS shall send letters to limited access NE
multispecies permit holders notifying them of such TACs.
(i) Stocks other than GB cod, GB yellowtail flounder, and GB winter
flounder. With the exception of GB cod, GB yellowtail flounder, and GB
winter flounder, 100 percent of the Incidental Catch TACs specified in
this paragraph (b)(5) shall be allocated to the Regular B DAS Program
described in paragraph (b)(6) of this section.
(ii) GB cod. The Incidental Catch TAC for GB cod specified in this
paragraph (b)(5) shall be subdivided as follows: 50 percent to the
Regular B DAS Program described in paragraph (b)(6) of this section; 16
percent to the CA I Hook Gear Haddock SAP described in paragraph (b)(7)
of this section; and 34 percent to the Eastern U.S./Canada Haddock SAP
described in paragraph (b)(8) of this section.
(6) * * *
(iv) * * *
(J) * * *
(3) * * *
(i) The net must be constructed with four seams (i.e., a net with a
top and bottom panel and two side panels), and include at least the
following net sections as depicted in Figure 1 of this part (this
figure is also available from the Administrator, Northeast Region): Top
jib, bottom jib, jib side panels (x 2), top wing, bottom wing, wing
side panels (x 2), bunt, square, square side panels (x 2), first top
belly, first bottom belly, first belly side panels (x 2), and second
bottom belly.
(ii) The top and bottom jibs, jib side panels, top and bottom
wings, and wing side panels, bunt, and first bottom belly (the first
bottom belly and all portions of the net in front of the first bottom
belly, with the exception of the square and the square side panels)
must be at least two meshes long in the fore and aft direction. For
these net sections, the stretched length of any single mesh must be at
least 7.9 ft (240 cm), measured in a straight line from knot to knot.
(iii) Mesh size in all other sections must be consistent with mesh
size requirements specified under Sec. 648.80 and meet the following
minimum specifications: Each mesh in the square, square side panels,
and second bottom belly must be 31.5 inches (80 cm); each mesh in the
first top belly, and first belly side panels must be at least 7.9
inches (20 cm); and 6 inches (15.24 cm) or larger in sections following
the first top belly and second bottom belly sections, all the way to
the codend. The mesh size requirements of the top sections apply to the
side panel sections.
(iv) The trawl must have at least 15 meshes (240 cm each) at the
wide end of the first bottom belly, excluding the gore.
(v) The trawl must have a single or multiple kite panels with a
total surface area of at least 19.3 sq. ft. (1.8 sq. m) on the forward
end of the square to help maximize headrope height, for the purpose of
capturing rising fish. A kite panel is a flat structure, usually semi-
flexible, used to modify the shape of trawl and mesh openings by
providing lift when a trawl is moving through the water.
* * * * *
0
10. In Sec. 648.86, revise paragraph (c) to read as follows:
Sec. 648.86 NE Multispecies possession restrictions.
* * * * *
(c) Atlantic halibut. A vessel issued a NE multispecies permit
under Sec. 648.4(a)(1) may land or possess on board no more than one
Atlantic halibut per trip, provided the vessel complies with other
applicable provisions of this part, unless otherwise specified in Sec.
648.90(a)(5)(i)(D)(2).
* * * * *
0
11. In Sec. 648.87, revise paragraph (c)(2)(i) to read as follows:
Sec. 648.87 Sector allocation.
* * * * *
(c) * * *
(2) * * *
(i) Regulations that may not be exempted for sector participants.
The Regional Administrator may not exempt participants in a sector from
the following Federal fishing regulations: NE multispecies year-round
closure areas; permitting restrictions (e.g., vessel upgrades, etc.);
gear restrictions designed to minimize habitat impacts (e.g., roller
gear restrictions, etc.); reporting requirements; and AMs specified at
Sec. 648.90(a)(5)(i)(D). For the purposes of this paragraph (c)(2)(i),
the DAS reporting requirements specified at Sec. 648.82; the SAP-
specific reporting requirements specified at Sec. 648.85; and the
reporting requirements associated with a dockside monitoring program
specified in paragraph (b)(5)(i) of this section are not considered
reporting requirements, and the Regional Administrator may exempt
sector participants from these requirements as part of the approval of
yearly operations plans. This list may be modified through a framework
adjustment, as specified in Sec. 648.90.
* * * * *
0
12. In Sec. 648.89, revise paragraphs (e)(1) and (e)(3)(ii) to read as
follows:
Sec. 648.89 Recreational and charter/party vessel restrictions.
* * * * *
(e) Charter/party vessel restrictions on fishing in GOM closed
areas and the Nantucket Lightship Closed Area--(1) GOM Closed Areas.
Unless otherwise specified in this paragraph (e)(1), a vessel fishing
under charter/party regulations may not fish in the GOM closed areas
specified at Sec. 648.81(d)(1) through (f)(1) during the time periods
specified in those paragraphs, unless the vessel has on board a valid
letter of authorization issued by the Regional Administrator pursuant
to Sec. 648.81(f)(2)(iii) and paragraph (e)(3) of this section. The
conditions and restrictions of the letter of authorization must be
complied with for a minimum of 3 months if the vessel fishes or intends
to fish in the seasonal GOM closure areas; or for the rest of the
fishing year, beginning with the start of the participation period of
the letter of authorization, if the vessel fishes or intends to fish in
the year-round GOM closure areas. A vessel fishing under charter/party
regulations may not fish in the GOM Cod Spawning Protection Area
specified at Sec. 648.81(n)(1) during the time period specified in
that paragraph, unless the vessel complies with the requirements
specified at Sec. 648.81(n)(2)(iii).
* * * * *
(3) * * *
(ii) Fish species managed by the NEFMC or MAFMC that are harvested
or possessed by the vessel, are not sold or intended for trade, barter
or sale, regardless of where the fish are caught;
* * * * *
0
13. In Sec. 648.90, revise paragraph (a)(4)(iii)(C) and add paragraphs
(a)(5)(i)(D), (a)(5)(i)(E), and (a)(5)(iv) to read as follows:
Sec. 648.90 NE multispecies assessment, framework procedures and
specifications, and flexible area action system.
* * * * *
(a) * * *
(4) * * *
(iii) * * *
(C) Yellowtail flounder catch by the Atlantic sea scallop fishery.
Yellowtail flounder catch in the Atlantic sea scallop fishery, as
defined in subpart D, shall be deducted from the ABC/ACL for each
yellowtail flounder stock pursuant to the restrictions specified in
subpart D
[[Page 26126]]
of this part and the process to specify ABCs and ACLs, as described in
paragraph (a)(4) of this section. Unless otherwise specified in this
paragraph (a)(4)(iii)(C), or subpart D of this part, the specific value
of the sub-components of the ABC/ACL for each stock of yellowtail
flounder distributed to the Atlantic sea scallop fishery shall be
specified pursuant to the biennial adjustment process specified in
paragraph (a)(2) of this section. Based on information available, NMFS
shall re-estimate the expected scallop fishery catch of GB yellowtail
flounder for the current fishing year by January 15. If NMFS determines
that the scallop fishery will catch less than 90 percent of its GB
yellowtail flounder sub-ACL, the Regional Administrator may reduce the
scallop fishery sub-ACL to the amount projected to be caught, and
increase the groundfish fishery sub-ACL by any amount up to the amount
reduced from the scallop fishery sub-ACL. The revised groundfish
fishery sub-ACL shall be distributed to the common pool and sectors
based on the process specified in paragraph (a)(4)(E)(1) of this
section.
* * * * *
(5) * * *
(i) * * *
(D) AMs for both stocks of windowpane flounder, ocean pout, and
Atlantic halibut. At the end of each fishing year, NMFS shall determine
if the overall ACL for northern windowpane flounder, southern
windowpane flounder, ocean pout, or Atlantic halibut was exceeded. If
the overall ACL for any of these stocks is exceeded, NMFS shall
implement the appropriate AM, as specified in this paragraph
(a)(5)(i)(D), in the second fishing year after the fishing year in
which the overage occurred, consistent with the Administrative
Procedure Act. For example, if NMFS determined the overall ACL for
northern windowpane flounder was exceeded in fishing year 2012, the
applicable AM would be implemented for fishing year 2014.
(1) Windowpane flounder and ocean pout. If NMFS determines the
overall ACL for either stock of windowpane flounder or ocean pout is
exceeded, as described in this paragraph (a)(5)(i)(D)(1), by any amount
between the management uncertainty buffer and up to 20 percent, the
applicable small AM area for the stock shall be implemented, as
specified in paragraph (a)(5)(i)(D) of this section. If the overall ACL
is exceeded by 21 percent or more, the applicable large AM area(s) for
the stock shall be implemented, as specified in paragraph (a)(5)(i)(D)
of this section. The AM areas defined below are bounded by the
following coordinates, connected in the order listed by rhumb lines,
unless otherwise noted. Any vessel issued a limited access NE
multispecies permit and fishing with trawl gear in these areas may only
use a haddock separator trawl, as specified in Sec.
648.85(a)(3)(iii)(A); a Ruhle trawl, as specified in Sec.
648.85(b)(6)(iv)(J)(3); a rope separator trawl, as specified in Sec.
648.81(n)(3)(i)(A); or any other gear approved consistent with the
process defined in Sec. 648.85(b)(6). If a sub-ACL for either stock of
windowpane flounder or ocean pout is allocated to another fishery,
consistent with the process specified at Sec. 648.90(a)(4), and AMs
are developed for that fishery, the groundfish fishery AM shall only be
implemented if the sub-ACL allocated to the groundfish fishery is
exceeded (i.e., the sector and common pool catch for a particular
stock, including the common pool's share of any overage of the overall
ACL caused by excessive catch by other sub-components of the fishery
pursuant to Sec. 648.90(a)(5) exceeds the common pool sub-ACL) and the
overall ACL is also exceeded.
Northern Windowpane Flounder and Ocean Pout Small AM Area
------------------------------------------------------------------------
Point N. latitude W. longitude
------------------------------------------------------------------------
NWS1........................... 41[deg]10' 67[deg]40'
NWS2........................... 41[deg]10' 67[deg]20'
NWS3........................... 41[deg]00' 67[deg]20'
NWS4........................... 41[deg]00' 67[deg]00'
NWS5........................... 40[deg]50' 67[deg]00'
NWS6........................... 40[deg]50' 67[deg]40'
NWS1........................... 41[deg]10' 67[deg]40'
------------------------------------------------------------------------
Northern Windowpane Flounder and Ocean Pout Large AM Area
------------------------------------------------------------------------
Point N. latitude W. longitude
------------------------------------------------------------------------
NWL1........................... 42[deg]10' 67[deg]40'
NWL2........................... 42[deg]10' 67[deg]20'
NWL3........................... 41[deg]00' 67[deg]20'
NWL4........................... 41[deg]00' 67[deg]00'
NWL5........................... 40[deg]50' 67[deg]00'
NWL6........................... 40[deg]50' 67[deg]40'
NWL1........................... 42[deg]10' 67[deg]40'
------------------------------------------------------------------------
Southern Windowpane Flounder and Ocean Pout Small AM Area
------------------------------------------------------------------------
Point N. latitude W. longitude
------------------------------------------------------------------------
SWS1........................... 41[deg]10' 71[deg]30'
SWS2........................... 41[deg]10' 71[deg]20'
SWS3........................... 40[deg]50' 71[deg]20'
SWS4........................... 40[deg]50' 71[deg]30'
SWS1........................... 41[deg]10' 71[deg]30'
------------------------------------------------------------------------
Southern Windowpane Flounder and Ocean Pout Large AM Area 1
------------------------------------------------------------------------
Point N. latitude W. longitude
------------------------------------------------------------------------
SWL1........................... 41[deg]10' 71[deg]50'
SWL2........................... 41[deg]10' 71[deg]10'
SWL3........................... 41[deg]00' 71[deg]10'
SWL4........................... 41[deg]00' 71[deg]20'
SWL5........................... 40[deg]50' 71[deg]20'
SWL6........................... 40[deg]50' 71[deg]50'
SWL1........................... 41[deg]10' 71[deg]50'
------------------------------------------------------------------------
Southern Windowpane Flounder and Ocean Pout Large AM Area 2
------------------------------------------------------------------------
Point N. latitude W. longitude
------------------------------------------------------------------------
SWL7........................... (\1\) 73[deg]30'
SWL8........................... 40[deg]30' 73[deg]30'
SWL9........................... 40[deg]30' 73[deg]50'
SWL10.......................... 40[deg]20' 73[deg]50'
SWL11.......................... 40[deg]20' (\2\)
SWL12.......................... (\3\) 73[deg]58.5'
SWL13.......................... (\4\) 73[deg]58.5'
SWL14.......................... 40[deg]32.6' (\5\) 73[deg]56.4' (\5\)
SWL7........................... (\1\) 73[deg]30'
------------------------------------------------------------------------
\1\ The southern-most coastline of Long Island, NY at 73[deg]30' W.
longitude.
\2\ The eastern-most coastline of NJ at 40[deg]20' N. latitude, then
northward along the NJ coastline to point SWL12.
\3\ The northern-most coastline of NJ at 73[deg]58.5' W. longitude.
\4\ The southern-most coastline of Long Island, NY at 73[deg]58.5' W.
longitude.
\5\ The approximate location of the southwest corner of the Rockaway
Peninsula, Queens, NY, then eastward along the southern-most coastline
of Long Island, NY (excluding South Oyster Bay), back to point SWL7.
(2) Atlantic halibut. If NMFS determines the overall ACL is
exceeded for Atlantic halibut, any vessel issued a limited access NE
multispecies permit, an open access NE multispecies Handgear B permit,
an open access NE multispecies Category K permit, or a limited access
monkfish permit and fishing under the monkfish Category C or D permit
provisions, may not fish for, possess, or land Atlantic halibut for the
fishing year in which the AM is implemented as specified in paragraph
(a)(5)(i)(D) of this section.
(E) AMs for SNE/MA winter flounder and Atlantic wolffish. A vessel
issued a limited access NE multispecies permit, an open access NE
multispecies Handgear B permit, an open access NE multispecies charter/
party permit, or a limited access monkfish permit and fishing under the
monkfish Category C or D permit provisions may not fish for, possess,
or land SNE/MA winter flounder, as specified in Sec. 648.86(l), as a
proactive AM to prevent the overall ACL for these stocks from being
exceeded.
* * * * *
[[Page 26127]]
(iv) AMs if the sub-ACL for the Atlantic sea scallop fishery is
exceeded. At the end of the scallop fishing year, NMFS shall evaluate
Atlantic sea scallop fishery catch to determine whether a scallop
fishery sub-ACL has been exceeded. On January 15, or when information
is available to make an accurate projection, NMFS will also determine
whether the overall ACL for each stock allocated to the scallop fishery
has been exceeded. When evaluating whether the overall ACL has been
exceeded, NMFS will add the maximum carryover available to sectors, as
specified at Sec. 648.87(b)(1)(i)(C), to the estimate of total catch
for the pertinent stock. If catch by scallop vessels exceeds the
pertinent sub-ACL specified in paragraph (a)(4)(iii)(C) of this section
by 50 percent or more, or if scallop catch exceeds the scallop fishery
sub-ACL and the overall ACL for that stock is also exceeded, then the
applicable scallop fishery AM shall take effect, as specified in Sec.
648.64 of the Atlantic sea scallop regulations.
* * * * *
0
14. In part 648, revise Figure 1 to read as follows:
BILLING CODE 3510-22-P
[[Page 26128]]
[GRAPHIC] [TIFF OMITTED] TR02MY12.001
[FR Doc. 2012-10526 Filed 5-1-12; 8:45 am]
BILLING CODE 3510-22-C