Fisheries of the Northeastern United States; Northeast Multispecies Fishery; Secretarial Interim Action, 17030-17065 [E9-8092]
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Federal Register / Vol. 74, No. 69 / Monday, April 13, 2009 / Rules and Regulations
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 080521698–9067–02]
RIN 0648–AW87
Fisheries of the Northeastern United
States; Northeast Multispecies
Fishery; Secretarial Interim Action
AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Temporary final rule; interim
measures; request for comments.
SUMMARY: NMFS implements this final
interim rule pursuant to its authority to
issue interim management measures
under the authority of the MagnusonStevens Fishery Conservation and
Management Act (Magnuson-Stevens
Act). This action is intended to
immediately reduce overfishing on
certain stocks managed by the Northeast
(NE) Multispecies Fishery Management
Plan (FMP), without jeopardizing the
likelihood that overfished stocks can
achieve rebuilding objectives until longterm measures can be implemented
under Amendment 16 to the FMP.
Measures for the commercial fishery
include an expanded differential daysat-sea (DAS) area in Southern New
England (SNE), where a vessel will be
charged 2 days for every day fished, and
modified groundfish trip limits. In
addition, this action maintains the
scheduled fishing year (FY) 2009 DAS
reduction included in the FMP, which
results in an approximate 18-percent
reduction in Category A DAS. For
private recreational vessels fishing in
the Exclusive Economic Zone (EEZ),
and for federally permitted charter/party
vessels, this action extends in time a
seasonal prohibition on the possession
of Gulf of Maine (GOM) cod, and
prohibits the possession of SNE/MidAtlantic (MA) winter flounder. For
federally permitted charter/party
vessels, this action implements a trip
limit for Georges Bank (GB) cod. In
addition, this action implements
measures to mitigate some of the
negative, short-term economic impacts
of the FMP by expanding the Closed
Area I (CA I) Hook Gear Haddock
Special Access Program (SAP);
modifying the DAS Leasing Program,
the Regular B DAS Program, and the
DAS Transfer Program; continuing the
Eastern U.S./Canada Haddock SAP; and
implementing a reduction in the
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haddock minimum size to 18 inches (45
cm) for both commercial and
recreational vessels. This action also
specifies management measures for the
U.S./Canada Management Area for FY
2009. NMFS anticipates that the interim
measures will need to be renewed upon
the rule’s expiration for an additional
185 days. Therefore, NMFS is requesting
public comments on these measures;
comments received will be considered
during any subsequent action to extend
this final interim rule.
DATES: Effective May 1, 2009, through
October 28, 2009. Comments must be
received by June 12, 2009.
ADDRESSES: You may submit comments,
identified by 0648–AW87, by any one of
the following methods:
• Electronic Submissions: Submit all
electronic public comments via the
Federal e-rulemaking portal: https://
www.regulations.gov.
• Mail: Paper, disk, or CD–ROM
comments should be sent to Patricia A.
Kurkul, Regional Administrator,
National Marine Fisheries Service, 55
Great Republic Drive, Gloucester, MA
01930–2276. Mark the outside of the
envelope: ‘‘Comments on NE
Multispecies Final Interim Rule.’’
• Fax: (978) 281–9135.
Instructions: All comments received
are part of the public record and will
generally be posted to https://
www.regulations.gov without change.
All Personal Identifying Information (for
example, name, address, etc.)
voluntarily submitted by the commenter
may be publicly accessible. Do not
submit confidential business
information or otherwise sensitive or
protected information.
NMFS will accept anonymous
comments (enter ‘‘N/A’’ in the required
fields, if you wish to remain
anonymous). Attachments to electronic
comments will be accepted in Microsoft
Word, Excel, WordPerfect, or Adobe
PDF formats only.
NMFS prepared a Final Regulatory
Flexibility Analysis (FRFA), which
consists of the Initial Regulatory
Flexibility Analysis (IRFA), public
comments and responses, and the
summary of impacts and alternatives
contained in the Classification section
of the preamble of this final rule. Copies
of the small entity compliance guide are
available from the Regional
Administrator, NMFS, Northeast
Regional Office, at the address noted
above. Copies of the Environmental
Assessment (EA) prepared for this rule
may be found at the following Internet
address: https://www.nero.noaa.gov/
nero/regs/frdoc/08/
08MultiInterimEA.pdf.
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Written comments regarding the
burden-hour estimates or other aspects
of the collection-of-information
requirements contained in this rule may
be submitted to the Northeast Regional
Office and by e-mail to
David_Rostker@omb.eop.gov, or fax to
(202) 395–7285.
FOR FURTHER INFORMATION CONTACT:
Thomas Warren, Fishery Policy Analyst,
(978) 281–9347, fax (978) 281–9135.
SUPPLEMENTARY INFORMATION: A
proposed interim rule was published in
the Federal Register on January 16,
2009 (74 FR 2959), which includes
detailed information on the background
and reasons pertinent to the need to
reduce fishing effort in the NE
multispecies fishery for FY 2009.
Comments on the proposed rule were
accepted through February 17, 2009,
which are summarized and responded
to below. The FMP specifies the
management measures for 12 species,
and a total of 19 stocks of groundfish in
Federal waters off the New England and
Mid-Atlantic coasts. Species managed
by the FMP are Atlantic cod, haddock,
yellowtail flounder, pollock, American
plaice, witch flounder, white hake,
windowpane flounder, Atlantic halibut,
winter flounder, ocean pout, and
redfish. In 2008, the effectiveness of the
management measures and the validity
of the status determination criteria
(biological reference points) were fully
evaluated. This planned assessment of
the biological reference points
(Groundfish Assessment Review
Meeting (GARM III)) was part of the
FMP’s biennial adjustment process to be
used for setting fishery measures for FY
2009 (May 1, 2009–April 30, 2010), and
was also part of the rebuilding strategy,
which sought to evaluate the more
fundamental scientific information midway through the rebuilding period for
most stocks. Although the Council
intended to meet a required May 1,
2009, implementation date for
Amendment 16, due to the timing and
the somewhat unanticipated results
from GARM III (September 2008), the
Council developed a revised
Amendment 16 schedule, which, if
approved, is now expected to be
implemented on May 1, 2010. In
addition, the Council voted on
September 4, 2008, to request that
NMFS implement an interim action for
the duration of FY 2009, and
recommended a specific suite of
management measures for the interim
action. As explained fully in Measure 12
under ‘‘Proposed Commercial
Measures’’ of the proposed rule, NMFS
did not propose the Council’s
recommendations in the proposed rule
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because NMFS believed that the
Council’s recommended alternative
would allow overfishing to continue for
several stocks and not achieve
rebuilding objectives.
A summary of the GARM III results
that formed the basis for the proposed
interim rule is in Table 1 below.
Overfishing is occurring on stocks when
the ratio of the fishing mortality rate (F)
to the F that results in the maximum
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sustainable yield (MSY) (Fmsy) is
greater than 1.0, and a stock is
overfished if the ratio of the biomass
level (B) to the B that produces MSY
(Bmsy) is equal to or less than 0.5.
TABLE 1—GARM III STOCK STATUS DETERMINATION CRITERIA AND 2007 STATUS
Species
Stock
Cod ............................................................................
GB ....................
GOM .................
GB ....................
GOM .................
GB ....................
SNE/MA ............
CC/GOM ...........
...........................
...........................
GB ....................
GOM .................
SNE/MA ............
...........................
...........................
...........................
North .................
South ................
...........................
...........................
Haddock ....................................................................
Yellowtail flounder .....................................................
American plaice ........................................................
Witch flounder ...........................................................
Winter flounder ..........................................................
Redfish ......................................................................
White hake ................................................................
Pollock* .....................................................................
Windowpane* ............................................................
Ocean pout ...............................................................
Atlantic halibut ...........................................................
Fmsy
Bmsy (mt)
0.2466
0.237
0.350
0.430
0.254
0.254
0.239
0.190
0.200
0.260
0.283
0.248
0.038
0.125
5.660
0.500
1.470
0.760
0.073
148,084
58,248
158,873
5,900
43,200
27,400
7,790
21,940
11,447
16,000
3,792
38,761
271,000
56,254
2.0
1.4
0.34
4.94
49,000
2007
Fishing
mortality
(2007
F/Fmsy)
1.2
1.9
0.49
0.8
1.1
1.6
1.7
0.5
1.5
1.1
1.5
2.6
0.1
1.2
1.9
3.9
1.3
0.5
0.9
2007
Biomass
(2007
B/Bmsy)
0.12
0.58
2.05
0.99
0.22
0.13
0.25
0.51
0.30
0.31
0.29
0.09
0.64
0.35
0.45
0.38
0.62
0.10
0.03
Estimated
2008 fishing
mortality
0.41
0.300
0.083
0.250
0.130
0.120
0.289
0.099
0.296
0.131
0.317
0.265
0.008
0.065
10.975
1.96
1.85
N/A
0.06
* Pollock and windowpane flounder information was revised subsequent to GARM III in order to utilize 3-yr averages, and incorporate the fall
survey data for pollock; pollock Fmsy is listed in terms of relative exploitation index (catch per centered 3-yr survey index).
N/A indicates an estimate of F in 2008 was unavailable for this stock.
Although NMFS’ initial fishing
mortality rate goals for the FY 2009
interim period are unchanged, based on
public comment, NMFS is modifying
several of the measures proposed in the
proposed interim rule, and asking for
public comment on the modified final
rule. This decision to modify measures
means that, even though substantial
reductions in F will be achieved by this
rule, overfishing will continue on
certain stocks—notably GB cod, witch
flounder, pollock, and northern
windowpane flounder—during the
duration of this interim action. Under
section 305(c) of the Magnuson-Stevens
Act, NMFS may implement an interim
rule that reduces overfishing on
overfished stocks, without necessarily
ending overfishing. In this instance, the
purpose of the interim rule is to reduce
or end overfishing and help ensure that
stocks rebuild consistent with
Amendment 13 objectives for FY 2009,
and to reduce overfishing on the three
other stocks, which were recently
identified as being overfished. The
measures implemented through this rule
will satisfy these objectives, while at the
same time mitigating, to the extent
practicable, the impacts on the fishing
community. As indicated by the EA and
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the comments received on the proposed
rule, ending overfishing on all
multispecies stocks in this interim rule
would result in substantial negative
consequences to the fishing industry.
The Council is developing mitigating
measures in Amendment 16, primarily
through sector proposals, that should
help to offset these negative
consequences. The full range of possible
mitigation measures cannot be
implemented in this interim rule
because they have not been fully
developed and analyzed. While there is
some decrease in the likelihood that GB
cod and other stocks will rebuild within
the time prescribed by the Amendment
13 rebuilding plan as a result of this
final rule, the action should not
significantly jeopardize the likelihood
that Amendment 13’s rebuilding
objectives will be met, particularly
given the short-term nature of this
interim rule and the fact that additional
measures will be implemented through
Amendment 16. Therefore, in exercising
the flexibility provided by section
305(c) of the Magnuson-Stevens Act,
NMFS has determined that the
modifications to the proposed rule as
described below are justifiable because
they are necessary to mitigate impacts
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on the fishing industry to the extent
practicable, without fatally jeopardizing
the likelihood that overfished
multispecies stocks will achieve their
rebuilding objectives through
Amendment 16 measures. The rationale
for determining the extent of acceptable
changes to the proposed rule follows.
Generally speaking, these final
interim measures reduce overfishing to
a lesser degree than the proposed
interim action, as explained later in this
preamble. This action includes several
elements of the Council’s proposed
alternative, but contains additional
measures to further protect stocks that
are in the most critical condition, such
as SNE/MA winter flounder.
Management measures implemented
under this action include: An expansion
of the status quo 2:1 SNE Differential
DAS Area measures; a witch flounder
trip limit of 1,000 lb (453.6 kg) per DAS,
up to 5,000 lb (2,268 kg) per trip; zero
retention limits for SNE winter flounder
(for both commercial and recreational
vessels), northern windowpane
flounder, and ocean pout; a 2-week
extension of the seasonal prohibition on
the retention of GOM cod for both
private recreational and party/charter
vessels, (i.e., revised to encompass
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November through April 15); a bag limit
of 10 GB cod per person per day for
party/charter vessels operating in all
areas; and mitigation measures that
include modifications to the DAS
Leasing, Transfer, and Regular B DAS
Programs, expansion in area and season
of the CA I Hook Gear Haddock SAP,
renewal of the Eastern U.S./Canada
Haddock SAP, and reduction of the
haddock minimum fish size from 19
inches (48.3 cm) to 18 inches (45.7 cm)
for both commercial and recreational
vessels. This action does not implement
the proposed expansion of the GOM
Differential DAS Area (i.e., the Interim
Differential DAS Area), or the proposed
SNE Closure Area. In addition, this
action maintains the Amendment 13
default measure for FY 2009, whereby
Category A DAS are reduced by 18.2
percent, and maintains the status quo
2:1 GOM Differential DAS Area
measures.
For reasons explained in the preamble
to the proposed interim rule, the
proposed fishing mortality targets were
either Fmsy (for windowpane flounder,
GOM winter flounder, GB winter
flounder, witch flounder, pollock, GB
haddock, GOM haddock, GOM cod, GB
cod, American plaice, redfish, and
ocean pout), or Frebuild (GB cod, GB
yellowtail flounder, SNE/MA yellowtail
flounder, Cape Cod (CC)/GOM
yellowtail flounder, SNE/MA winter
flounder, white hake, and Atlantic
halibut). The proposed interim
measures would not have achieved
Frebuild for GB cod; however, they
would have achieved Fmsy for this
stock. The proposed measures also
would not have achieved the Fmsy
target for northern windowpane
flounder, or the Frebuild target for SNE/
MA winter flounder.
GARM III provided example estimates
of Frebuild for overfished stocks,
making assumptions about the rebuild
period end-dates and the starting stock
conditions at the beginning of the
rebuilding periods. In doing so, GARM
III assumed that the catch in FY 2008
will be the same as the catch in FY
2007. In contrast, for this interim action,
an estimated catch in FY 2008 was used
to recalculate the starting stock
conditions in FY 2008, and the
associated Frebuilds. For Amendment
16, the Council’s Plan Development
Team (PDT) estimated catch for the
entire FY 2008 based upon an
extrapolation of landings data for
calendar year (CY) 2008 through June
2008. As explained further in the
proposed interim rule preamble, this
interim action relies on the PDT’s
estimated landings for FY 2008, and
derived estimates of fishing mortality
rates for CY 2008 and the recalculated
Frebuilds. Because the measures
implemented by this action will be
effective in FY 2009, an estimate of
fishing mortality in CY 2008 more
closely represents the starting
conditions of the remainder of the
rebuilding periods. For GB yellowtail
flounder, Frebuild was calculated
utilizing an assumed catch in CY 2008
of 2,500 mt.
The target reductions for pollock and
the two windowpane flounder stocks
were revised from the proposed rule in
order to be consistent with the other
stocks. In the proposed rule, the target
reductions for all stocks except these
three were based upon an estimate of
fishing mortality in 2008. In contrast,
the target reductions for pollock and the
two stocks of windowpane flounder
were based upon the fishing mortality in
2007. Thus, this final rule utilizes a
starting fishing mortality estimate in
2008 for all stocks. Because the estimate
of fishing mortality in 2008 was greater
than that observed in 2007 for these
three stocks, the effect of this change is
an increase in the percentage reduction
necessary to reduce fishing mortality to
Fmsy. For the calculation of F in 2008,
for pollock, the PDT calculated an
assumed catch in 2008 and for the
windowpane flounder stocks, catch in
2008 was assumed to be equal to the
catch in 2007.
In contrast to the proposed interim
rule, which would not have attained the
proposed interim goals for two stocks
(i.e., SNE/MA winter flounder and
Northern windowpane flounder), nor
the updated Fmsy goal for pollock
(which was updated after the proposed
interim rule was published),
management measures implemented
through this final rule do not attain the
stated goals for five stocks (SNE/MA
winter flounder, Northern windowpane
flounder, pollock, GB cod, and witch
flounder). However, for four of these
five stocks, the rebuilding timeline
extends beyond 2014 (a 2026
Amendment 13 end date for GB cod;
and a 2017 Amendment 16 proposed
end date for Northern windowpane
flounder, witch flounder, and pollock).
Because these four stocks have longer
rebuilding timelines associated with
them, additional time is available to
ensure that the rebuilding goals of the
FMP are met. However, to maintain the
FMP rebuilding trajectories and to meet
the statutory rebuild dates, the Council
will need to consider whether further
adjustments in fishing mortality are
needed. If further adjustments are
needed, the Council will need to
account for this in future actions,
possibly even in Amendment 16. Given
the likely rebuilding schedules and the
original justification for the expanded
differential DAS counting area in the
GOM and northern GB in the proposed
interim rule (primarily to protect
pollock and witch flounder), NMFS is
not implementing the proposed
expanded differential DAS counting
area in this final rule, and is
maintaining the status quo inshore GOM
Differential DAS Area. The SNE Closure
Area was included in the proposed
interim rule primarily to protect SNE/
MA winter flounder. Although this
stock has a rebuilding timeline of 2014,
given the concern raised by the public
regarding the severe economic impacts
that would be imposed by this closure
area and the potential for this closure to
lead to shifts in effort to other areas and
other stocks, NMFS is instead
implementing in this same area, slightly
modified, a requirement for 2:1
differential DAS counting. To strictly
control effort on SNE/MA winter
flounder, NMFS is implementing a zero
landing limit for SNE/MA winter
flounder for both commercial and
recreational vessels throughout the
range of the stock. Table 2 identifies the
2009 target Fs as published in the
proposed interim rule, and provides a
comparison of the estimated fishing
mortality reductions achieved for
measures proposed in the proposed
interim rule, and the measures
implemented by this final interim rule.
TABLE 2—COMPARISON OF FISHING MORTALITY REDUCTIONS FOR THE PROPOSED AND FINAL INTERIM RULES
2009
proposed
F target
Species
Stock
Cod ....................................................
GB ....................
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0.247
(Fmsy)
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F reduction
objective
¥40%
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F value for
proposed
interim
action
0.208
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F reduction
achieved
F value for
final interim
action
F reduction
achieved
¥49%
0.295
¥28%
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TABLE 2—COMPARISON OF FISHING MORTALITY REDUCTIONS FOR THE PROPOSED AND FINAL INTERIM RULES—
Continued
Species
2009
proposed
F target
Stock
GOM .................
Haddock ............................................
GB ....................
GOM .................
Yellowtail Flounder ............................
American Plaice ................................
GB ....................
SNE/MA ............
CC/GOM ...........
...........................
Witch Flounder ..................................
...........................
Winter Flounder ................................
GB ....................
GOM .................
Redfish ..............................................
SNE/MA ............
...........................
White Hake .......................................
Pollock ...............................................
...........................
...........................
Windowpane Flounder ......................
North .................
South ................
Ocean Pout .......................................
...........................
Atlantic halibut ...................................
...........................
Because of the substantial changes
made to the proposed interim measures,
and the resulting changes in the
expected Fs as a consequence of these
changes, this final rule also implements
revised target TACs and Incidental
Catch TACs. The target TACs, and the
Incidental TACs that are based on these
targets, are specified as follows: For
those stocks where the measures
implemented by this rule are expected
to reduce F to below the F target, the
target TACs are set based on the
estimated F achieved from the
management measures in this action; for
those stocks with Fs that are less than
the proposed rule F targets, the target
TACs will be set based on the proposed
F targets. See Measure 3 under
‘‘Approved Commercial Measures’’ for
further details on these final target
TACs.
Management Measures
All measures in effect prior to May 1,
2009, including the scheduled default
DAS reduction measures, that are not
amended by this final interim rule, will
remain in effect on and after May 1,
2009. This interim action implements
management measures to reduce fishing
mortality on the commercial and
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0.237
(Fmsy)
0.350
(Fmsy)
0.430
(Fmsy)
0.109 (Freb)
0.072 (Freb)
0.238 (Freb)
0.190
(Fmsy)
0.200
(Fmsy)
0.260
(Fmsy)
0.283
(Fmsy)
0.000 (Freb)
0.038
(Fmsy)
0.084 (Freb)
5.660
(Fmsy)
0.500
(Fmsy)
1.470
(Fmsy)
7.600
(Fmsy)
0.044 (Freb)
F reduction
objective
F value for
proposed
interim
action
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F value for
final interim
action
F reduction
achieved
¥21%
0.203
¥32%
0.247
¥18%
322%
0.049
¥38%
0.062
¥25%
72%
0.159
¥36%
0.205
¥18%
¥16%
¥38%
¥18%
92%
0.109
0.017
0.174
0.056
¥16%
¥86%
¥40%
¥43%
0.109
0.073
0.167
0.084
¥16%
¥39%
¥42%
¥15%
¥32%
0.167
¥44%
0.247
¥17%
98%
0.108
¥18%
0.114
¥13%
¥11%
0.286
¥10%
0.265
¥16%
¥100%
375%
0.052
0.004
¥80%
¥50%
0.100
0.007
¥62%
¥13%
29%
¥51%
0.033
6.520
¥49%
NA
0.054
9.342
¥17%
¥19%
¥83%
....................
NA
2.229
¥22%
¥29%
....................
NA
1.392
¥32%
NA
....................
NA
....................
....................
¥27%
....................
NA
....................
....................
recreational fisheries without
compromising rebuilding objectives,
and revises several management
programs to mitigate the negative
economic and social impacts. The
interim action is intended to ensure
consistency, to the extent practicable in
an interim rule, with the national
standards and required provisions of the
Magnuson-Stevens Act. This action also
specifies target TACs for all managed
stocks, and annual specifications for
stocks managed by the U.S./Canada
Resource Sharing Understanding
(Understanding). As is more fully
discussed later in this document, these
measures will result in both quantifiable
and non-quantifiable reductions in
fishing mortality for all of the NE
multispecies stocks managed under the
FMP.
The interim measures are designed to
work in conjunction with the FMP to
reduce fishing mortality and continue to
maintain progress toward achieving the
rebuilding requirements of the FMP.
The analysis of this action presumes
that the measures will be in effect
throughout FY 2009, and that a
subsequent management action
(Amendment 16) will be implemented
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F reduction
achieved
Sfmt 4700
on May 1, 2010. The FMP management
measures include an FY 2009 default
measure that will change the allocation
ratio of Category A:B DAS from 55:45 to
45:55. This measure, because it is not an
action implemented by this interim
action, is not discussed specifically in
the description of the interim measures
that follow. In addition, this action
continues existing measures in the FMP
associated with the GOM Differential
DAS Area, as discussed further below.
NMFS anticipates that this interim
action will be renewed upon its
expiration for an additional 185 days,
given that the Council does not
anticipate the implementation of
Amendment 16 until May 2010 and that
the Council recommended that any
interim action implemented by NMFS
should be in effect for all of FY 2009.
Several measures were modified from
the proposed to the final rule based
upon public comments received and
further analysis of proposed measures,
to mitigate the negative economic
impacts of the management measures on
the fishing industry and fishing
communities without compromising
long-term rebuilding of overfished
stocks. Although these revisions will
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result in less reduction to fishing
mortality than the measures proposed,
such changes should not undermine
efforts to rebuild stocks within the
established timeframes. Such measures
will continue to reduce F on all stocks
and eliminate overfishing on all but four
stocks (pollock, GB cod, witch flounder,
and northern windowpane flounder).
Three of these stocks are newly
classified as overfished (pollock, witch
flounder, and northern windowpane
flounder), and the rebuilding programs
developed by the Council in draft
Amendment 16 include rebuilding
timelines extending to 2017. The
rebuilding timeline for GB cod extends
through 2026. Given this, there should
be sufficient opportunity for future
management actions to end overfishing
and rebuild these stocks, as necessary.
The following describes the measures
implemented by this final interim rule.
Approved Commercial Measures
1. Differential DAS Counting
This action maintains the existing
differential DAS counting area in the
GOM, as established in the FMP.
However, in SNE, the existing SNE
Differential DAS Area is replaced by the
Interim SNE Differential DAS Area. This
area includes waters between 40°30′ and
41°30′ N. lat., and west of 68°50′ W.
long. (i.e., west of the border of the
Western U.S./Canada Area) to the shore,
including all of Nantucket Sound and
the Great South Channel. The Interim
SNE Differential DAS Area is being
implemented primarily as a means to
reduce F on SNE winter flounder and
SNE/MA yellowtail flounder.
With the exception of vessels fishing
with hook gear in the Interim SNE
Differential DAS Area, all NE
multispecies vessels declared into and
fishing under a NE multispecies
Category A DAS within either the GOM
or Interim SNE Differential DAS Areas
for any portion of a trip will be charged
at a rate of 2:1 for the entire trip. In
other words, with the exception noted
above, if a vessel declares into, and
fishes in, either the GOM or Interim
SNE Differential DAS Area for 10 hr, the
vessel’s DAS balance would be charged
20 hr. NE multispecies vessels declared
into and fishing under a Category A
DAS in the Interim SNE Differential
DAS Area using hook gear will be
charged DAS at a rate of 1:1, provided
such vessels have only hook gear on
board. The hook gear exception to the
differential DAS counting rate is based
upon data that indicate that the catch
rate of winter flounder and yellowtail
flounder, the primary species targeted
by this measure, by hook gear is likely
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to be very low and, in conjunction with
a zero retention limit for SNE winter
flounder, will not substantially affect F
reductions achieved by this action.
A vessel will not be charged at the
differential DAS rate if it declares into
and transits to another area outside of
one of the differential DAS areas. For
example, if a vessel steams through the
GOM Differential DAS Area on its way
to and from the fishing grounds in the
U.S./Canada Management Area, where
DAS are not counted differentially, it
will not be charged at the 2:1 rate for the
parts of the trip spent steaming through
the GOM Differential DAS Area. If a
vessel declares and fishes both inside
and outside of the GOM Differential
DAS Area or the Interim SNE
Differential DAS Area on the same trip,
it will be charged differential DAS at a
rate of 2:1 for the entire trip. This does
not change the way that DAS are
charged for vessels fishing in the GOM
Differential DAS Area. However,
charging differential DAS at a rate of 2:1
for the entire trip does represent a
change in the way DAS are currently
charged under the existing SNE
Differential DAS Area implemented
under FW 42. This change is based
upon the revised area encompassed by
the Interim Differential DAS Area, as
further explained in the response to
Comment 15.
Consistent with current regulations,
vessels are required to declare their
intent to fish in one or both of the
differential DAS areas via the vessel
monitoring system (VMS) prior to
leaving port. However, the
Administrator, Northeast Region, NMFS
(Regional Administrator) currently has
the authority to require the fishery to
utilize the ‘‘call-in system’’ on a
temporary basis instead of the VMS for
DAS accounting if the vessel fishes
inside/outside of the VMS demarcation
line on the same trip, if the VMS system
was down for an extended period of
time, or for some other unforeseen
circumstance. In such a circumstance,
vessels fishing any portion of a trip
inside one or both of the differential
DAS areas will be charged at the rate of
2:1 for the entire trip.
The interaction of current groundfish
and non-groundfish regulatory programs
and the different DAS counting rules
remain unchanged under this action
(e.g., the cod running clock, DAS
charging rules for Day gillnet vessels,
the application of daily possession
limits for certain stocks, the Eastern
U.S./Canada Area rules, use of Regular
B DAS, and monkfish/groundfish
permitted vessels fishing under a NE
multispecies DAS). For example, a
vessel fishing in the GOM Differential
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Sfmt 4700
DAS Area for 25 hr that caught 1,600 lb
(726 kg) of GOM cod (i.e., 2 day’s worth)
would not be required to submit the cod
running clock form via VMS in order to
account for the additional day’s worth
of cod harvested. In addition, a Day
gillnet vessel declared into and fishing
in the GOM Differential DAS Area
would be charged DAS at a rate of 2:1
for any trip less than or equal to 3 hr
in duration, or greater than 7.5 hr in
duration and 15 hr for any trip greater
than 3 hr, or less than or equal to 7.5
hr in duration. For vessels fishing in
multiple geographic areas in which
different rules apply (such as
differential DAS counting and trip
limits), the most restrictive rule would
apply for the entire trip. The current
regulations that allow monkfish
Category C and D vessels to fish as a
monkfish Category A or B vessel, and
land monkfish under certain conditions,
will still apply. As described in detail
below under Item 9 ‘‘Mitigating
Measures,’’ the DAS rules that apply to
monkfish Category C and D vessels
fishing in the GOM Differential DAS
Area are modified by this action to
minimize any impact these measures
may have on the ability of such vessels
to fish for monkfish.
2. Modified Trip Limits
Under this interim rule, NE
multispecies vessels are not allowed to
fish for, possess, or land more than
1,000 lb (453.6 kg) per DAS, up to 5,000
lb (2,268 kg) per trip of witch flounder.
In addition, no retention of SNE winter
flounder, northern windowpane
flounder, or ocean pout is allowed.
Vessels fishing for winter flounder or
windowpane flounder in multiple stock
areas are subject to the most restrictive
possession limit for the pertinent
species. In other words, if a vessel fishes
in the SNE winter flounder stock area
and the GB winter flounder stock area
on the same trip, the vessel will be
subject to the prohibition on retention of
winter flounder for that trip. Lastly, as
explained further under Measure 6
under ‘‘Approved Commercial
Measures’’ of the preamble (‘‘Annual
Specifications for U.S./Canada
Management Area’’), a limit of 5,000 lb
(2,268 kg) of GB yellowtail flounder per
trip is specified. Modifications to trip
limits are implemented as a means to
reduce fishing mortality or increase
yield because they are a management
tool that can target particular stocks and
are an important component of the
current FMP.
3. Specification of Target TACs
Target TACs are utilized in the FMP
as one method of evaluating the success
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Federal Register / Vol. 74, No. 69 / Monday, April 13, 2009 / Rules and Regulations
of management measures and providing
a way to make simple comparisons
between different fishing years.
Secondly, target TACs form the basis of
calculating allocations of GB cod to
sectors and the incidental catch TACs
for the Special Management Programs.
This final interim rule implements
target TACs for FY 2009. The proposed
rule indicated that the target TACs
would be based upon either Fmsy or
Frebuild for each stock. For stocks that
were previously considered overfished,
target TACs were proposed to be based
upon Frebuild, with one exception for
GB cod. For GB cod, the target TAC was
proposed to be based upon Fmsy, for
reasons specified in the proposed
interim rule. In contrast, for stocks that
have been newly classified as overfished
based upon the results of GARM III, the
target TACs were proposed to be based
upon Fmsy. However, this final interim
rule specifies target TACs based upon
either the Ftarget for each stock (i.e.,
Fmsy or Frebuild) or the F resulting
from measures implemented by this
action (i.e., estimated F), whichever is
higher. For stocks where the estimated
F is lower than the Ftarget,
implementing target TACs based upon
the Ftarget allows for increased yield.
For stocks where the estimated F is
higher than the Ftarget, implementing
target TACs based upon the estimated F
more accurately reflects catch
anticipated from measures implemented
by this action. Table 3 lists the target
TACs for FY 2009, based upon GARM
III data, and an estimate of F for each
stock during CY 2008.
TABLE 3—TARGET TACS (MT) FOR FY
2009—Continued
Target
TAC
Species
Stock
Haddock ....................
Haddock ....................
Yellowtail flounder ....
Yellowtail flounder ....
Yellowtail flounder ....
Plaice ........................
Witch flounder ...........
Winter flounder .........
Winter flounder .........
Winter flounder .........
Redfish ......................
White hake ................
Pollock ......................
Windowpane flounder
Windowpane flounder
Halibut .......................
GB ...........
GOM ........
GB ...........
SNE/MA ...
CC/GOM ..
..................
..................
GB ...........
GOM ........
SNE .........
..................
..................
..................
North ........
South .......
..................
89,055
1,564
*1,617
389
860
3,214
1,129
2,004
379
0
8,614
2,376
6,346
581
279
68
* A hard TAC, set through a separate process described in Measure 5 of this preamble.
4. Revisions to Incidental Catch TACs
and Allocations to Special Management
Programs
This final rule revises the
specification of incidental catch TACs
applicable to the Special Management
Programs of the FMP for FY 2009, based
upon the most recent scientific
information. Incidental catch TACs are
specified for certain stocks of concern
for Special Management Programs in
order to limit the amount of catch of
stocks of concern that can be caught
under such programs, and to fully
account for fishing mortality. The
incidental catch TACs apply to catch
(landings and discards) caught under
Category B DAS (either Regular or
Reserve B DAS) on trips that end on a
TABLE 3—TARGET TACS (MT) FOR FY Category B DAS. The catch of stocks for
which incidental catch TACs are
2009
specified on trips that start under a
Category B DAS and then flip to a
Target
Species
Stock
Category A DAS do not accrue toward
TAC
such TACs.
A stock of concern is defined as a
Cod ........................... GB ...........
5,501
Cod ........................... GOM ........
10,724 stock that is in an overfished condition
17035
or subject to overfishing. Due to the
revised status of stocks (GARM III) that
is adopted under this action, an
incidental catch TAC is no longer
appropriate for American plaice,
because it is no longer considered a
stock of concern. Further, new
incidental catch TACs are required for
GOM winter flounder and pollock
because they are now considered stocks
of concern. The percentages that the
TACs are based on remain unchanged,
with the exception of witch flounder,
which is reduced from 5 percent to 2
percent, due to its overfished status and
the fact that the F and total catch need
to be reduced. The incidental catch
TACs for GOM winter flounder are set
at 5 percent, based on the rationale
described in Framework (FW) 40A to
the FMP: If the recent catch levels are
less than the expected future catch
levels, and 2009 management measures
are likely to achieve more than the
required reduction in F, then the size of
an incidental catch TAC relative to the
size of the overall TAC is larger (set as
a larger percent). The incidental catch
TAC for pollock is set at 5 percent
because of the prevalence of pollock
catch in the Special Management
Programs, and based upon the rationale
cited above. The utility of the Special
Management Programs would be
severely constrained if the incidental
catch TAC is set too low. The number
of total incidental catch TACs is
increased from the current number (8),
to 10. Due to the severe F reduction
necessary for the SNE/MA stock of
winter flounder, no retention of this
stock is allowed, and there is no
incidental catch TAC specified (see
additional discussion under Section 9 of
this preamble, Mitigating Measures).
The calculation of incidental catch
TACs by stock based on the target TACs
is shown in Table 4.
TABLE 4—INCIDENTAL CATCH TACS FOR FY 2009 (MT)
Percentage
of total
TAC
Stock
Target TAC
2
1
2
1
1
5
2
2
2
5
5,501
10,724
1,617
860
389
6,346
1,129
2,004
2,376
379
GB cod ...................................................................................................................................................
GOM cod ...............................................................................................................................................
GB yellowtail ..........................................................................................................................................
CC/GOM yellowtail ................................................................................................................................
SNE/MA yellowtail .................................................................................................................................
Pollock ...................................................................................................................................................
Witch flounder ........................................................................................................................................
GB winter flounder .................................................................................................................................
White hake .............................................................................................................................................
GOM winter ............................................................................................................................................
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E:\FR\FM\13APR2.SGM
13APR2
Incidental
TAC
110
107.2
32.3
8.6
3.9
317.3
22.6
40.1
47.5
19.0
17036
Federal Register / Vol. 74, No. 69 / Monday, April 13, 2009 / Rules and Regulations
This final interim rule also modifies
the allocation of the incidental catch
TACs to the various Special
Management Programs due to the
changes in status of stocks, and to
optimize the design of the programs
based on the operation of the programs
since their inception. For example, the
Eastern U.S./Canada Haddock SAP was
not used at all in FY 2007, and only two
trips were taken in the area in FY 2006.
Therefore, the percent allocations to this
SAP are reduced for GB cod, GB
yellowtail, and GB winter flounder, and
the percent allocation to the Regular B
DAS Program is increased due to higher
participation in that program
historically. Secondly, this rule
provides the Regional Administrator the
authority to modify the allocations
among programs in-season, or prior to
the beginning of the season, because it
is difficult to estimate the appropriate
TAC, since the level of participation and
catch rates of stocks of concern in the
various programs is highly variable. The
changes to the allocations are
summarized in Table 5. Table 6 contains
the incidental catch TACs that result
from applying the percentages in Table
5 to the incidental TACs in Table 4.
TABLE 5—MODIFICATIONS TO THE INCIDENTAL CATCH TAC ALLOCATIONS FOR FY 2009
Regular B DAS Program
Stock
Current
GB Cod ............................................................................
GB Yellowtail flounder .....................................................
GB Winter flounder ..........................................................
Pollock ..............................................................................
GOM Winter flounder .......................................................
GOM Cod .........................................................................
White hake .......................................................................
CC/GOM Yellowtail flounder ............................................
SNE/MA Yellowtail flounder .............................................
Witch flounder ..................................................................
Plaice ...............................................................................
50%
50%
50%
None
None
100%
100%
100%
100%
100%
100%
New
Eastern U.S./Canada
Haddock SAP
Closed Area I Hook Gear
Haddock SAP
Current
70%
80%
80%
90%
100%
100%
100%
100%
100%
100%
None
New
Current
New
34%
50%
50%
None
....................
....................
....................
....................
....................
....................
....................
14%
20%
20%
5%
....................
....................
....................
....................
....................
....................
....................
16%
....................
....................
None
....................
....................
....................
....................
....................
....................
....................
No change
....................
....................
5%
....................
....................
....................
....................
....................
....................
....................
TABLE 6—SPECIFICATION OF INCIDENTAL CATCH TACS FOR SPECIAL MANAGEMENT PROGRAMS (MT) FOR FY 2009
Regular B
DAS Program
Stock
Eastern U.S./
Canada
Haddock SAP
Closed Area I
Hook Gear
Haddock SAP
77
107.2
25.8
8.6
3.9
285.6
22.6
32.1
47.5
19.0
15.4
na
6.5
na
na
15.9
na
8.0
na
na
17.6
na
na
na
na
15.9
na
na
na
na
GB Cod ........................................................................................................................................
GOM Cod .....................................................................................................................................
GB Yellowtail flounder .................................................................................................................
CC/GOM Yellowtail flounder ........................................................................................................
SNE/MA Yellowtail flounder .........................................................................................................
Pollock .........................................................................................................................................
Witch flounder ..............................................................................................................................
GB Winter flounder ......................................................................................................................
White hake ...................................................................................................................................
GOM Winter flounder ...................................................................................................................
5. Annual Specifications for U.S./
Canada Management Area
In consultation with the Council,
NMFS annually implements
management measures for the U.S./
Canada Management Area through
proposed and final rules. For FY 2009,
because NMFS is implementing
management measures for the entire
fishery to reduce fishing mortality as
described above, NMFS is including the
specification of the TACs and other
measures for the U.S./Canada
Management Area in this final interim
rule in order to streamline the
regulatory process.
The FMP specifies a procedure for
setting annual hard TAC levels (i.e., the
fishery or area closes when a TAC is
reached) for Eastern GB cod, Eastern GB
haddock, and GB yellowtail flounder in
the U.S./Canada Management Area,
which is described in the proposed
interim rule. The specific justification
for the FY 2009 TACs, which were
based upon the most recent stock
assessments, is also described in the
proposed rule. On October 8, 2008, the
Council approved, consistent with the
2008 Guidance Document, the following
U.S./TACs recommended by the
Transboundary Management Guidance
Committee: 527 mt of Eastern GB cod;
11,100 mt of Eastern GB haddock; and
1,617 mt of GB yellowtail flounder. The
FY 2009 TACs for the U.S./Canada
Management Area represent a decrease
for cod and yellowtail flounder, and an
increase for haddock compared to those
specified for FY 2008 (Tables 7 and 8).
TABLE 7—FY 2009 U.S./CANADA TACS (MT) AND PERCENTAGE SHARES (IN PARENTHESES)
GB Cod
Total Shared TAC ........................................................................................................................
U.S. TAC ......................................................................................................................................
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1,700
527 (31)
E:\FR\FM\13APR2.SGM
13APR2
GB Haddock
30,000
11,100 (37)
GB Yellowtail
Flounder
2,100
1,617 (77)
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Federal Register / Vol. 74, No. 69 / Monday, April 13, 2009 / Rules and Regulations
TABLE 7—FY 2009 U.S./CANADA TACS (MT) AND PERCENTAGE SHARES (IN PARENTHESES)—Continued
GB Cod
Canada TAC ................................................................................................................................
1,173 (69)
GB Haddock
18,900 (63)
GB Yellowtail
Flounder
483 (23)
TABLE 8—FY 2008 U.S./CANADA TACS (MT) AND PERCENTAGE SHARES (IN PARENTHESES)
GB Cod
Total Shared TAC ........................................................................................................................
U.S. TAC ......................................................................................................................................
Canada TAC ................................................................................................................................
2,300
667 (29)
1,633 (71)
GB Haddock
23,000
8,050 (35)
14,950 (65)
GB Yellowtail
Flounder
2,500
* 1,950 (78)
550 (22)
* Adjusted downward to 1,868.7 mt due to overharvest of FY 2007 TAC.
The regulations for the
Understanding, promulgated by the
final rule implementing Amendment 13,
state that any overages of the GB cod,
haddock, or yellowtail flounder TACs
that occur in a given fishing year will
be subtracted from the respective TAC
in the following fishing year.
Therefore, should an analysis of the
catch of the shared stocks by U.S.
vessels indicate that an over-harvest
occurred during FY 2008, the pertinent
TAC will be adjusted downward in
order to be consistent with the FMP and
Understanding. Although it is very
unlikely, it is possible that a very large
over-harvest could result in an adjusted
TAC of zero. If an adjustment to one of
the FY 2008 TACs of cod, haddock, or
yellowtail flounder is necessary, the
public will be notified through
publication in the Federal Register and
through a letter to permit holders.
NMFS is also implementing, through
the authority granted to the Regional
Administrator by the FMP, measures to
optimize the harvest of the shared
resources. The regulations under
§ 648.85(a)(3)(iv)(D) provide the
Regional Administrator the authority to
implement in-season adjustments to
various measures in order to prevent
over-harvesting, or to facilitate
achieving the TAC.
Based on the Council’s vote to
postpone the opening of the Eastern
U.S./Canada Area for vessels fishing
with trawl gear in FY 2008 from May 1,
2008, to August 1, 2008, and the success
of this management measure in slowing
the annual catch rate of cod during the
early part of the year, NMFS is
implementing this same measure for FY
2009. Thus, the FY 2009 opening of the
Eastern U.S./Canada Area for trawl
vessels will be August 1, 2009; more
selective longline gear is allowed access
during May through July. Such vessels
will be limited to a cod catch of 5
percent of the cod TAC, or 26.4 mt. The
objective of this action is to prevent
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20:07 Apr 10, 2009
Jkt 217001
trawl fishing in the Eastern U.S./Canada
Area during the time period when cod
bycatch is likely to be very high. The
goal of this measure is to prolong access
to this area in order to maximize the
catch of available cod, haddock, and
yellowtail flounder.
Secondly, the Regional Administrator
is implementing a possession limit of
5,000 lb (2,268 kg) per trip for GB
yellowtail flounder. Although the
regulations under § 648.86(a)(3)(iv)(C)
indicate an initial trip limit of 10,000 lb
(4,536 kg) at the beginning of a fishing
year for GB yellowtail flounder, based
on the yellowtail flounder catch rate
from the U.S./Canada Management Area
under a 5,000-lb (2,268-kg) trip limit
during FY 2008, and analyses
conducted by NMFS during FY 2007, a
5,000-lb (2,268-kg) trip limit is an
appropriate trip limit to allow
harvesting of the TAC, and to increase
the likelihood that further restrictions
during the fishing year to slow the catch
rate will be unnecessary.
Third, the Regional Administrator is
allowing the use of the Ruhle Trawl in
the Eastern U.S./Canada Area. Under
permanent regulations, only a flounder
net and the haddock separator trawl are
permanently authorized for such use.
The Ruhle trawl, which is a modified
trawl that substantially reduces the
catch rate of most stocks of concern, was
approved for use in the Regular B DAS
Program and the Eastern U.S./Canada
Haddock SAP (73 FR 40186, July 14,
2008). Approval of the use of the Ruhle
trawl in the Eastern U.S./Canada Area
through this interim rule will provide
another alternative for trawl vessel
operators and, therefore, provide
additional flexibility. As detailed in the
July 14, 2008 final rule, the Ruhle trawl
has been demonstrated to substantially
reduce catch of many species of
groundfish, and therefore its use is
consistent with the management
objectives for the Eastern U.S./Canada
Area.
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Lastly, the Regional Administrator is
implementing zero trips into the CA II
Yellowtail Flounder SAP during FY
2009, based on a determination that the
available TAC of GB yellowtail flounder
is insufficient to support a minimum
level of fishing activity within the CA II
Yellowtail Flounder SAP. The Regional
Administrator has the authority to
determine the allocation of the total
number of trips into the CA II Yellowtail
Flounder SAP based upon several
criteria, including GB yellowtail
flounder TAC level and the amount of
GB yellowtail flounder caught outside of
the SAP. As implemented by FW 40B,
zero trips to this SAP should be
allocated if the available GB yellowtail
flounder catch is not sufficient to
support 150 trips with a 15,000-lb
(6,804-kg) trip limit (i.e., if the available
GB yellowtail flounder catch is less than
1,021 mt). This calculation takes into
account the projected catch from the
area outside of the SAP. Based on the
estimate for catch outside of the SAP
utilized for FY 2008 (1,376 mt), and the
proposed GB yellowtail flounder TAC
for FY 2009 (1,617 mt), there is
insufficient available catch to allow the
SAP to proceed (i.e., 1,617 ¥ 1,376 =
241; 241 < 1,021 mt).
6. Haddock TAC for the CA I Hook Gear
Haddock SAP
Under this action, a haddock TAC for
the CA I Hook Gear Haddock SAP is set
based upon the GARM III stock
assessment and a formula implemented
in FW 42. The haddock TAC in a
particular year is based upon the TAC
that was specified for the SAP in 2004
(1,130 mt), scaled according to the size
of the exploitable biomass of western
GB haddock compared to the biomass
size in 2004 (35,317 mt). The size of the
western component of the GB haddock
stock is estimated at 35 percent of the
size of the total GB haddock stock.
Because the 2009 exploitable biomass of
haddock is 321,870 mt, the formula and
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13APR2
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resultant TAC is as follows:
((.35)(321,870)/35,317) × 1,130 = 3,604.5
mt. This action implements further
modifications to this SAP, as discussed
in Item 9 below.
7. Elimination of the SNE/MA Winter
Flounder SAP
The SNE/MA Winter Flounder SAP
regulations allow a limited access NE
multispecies vessel fishing for summer
flounder west of 72°30′ W. long. to
retain up to 200 lb (91 kg) of winter
flounder while not under a NE
multispecies DAS, provided the vessel
complies with various restrictions. Due
to the severely depleted status of SNE/
MA winter flounder, and the goal of
reducing F to as close to zero as
practicable, this final rule eliminates
this SAP. Because the SAP could enable
limited targeting of winter flounder,
elimination of the SAP may prevent
some catch of winter flounder from
occurring.
8. Elimination of the State Waters
Winter Flounder Exemption
The State Waters Winter Flounder
Exemption allows vessels issued a NE
multispecies permit to fish in state
waters for winter flounder using gear
with mesh smaller than required for
other vessels in the fishery (provided
various requirements and criteria are
met). Due to the severely depleted status
of the SNE/MA winter flounder stock,
and the goal of reducing F to as close
to zero as practicable, this final rule
eliminates this SAP. Because the SAP
could enable limited targeting of winter
flounder, elimination of the SAP may
prevent some catch of winter flounder
from occurring.
9. Mitigating Measures
CA I Hook Gear Haddock SAP
Expansion. For reasons explained in the
Comments section below, this final rule
implements modifications to the CA I
Hook Gear Haddock SAP to expand its
scope and change some of the
restrictions in order to increase
opportunity to access GB haddock and
provide additional flexibility to vessels.
The expansion has been determined to
be consistent with the goals of the FMP.
Specifically, this rule modifies the time
period for the SAP from October
through December, to May through
January, and expands the area within
CA I where vessels may fish to the east
and south, to encompass the entire
northern half of CA I. This rule
eliminates the division of the SAP into
two time periods, as well as the
allocation of the haddock TAC to the
two time periods. All limited access NE
multispecies DAS vessels fishing with
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hook gear may fish in the SAP at any
time (provided the SAP is open),
regardless of whether the vessel is
enrolled in a sector or is in the
‘‘common pool.’’ This final rule also
implements a provision that was not
included in the Council’s alternative,
which is a prohibition on the use of
squid as bait when fishing in this SAP,
in order to allow haddock to be targeted
with increased likelihood that the catch
rate of cod will be low. This prohibition
is based upon analysis of experimental
fishery data during the comment period
for this action that indicated high
bycatch of cod may occur when using
squid as bait. This final rule also
eliminates the requirement that vessels
intending to participate in the SAP
provide a yearly notification to the
observer program in advance of the SAP
season, because the removal of the
sector and non-sector seasons for this
SAP no longer make this notification
necessary to assist in the deployment of
observers. The requirement to notify the
observer program 72 hr in advance of
each trip is maintained. These measures
were not included in the proposed rule
and NMFS is soliciting comments on
this aspect of the rule.
Reduction of Haddock Minimum Size.
Under this interim action, the haddock
minimum size is reduced to 18 inches
(45 cm) for both the commercial and
recreational fisheries in order to
increase yield and decrease bycatch (as
defined by the Magnuson-Stevens Act).
Information from GARM III indicates
that the GB stock is very large and is
rebuilt, while the GOM stock is 99percent rebuilt. Furthermore, a portion
of the large 2003 year class of haddock
is still below the current 19-inch (47.5cm) minimum size. A reduced
minimum size for haddock will allow
vessels to retain more haddock, thereby
increasing yield for this species. Other
recreational measures are described
under Measure 10 under ‘‘Approved
Commercial Measures’’ of the preamble
to this final interim rule.
Extension of the Eastern U.S./Canada
Haddock SAP. The Eastern U.S./Canada
Haddock SAP, which is set to expire at
the end of FY 2008 on April 30, 2009,
is extended through this interim action,
in order to continue to facilitate access
to GB haddock. This SAP allows vessels
fishing with trawl gear to fish in a
portion of the Eastern U.S./Canada Area,
including a section of the northern
portion of CA II (the ‘‘triangle’’), under
a Regular B DAS or a Reserve B DAS.
This SAP allows a vessel to utilize a
Category B DAS and fish in the
‘‘triangle,’’ which is not otherwise
accessible. The geographic area remains
unchanged, and the rules that apply
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remain unchanged, with the exception
of the reallocation of the incidental
catch TACs (see Table 5).
When fishing in this SAP, vessels
must fish with either a haddock
separator trawl or a Ruhle Trawl, and
are subject to restrictive possession
limits in order to provide an incentive
to correctly use the specialized trawl
gear to help minimize bycatch of stocks
of concern. Catch of stocks of concern
on trips that end under a B DAS count
toward the incidental catch TACs
specified for pollock, GB cod, GB winter
flounder, and GB yellowtail flounder
(see Table 6). The total amount of these
stocks of concern caught is limited by
these incidental catch TACs and the
program is typically subject to a higher
level of observer coverage than the NE
multispecies fishery at large.
Furthermore, there are specialized rules
that apply when fishing in this SAP,
including those regarding observer
notification, VMS declaration, reporting
requirements, and a no discard
provision.
Modifications to the Regular B DAS
Program. The Regular B DAS Program
was designed to provide opportunities
to target healthy stocks without
threatening stocks for which a mortality
reduction is required. The program
allows the use of Regular B DAS under
restrictions designed to minimize
impacts of stocks of concern. Under this
interim rule, in addition to the
modifications implemented under
Measure 5 under ‘‘Approved
Commercial Measures’’ of the preamble
to this final interim rule (Revisions to
Incidental Catch TACs and Allocations
to Special Management Programs),
several revisions are made to the
Regular B DAS Program in order to
address the current status of stocks and
necessary reductions to F, as well as to
maintain the usefulness of the Regular
B DAS Program. Under current
regulations, the Regional Administrator
has the authority to close the Regular B
DAS Program if it is projected that
continuation of the Regular B DAS
Program would undermine the
achievement of the objectives of the
FMP. In addition to monitoring the
incidental TACs proposed under
Section 5 of the preamble, NMFS will
closely monitor the level of discarding
of stocks that are proposed to have zero
retention, but for which there is no
incidental TAC (i.e., SNE/MA winter
flounder, northern windowpane
flounder, and ocean pout) to ensure that
fishing mortality objectives for all stocks
are not jeopardized.
In order to prevent the quarterly
incidental catch TACs from limiting the
usefulness of the program, any quarterly
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incidental catch TAC that remains
uncaught from quarters one, two, and/
or three will roll over into the
subsequent quarter.
Due to the number of flatfish stocks
that need reductions in F, the use of low
profile (tie-down) gillnets under this
interim action are prohibited on trips
fishing under the Regular B DAS
Program. Within the NE multispecies
fishery, flatfish are traditionally targeted
by reducing the vertical height of
bottom-set gillnets by tying the floatline
of a gillnet to the leadline, or modifying
the construction of the floatline to
reduce or eliminate its buoyancy. Thus,
because most stocks of concern are
flatfish and targeting stocks of concern
is not consistent with the goals of the
Regular B DAS Program, the use of low
profile gillnet gear is prohibited under
this Program. The use of gillnet gear to
catch haddock is still allowed.
Under current regulations, when 100
percent of the Incidental Catch TAC for
white hake has been harvested, vessels
fishing under a Regular B DAS are
prohibited from retaining white hake.
This is in contrast to the rules
pertaining to the other Incidental Catch
TACs in the Regular B DAS Program
whereby, when the TAC is projected to
be harvested, the use of Regular B DAS
is prohibited in the pertinent stock area
for the duration of the quarter. This final
interim rule treats pollock and witch
flounder in the same manner as white
hake. Therefore, when 100 percent of
the Incidental Catch TAC for white
hake, pollock, or witch flounder is
harvested, vessels fishing under a
Regular B DAS will be prohibited from
retaining white hake, pollock, or witch
flounder, respectively. Because white
hake, pollock, and witch flounder have
stock areas that cover the GOM, GB, and
SNE/MA areas, if the harvest of the TAC
were to trigger a shutdown of the
pertinent stock area, the entire Regular
B DAS Program would be shut down.
The Regional Administrator is provided
the authority to modify the pertinent
possession restriction, or implement
other measures, including a partial
closure for the Regular B DAS Program,
in order to prevent excessive discarding
of the stock.
DAS Leasing Program Modifications.
Under this rule, the current prohibition
on leasing DAS between sector and
common pool vessels is eliminated in
order to increase flexibility and
efficiency in the DAS leasing market.
Secondly, the limit on the maximum
number of DAS that a vessel sector and
common-pool vessel may lease is
eliminated. Amendment 13
implemented a restriction that a lessee
may lease Category A DAS in an amount
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up to the vessel’s FY 2001 allocation
(excluding carry-over DAS from the
previous year, or additional DAS
associated with obtaining a Large Mesh
permit). This restriction is removed in
order to increase flexibility and
efficiency in the DAS leasing market.
These mitigation measures, including
the DAS Transfer Program modifications
described below, will also enhance the
likelihood of compliance with the
measures by providing additional
fishing opportunities.
DAS Transfer Program Modifications.
Under this final rule, the DAS
conservation tax is removed from the
DAS Transfer Program. Specifically, the
mandatory reduction of Category A and
B DAS (20 percent), and Category C
DAS (90 percent), will no longer apply
when vessels participate in the DAS
Transfer Program. The Council is
expected to propose modifications to
the DAS Transfer Program in
Amendment 16 in order to provide an
additional incentive to permanently
transfer groundfish DAS, provide for
parity of the DAS Transfer Program with
the DAS Leasing Program, facilitate
consolidation of permits, and provide
flexibility for vessels to mitigate the
negative impacts of DAS reductions and
other management measures. NMFS is
implementing this temporary
modification to the program for the
same reasons the Council is expected to
propose such changes. The limited
duration of the tax-free period (due to
the limited duration of the proposed
interim action) will limit the amount of
any effect the change may have on
increasing the overall DAS use rate.
Monkfish DAS Rules to Mitigate
Impacts of Groundfish Interim Action.
Because vessels with a limited access
Monkfish Category C and D permit are
required to concurrently use a
groundfish DAS in most circumstances,
the differential DAS requirements
implemented by this final rule impact
such vessels. Although vessels fishing
under concurrent monkfish and
groundfish DAS in a differential DAS
area still utilize monkfish DAS at a 1:1
rate, the fact that their groundfish DAS
are used at the rate of 2:1 indirectly
limits the ability for such vessels to fish
for monkfish in the future, because once
a vessel runs out of groundfish DAS,
their ability to fish under a monkfishonly DAS is limited. This final rule
provides economic relief to groundfish
vessels that also possess either a
Category C or D monkfish permit by
allowing these vessels to accrue a
monkfish-only DAS while fishing for
groundfish in a 2:1 differential DAS
counting area.
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For example, a limited access
monkfish Category C or D vessel with 40
groundfish DAS and 31 monkfish DAS
that fished under a monkfish DAS
exclusively in a 2:1 differential DAS
counting area for 20 days would use all
of its 40 DAS groundfish allocation and,
concurrently, 20 DAS of its monkfish
allocation (because monkfish DAS are
counted on a 1:1 basis in the differential
DAS area). Thus, the vessel would have
a remaining balance of 11 monkfish
DAS, and zero groundfish DAS. Without
a regulatory change that allows a vessel
to accrue a monkfish-only DAS while
fishing for groundfish in a 2:1
differential DAS area, once the vessel
used up its groundfish DAS, the vessel
would be unable to fish monkfish-only
DAS and, in this example, the use of the
11 remaining monkfish DAS would
have to be foregone. This action will
restore the ability for the vessel to use
its remaining 11 monkfish DAS, in this
example, because the vessel would be
eligible to receive up to a total of 20
monkfish-only DAS as a result of fishing
in the 2:1 groundfish differential DAS
area. Since the vessel in this example
would only have 11 monkfish DAS left,
its monkfish-only DAS would be capped
at 11. This measure was not included in
the proposed rule, and NMFS is
soliciting comments on this provision.
10. Recreational Measures
This action reduces fishing mortality
on the GOM cod, GB cod, and SNE
winter flounder fisheries for private
recreational vessels fishing in the EEZ
and for federally permitted charter/party
vessels, commensurate with the
reduction proposed for the commercial
fishery. The seasonal prohibition on the
possession of GOM cod for both private
recreational and charter/party vessels is
extended from its current duration of
November through March, to November
through April 15, and a GB cod trip
limit of 10 cod per person per day for
charter/party vessels is implemented,
consistent with the GB cod trip limit for
private recreational vessels. Retention of
winter flounder caught in the SNE/MA
stock area is prohibited for both private
recreational and charter/party vessels.
Recreational vessels in possession of
winter flounder caught outside of the
SNE/MA winter flounder stock area may
transit this area, provided all bait and
hooks are removed from fishing rods,
and any winter flounder on board has
been gutted and stored. Lastly, as a
mitigation measure as further described
above, the minimum size for haddock
caught by recreational vessels fishing in
the EEZ and federally permitted charter/
party vessels is reduced to 18 inches
(45.7 cm).
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11. Revised FY 2009 GB Cod TACs for
Sectors
As highlighted above in Measure 3
under ‘‘Approved Commercial
Measures’’ (‘‘Specification of Target
TACs’’), this final interim rule revises
several of the FY 2009 target TACs
originally proposed for this action.
Because the GB cod target TAC serves
as the basis for calculating the GB cod
TAC allocated to approved sectors, this
final rule also revises the FY 2009 sector
GB cod TAC allocations. Proposed rules
specifying the 2009 GB cod TAC
allocations for both the GB Cod Hook
Sector and the GB Cod Fixed Gear
Sector were published in the Federal
Register on February 10, 2009 (74 FR
6564), and February 12, 2009 (74 FR
7029), respectively. These allocations
were based upon an available U.S. share
of the GB cod TAC of 3,506 mt, and the
proposed interim rule listed the GB Cod
Hook Gear Sector GB cod TAC as 284
mt (based upon an 8.09-percent share of
the U.S. portion of the TAC), and the GB
Cod Fixed Gear Sector GB cod TAC as
408 mt (based upon an 11.64-percent
share of the U.S. portion of the TAC).
Because this final interim rule revises
the overall target TAC for GB cod from
3,506 mt to 4,328 mt, the GB cod
allocations to these sectors are increased
to 350.1 mt for the GB Cod Hook Sector
and 503.8 mt for the GB Cod Fixed Gear
Sector.
12. Extension of the Deadline for Gillnet
Designation
The current regulations at
§ 648.4(c)(2)(iii)(A) require vessels
fishing with gillnet gear to make an
annual designation as either a Day or
Trip gillnet vessel when the vessel is
issued or renews a limited access NE
multispecies permit. Once a vessel has
elected this designation, the vessel may
not change its declaration for the
remainder of the fishing year. As further
explained in Measure 1 under
‘‘Approved Commercial Measures,’’ this
designation dictates the manner in
which DAS are counted for such
vessels. Because these final interim
measures will affect how DAS are
counted during FY 2009, and because
such measures were not known to the
public until after many vessels had
already selected a gillnet designation for
FY 2009, this final interim rule allows
a vessel owner to change the gillnet
designation associated with his/her
permit through June 12, 2009. This
provides additional time for the vessel
owner to review the final interim
measures and revise the gillnet
designation for his/her permit, if
necessary.
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Comments and Responses
Eighty-eight comments were received
during the comment period on the
proposed interim rule and
accompanying EA, from 63 individuals,
11 commercial fishing organizations, 2
state senators, 8 U.S. Senators, 9 U.S.
Congressmen, 2 state resource
management agencies (Massachusetts
Division of Marine Fisheries (DMF) and
the Maine Department of Marine
Resources (DMR)), 2 conservation
organizations, 2 municipalities (New
Bedford, MA, and East Hampton, NY),
and the Council.
Legal Authority for Interim Action
Comment 1: Four members of the
commercial fishing industry, two
organizations representing the
commercial fishing industry (Northeast
Seafood Coalition and Westend
Fisherman’s Association), an
environmental organization (The Pew
Environmental Group), and seven U.S.
Senators stated that there is no legal
requirement for interim measures to
reduce fishing effort to the extent that
the interim rule proposes to do.
Response: Section 305(c) of the
Magnuson-Stevens Act authorizes the
Secretary to implement interim
measures to reduce or address
overfishing if he/she finds that
overfishing exists, as more fully
explained elsewhere in this preamble.
Guidelines to help clarify this authority
(63 FR 24212; May 1, 1998) allow
discretion and flexibility with respect to
the scope and severity of the action.
When proposing the interim measures,
NMFS considered recent stock status
and the need for substantial reductions
in F to help ensure that overfished
stocks remain on their Amendment 13
rebuilding trajectories. However, after
review of public comments, NMFS has
modified the management measures
implemented under this final interim
rule from those that were proposed, to
target stocks in most immediate need of
reductions; e.g., SNE winter flounder,
and northern windowpane flounder; to
reduce negative impacts on fishermen to
the extent practicable in the context of
this interim rule, without jeopardizing
the likelihood of meeting rebuilding
objectives of overfished multispecies
stocks. Because NMFS is not
implementing the proposed expanded
differential DAS accounting in the GOM
and northern portions of GB, and
because this final interim rule replaces
the SNE Closure Area with differential
DAS counting, this final interim rule
will result in smaller F reductions for
several of the stocks than the proposed
measures would have, and will not
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provide as much assurance that
rebuilding goals will be met for
overfished stocks. However, these final
interim measures should not impede
progress of attaining FMP rebuilding
objectives, provided adequate
adjustments, if necessary, are made by
the Council in future years. This is due,
in part, to the fact that several
overfished stocks have extended
rebuilding periods (GB cod—2026,
Atlantic halibut—2058, and CC/GOM
yellowtail flounder—2023), which
allows more time for the stocks to
respond to management. In addition, the
Council has adopted draft rebuilding
programs in Amendment 16 for stocks
recently classified as overfished
(pollock, witch flounder, GB winter
flounder, and northern windowpane
flounder) that will likely set a
rebuilding end-date as 2017 for these
stocks. The measures implemented by
this final interim rule do achieve
substantial reductions in F for the
targeted stocks, including a 62-percent
reduction for SNE/MA winter flounder
and a 39-percent reduction for SNE/MA
yellowtail flounder.
Goal of Interim Action and Magnitude
of Management Measures
Comment 2: Fifty-seven commenters,
including commercial fishermen,
commercial fishing organizations,
municipalities, state fisheries
organizations, and state senators
questioned why such severe interim
restrictions are necessary. Twenty
commenters questioned NMFS’s
justification and compliance with the
Magnuson-Stevens Act, particularly
National Standard (NS) 8. Many
characterized the proposed interim rule
as failing to balance the need to reduce
overfishing and rebuild stocks with the
need to maintain a viable fishery and
infrastructure. Some claimed that NMFS
is ignoring the provisions of the
Magnuson-Stevens Act that provide
flexibility to achieve an appropriate
balance. Others asked what stocks have
collapsed to warrant such extreme
measures.
Response: Based upon the best
available science (GARM III), NMFS
believes substantial reductions in F are
necessary for stocks in most need of
protection in order to ensure that
rebuilding objectives are not
jeopardized. When determining final
management measures for this rule,
NMFS considered the requirements of
the Magnuson-Stevens Act, including
the minimization of adverse economic
impacts, the status of stocks, and the
requirements of the FMP. As stated in
the proposed interim rule, NMFS’s goal
for this interim action is to implement
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measures to reduce overfishing, while
addressing the need to help sustain
fishing communities, without
compromising rebuilding objectives and
statutory rebuilding timelines. Relying
on the additional flexibility inherent in
implementing an interim rule under
section 305(c) of the Magnuson-Stevens
Act, as more fully explained elsewhere
in this preamble, NMFS balanced the
need to reduce overfishing and rebuild
stocks with the need to minimize
adverse impacts on fishing industry
businesses and sustain fishing
communities. However, based on public
comments that the proposed
management measures would create
severe economic hardship, and further
analysis of the impacts of several
additional alternative combinations of
management measures, NMFS is not
implementing the proposed interim
measures of 2:1 differential DAS
counting in the GOM and northern GB
area as this measure was primarily
intended to reduce F on pollock and
witch flounder. Given that there is no
current rebuilding program for pollock,
witch flounder, or northern
windowpane flounder, and that the
Amendment 16 rebuilding programs
likely to be proposed for these stocks
have a rebuilding timeline of 2017,
NMFS believes that there is additional
time for the Council to ensure that
these, and other newly overfished
stocks, are rebuilt as intended under
Amendment 16. Further, given concern
raised by the public regarding the severe
economic impacts that would be
imposed by the SNE Closure Area,
NMFS is not implementing that
proposed measure, but is instead
implementing a modified 2:1
differential DAS counting area, with a
zero landing limit for SNE winter
flounder, to discourage effort on this
stock. As stated in response to Comment
1 above, NMFS believes that, despite
these revisions, the FMP rebuilding
goals are still achievable, although
additional restrictions may likely be
necessary in the future to achieve the
goals.
This action includes several measures
intended to minimize the adverse
economic impacts associated with effort
reduction measures. These include a
reduction in the haddock minimum size
restriction, revisions to the DAS Leasing
Program, elimination of the
conservation tax in the DAS Transfer
Program, continuation of the Eastern
U.S./Canada Haddock SAP,
modifications to the Regular B DAS
Program, and expansion of the CA I
Hook Gear Haddock SAP. As described
in the EA associated with this action,
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these measures should provide
additional flexibility and fishing
opportunity for vessels that would
otherwise not be available.
In summary, in response in public
comments, NMFS, within the limits
associated with implementing an
interim rule under section 305(c) of the
Magnuson-Stevens Act, has made
several changes from the proposed rule
to mitigate negative economic impacts
and address industry concerns regarding
disproportionate impacts of particular
measures, consistent with NS 8. As
described in more detail under the
description of management measures
above, the principal changes from the
proposed rule are as follows: (1)
Replacement of the SNE Closure Area
with 2:1 differential counting in this
area; (2) expansion in time and area of
the CA I SAP; (3) modification of the
rules regarding monkfish DAS to
mitigate unintended impacts of the
existing GOM Differential DAS Area and
the Interim SNE Differential DAS Area;
and (4) modification of how vessels are
charged DAS when fishing inside and
outside of a differential DAS area on the
same trip, i.e., vessels will be charged
DAS based on the area that they are
fishing in.
Comment 3: One commenter asked
how NMFS can reconcile the magnitude
of the impacts of this rule, based on the
status of the stocks, with its October
2007 determination that there was not a
fishery resource disaster.
Response: In 2007, Massachusetts,
New Hampshire, and Maine requested
that NMFS make a determination that
there was a fishery resource disaster
affecting them. NMFS denied those
requests because the statutory
requirements for such a finding were
not met. Although the most recent stock
assessments indicate that many
groundfish stocks are overfished, several
important stocks have recovered, or are
close to recovery. The fact that
substantial reductions in F are still
necessary to rebuild stocks and
eliminate overfishing is not inconsistent
with the 2007 denial of the requests for
a fishery resource disaster declaration.
NMFS’s response to the Commonwealth
of Massachusetts included the
following: ‘‘The National Oceanic and
Atmospheric Administration’s National
Marine Fisheries Service (NMFS) has
carefully analyzed the data regarding
the Massachusetts groundfish fishery
and also the provisions regarding a
commercial fishery failure due to a
fishery resource disaster under
Magnuson-Stevens Act sections 312(a)
and 315. Although we understand that
there has been economic difficulty in
the groundfish-dependent communities
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of Massachusetts and we are very
sympathetic, we find that your request
for a determination of a commercial
fishery failure due to a fishery resource
disaster does not meet the requirements
for such a finding under Sections 312 or
315 of the Magnuson-Stevens Act. Our
latest research shows encouraging
increases in most of the groundfish
stocks including cod, haddock, and
Georges Bank yellowtail. Even though
fishing revenues show some declines,
the commercial fishery itself, although
diminished, has not failed.’’
Evaluation of the Council Proposal for
FY 2009
Comment 4: Twenty-one commenters,
including eight U.S. Senators and nine
U.S. Congressmen, supported adoption
of the Council’s recommended interim
measures. Some commenters questioned
why NMFS disregarded the Council’s
proposal, noting their belief that the
Council proposal is better for fishermen
and the fish, and stating that the
Council proposal would itself cause
economic harm. Many commenters
believed that the Council’s proposal
represents a better bridge to
Amendment 16. Several commenters
claimed that input controls such as DAS
have failed to prevent overfishing and
have increased discarding and foregone
yield, with some supporting the TACpayback provision of the Council’s
proposal, in particular. Three
commenters suggested that NMFS
implement a requirement for all
groundfish vessels to submit daily catch
reports through VMS as a means to
improve reporting and move toward an
output control management system.
Response: As explained in the
response to Comment 2 above, NMFS’s
goal for the interim action is to reduce
F on the groundfish stocks while
minimizing economic impacts to the
extent practicable, without jeopardizing
rebuilding objectives. NMFS carefully
considered the Council’s recommended
alternative, but ultimately rejected it for
several reasons, the principal reason
being that it would not have reduced F
sufficiently to meet NMFS’s goals for 7
of 12 stocks. As part of the EA, NMFS
analyzed the no action alternative as a
proxy for the Council’s alternative using
the closed area model (CAM). The
results indicated that F reductions
achieved by the Council’s alternative
would be insufficient for a number of
stocks (7 of the 12 stocks requiring F
reductions). Subsequent to the
publication of the proposed interim
rule, NMFS analyzed the Council’s
alternative and the results were
essentially the same as the results of the
analysis of the no action alternative.
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After the end of the comment period,
NMFS conducted additional analyses
comparing the Council’s proposed
interim alternative, NMFS’s proposed
measures, and other alternatives. Based
on those analyses, the loss of yield over
time is greater for the measures
recommended by the Council than for
either the measures originally proposed
by NMFS or those implemented by this
final interim rule. Accordingly, the
measures implemented by this interim
action will preserve more TAC for more
stocks in future years than those
recommended by the Council. This
aspect is important in the context of
measures included in draft Amendment
16, as those measures rely heavily upon
TACs to control the fishery in the form
of sector allocations or annual catch
limits and the associated accountability
measures. Finally, deductions of TAC
overharvests in the subsequent fishing
year, as specified in the Council’s
proposal, are outside the possible scope
of this interim action (or any subsequent
interim action during FY 2009), because
the effectiveness of interim actions is
limited to a maximum of 366 days.
NMFS believes that an interim rule is
not the appropriate means to transition
toward a new management structure, or
to implement novel management tools;
it is intended to address short-term
needs to end or reduce overfishing
while the Council is developing longerterm measures for the fishery. NMFS
cannot effectively implement new
measures (such as an expanded VMS
reporting requirement or sector
management) to transition toward a new
management system that has not yet
been decided upon, nor can it build the
foundation for a program that has not
yet been selected by the Council.
Although the Council has stated its
intent to move toward an output-based
management system, and NMFS is
supportive of this goal, the current FMP
controls fishing effort principally
through DAS, in conjunction with trip
limits and closures, and the Council
will need to make transitions to
different approaches through future
amendments to the FMP.
Scientific Basis of Interim Action
Comment 5: Five commenters
expressed concern about the quality of
the data and underlying science and
stock assessments used to develop the
proposed interim rule. Specific
comments related to the level of
uncertainty due to the ‘‘retrospective
patterns’’ associated with some stock
assessments, and the stock size estimate
for SNE/MA winter flounder.
Response: The scientific data upon
which this interim action is based are
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the most recent stock assessments,
referred to as GARM III, which were
conducted from November 2007 through
August 2008. GARM III was a regional,
scientific peer review process for the
purpose of providing benchmark
assessments for the 19 groundfish stocks
managed under the FMP. The
assessments included extensive peer
review from independent scientists. Of
the 14 groundfish stocks assessed in
GARM III based on an analytical
assessment model, 7 stocks exhibited
retrospective patterns that were
considered severe enough that an
adjustment to the population numbers
and fishing mortality in 2007 was
deemed necessary before determining
current stock status and generating stock
projections. The largest retrospective
patterns were observed in GB yellowtail
flounder, GOM winter flounder, and
SNE/MA winter flounder. NMFS agrees
that further work on the nature and
causes of retrospective patterns is
required. Notwithstanding the concerns
regarding retrospective patterns, GARM
III represents the best available science,
and its use is consistent with NS 2. This
was confirmed in a February 17, 2009
Department of Commerce Inspector
General’s report.
Support for Proposed Measures for
Interim Action
Comment 6: One commenter from an
environmental organization (The Ocean
Conservancy) supported the proposed
interim rule and stated that it is
consistent with the current management
regime, comprehensive, and simple. The
commenter noted that the measures fall
short of preventing overfishing in some
cases, advocated hard TAC backstops
for stocks of concern to increase
accountability, and suggested that the
goal should be Frebuild for stocks that
were newly declared overfished. The
commenter also recommended that
NMFS should take strong action in
2009, otherwise the measures necessary
to rebuild stocks after allowing another
year of overfishing will make the
procedural and administrative changes
outlined in draft Amendment 16 much
harder to successfully implement. One
member of the public believed that
NMFS should reduce fishing effort more
than proposed.
Response: NMFS agrees with the
commenter that strong action is
necessary for 2009, but disagrees that
the goal for newly declared stocks
should be Frebuild and that hard TAC
backstops are appropriate for an interim
action. Although NMFS set a goal of
Fmsy in the proposed interim action for
stocks recently declared overfished
(witch flounder, GB winter flounder,
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northern windowpane flounder, and
pollock), the interim action provisions
of the Magnuson-Stevens Act (section
305(c)) do not specifically require that
an interim action end overfishing, but
rather only reduce or address
overfishing as more fully described
elsewhere in this preamble. Despite that
management measures in this final
interim rule have been relaxed from
what the proposed interim rule
measures would have implemented,
NMFS believes that the FMP rebuilding
goals are still achievable, although
additional restrictions in Amendment
16 or other actions will likely be
necessary to achieve such goals.
NMFS analyzed a hard-TAC
alternative, but rejected the alternative
because: (1) It is likely that the TACs for
at least two stocks (GB cod and pollock)
would have resulted in fishery closures
relatively early in each trimester; and (2)
the complexity of a hard TAC
management system and the associated
cost and difficulties in its
implementation to both the fishing
industry and NMFS would make it
impractical, if not impossible, to
successfully and effectively implement
in the short period of an interim action;
and it would possibly be inconsistent
with Magnuson-Stevens Act national
standards and required provisions,
because of disproportionate impacts on
the fishing industry that could result
from such a temporary, short-term
action.
Safety Concerns
Comment 7: Four commenters,
including nine U.S. Congressmen, and
seven U.S. Senators, were concerned
that the proposed interim rule did not
adequately consider safety issues for
small and mid-sized vessels.
Specifically, they believed that the
proposed differential DAS area in the
GOM and GB, and the SNE Closure Area
would create an incentive for vessels to
steam to offshore fishing grounds or
farther from their ports of departure and
therefore be fishing in a less safe
manner than if they were fishing closer
to shore or their home port.
Response: As explained elsewhere in
this preamble, based on public
comment, this action does not
implement the proposed expansion of
the differential DAS counting in the
GOM and GB, or the SNE Closure Area,
and, therefore, largely addresses any
safety issues associated with these two
measures that the public may have been
concerned about. Although NMFS is
implementing 2:1 counting largely in
the same area as the proposed SNE
Closure Area (referred to in the rule as
the ‘‘Interim SNE Differential DAS
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Area’’), this revision would not pose any
additional safety concerns beyond those
already associated with the status quo
GOM Differential DAS Area. NMFS
agrees that differential DAS areas are
among the many factors that confront a
vessel operator in trying to achieve a
profitable fishing trip in a safe manner.
However, modifications to the DAS
Leasing and Transfer Programs
implemented by this interim action may
provide additional DAS necessary for
vessels to fish within the differential
DAS areas and remain closer to shore,
reducing safety concerns associated
with measures implemented by this
action. Finally, because the Interim SNE
Differential DAS Area abuts the
coastline, similar to the status quo GOM
Differential DAS Area, vessels that
declare into this area will be required to
burn 2 DAS for every 1 day fished,
regardless of where they fish on that
trip. This is consistent with the
provisions of the GOM Differential DAS
Area and is based upon the same
rationale offered by the Council when
the GOM Differential DAS Area was
adopted under FW 42.
Mixed-Stock Exception
Comment 8: Four comments were
received, including one from nine U.S.
Congressmen, that suggested that NMFS
should consider the mixed-stock
exception in the NS 1 guidelines to
prevent the depleted condition of one
stock from influencing the management
measures developed for other stocks,
resulting in management measures that
are overly restrictive and reduce yield.
Response: NMFS agrees that, under
the current FMP, the depleted condition
of some stocks result in management
measures that impact non-depleted
stocks due to the commingled nature of
the fishery and the management tools
used, particularly DAS. However, NMFS
disagrees that reliance on the mixedstock exception can provide relief in the
current situation, due to the number and
nature of the particular stocks that are
driving the management measures, and
the constraints and conditions on the
use of the mixed-stock exception in NS
1. The mixed-stock exception provides
a very limited exception, with strict
criteria, for ending overfishing of certain
stocks, but not for rebuilding
requirements and statutory time
requirements. In fact, the new NS 1
Guidelines do not allow the mixed-stock
exception to be used for overfished
stocks. The Magnuson-Stevens Act
mandates rebuilding of overfished
stocks in most cases within 10 years. FY
2009 marks the midpoint of most of the
rebuilding plans implemented under
Amendment 13. Data from GARM III
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indicate that many of the 13 overfished
stocks are substantially below biomass
levels that can produce MSY such that
substantial reductions in F are necessary
to rebuild these stocks by the end of the
rebuilding periods (i.e., by 2014 for
most stocks). Accordingly, these stocks
are not eligible for the mixed-stock
exception and, even if they were,
continuing to subject such stocks to
high levels of fishing effort would
decrease the probability that these
stocks will rebuild within the mandated
timelines without substantial F
reductions within the next few years.
Based on GARM III, the only stocks
that are subject to overfishing, and not
overfished, are GOM cod and the
southern stock of windowpane flounder.
Evaluation of whether these stocks
would meet the threshold criterion for
allowing overfishing does not make
sense in this circumstance, because both
stocks require relatively small F
reductions (21 percent), compared with
most of the other stocks. The current
status of GOM cod and southern
windowpane flounder is not causing a
situation where management measures
designed for these stocks are resulting in
excessively restrictive measures on
other stocks. Nevertheless, this interim
rule will allow overfishing to continue
for the duration of this interim action on
GB cod, witch flounder, pollock, and
northern windowpane flounder under
authority found in section 305(c) of the
Magnuson-Stevens Act, as is more fully
explained elsewhere in this preamble.
Thus, by allowing overfishing on these
stocks, this final interim rule results in
the same type of mitigation of negative
impacts as would result if the mixedstock exception were evoked.
SNE Closure Area
Comment 9: Twenty-eight
commenters supported the proposed
SNE Closure Area, including three
members of the public and four
commercial fishermen. Although several
commenters believed the proposed
closure was a proactive measure, most
stated that such a restriction was long
overdue, and necessary to rebuild the
SNE/MA stock of winter flounder. One
commenter believed that the area
between Nantucket and CA I is
particularly important to protect.
Commenters noted the importance of
winter flounder to the ecosystem and
observed that the SNE winter flounder
stock used to support a vibrant fishery
and was a source of employment for
fishing communities. One commenter
noted that a closure area would provide
the best chance of recovery for the stock.
Another commenter strongly supported
the provision that would allow hook
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17043
vessels to fish in the closure area due to
the selectivity of the gear, and noted
that the closure area does not exclude
fishermen, but only certain gear types.
Five commenters who did not support
the proposed SNE Closure Area
suggested restrictions on the number or
type of gillnets fished and the required
use of specialized trawl gears in order
to reduce catch of winter flounder.
Some commenters expressed concerns
such as an effort shift to targeting
lobsters, and others acknowledged the
economic hardship such a closure
would cause. Suggestions for
modification of the closure area
included reducing the overall size and/
or allowing more access, such as
allowing groundfish vessels to use
roundfish gillnets or tended roundfish
gillnets (provided that winter flounder
are not retained).
Response: NMFS agrees that the
proposed SNE Closure Area would have
afforded protection for winter flounder
and served as an important factor in
rebuilding the SNE/MA stock of winter
flounder. Although the use of
specialized gears may be effective in
reducing the catch of flatfish, including
winter flounder, a requirement for the
use of specialized gear for an interim
action (or limited duration) is not
practical due to the cost of purchasing
such gear and possible lack of
availability. Further, this final action
would implement a differential DAS
area instead of a closure, and does not
exclude gillnet or trawl gear. However,
as explained in the response to
Comment 10, below, NMFS is instead
implementing an expanded differential
DAS area in SNE to mitigate the
economic impacts of the interim action
without unnecessarily compromising
efforts to rebuild overfished stocks. All
commercial and recreational vessels
fishing in the Interim SNE Differential
DAS Area will be subject to a zero
landing limit on SNE winter flounder to
strictly control F for this stock.
Comment 10: Thirty-two commenters,
including commercial fishing
organizations, state fishery management
organizations, and elected officials, did
not support the proposed SNE Closure
Area. The principal concern of 14
commenters was the anticipated
economic impacts. Three commenters
noted that the closure area is important
fishing grounds for 16 vessels, and
predicted a loss of 30 percent of income
for fishermen, with a severe impact on
the ports of Point Pleasant and Belford,
NJ, where the majority of groundfish are
landed in NJ. Several commenters noted
that winter flounder is the only
available groundfish off NJ, and stated
that it is an important component of the
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mix of species targeted. Their concern
was heightened by the potential for
cumulative negative impacts of the
recent regulatory changes in other
fisheries such as the Atlantic scallop
fishery on such vessels. Two
commenters expressed concern
regarding the potential negative
economic impact on the port of New
Bedford, due to its reliance on winter
flounder. Two commenters noted that
there may be disproportionate impact
on small, groundfish-dependent vessels
with home ports near the proposed SNE
Closure Area that are too small, or lack
adequate manpower to transit long
distances and fish in areas outside of the
closure.
Response: Based on its economic
analysis, NMFS agrees that groundfishdependent vessels would be more
severely impacted by the proposed
interim measures than vessels that rely
on groundfish for a lower percentage of
their income, and that vessels that
would have fished for groundfish in the
area of the proposed SNE Closure Area
would be substantially impacted if they
fish with gillnets or trawl gear. For those
vessels that would have been most
impacted by the proposed interim rule,
medium and large boats would be
slightly more impacted than small
vessels; but, in general, the analysis
indicated that the impacts among small,
medium, and large vessels would be
similar. In order to mitigate impacts on
vessels that fish in this geographic area,
but still provide a substantial reduction
in fishing mortality for SNE/MA winter
flounder and other stocks in this area
consistent with rebuilding objectives,
NMFS is implementing 2:1 differential
DAS counting instead of the proposed
closure. In addition to differential DAS
counting, all vessels will be prohibited
from retaining winter flounder
throughout the SNE winter flounder
stock area. Vessels fishing with hook
gear will not be charged DAS at the
differential rate due to the low catch
rates of winter flounder by hook gear.
Although this change from the
proposed rule will not allow vessels to
target or land winter flounder in this
area, there is the potential for vessels to
land other species, such as haddock,
pollock, and cod. This would allow for
at least some groundfish landings from
all gears fishing in this area and reduce
the economic impacts of the interim
measures compared to those anticipated
from the proposed measures. In
addition, this change is likely to reduce
the potential for effort shifts into other
geographic areas or other fisheries by
maintaining a smaller directed fishery
within SNE. The estimated reduction in
F resulting from this change will be
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closer to the objectives of this action
and reduce the amount of lost yield for
several stocks, particularly GB haddock,
SNE/MA yellowtail flounder, American
plaice, and white hake.
Comment 11: Seven commenters,
including DMR, the Monkfish Defense
Fund, and the Garden State Seafood
Association, expressed concern about
potential harmful impacts that the
proposed SNE Closure Area would have
on vessels with limited access Monkfish
Category C and D permits (those with
both a limited access monkfish and a NE
multispecies permit). The commenters
stated that there is a robust monkfish
fishery in the area, and asserted that the
large mesh (10–12 inch (25–30 cm,
respectively)) gear used does not catch
winter flounder or yellowtail flounder
in meaningful quantities. Further, some
asserted that the impact on such vessels
would be unfair because Category A and
B vessels would still be allowed to fish
in the area. One commenter was
concerned about the proposed
exemptions, which would allow other
non-groundfish fisheries to occur in the
proposed closure area.
Response: NMFS agrees that, as
proposed, the SNE Closure Area would
have negatively impacted vessels with a
limited access Monkfish Category C or
D permit, because, under current
groundfish rules, such vessels may not
fish in the SNE Monkfish and Skate
Gillnet Exemption Area (which
overlapped the proposed SNE Closure
Area) unless they are fishing under a
‘‘monkfish only’’ DAS. Because this
final rule does not implement the
proposed SNE Closure Area, NMFS
believes that negative impact on
monkfish Category C and D vessels is
greatly reduced. To avoid further
negative impact on the monkfish fishery
that could occur because Monkfish
Category C and D vessels will use
groundfish DAS at a higher rate in the
differential DAS counting areas (both in
the GOM and SNE), this final rule
allows vessels to fish their additional
monkfish DAS as ‘‘monkfish only’’ DAS.
As explained in detail in Measure 9
under ‘‘Approved Commercial
Measures’’ of the preamble to this rule
(‘‘Mitigating Measures’’), Monkfish
Category C and D vessels fishing in
either the GOM Differential DAS Area or
the Interim SNE Differential DAS Area
will accrue a monkfish-only DAS at the
rate of one monkfish DAS for every two
groundfish DAS used in the differential
areas.
The regulatory exemptions enable
non-groundfish fisheries to continue to
fish in the proposed closure area to
continue, due to the nature of the
exemptions and the restrictions
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associated with the exemptions.
Exempted fisheries are required to
maintain an incidental catch of
regulated species that is less than or
equal to 5 percent of the weight of fish
on board and must not jeopardize
groundfish fishing mortality objectives.
Further, the exemptions and exempted
fisheries have strict limitations that
minimize the potential for adversely
impacting groundfish, including gear,
area, and seasonal restrictions designed
to decrease interaction with groundfish
stocks. Because the closure area has
been revised to a differential DAS
counting area, the concern about
allowing exempted fishery participants
into the SNE Closure Area while
groundfish vessels fishing with certain
gears are excluded should be addressed.
Comment 12: Five commenters were
concerned that the proposed SNE
Differential DAS Area would be
ineffective at achieving its objective of
reducing fishing mortality on winter
flounder, and instead suggested DAS or
trip limits as a better means of
controlling fishing effort. Some
commenters believed that overfishing is
not responsible for the depleted status
of winter flounder, but instead
attributed the low stock size to habitat
loss; or predation by striped bass, spiny
dogfish, or gray seals.
Response: NMFS acknowledges that
the proposed SNE Closure Area would
not have completely eliminated F on
winter flounder, because the potential
for unavoidable bycatch of winter
flounder from other fisheries, although
limited, would result in some level of
fishing mortality on this stock. Both
DAS and trip limits have advantages
and disadvantages as management tools.
DAS restrictions such as differential
DAS counting will allow more fishing
opportunity in the area than a closure,
but, depending upon a vessel’s DAS
allocation and its ability to lease DAS,
such measures may not cause a
particular vessel to reduce its fishing
effort in the geographic area proposed
for the 2:1 DAS counting. Overall,
however, such measures do reduce
fishing effort and are effective at
reducing F on stocks predominantly
caught in a particular area. Trip limits
can be effective at limiting a vessel’s
catch of a particular species, and may
influence fishing behavior, but can
cause regulatory discarding or highgrading. As explained in the response to
Comment 10, NMFS modified the
measures of this interim rule from those
originally proposed. This final rule
implements a differential DAS counting
area in SNE in order to reduce F on
SNE/MA winter flounder and other
stocks in the area that also require
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reductions in F. In addition, this rule
implements a zero retention limit for
SNE/MA winter flounder to further
reduce F on this stock. Thus, in
conjunction with the overall DAS
reduction, NMFS has relied upon DAS
and trip limits to reduce F on SNE
winter flounder to the extent possible,
short of the proposed closure area.
Although this measure does not reduce
fishing mortality on SNE/MA winter
flounder to a level necessary for
rebuilding (which is an F of zero), it
does end overfishing on this stock.
Further restrictions may be needed in
Amendment 16 to reduce F in this stock
to a level consistent with rebuilding
objectives.
With respect to whether there are
other factors responsible for the
depleted status of the stock, the major
non-fishing impact that has been
identified and documented is a
correlation between warmer winter/
early spring water temperatures and
increased predation on winter flounder
larvae by Crangon shrimp and some
other planktonic predators. These
factors may have negatively impacted
recruitment levels since the early 1990s.
Notwithstanding environmental factors,
fishing mortality has been, and remains
at a level that is not sustainable, and not
compatible with stock rebuilding. Thus,
further reductions in fishing effort are
necessary to rebuild this stock, as
required by the Magnuson-Stevens Act.
Interim Differential DAS Area
Comment 13: Five comments,
including one from a commercial
fishery organization (Associated
Fisheries of Maine), suggested that the
DAS reduction proposed by the interim
rule, including that from the Interim
Differential DAS Area, is too drastic and
that the Interim Differential DAS Area is
larger than necessary to achieve the
target fishing mortality reductions,
resulting in loss of optimum yield (OY)
in the fishery. One respondent indicated
that, because the proposed Interim
Differential DAS Area is so large, there
would be no incentive for vessels to fish
outside of the area, resulting in
increased F on species within the area
such as GOM cod.
Response: Because many of the stocks
managed by the FMP co-occur, and
much of the fishing gear used to harvest
groundfish stocks is limited in its ability
to selectively target particular stocks, it
is very difficult to design management
measures that precisely achieve
different conservation objectives for
every stock. Management measures
designed to achieve a particular F
reduction for one stock will likely
achieve larger than necessary reductions
in F for other stocks. DAS, one of the
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principal tools of the FMP controlling
fishing effort in the fishery, is a difficult
and often blunt tool with which to target
F reductions on specific stocks.
As explained elsewhere in this
preamble, including in the response to
Comments 2 and 10, NMFS is not
implementing the proposed interim
measures of an expanded differential
DAS area in the GOM and northern
portions of GB based upon public
comment and additional analysis.
Although the revised measures
implemented by this final interim rule
do not achieve the target F reductions
for all stocks, these measures achieve
substantial F reductions for all stocks,
particularly those that are severely
overfished, including SNE/MA winter
flounder and SNE/MA yellowtail
flounder. In addition, according to the
analysis conducted to support this
action, the measures implemented by
this final interim rule are expected to
result in more yield of all stocks than
the measures included in the proposed
interim rule. Finally, this analysis
suggests that measures implemented by
this final interim rule are not likely to
result in additional shifts in effort and
will not increase F on stocks such as
GOM cod.
Comment 14: Ten comments,
including those from two commercial
fishery organizations (Northeast Seafood
Coalition and Associated Fisheries of
Maine), suggested that fishing effort will
shift inshore because the size of the
proposed Interim Differential DAS Area,
which includes all of the GOM and
northern portions of GB, limits the areas
not subject to differential DAS counting.
Four commenters indicated that this
would increase fishing pressure on
GOM cod, CC/GOM yellowtail flounder,
and winter flounder stocks, as well as
discards of other stocks, possibly
resulting in more onerous regulations
for FY 2010. One individual
recommended that no changes should
be made to existing differential DAS
areas and believed that shifting effort
inshore as part of the interim action
would result in reduced yield of
offshore stocks.
Response: As noted above in the
discussion of Comment 13, this final
interim rule does not implement the
proposed Interim Differential DAS Area,
but rather maintains the existing GOM
Differential DAS Area and an expanded
differential DAS area in SNE. Analysis
of these measures utilized the CAM,
which estimates shifts in fishing effort
to maximize vessel profit in response to
management measures. This analysis
indicates that the measures
implemented by this final interim rule
would not increase F on inshore stocks,
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but would continue to decrease F on
GOM cod, CC/GOM yellowtail flounder,
and GOM winter flounder. By
maintaining the existing GOM
Differential DAS Area closer to shore,
yield of offshore stocks will not likely
be reduced by this interim action.
NMFS acknowledges that more
onerous restrictions may be necessary in
FY 2010 and beyond to ensure that
stocks rebuild within established
rebuilding timeframes. However, even
though the revised measures
implemented by this final interim rule
are less restrictive than those originally
proposed and may not achieve Frebuild
or Fmsy for all stocks, such measures
continue to reduce F on all stocks and
would help continue to rebuild
overfished stocks.
Comment 15: One individual
recommended that the interim action
should be revised to only charge DAS at
a rate of 2:1 for the time spent within
the Interim Differential DAS Area,
suggesting that VMS has the capacity to
support such a measure, as reflected in
the measures for the SNE Differential
DAS Area implemented under FW 42.
Response: NMFS acknowledges that
VMS has the capacity to identify the
time a vessel spends in particular areas
and could implement the
recommendations made by the
commenter. However, NMFS is
concerned that failing to charge DAS at
a rate of 2:1 for the entire trip, regardless
of area fished, would undermine the
effectiveness of this measure by
allowing vessels to fish for short
durations within the differential DAS
areas on their return to port and,
thereby, minimize the resulting DAS
charge. This was the rationale provided
in the Council’s recommendation on
how to count DAS in the GOM
Differential DAS Area implemented
under FW 42. As a result, this final
interim rule does not change the manner
in which the differential DAS counting
rate is applied in the GOM, but adopts
the same approach for the Interim SNE
Differential DAS Area based upon the
same rationale.
Comment 16: Three individuals,
including one commercial fishery
organization (Associated Fisheries of
Maine), recommended that, in lieu of
differential DAS counting in the GOM
and northern portions of GB, the F
objectives of the interim action would
be better achieved by implementing trip
limits on particular stocks, including
witch flounder and pollock, and
reducing the trip limit for GB cod. In
addition, the representative from the
DMR recommended implementing zero
possession limits for SNE/MA winter
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flounder, ocean pout, and both stocks of
windowpane flounder.
Response: NMFS did not analyze an
alternative that relies solely on trip
limits instead of differential DAS
counting in the GOM because it is
unlikely that reliance upon trip limits
alone would achieve the stated
objectives for the stocks in the GOM.
The Plan Development Team analyzed
the daily trip limits that would be
necessary to achieve the Amendment 16
rebuilding objectives for each stock.
However, that analysis also
incorporated a 24-hour minimum DAS
charge in order to achieve the
conservation objectives for each stock.
Reliance upon a combination of
measures, including DAS as the
principal effort reduction measure, is
necessary to achieve the F reductions
required to rebuild overfished stocks as
much as practicable in this interim
action. Trip limits frequently result in
regulatory discarding and must be
balanced with other measures to
minimize unnecessary bycatch, as
mandated by the Magnuson-Stevens
Act. This interim action implements a
suite of measures, including both
differential DAS counting and trip
limits to reduce F and continue to
rebuild overfished stocks.
One of the objectives of this interim
action is to implement measures that are
consistent, to the maximum extent
practicable, with measures being
considered in the Council’s
development of Amendment 16, the
action that will follow this interim
action. Mirroring the Amendment 16
measures will reduce uncertainty and
impacts associated with transitioning
from interim measures to the long-term
management measures under
Amendment 16. Draft effort-control
measures currently included in
Amendment 16 for non-sector vessels
incorporate differential DAS counting in
four large areas encompassing an area
larger than the Interim Differential DAS
Area and the SNE Closure Area
originally proposed for this interim
action. Although the draft Amendment
16 measures do not include a trip limit
for witch flounder, this final interim
rule implements a trip limit of 1,000 lb
(453.6 kg) per DAS, up to 5,000 lb (2,268
kg) per trip of witch flounder to further
reduce F on this stock based upon
recommendations from the public and
the Council. In addition, both draft
Amendment 16 measures and this
interim action include zero retention
limits for SNE/MA winter flounder and
northern windowpane flounder. This
interim action also includes a zero
possession limit for ocean pout. For
southern windowpane flounder, the
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GOM Differential DAS Area, in
conjunction with the Interim SNE
Differential DAS Area, is sufficient to
achieve the necessary F reductions for
this stock and a zero retention limit for
this stock is unnecessary.
Comment 17: Two individuals,
including one commercial fishery
organization (Associated Fisheries of
Maine) suggested that differential DAS
counting is not needed in the Eastern
U.S./Canada Area due to the existence
of hard TAC management in the area.
Response: NMFS agrees that
differential DAS counting is not
necessary in the Eastern U.S./Canada
Area. As noted above, this final interim
rule does not implement the Interim
Differential DAS Area, as proposed, and,
when replacing the SNE Closure Area
with 2:1 differential DAS counting,
removed differential DAS counting from
that area of the Interim SNE Differential
DAS Area that overlapped with the
U.S./Canada Management Area.
Comment 18: One commercial
fisherman noted an error in the
description of the economic impacts of
the proposed measures in the preamble
of the proposed interim rule. This
commenter indicated that, for vessels
fishing exclusively within the GOM, an
18-percent reduction in DAS combined
with differential DAS counting at a rate
of 2:1 would result in a 59-percent
reduction in available DAS, not 36
percent, as stated in the preamble of the
proposed interim rule.
Response: NMFS acknowledges this
error in the preamble of the proposed
rule, but notes that the impacts were
correctly reported in the EA supporting
this action. The Final Regulatory
Flexibility Analysis developed for this
action and summarized in this preamble
correctly describes the revised impacts
of this action.
CA I Hook Gear Haddock SAP
Comment 19: Eighteen commenters
supported expanding the CA I Hook
Gear Haddock SAP, as requested by the
Council. Supporters noted that an
expansion of the SAP would be an
important means of mitigating the
negative impacts of the interim action
and enable more access to the healthy
stock of GB haddock, while not
undermining the status of GB cod. Some
commenters noted the existence of
pertinent data supporting the contention
that the expanded SAP would be
consistent with the FMP, and wondered
whether an oversight by NMFS had
resulted in its conclusions stated in the
proposed rule. One commenter
estimated that the economic benefits of
the expanded SAP would be tens of
millions of dollars, and another noted
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that it offered mitigation with very little
associated risk. One commenter noted
that the SAP benefits vessels in the 40to 50-ft (18–22-m) range, but not smaller
vessels, due to the distance of the SAP
from shore. Lastly, one commenter was
confused by the calculation of the
haddock TAC.
Response: Pertinent data that support
expanding the CA I Hook Gear Haddock
SAP as recommended were not
available to NMFS prior to the
publication of the proposed rule, but
were brought to the attention of NMFS
during the public comment period by
the Cape Cod Commercial Hook
Fishermen’s Association. This
information includes the results of
research in CA I that has been reviewed
by the Council’s Research Steering
Committee (RSC) and supported in its
May 30, 2007, report. Although the RSC
cautioned against the broad application
of the results of this research outside of
the season and areas tested, a review of
the relevant research, including a
review by the DMF, indicated that catch
rates of haddock with hook gear using
a range of baits was significantly higher
than cod, and that the catch rates of
species in the proposed expanded area
are not higher than in the current SAP.
Based on this information, NMFS is
implementing revisions to the CA I
Hook Gear Haddock SAP, including the
expansion of both the season and the
SAP area in this final interim rule.
NMFS is also prohibiting the use of
squid as bait, based upon recent
research indicating that squid caught
higher amounts of cod than any other
bait, but is soliciting further comments
on this prohibition. The expansion of
this SAP will help mitigate some of the
negative economic impacts of this
action on vessels fishing with hook gear.
The elimination of the rules separating
sector and common-pool vessels into
separate seasons will also provide
additional flexibility for all participants.
Finally, the calculation of the haddock
TAC for this SAP is described in
Measure 6 under ‘‘Approved
Commercial Measures’’ of the preamble
of this final interim rule. However,
further explanation about the derivation
of the formula used to calculate the
haddock TAC for this SAP is available
in the EA supporting FW 42 to the FMP.
Comment 20: One commercial
fisherman requested that, because of the
uncertainty associated with the final
interim measures and when such
measures would be made public, the
final interim rule should allow gillnet
vessels the opportunity to change the
gillnet designation associated with their
permit (i.e., as either a Day or Trip
gillnet vessel) after the permit has been
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issued, citing a similar allowance in a
2002 interim final rule.
Response: NMFS agrees with the
commenter. Since gillnet vessel owners
may have renewed their groundfish
permits and selected a particular gillnet
designation for FY 2009 without
knowledge of the final interim
measures, and because this designation
is effective for the remainder of the
fishing year and defines how gillnet
vessels can operate, NMFS will allow a
vessel owner that has already elected a
gillnet designation prior to May 1, 2009,
to change the gillnet designation
associated with his/her permit through
June 12, 2009. This will provide
additional time for the vessel owner to
review the final interim measures and
revise the gillnet designation for his/her
permit, if necessary.
Comment 21: Two commenters did
not support the termination of the SNE
Winter Flounder SAP because they
asserted that the SAP works to reduce
discarding in the summer flounder
fishery in the spring and fall. Further,
they suggested a requirement that
vessels fishing in the SAP use mesh size
consistent with the FMP.
Response: The SNE/MA Winter
Flounder SAP currently allows a limited
access NE multispecies vessel fishing
for summer flounder west of 72° 30’ W.
long. to retain up to 200 lb (91 kg) of
winter flounder while not under a NE
multispecies DAS, provided the vessel
complies with various restrictions. Due
to the severely depleted status of SNE/
MA winter flounder, and the goal of
reducing F to as close to zero as
practicable, elimination of this SAP is
justified. Although the SAP can be
effective at reducing discarding, the
SAP may also enable limited targeting of
winter flounder. Vessels are more likely
to modify their fishing practices and
attempt to avoid encountering winter
flounder if winter flounder possession is
not allowed.
Comment 22: One commenter stated
that NMFS should prepare an
Environmental Impact Statement (EIS)
in order to analyze the potential impacts
of the alternatives considered, instead of
an EA.
Response: NMFS believes that its
analysis of the impacts of the
alternatives complies with the National
Environmental Policy Act (NEPA).
NEPA provides a mechanism for
identifying and evaluating
environmental impacts associated with
Federal actions, and for considering a
reasonable range of alternatives to avoid
or minimize adverse environmental
impacts. As fully explained in the EA,
NMFS concluded that the preparation of
an EIS for this action is not necessary.
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Comment 23: One commercial
fisherman supported the delayed
opening of the Eastern U.S./Canada
Area until August 1.
Response: NMFS agrees that it is
prudent and consistent with Council
intent to delay the opening of the
Eastern U.S./Canada Area for trawl gear
until August 1, 2009. As fully explained
in the proposed interim rule, a delayed
opening of the Eastern U.S./Canada
Area is intended to maximize the
harvest of cod and other species from
the area by reducing the catch rate of
cod, and avoiding early closure of the
area.
Comment 24: Three comments were
received, including one from the GB
Cod Fixed Gear Sector, one from the GB
Cod Hook Sector, and one from a
commercial fishery organization (Cape
Cod Commercial Hook Fisherman’s
Association), requesting that the interim
action include a provision that would
allow the GB Cod Hook Sector to
transfer or lease GB cod quota to the GB
Cod Fixed Gear Sector. Respondents
cited the substantially reduced FY 2009
target TAC for GB cod and the
likelihood that the GB Cod Fixed Gear
will catch its allocation of that stock and
be shut down prior to the end of FY
2009.
Response: Under the current
regulations, existing sectors are
allocated a portion of the yearly GB cod
TAC based upon the landings histories
of participating vessels. A sector can
only change its share of the GB cod TAC
by adding or removing participating
vessels from its roster. The draft
measures in Amendment 16 include
provisions that would allow the transfer
of sector allocations of particular stocks,
but these provisions have not been
selected as a preferred alternative or
formally adopted by the Council. As
indicated in the response to Comment 4,
NMFS believes that an interim rule is
not the appropriate means to implement
novel management tools such as sector
quota trading; it is intended to address
short-term needs to end or reduce
overfishing while the Council is
developing longer-term measures for the
fishery. Moreover, as detailed above in
Measure 12 under ‘‘Approved
Commercial Measures’’ of this
preamble, because this final interim rule
revises the 2009 GB cod target TAC to
reflect estimated F rather than Fmsy, the
GB cod TAC allocations to both sectors
will increase by 66.1 mt for the GB Cod
Hook Sector and by 95.8 mt for the GB
Cod Fixed Gear Sector. As a result, this
revised measure should help address
the concerns identified by the
commenters.
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DAS Leasing
Comment 25: One commercial
fisherman and one representative of the
GB Cod Fixed Gear Sector opposed the
removal of the DAS leasing cap,
indicating that it would activate latent
effort and undermine the intent of the
interim action to reduce overfishing. In
addition, the respondents objected to
the apparent contradiction between
drastically cutting DAS through
allocation reductions and differential
DAS counting, but increasing the access
to DAS by allowing vessels to lease an
unlimited number of DAS from other
vessels.
Response: NMFS disagrees that the
removal of the DAS leasing cap conflicts
with the objectives of the interim action.
The objectives of this interim action
include ending overfishing and
rebuilding overfished stocks. However,
because effort reductions necessary to
achieve the conservation objectives of
this action impose substantial economic
impacts on the groundfish fishery,
another objective of this interim action
is to mitigate the economic impacts of
effort controls as much as practicable.
Analysis supporting this action
indicates that some vessels, particularly
those with low DAS allocations and
high expenses, will require additional
DAS to remain economically viable.
Because nearly 15 percent of vessels
participating in the DAS Leasing
Program in recent years were limited by
the DAS leasing cap, eliminating this
cap through the interim action would
enable groundfish vessels greater
opportunity to obtain additional DAS
and remain economically viable. In
conjunction with DAS reductions and
differential DAS counting, the measures
implemented by this interim action
would not increase F on overfished
stocks and would achieve both the
conservation and mitigation objectives
of this action.
Comment 26: Representatives of both
the GB Cod Hook and Fixed Gear
Sectors and one commercial fishery
organization (Cape Cod Commercial
Hook Fisherman’s Association)
supported changes to the DAS Leasing
Program to allow sector vessels to lease
DAS to and from non-sector vessels,
citing the limited number of DAS
available to sector vessels and the need
to continue to acquire more DAS to
operate under the DAS system until
sectors could be allocated quota for all
groundfish stocks under Amendment
16.
Response: NMFS agrees. Currently,
sector effort is managed by a hard TAC
on GB cod and by DAS for all other
stocks. Accordingly, sectors are
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impacted by DAS restrictions nearly as
much as common pool vessels. As noted
in the response to Comment 25, analysis
supporting this interim action indicates
that some vessels will need to acquire
additional DAS to remain economically
viable. Because the DAS Leasing
Program already imposes size
restrictions on which vessels can lease
to and from one another, continuing to
prohibit vessels participating in sectors
from leasing to non-sector vessels limits
the pool of DAS available for leasing,
especially considering the fact that
sectors are only restricted by hard TACs
for one stock at this time. Therefore, in
order to increase flexibility and
efficiency in the DAS market and
provide greater access to available DAS,
this interim action allows groundfish
DAS vessels to lease DAS to and from
any other groundfish DAS vessel.
Comment 27: One commercial fishery
organization (West End Fisherman’s
Association) recommended the interim
action implement measures in the
recreational fishery. One party/charter
operator indicated that party/charter
vessels fishing on multiple day trips
will benefit from being able to take
advantage of double bag limits for trips
over 15 hours, but suggested that it was
not supported by any analysis. This
commenter also highlighted that
previous efforts to impose such a bag
limit on party/charter vessels was not
included because it would have resulted
in severe economic impacts to such
operations and noted that similar
measures are currently not being
considered by the Council under
Amendment 16. The party/charter
operator further indicated that the
decrease in size limit for haddock will
not help party/charter vessels operating
on GB, as most haddock are found in
closed areas inaccessible to recreational
vessels.
Response: The measures implemented
by this interim action include
restrictions on the recreational fishery,
namely a daily GB cod bag limit for
party/charter vessels and, for both
private recreational vessels and party/
charter vessels, extension of the closed
season for GOM cod and a possession
prohibition for SNE/MA winter
flounder. NMFS disagrees that the GB
cod bag limit for party/charter vessels is
not supported by any analysis. In fact,
the biological, economic, and social
analyses supporting this provision are
detailed in Sections 17.1, 17.2, and 17.3
of the EA supporting this action,
respectively. The respondent is correct
that the measures proposed under
Amendment 16 may not include a
similar provision, but that does not
mean that the measures included in this
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interim action are unnecessary. In fact,
such measures are necessary to ensure
a similar reduction in F on GB cod
across both the commercial and
recreational fisheries, consistent with
the objectives of this action. Finally,
despite the fact that charter/party
vessels cannot access closed areas on
GB, the reduced haddock size limit is
expected to increase opportunities for
recreational vessels to retain haddock in
all areas open to such vessels. A similar
size reduction for GOM haddock is
proposed under Amendment 16 for
consideration at public hearings.
Comment 28: One commenter stated
that the proposed GB cod TAC was too
low, and noted the economic impacts of
a lower TAC.
Response: Typically, the size of the
GB cod target TAC is set based upon a
projection of the catch that will be
associated with a particular F and stock
size for a given year. As noted in
Measure 3 under ‘‘Approved
Commercial Measures’’ of this
preamble, this final interim rule has
changed the manner in which target
TACs were calculated from that in the
proposed rule. In the case of the GB cod
target TAC for FY 2009, this target TAC
is based upon the F expected to result
from measures implemented by this
action and the GARM III estimation of
stock size for 2009 and is specified as
5,501 mt. Although this is an increase
to the TAC specified in the proposed
rule, it is a decrease in the size of the
TAC relative to the past TACs. This is
due to the reductions in F estimated to
be achieved by measures implemented
by this final interim rule. The estimated
2009 F is lower than the objective set
during the first 5 years of the rebuilding
period. Although the stock size is
increasing, the relatively low estimated
2009 F results in a lower target TAC.
The proposed rule incorrectly stated
that the FY 2009 GB cod TAC would be
3,506 mt, because the Canadian TAC of
1,173 mt had been subtracted. The FMP
precedent for specifying the GB cod
target TAC is to specify the TAC that
corresponds to the whole stock,
including the Canadian portion of the
TAC, resulting in a total GB cod target
TAC of 5,501 mt (4,328 mt available to
U.S. vessels, plus 1,173 mt available to
Canadian vessels) for FY 2009.
Comment 29: Three commenters
believed that the economic analysis
underestimated the economic impacts,
and noted specific concerns regarding
the analysis of impacts on the states of
New York and Maine. One commenter
referenced a break-even analysis that
NMFS had prepared, and noted that
many vessels will not be able to break
even. One commenter stated that the
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revenue analysis is flawed, and one
commenter noted that a 31-percent
reduction in revenue is enough to
destroy most small businesses.
Response: NMFS believes that the
economic analysis provides sufficient
information for decision makers to
compare the potential economic impacts
among alternatives in order to select an
alternative that best complies with the
Magnuson-Stevens Act. The aggregate
economic impacts of the alternatives are
included in the EA, including estimates
of revenue reductions, by state, for each
alternative. For each alternative, the
estimated changes in groundfish trip
revenue and total trip revenue are
provided, and expressed as a percent
change in revenue and the estimated
revenue in dollars by state. As noted
above, this final interim rule
implements measures that are changed
from those in the proposed rule.
Therefore, the estimated economic
impacts reported for the preferred
alternative in the EA prepared for this
action and summarized in this preamble
reflect impacts associated with revised
measures and will not be consistent
with the impacts cited by the
commenters. For example, the original
analysis indicated that, for Maine
groundfish vessels, the average total
revenue would decline by 34 percent
and the estimated total revenue would
be $12,277,101. However, the updated
economic analysis based upon revised
measures indicates that the impacts to
Maine would be a 12.2-percent
reduction in total revenue, and the
revised estimate of total revenue would
be $16,419,523. This revised analysis
indicates that, for New York, groundfish
vessels would see a decline in average
total revenue of about 4.2 percent (6
percent was estimated in the proposed
rule), and the estimated total revenue
would be $13,710,083 ($13,430,633 was
estimated in the proposed rule) under
the measures implemented by this final
interim rule. Although the estimates of
percentage reductions in the EA
represent the best estimation of the
relative amount of revenue reduction
anticipated, the estimated revenue in
dollars, by state, that would result from
each alternative is an underestimation,
because the analysis used only a subset
of the total fishery data due to missing
information.
Comparisons of past economic
analyses of FMP management measures
with the realized economic impacts
have shown that the CAM tends to
overestimate the economic impacts of
management measures. NMFS
acknowledges that an analysis of the
short-term impacts on the regional
economy was not conducted (input/
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output model analysis). An input/
output analysis provides an estimation
of how changes in the economic activity
of a particular industry would affect
other industries from which it
purchases and to which it sells goods
and services. Thus, in addition to
reductions in harvesting revenues, this
analysis captures losses associated with
the commercial fishing industry buying
fewer inputs and the upstream losses
that result from less product being
available to local seafood dealers and
processors. Such secondary and tertiary
impacts are proportional to the direct
impacts on the fishing industry (which
have been estimated), and the lack of an
input/output analysis does not prevent
a reasonable and informed comparison
of management alternatives.
The economic analysis for the
measures implemented by this final
interim rule indicates that the total
reduction in groundfish trip revenue
would be approximately 14.7 percent, or
$14.8 million. Based on the break-even
analysis, NMFS agrees that some small
businesses may not be able to remain
profitable, and many will have to lease
DAS in order to remain profitable.
However, as stated above, the CAM
tends to overestimate revenue
reductions. Vessels typically modify
their fishing behavior in response to
new regulations, and increase fishing
effort on other non-groundfish species.
Some vessels will be able to lease
additional DAS and continue fishing at
a level that produces a similar amount
of revenue as in the past, but at a
reduced profit margin, while other
vessels will either continue to fish at an
economic loss, or cease fishing.
Changes From the Proposed Rule
NMFS has made several changes to
the proposed rule, including changes as
a result of public comment. Some of
these changes are substantive changes,
whereas others are administrative in
nature, clarify new management
measures, or correct inadvertent errors
or omissions in the proposed rule.
These changes are listed below in the
order that they appear in the
regulations.
In § 648.4, paragraph (c)(2)(iii)(C) is
added to allow gillnet vessels that have
already elected a gillnet designation as
a Day or Trip gillnet vessel to change
this designation through June 31, 2009.
In § 648.81, the proposed addition of
paragraph (n) has been removed because
the proposed SNE Closure Area is not
implemented by this final interim rule.
In § 648.82, paragraph (e)(4) has been
revised to retain the existing GOM
Differential DAS Area, rather than
implementing the proposed Interim
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Differential DAS Area and to insert an
additional Interim SNE Differential DAS
Area. In addition, paragraph (e)(4)(iii)
has been revised to include provisions
for applying the differential DAS
counting rate to vessels fishing in either
the GOM Differential DAS Area or the
Interim SNE differential DAS Area,
including measures to reflect that NE
multispecies vessels fishing with hook
gear in the Interim SNE Differential DAS
Area will not be charged DAS at a rate
of 2:1.
In § 648.85, paragraph (a)(3)(viii) has
been revised to reflect revised
declaration requirements associated
with declaring into one or both of the
differential DAS areas defined under
§ 648.82(e)(4). Proposed revisions to
paragraph (b)(7) of this section have
been removed and paragraph (b)(7) has
been suspended in its entirety. Instead,
paragraph (b)(11) has been added in
order to revise the CA I Hook Gear
Haddock SAP regulations to expand the
scope of the SAP in both season and
area, eliminate the split in the season
and TAC between sector and non-sector
vessels, and prohibit the use of squid as
bait. Paragraph (b)(10)(i)(F) has been
revised to reflect the implementation of
differential DAS counting in SNE.
Paragraphs (b)(10)(v)(G) through (I) have
been added to identify the GB yellowtail
flounder, GB winter flounder, and GOM
winter flounder stock areas,
respectively, for the purposes of the
Regular B DAS Program.
In § 648.86, paragraph (l) has been
revised to include references the Interim
SNE Differential DAS Area
implemented under this final interim
rule. In addition, paragraph (m) has
been revised to reflect a new trip limit
for witch flounder instead of a revised
trip limit for white hake. The existing
trip limit for white hake specified at
§ 648.86(e) will remain in effect.
In § 648.92, paragraphs (b)(1)(i),
(b)(1)(iii)(A), (b)(2), and (b)(8)(v) have
been suspended; and paragraphs
(b)(1)(iii)(C), (b)(1)(vi), (b)(8)(vi), and
(b)(10) have been added to mitigate the
impacts of the interim management
measures on the monkfish fishery.
In § 648.95, paragraph (h) has been
suspended and paragraph (i) has been
added to replace reference to paragraph
§ 648.92(b)(2), because that paragraph
has been suspended, and to insert
reference to the newly added
§ 648.92(b)(10).
Classification
NMFS has determined that the
management measures implemented by
this final interim rule are necessary for
the conservation and management of the
NE multispecies fishery, and are
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17049
consistent with the Magnuson-Stevens
Act and other applicable laws.
There is good cause under 5 U.S.C.
553(d)(3) to waive the 30-day delay in
effective date for the measures
implemented by this final interim rule.
This final interim rule would
immediately reduce fishing mortality for
all stocks managed under the FMP in
order to continue to rebuild overfished
stocks. As a result of the January 23,
2009, February 17, 2009, and February
23, 2009, Federal Court Orders in the
case of Commonwealth of
Massachusetts and State of New
Hampshire v. Carlos M. Gutierrez (Civil
Action No.: 06–12110–EFH), several
critical conservation measures in the NE
multispecies fishery have been vacated
for the latter portion of FY 2008. While
the precise impacts of these Court
Orders are unknown at this time, it is
likely that the vacation of these
measures, particularly restrictive trip
limits and differential DAS counting,
caused fishing mortality to increase on
overfished stocks due to increased
fishing effort. Because such increases in
fishing effort occurred during peak
spawning periods for particular
overfished stocks, the impacts of these
Court Orders could affect efforts to
rebuild such stocks. As a result, it is
imperative that interim measures
designed to reduce fishing mortality on
all groundfish stocks be implemented
quickly. In order to avoid unnecessary
confusion about which regulations are
in effect, and, thereby, increase
compliance with, and the effectiveness
of, conservation measures implemented
under this final interim rule, such
measures must become effective by the
start of the fishing year on May 1, 2009.
While this final interim rule implements
measures that will reduce fishing effort
in the NE multispecies fishery, such
measures are necessary to ensure longterm economic benefits associated with
rebuilt stocks. Thus, it would be
contrary to the public interest to delay
the effectiveness of measures
implemented by this final interim rule.
In addition, while NOAA believes
there is sufficient support in the record
to justify the changes between the
proposed and final interim rule, NOAA
nonetheless believes there is good cause
to waive notice and opportunity to
comment on these changes under 5
U.S.C. 553(b)(B). This good cause
waiver is based upon the same reasons
described above concerning the waiver
of the 30-day delay in effective date.
An EA was prepared for this action
that analyzed the environmental
impacts of the measures being
implemented, as well as alternatives to
such measures. This EA was revised
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since the publication of the proposed
rule to include further analysis of
several additional alternative
combinations of management measures.
A copy of the Finding of No Significant
Impact for the EA prepared for this
action is available from the Regional
Administrator (see ADDRESSES).
This final interim rule has been
determined to be significant for the
purposes of Executive Order (E.O.)
12866.
This final interim rule does not
contain policies with Federalism or
‘‘takings’’ implications as those terms
are defined in E.O. 13132 and E.O.
12630, respectively.
Final Regulatory Flexibility Analysis
(FRFA)
NMFS, pursuant to section 604 of the
Regulatory Flexibility Act (RFA),
prepared this FRFA in support of the
measures implemented by this final
interim rule. The FRFA incorporates the
updated economic impacts summarized
in the IRFA, but revised this final
interim rule to account for changes from
the proposed rule measures
implemented by this final action. A
summary of the IRFA was published in
the proposed rule for this action and is
not repeated here. A description of why
this action was considered, the
objectives of, and the legal basis for this
rule are contained in the preamble to
the proposed and this final rule and are
not repeated here. A copy of this
analysis is available from the Regional
Administrator (see ADDRESSES).
Summary of the Issues Raised by Public
Comments in Response to the IRFA
A Summary of the Assessment of the
Agency of Such Issues, and A Statement
of Any Changes Made From the
Proposed Rule as a Result of Such
Comments
Comment A: One commenter
estimated that the economic benefits of
an expanded CA I Hook Gear Haddock
SAP would be tens of millions of dollars
and recommended that NMFS
implement measures to expand this
SAP.
Response: As highlighted in the
response to Comment 19 above, NMFS
has implemented several revisions to
the CA I Hook Gear Haddock SAP
through this final interim rule. Because
this final interim rule would
substantially increase both the size and
extend the season of this SAP, it is
unclear how such revisions would affect
participation in this SAP. It is likely that
participation would increase in both the
number of participants and the number
of fishing trips throughout the expanded
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season. As a result, it is difficult to
accurately predict the economic impacts
associated with this measure.
Qualitatively, the economic impacts are
likely to be positive, as this measure
provides greater access to available
haddock resources and at a higher catch
rate than would otherwise be
experienced outside of the SAP because
of its location within CA I.
Comment B: As highlighted in
Comment 29 above, three commenters
believed that the economic analysis
underestimated the economic impacts of
the proposed measures, highlighted
specific concerns regarding the analysis
of impacts on New York and Maine, and
noted that many vessels will not be able
to break even. One commenter stated
that the revenue analysis is flawed and
one commenter noted that a 31-percent
reduction in revenue is enough to
destroy most small businesses.
Response: The response to Comment
29 explains that economic impacts were
underestimated due to missing data and
the fact that an analysis of secondary
and tertiary economic impacts of the
proposed measures on other industries
that interact with the fishing industry
was not conducted. However, when
compared to assessments of economic
impacts associated with previous
actions, the estimated economic impacts
to the directed fishery often
overestimated realized impacts.
Description of and Estimate of the
Number of Small Entities to Which the
Final Interim Rule Would Apply
The Preferred Alternative would
affect regulated entities engaged in
commercial fishing for groundfish and
entities that provide recreational fishing
services to anglers. These entities
include any vessel that has been issued
either an open access or a limited access
Federal permit under the FMP. During
FY 2007, 2,822 vessels were issued
commercial limited access and open
access NE multispecies permits. Of
these, only 739 actually landed
groundfish. A total of 762 NE
multispecies party/charter permits were
issued during FY 2007. Additionally,
limited access permit holders (1,525
during FY 2007) may take passengers for
hire, but do not possess a party/charter
permit, since the FMP prohibits issuing
both an open access and a limited
access permit to the same vessel. Of the
762 vessels issued an open access party/
charter permit, only 128 reported taking
at least one for-hire trip, and only 74
reported keeping groundfish on one or
more trips.
The size standard for commercial
fishing entities is $4 million in sales,
while the size standard for party/charter
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operators is $7 million in sales.
Available data indicate that, based on
2005–2007 average conditions, median
gross sales by commercial fishing
vessels were just over $200,000, and no
single fishing entity earned more than
$2 million. Available data are not
adequate to identify affiliated vessels, so
each operating unit is considered a
small entity for purposes of the RFA.
For regulated party/charter operators,
the median value of gross receipts from
passengers was just over $9,000, and did
not exceed $500,000 in any year during
2001 to 2007. Therefore, all regulated
commercial fishing and all regulated
party/charter operators are determined
to be small entities under the RFA, and,
accordingly, there are no differential
impacts between large and small entities
under this rule. The remaining
discussion describes the number of
regulated entities, the number of
participating regulated entities, and the
potential economic impacts on
participating regulated entities for
party/charter operators and for
commercial fishing vessels.
Description of the Projected Reporting,
Recordkeeping, and Other Compliance
Requirements of This Final Interim Rule
This final interim rule contains
collection-of-information requirements
that have previously been subject to
review and approval by OMB under
control number 0648–0202 and
0648.0212. Public reporting burden for
these collections of information are
estimated as follows:
1. VMS purchase and installation,
OMB# 0648–0202 (1 hr/response);
2. VMS proof of installation, OMB#
0648–0202 (5 min/response);
3. Automated VMS polling of vessel
position, OMB# 0648–0202 (5 sec/
response);
4. Declaration of intent to participate
in the Regular B DAS Program, or fish
in the U.S./Canada Management Areas
and any associated SAPs, and the DAS
type to be used via VMS prior to each
trip into the one of these programs,
OMB# 0648–0202 (5 min/response);
5. Notice requirements for observer
deployment prior to every trip into the
Regular B DAS Program or the U.S./
Canada Management Areas and
associated SAPs OMB# 0648–0202, (2
min/response);
6. Standardized catch reporting
requirements while participating in the
Regular B DAS Program, the CA I Hook
Gear Haddock SAP, or the U.S./Canada
Management Area and its associated
SAPs, OMB# 0648–0212 (15 min/
response);
7. Standardized reporting of Universal
Data I.D. while participating in the
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Regular B DAS Program or fishing in the
U.S./Canada Management Area,
associated SAPs, and CA I SAP, OMB#
0648–0212 (15 min/response);
8. DAS ‘‘flip’’ notification via VMS for
the Regular B DAS Program, OMB#
0648–0202 (5 min/response);
9. Sector Manager daily reports for CA
I Hook Gear Haddock SAP, OMB# 0648–
0212 (2 hr/response);
10. DAS Leasing Program application,
OMB# 0648–0202 (10 min/response);
11. DAS Transfer Program
application, OMB# 0648–0202 (10 min/
response); and
12. Declaration of intent to fish inside
and outside of the Eastern U.S./Canada
Area on the same trip, OMB# 0648–0202
(5 min/response).
13. Declaration of area and gear via
VMS when fishing under a NE
multispecies DAS, OMB# 0648–0202 (5
min/response); and
14. Declaration of entry into the GOM
and SNE Differential DAS Area when
not fishing or transiting via VMS, OMB#
0648–0202 (5 min/response).
These estimates include the time for
reviewing instructions, searching
existing data sources, gathering and
maintaining the data needed, and
completing and reviewing the collection
of information. Send comments
regarding these burden estimates or any
other aspect of this data collection,
including suggestions for reducing the
burden, to NMFS (see ADDRESSES) and
by e-mail to
David_Rostker@omb.eop.gov, or fax to
202–395–7285.
Notwithstanding any other provision
of the law, no person is required to
respond to, and no person shall be
subject to penalty for failure to comply
with, a collection of information subject
to the requirements of the PRA, unless
that collection of information displays a
currently valid OMB control number.
Description of Steps the Agency Has
Taken To Minimize the Significant
Economic Impact on Small Entities
Consistent With the Stated Objectives of
Applicable Statutes
During the development of this final
interim rule, NMFS considered and
fully analyzed five alternatives,
including the no action alternative, a
differential DAS alternative, a DAS
reduction and closed area alternative,
the original proposed measures, and the
measures implemented by this final
interim rule. Three other alternatives
were considered, but rejected, including
the measures recommended by the
Council, an expanded Regular B DAS
Program alternative, and a hard TAC
alternative. The reasons behind rejecting
the Council’s preferred alternative are
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explained in the preamble of the
proposed interim rule and further
discussed in the response to Comment
4 above. The expanded Regular B DAS
Program alternative was rejected
because it would have required vessels
to use specialized nets that would have
been costly to acquire. In addition, this
alternative would have resulted in
unnecessary loss of yield from several
groundfish stocks. The hard TAC
alternative was an attempt to increase
the effectiveness of the Council’s
recommended measures. However, this
alternative was rejected because it
would likely have resulted in early
closure of the fishery and would have
been complex, costly, and impractical to
implement for the short duration of an
interim action.
In response to comments emphasizing
the economic impacts of the proposed
measures, NMFS partially analyzed
three additional alternatives that
included various combinations of
differential DAS areas, closure areas,
and trip limits in order to minimize the
economic impacts of this action without
compromising the ability of the fishery
to achieve the long-term rebuilding
objectives in the FMP. One of these
alternatives was selected as the
preferred alternative for this action and
is implemented by this final interim
rule. As discussed in the responses to
comments, the measures implemented
by this final interim rule reduce F on all
stocks, but do not achieve the F
objectives for GB cod and witch
flounder. However, this will not
compromise the ability of the fishery to
rebuild overfished stocks, provided
additional measures to end overfishing
and rebuild overfished stocks are
implemented through future
management actions, as necessary.
While the no action alternative would
result in the fewest economic impacts (a
reduction of total trip revenue of
approximately 7.7 percent, or $12.2
million, and a reduction of groundfish
trip revenue of 12.1 percent, or $12.2
million), that alternative would also
achieve the least amount of reduction in
F. In contrast, the measures
implemented by this final interim rule
would result in substantially higher
reductions in F for some stocks, while
minimizing reductions in both
groundfish and total revenue than the
other alternatives considered. It is
estimated that these measures would
achieve much lower reductions in both
total trip revenue (a reduction of 9.4
percent, or $14.8 million) and
groundfish trip revenue (a reduction of
14.7 percent, or $14.8 million) when
compared to the other three alternatives
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17051
considered, including the originally
proposed measures (see the
Classification section of the preamble of
the proposed interim rule for a full
discussion of the economic impacts
associated with those alternatives). This
is true across all states. This action is
expected to result in positive economic
impacts to vessels operating out of New
Jersey due to the replacement of the
existing SNE Differential DAS Area with
the Interim SNE Differential DAS Area.
In addition, the measures implemented
by this action achieve a higher yield
from several groundfish stocks as a
result of higher landings than the other
alternatives. As noted in the response to
Comment 4, preserving future yield in
the fishery becomes increasingly
important as the fishery moves toward
quota-driven management regimes such
as sector management, as proposed in
draft Amendment 16, and annual catch
limits mandated by the recent revision
to the Magnuson-Stevens Act.
In addition to revisions designed to
continue to reduce overfishing, this
action also implements a number of
measures intended to mitigate the
economic impacts of effort reductions
associated with conservation measures.
These measures include revisions to the
DAS Leasing and Transfer Programs,
modifications to the Regular B DAS
Program, continuation of the Eastern
U.S./Canada Haddock SAP, expansion
of the CA I Hook Gear Haddock SAP in
both area and season, and a reduction in
the minimum size of haddock for both
recreational and commercial vessels.
Modifications to the DAS Leasing
Program attempt to remove
administrative barriers that would
unnecessarily limit the ability of vessels
to lease DAS to one another. This
increases flexibility and efficiency in
the program by providing greater
opportunities for vessels to acquire and
sell DAS to other similar-sized vessels.
In addition, analysis indicates that 15
percent of vessels participating in the
DAS Leasing Program were affected by
the DAS leasing cap in FY 2007.
Elimination of this cap through this
final interim rule eliminates that
restriction and will help enable vessels
to acquire sufficient DAS to remain
economically viable. Modifications to
the DAS Transfer Program eliminate the
DAS conservation tax. This is expected
to encourage transfers and will likely
result in more efficient operations, as
vessel owners could combine DAS and
other fishing permits from multiple
vessels onto one operational platform.
Revisions to the Regular B DAS
Program, including the redistribution of
incidental catch TACs and quarterly
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TAC roll-over, are intended to increase
the efficiency of the program and
provide more opportunities for vessels
to take advantage of this program.
Because the original intent of the
Regular B DAS Program was to
encourage the selective harvest of
healthy stocks while minimizing the
catch of overfished stocks, increasing
participation in this program is one
additional means of accomplishing the
dual objectives of this action: Ensuring
continued progress toward rebuilding
overfished stocks while mitigating the
economic impacts to the extent
practicable. Measures to expand the CA
I Hook Gear Haddock SAP would also
contribute toward achieving these two
objectives by greatly increasing
opportunities to harvest the abundant
haddock resource on GB using gear
proven to selectively harvest this stock,
while minimizing the bycatch of cod.
The extension of the season from 3
months to 9 months also enables vessels
to take advantage of market conditions
to maximize economic return on trips
into this SAP. Finally, although slower
growth rates delayed recruitment of
recent large year classes of haddock into
the fishery, most of these fish have
reached sizes susceptible to capture by
existing mesh sizes. This action reduces
the minimum size limit for haddock
from 19 inches (48.3 cm) to 18 inches
(45.7 cm) to increase yield from this
species and increase revenue in the
groundfish fishery.
In summary, the measures
implemented by this action attempt to
strike a balance, under the authority of
section 305(c) of the Magnuson-Stevens
Act, between continuing efforts to
reduce overfishing and rebuild
overfished stocks and minimizing
economic impacts to affected entities, as
required by the Magnuson-Stevens Act
and other applicable law. While this
action does not implement measures
that would, by themselves, achieve all
of the mortality objectives outlined in
the preamble, together with measures in
draft Amendment 16 and potential
future actions, these measures will
assist the fishery to meet the
requirements to rebuild overfished
stocks and maintain participation of
fishing communities in the groundfish
fishery, as required by the MagnusonStevens Act, during the transition to
more sustainable fishing practices in
future years, without jeopardizing
rebuilding objectives.
Section 212 of the Small Business
Regulatory Enforcement Fairness Act of
1996 states that, for each rule or group
of related rules for which an agency is
required to prepare a FRFA, the agency
shall publish one or more guides to
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assist small entities in complying with
the rule, and shall designate such
publications as ‘‘small entity
compliance guides.’’ The agency shall
explain the actions a small entity is
required to take to comply with a rule
or group of rules. As part of this
rulemaking process, a letter to permit
holders that also serves as the small
entity compliance guide (the guide) was
prepared. Copies of this final rule are
available from the Northeast Regional
Office (see ADDRESSES), and the guide,
i.e., permit holder letter, will be sent to
all holders of permits for the
multispecies and monkfish fisheries.
The guide and this final rule will be
available upon request.
List of Subjects in 50 CFR Part 648
Fisheries, Fishing, Reporting and
recordkeeping requirements.
Dated: April 6, 2009.
James W. Balsiger,
Acting Assistant Administrator for Fisheries,
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 § 648.4, paragraph (c)(2)(iii)(A) is
suspended and paragraph (c)(2)(iii)(C) is
added to read as follows:
■
§ 648.4
Vessel permits.
*
*
*
*
*
(c) * * *
(2) * * *
(iii) * * *
(C) For vessels fishing for NE
multispecies with gillnet gear, with the
exception of vessels fishing under the
Small Vessel permit category, an annual
declaration as either a Day or Trip
gillnet vessel designation as described
in § 648.82(j). A vessel owner electing a
Day or Trip gillnet designation must
indicate the number of gillnet tags that
he/she is requesting, and must include
a check for the cost of the tags. For the
2009 fishing year, a vessel owner that
has already elected this designation
prior to May 1, 2009, may change this
designation through June 12, 2009. For
the 2009 fishing year only, a vessel may
fish under more than one gillnet
category. A permit holder letter will be
sent to the owner of each eligible gillnet
vessel, informing him/her of the costs
associated with this tagging requirement
and providing directions for obtaining
tags. Incomplete applications, as
described in paragraph (e) of this
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section, will be considered incomplete
for the purpose of obtaining
authorization to fish in the NE
multispecies gillnet fishery and will be
processed without a gillnet
authorization.
*
*
*
*
*
■ 3. In § 648.14:
■ A. Paragraphs (a)(50), (53), (121),
(129), (130), (132), (146), (153), (165),
(173) through (175), and (177) are
suspended.
■ B. Paragraphs (c)(7), (23) through (26),
(33), (39), (50), (51), (57) through (78),
(81) through (83), (85), (86), (88), and
(89) are suspended.
■ C. Paragraphs (g)(4) and (5) are
suspended.
■ D. Paragraphs (a)(181) through (188),
(c)(90) through (134), and (g)(6) and (7)
are added.
The additions read as follows:
§ 648.14
Prohibitions.
*
*
*
*
*
(a) * * *
(181) Enter or fish in the Western
U.S./Canada Area or Eastern U.S./
Canada Area specified in § 648.85(a)(1),
unless declared into the area in
accordance with § 648.85(a)(3)(viii).
(182) If declared into one of the areas
specified in § 648.85(a)(1), fish during
that same trip outside of the declared
area, unless in compliance with the
applicable restrictions specified under
§ 648.85(a)(3)(viii)(A) or (B).
(183) Fail to notify NMFS via VMS
prior to departing the Eastern U.S./
Canada Area, when fishing inside and
outside of the area on the same trip, in
accordance with § 648.85(a)(3)(viii)
(A)(1).
(184) When fishing inside and outside
of the Eastern U.S./Canada Area on the
same trip, fail to abide by the most
restrictive DAS counting, trip limits,
and reporting requirements that apply,
as described in § 648.85(a)(3)(viii)(A).
(185) If fishing inside the Eastern
U.S./Canada Area and in possession of
fish in excess of what is allowed under
the most restrictive regulations that
apply outside of the Eastern U.S./
Canada Area, fish outside of the Eastern
U.S./Canada Area on the same trip, as
prohibited under § 648.85(a)(3)(viii)(A).
(186) Fail to comply with the
reporting requirements under
§ 648.85(a)(3)(viii)(A)(2) when fishing
inside and outside of the Eastern U.S./
Canada Area on the same trip.
(187) If fishing with trawl gear under
a NE multispecies DAS in the Eastern
U.S./Canada Area defined in
§ 648.85(a)(1)(ii), fail to fish with a
haddock separator trawl, flounder trawl
net, or Ruhle trawl, as specified in
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§ 648.85(a)(3)(ix) and (b)(10)(iv)(J)(3),
unless otherwise allowed under the
Eastern U.S./Canada Haddock SAP rules
in § 648.85(b)(8)(v)(E).
(188) Possess, land, or fish for
regulated species while in possession of
scallop dredge gear on a vessel not
fishing under the scallop DAS program
as described in § 648.53, or fishing
under a general scallop permit, unless
the vessel and the dredge gear conform
with the stowage requirements of
§ 648.23(b), or unless the vessel has not
been issued a multispecies permit and
fishes for NE multispecies exclusively
in state waters.
*
*
*
*
*
(c) * * *
(90) If fishing under the Eastern U.S./
Canada Haddock SAP, fish for, harvest,
possess, or land any regulated NE
multispecies from the area specified in
§ 648.85(b)(8)(ii), unless in compliance
with the restrictions and conditions
specified in § 648.85(b)(8)(v)(A) through
(M).
(91) If fishing under a Category B DAS
in the Closed Area II Yellowtail
Flounder SAP specified in
§ 648.85(b)(3), the Regular B DAS Pilot
Program specified in § 648.85(b)(10), or
the Eastern U.S./Canada Haddock SAP
Pilot Program specified in
§ 648.85(b)(8), remove any fish caught
with any gear, including dumping the
contents of a net, except on board the
vessel.
(92) Possess or land per trip more
than the possession or landing limits
specified under §§ 648.86(a), (c), (e), (g),
(h), (j), (l), (m), and (n) and 648.82(b)(5)
and (6), if the vessel has been issued a
limited access NE multispecies permit
or open access NE multispecies permit,
as applicable.
(93) Fail to declare through VMS the
intent to be exempt from the GOM cod
trip limit under § 648.86(l)(1), as
required under § 648.86(l)(4), or fish
north of the exemption line if in
possession of more than the GOM cod
trip limit specified under § 648.86(l)(1).
(94) Enter port, while on a NE
multispecies DAS trip, in possession of
more than the allowable limit of cod
specified in § 648.86(l)(1), unless the
vessel is fishing under the cod
exemption specified in § 648.86(l)(4).
(95) For vessels fishing in the NE
multispecies DAS program under the
provisions of § 648.10(c), the call-in
system, fail to remain in port for the
appropriate time specified in
§ 648.86(l)(1)(ii)(A), except for transiting
purposes, provided the vessel complies
with § 648.86(l)(3). For vessels fishing in
the NE multispecies DAS program
under the provisions of § 648.10(b), the
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VMS system, fail to declare through
VMS that insufficient DAS have elapsed
in order to account for the amount of
cod on board the vessel as required
under § 648.86(l)(1)(ii)(B).
(96) Enter port, while on a NE
multispecies DAS trip, in possession of
more than the allowable limit of cod
specified in § 648.86(l)(2).
(97) For vessels fishing in the NE
multispecies DAS program under the
provisions of § 648.10(c), the call-in
system, fail to remain in port for the
appropriate time specified in
§ 648.86(l)(2)(ii)(A), except for transiting
purposes, provided the vessel complies
with § 648.86(l)(3). For vessels fishing in
the NE multispecies DAS program
under the provisions of § 648.10(b), the
VMS system, fail to declare through
VMS that insufficient DAS have elapsed
in order to account for the amount of
cod on board the vessel as required
under § 648.86(l)(2)(ii)(B).
(98) Discard legal-sized NE regulated
multispecies, ocean pout, Atlantic
halibut, or monkfish while fishing
under a Regular B DAS in the Regular
B DAS Program, as described in
§ 648.85(b)(10)(iv)(E).
(99) If fishing under a Regular B DAS
in the Regular B DAS Program, fail to
comply with the DAS flip requirements
of § 648.85(b)(10)(iv)(E) if the vessel
harvests and brings on board more than
the landing limit for a groundfish stock
of concern specified in
§ 648.85(b)(10)(iv)(D), other groundfish
specified under § 648.86, or monkfish
under § 648.94.
(100) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
to comply with the requirements and
restrictions specified in
§ 648.85(b)(10)(iv)(A) through (F), (I),
and (J).
(101) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
to comply with the VMS requirement
specified in § 648.85(b)(10)(iv)(A).
(102) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
to comply with the observer notification
requirement specified in
§ 648.85(b)(10)(iv)(B).
(103) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
to comply with the VMS declaration
requirement specified in
§ 648.85(b)(10)(iv)(C).
(104) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
to comply with the landing limits
specified in § 648.85(b)(10)(iv)(D).
(105) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
to comply with the no discard and DAS
flip requirements specified in
§ 648.85(b)(10)(iv)(E).
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17053
(106) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
to comply with the minimum Category
A DAS and Category B DAS accrual
requirements specified in
§ 648.85(b)(10)(iv)(F).
(107) Use a Regular B DAS in the
Regular B DAS Program specified in
§ 648.85(b)(10), if the program has been
closed as specified in
§ 648.85(b)(10)(iv)(H) or (b)(10)(vi).
(108) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), use
a Regular B DAS after the program has
closed, as required under
§ 648.85(b)(10)(iv)(G) or (H).
(109) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
to comply with the reporting
requirements specified in
§ 648.85(b)(10)(iv)(I).
(110) If fishing in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(11), fail to comply with the
requirements and conditions specified
in § 648.85(b)(11)(iv), and (b)(11)(v) or
(b)(11)(vi), whichever is applicable.
(111) If fishing in the CA I Hook Gear
Haddock Access Area specified in
§ 648.85(b)(11)(ii), fail to comply with
the requirements and conditions
specified in § 648.85(b)(11)(iv), and
(b)(11)(v) or (b)(11)(vi), whichever is
applicable.
(112) Fish in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(11), outside of the season
specified in § 648.85(b)(11)(iii).
(113) If fishing in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(11), fail to comply with the
DAS use restrictions specified in
§ 648.85(b)(11)(iv)(A), and (b)(11)(v)(A)
or (b)(11)(vi)(A), whichever is
applicable.
(114) If fishing in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(11), fail to comply with the
VMS requirements specified in
§ 648.85(b)(11)(iv)(B).
(115) If fishing in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(11), fail to comply with the
observer notification requirements
specified in § 648.85(b)(11)(iv)(C).
(116) If fishing in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(11), fail to comply with the
VMS declaration requirement specified
in § 648.85(b)(11)(iv)(D).
(117) If fishing in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(11), fail to comply with the
gear restrictions specified in
§ 648.85(b)(11)(iv)(E), and (b)(11)(v)(B)
or (b)(11)(vi)(B), whichever is
applicable.
(118) If fishing in the CA I Hook Gear
Haddock SAP specified in
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§ 648.85(b)(11), fail to comply with the
landing limits specified in
§ 648.85(b)(11)(iv)(H), and (b)(11)(v)(C)
or (b)(11)(vi)(C), whichever is
applicable.
(119) If fishing in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(11), fail to comply with the
reporting requirement specified in
§ 648.85(b)(11)(v)(D) or (b)(11)(vi)(D),
whichever is applicable.
(120) Fish in the CA I Hook Gear
Haddock Access Area specified in
§ 648.85(b)(11)(ii), if that area is closed
as specified in § 648.85(b)(11)(iv)(I) or
(b)(11)(vi)(F).
(121) If fishing in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(11), fish with squid as bait,
as prohibited at § 648.85(b)(11)(iv)(J).
(122) Fish in the Eastern U.S./Canada
Haddock SAP specified in
§ 648.85(b)(8), if the SAP is closed as
specified in § 648.85(b)(8)(v)(L) or (N).
(123) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
to use a haddock separator trawl as
described under § 648.85(a)(3)(iii)(A), or
other approved gear as described under
§ 648.85(b)(10)(iv)(J).
(124) If fishing under a NE
multispecies Category A DAS in one or
both of the differential DAS areas
defined under § 648.82(e)(4)(i), fail to
declare into one or both of the areas
through VMS, as required under
§ 648.82(e)(4)(ii).
(125) If fishing under a NE
multispecies Category A DAS in one or
both of the differential DAS areas
defined in § 648.82(e)(4)(i), and under
the restrictions of one or more of the
Special Management Programs under
§ 648.85, fail to comply with the most
restrictive regulations.
(126) Possess or land more witch
flounder than allowed under
§ 648.86(m).
(127) Retain or land zero retention
stocks as specified under § 648.86(n).
(128) If possessing a Ruhle Trawl,
either at sea or elsewhere, as allowed
under § 648.85(b)(10)(iv)(J)(1) or
(b)(8)(v)(E)(1), fail to comply with the
net specifications under
§ 648.85(b)(10)(iv)(J)(3).
(129) If fishing as a private
recreational and charter/party vessel in
the SNE/MA winter flounder stock area
defined in § 648.85(b)(10)(v)(E), fish for
or retain winter flounder or transit this
area in possession of winter flounder
caught outside this area, unless all bait
and hooks are removed from fishing
rods and any winter flounder on board
has been gutted and stored.
(130) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
to use a haddock separator trawl as
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described under § 648.85(a)(3)(ix)(A), or
other approved gear as described under
§ 648.85(b)(10)(iv)(J).
(131) For vessels fishing inside and
outside the Eastern U.S./Canada Area on
the same trip, fail to comply with the
most restrictive regulations that apply
on the trip as required under
§ 648.85(a)(3)(viii)(A).
(132) For vessels fishing inside and
outside the Eastern U.S./Canada Area on
the same trip, fail to notify NMFS via
VMS that the vessel is electing to fish
in this manner, as required by
§ 648.85(a)(3)(viii)(A)(1).
(133) Fail to comply with the
restrictions on fishing and gear specified
in § 648.80(a)(3)(v), (a)(4)(v), (b)(2)(v),
and (c)(2)(iv) if the vessel has been
issued a limited access NE multispecies
permit and fishes with hook-gear in
areas specified in § 648.80(a), (b), or (c),
unless allowed under
§ 648.85(b)(11)(iv)(F).
(134) Discard legal-sized NE regulated
multispecies, ocean pout, or Atlantic
halibut while fishing under a Special
Access Program, as described in
§§ 648.85(b)(3)(xi), 648.85(b)(11)(iv)(H)
or 648.85(b)(8)(v)(I).
*
*
*
*
*
(g) * * *
(6) If the vessel is a private
recreational fishing vessel, fail to
comply with the seasonal GOM cod
possession prohibition described in
§ 648.89(c)(1)(vi), or, if the vessel has
been issued a charter/party permit or is
fishing under charter/party regulations,
fail to comply with the prohibition on
fishing under § 648.89(c)(5)(v).
(7) If fishing under the recreational or
charter/party regulations, fish for or
possess cod caught in the GOM
Regulated Mesh Area during the
seasonal GOM cod possession
prohibition under § 648.89(c)(1)(vi) or
(c)(5)(v), or fail to abide by the
appropriate restrictions if transiting
with cod on board.
*
*
*
*
*
§ 648.80
[Amended]
4. In § 648.80, paragraph (i) is
suspended.
■ 5. In § 648.81, paragraph (b)(2)(iv)(B)
is suspended, and paragraph
(b)(2)(iv)(C) is added to read as follows:
■
CA II in accordance with the provisions
of § 648.85(a)(3)(vii).
*
*
*
*
*
6. In § 648.82:
A. Paragraphs (e)(2) and (3);
(j)(1)(iii)(A) through (D); (k)(4)(iv) and
(x); and (l)(1)(iv) and (ix) are suspended.
■ B. Paragraphs (e)(4) and (5), and
(j)(1)(iii)(E), (F), and (G) are added.
The additions read as follows:
■
■
§ 648.82 Effort-control program for NE
multispecies limited access vessels.
*
*
*
*
*
(e) * * *
(4) Differential DAS. For a NE
multispecies DAS vessel that intends to
fish some or all of its trip, or fishes some
or all of its trip other than for transiting
purposes, under a Category A DAS in
one or both of the differential DAS
areas, as defined in paragraphs
(e)(4)(i)(A) and (B) of this section, with
the exception of Day gillnet vessels,
which accrue DAS in accordance with
paragraph (j)(1)(iii) of this section, each
Category A DAS, or part thereof, shall be
counted at the differential DAS rate
described in paragraph (e)(4)(iii) of this
section, and be subject to the
restrictions defined in this paragraph
(e).
(i) Differential DAS Areas.—(A) GOM
Differential DAS Area. The GOM
Differential DAS Area is defined by
straight lines connecting the following
points in the order stated:
Point
N. lat.
W. long.
GMD1 .............
43°30′ ......
GMD2 .............
GMD3 .............
GMD4 .............
43°30′ ......
43°00′ ......
43°00′ ......
GMD5
GMD6
GMD7
GMD8
42°30′
42°30′
41°30′
41°30′
Intersection
with Maine
Coastline.
69°30′.
69°30′.
69°55′ eastern
boundary,
WGOM
Closed Area.
69°55′.
69°30′.
69°30′.
70°00′.
.............
.............
.............
.............
GMD9 .............
§ 648.81 NE multispecies closed areas and
measures to protect EFH.
*
*
*
*
*
(b) * * *
(2) * * *
(iv) * * *
(C) The vessel has declared into the
Eastern U.S./Canada Area as specified
in § 648.85(a)(3)(viii) and is transiting
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......
......
......
......
North to intersection with
Cape Cod, Massachusetts, coast and 70°00″
W.
(B) Interim SNE Differential DAS
Area. The Interim SNE Differential DAS
Area is defined by straight lines
connecting the following points in the
order stated (a chart depicting this area
is available from the Regional
Administrator upon request):
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fish or fishes some or all of its trip other
than for transiting purposes under a
Category A DAS in the Interim SNE
Differential DAS Area shall have each
Point
N. lat.
W. long.
Category A DAS, or part thereof,
SNECA1 ...........
(1)
70°00′ counted at the ratio of 2 to 1 for the
SNECA2 ...........
41°30′
70°00′ entire trip, even if only a portion of the
SNECA3 ...........
41°30′
68°50′ trip is spent fishing in the Interim SNE
SNECA4 ...........
40°30′
68°50′
SNECA5 ...........
40°30′
(2) Differential DAS Area. Unless otherwise
specified in paragraph (e)(4)(iii) of this
1 Intersection of the shoreline of Cape Cod,
section, a NE multispecies DAS vessel
Massachusetts, and 70°00′ W. long.
fishing with hook gear that intends to
2 Intersection of the shoreline of Staten Isfish or fishes some or all of its trip other
land, New York, and 40°30′ N. lat.
than for transiting purposes under a
(ii) Declaration. A NE multispecies
Category A DAS in the Interim SNE
DAS vessel that intends to fish, or fishes Differential DAS Area shall have each
under a Category A DAS in one of the
Category A DAS, or part thereof,
differential DAS areas described in
counted at the ratio of 1 to 1 for the
paragraph (e)(4)(i) of this section, must,
entire trip. A vessel that has not
prior to leaving the dock, declare
declared its intent to fish in the Interim
through the VMS, in accordance with
SNE Differential DAS Area and that is
instructions to be provided by the
not transiting, as specified in paragraph
Regional Administrator, that the vessel
(e)(4)(v) of this section, may be in the
will fish in the GOM Differential DAS
Interim SNE Differential DAS Area,
Area, the Interim SNE Differential DAS
provided the vessel’s fishing gear is
Area, or both areas. A DAS vessel that
stowed in accordance with the
fishes in the Eastern U.S./Canada Area
provisions of § 648.23(b) for the entire
and intends to fish, or fishes,
time the vessel is in the area and the
subsequently in one or both of the
vessel declares immediately upon
differential DAS areas under a Category
entering the Interim SNE Differential
A DAS, must declare its intention to do
DAS Area, via VMS, that it is in the
so through its VMS prior to leaving the
area. A vessel that fishes in both the
dock at the start of the trip, or prior to
GOM Differential Area and the Interim
leaving the Eastern U.S./Canada Area, as SNE Differential DAS Area on the same
specified in § 648.85(a)(3)(viii)(A)(3).
trip will be charged DAS at the rate of
(iii) Differential DAS counting.—(A)
2:1 for the entire trip.
Differential DAS counting when fishing
(iv) Restrictions. A NE multispecies
in the GOM Differential DAS Area. For
vessel fishing under a Category A DAS
a NE multispecies vessel that intends to in one or both of the differential DAS
fish, or fishes for some or all of its trip
areas defined in paragraph (e)(4)(i) of
other than for transiting purposes under this section, under the restrictions of
a Category A DAS in the GOM
this paragraph (e)(4) and under the
Differential DAS Area, each Category A
restrictions of one or more of the Special
DAS, or part thereof, shall be counted at Management Programs under § 648.85,
the ratio of 2 to 1 for the entire trip, even must comply with the most restrictive
if only a portion of the trip is spent
DAS counting, trip limits, and reporting
fishing in the GOM Differential DAS
requirements, specified in this
Area. A vessel that has not declared its
paragraph (e)(4) and in § 648.85, under
intent to fish in the GOM Differential
the pertinent Special Management
DAS Area and that is not transiting, as
Program.
specified in paragraph (e)(4)(v) of this
(v) Transiting. A vessel may transit
section, may be in the GOM Differential either one or both of the differential
DAS Area, provided the vessel’s fishing DAS areas, as defined in paragraph
gear is stowed in accordance with the
(e)(4)(i) of this section, provided the
provisions of § 648.23(b) for the entire
gear is stowed in accordance with the
time the vessel is in the area, and the
provisions of § 648.23(b).
(5) Regular B DAS Program 24-hr
vessel declares immediately upon
clock. For a vessel electing to fish in the
entering the GOM Differential DAS
Regular B DAS Program, as specified at
Area, via VMS, that it is in the area. A
§ 648.85(b)(10), and that remains fishing
vessel that fishes in both the GOM
under a Regular B DAS for the entire
Differential Area and the Interim SNE
fishing trip (without a DAS flip), DAS
Differential DAS Area on the same trip
used shall accrue at the rate of 1 full
will be charged DAS at the rate of 2:1
DAS for each calendar day, or part of a
for the entire trip.
(B) Differential DAS counting when
calendar day fished. For example, a
fishing in the Interim SNE Differential
vessel that fished on one calendar day
DAS Area. With the exception of a
from 6 a.m. to 10 p.m. would be charged
vessel fishing with hook gear, a NE
24 hr of Regular B DAS, not 16 hr; a
multispecies DAS vessel that intends to vessel that left on a trip at 11 p.m. on
INTERIM SNE DIFFERENTIAL DAS
AREA
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Fmt 4701
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17055
the first calendar day and returned at 10
p.m. on the second calendar day would
be charged 48 hr of Regular B DAS
instead of 23 hr, because the fishing trip
would have spanned 2 calendar days.
For the purpose of calculating trip limits
specified under § 648.86, the amount of
DAS deducted from a vessel’s DAS
allocation shall determine the amount of
fish the vessel can legally land. For a
vessel electing to fish in the Regular B
DAS Program, as specified at
§ 648.85(b)(10), while also fishing in one
or both of the differential DAS areas
defined in paragraph (e)(4) of this
section, Category B DAS shall accrue at
the rate described in this paragraph
(e)(5), unless the vessel flips to a
Category A DAS, in which case the
vessel is subject to the pertinent DAS
accrual restrictions of paragraph
(e)(4)(iii) of this section for the entire
trip. For vessels electing to fish in both
the Regular B DAS Program, as specified
in § 648.85(b)(10), and in the Eastern
U.S./Canada Area, as specified in
§ 648.85(a), DAS counting will begin
and end according to the DAS
accounting rules specified in
§ 648.10(b)(2)(iii).
*
*
*
*
*
(j) * * *
(1) * * *
(iii) * * *
(E) A Day gillnet vessel fishing with
gillnet gear that has elected to fish in the
Regular B DAS Program, as specified in
§ 648.85(b)(10), under a Category B
DAS, is subject to the DAS accrual
provisions of paragraph (e)(5) of this
section.
(F) A Day gillnet vessel fishing with
gillnet gear under a NE multispecies
Category A DAS, when not subject to
differential DAS counting as specified
under paragraph (e)(4) of this section,
shall accrue 15 hr of DAS for each trip
of more than 3 hr, but less than or equal
to 15 hr. Such vessel shall accrue actual
DAS time at sea for trips less than or
equal to 3 hr, or more than 15 hr.
(G) A Day gillnet vessel fishing with
gillnet gear under a NE multispecies
Category A DAS that is fishing in one or
both of the differential DAS areas
specified in paragraph (e)(4)(i) of this
section and, therefore, subject to
differential DAS counting as specified
under paragraph (e)(4)(iii) of this
section, shall accrue DAS at a
differential DAS rate of 2 to 1 for the
actual hours used for any trip of less
than or equal to 3 hr in duration, and
for any trip of greater than 7.5 hr. For
such vessels fishing on any trip of more
than 3 hr, but less than or equal to 7.5
hr duration, vessels will be charged a
full 15 hr. For example, a Day gillnet
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vessel fishing in the Interim SNE
Differential DAS Area for 8 actual hr
would be charged 16 hr of DAS, or if
fishing for 5 actual hr, would be charged
15 hr of DAS.
*
*
*
*
*
■ 7. In § 648.83, paragraph (a)(1) and
(a)(3) are suspended and paragraph
(a)(4) is added to read as follows:A
§ 648.83
Multispecies minimum fish sizes.
(a) * * *
(4) Minimum fish sizes for
recreational vessels and charter/party
vessels that are not fishing under a NE
multispecies DAS are specified in
§ 648.89. Except as provided in § 648.17,
all other vessels are subject to the
following minimum fish sizes,
determined by total length (TL):
MINIMUM FISH SIZES (TL) FOR
COMMERCIAL VESSELS
Species
Sizes
(inches)
Cod ..........................................
Haddock ..................................
Pollock .....................................
Witch flounder (gray sole) .......
Yellowtail flounder ...................
American plaice ......................
Atlantic halibut .........................
Winter flounder (blackback) ....
Redfish ....................................
22 (55.9 cm)
18 (45.7 cm)
19 (48.3 cm)
14 (35.6 cm)
13 (33.0 cm)
14 (35.6 cm)
36 (91.4 cm)
12 (30.5 cm)
9 (22.9 cm)
*
*
*
*
*
8. In § 648.85:
A. Paragraphs (a)(3)(ii) and (iii); and
(a)(3)(v)(A), (B), and (C) are suspended.
■ B. Paragraphs (b)(4), (5), (6) and (7);
(b)(8)(v)(E)(2); and (b)(8)(v)(H) are
suspended.
■ C. Paragraphs (a)(3)(v)(D), (E), and (F);
(a)(3)(viii) and (ix); (b)(8)(v)(E)(3);
(b)(8)(v)(M) and (N); and (b)(9), (10), and
(11) are added.
The additions read as follows:
■
■
§ 648.85
Special management programs.
*
*
*
*
*
(a) * * *
(3) * * *
(v) * * *
(D) Total pounds of cod, haddock,
yellowtail flounder, winter flounder,
witch flounder, pollock, windowpane
flounder, and white hake kept;
(E) Date fish were caught and
statistical area in which fish were
caught; and
(F) Vessel Trip Report (VTR) serial
number, as instructed by the Regional
Administrator.
*
*
*
*
*
(viii) Declaration. To fish in the U.S./
Canada Management Area under a
groundfish DAS, a NE multispecies DAS
vessel, prior to leaving the dock, must
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declare through the VMS, in accordance
with instructions to be provided by the
Regional Administrator, which specific
U.S./Canada Management Area
described in paragraphs (a)(1)(i) or (ii) of
this section, or which specific SAP,
described in paragraph (b) of this
section, within the U.S./Canada
Management Area the vessel will fish
in, and comply with the restrictions and
conditions in paragraphs (a)(3)(viii)(A)
through (C) of this section. Vessels other
than NE multispecies DAS vessels are
not required to declare into the U.S./
Canada Management Areas.
(A) A vessel fishing under a NE
multispecies DAS in the Eastern U.S./
Canada Area may fish both inside and
outside of the Eastern U.S./Canada Area
on the same trip, provided it complies
with the most restrictive DAS counting,
trip limits, and reporting requirements
for the areas fished for the entire trip,
and provided it complies with the
restrictions specified in paragraphs
(a)(3)(viii)(A)(1) through (4) of this
section. On a trip when the vessel
operator elects to fish both inside and
outside of the Eastern U.S./Canada Area,
all cod, haddock, and yellowtail
flounder caught on the trip shall count
toward the applicable hard TAC
specified for the U.S./Canada
Management Area.
(1) The vessel operator must notify
NMFS via VMS any time prior to
leaving the dock at the start of the trip
or prior to leaving the Eastern U.S./
Canada Area (including at the time of
initial declaration into the Eastern U.S./
Canada Area) that it is also electing to
fish outside the Eastern U.S./Canada
Area. With the exception of vessels
participating in the Regular B DAS
Program and fishing under a Regular B
DAS, once a vessel that has elected to
fish outside of the Eastern U.S./Canada
Area leaves the Eastern U.S./Canada
Area, Category A DAS shall accrue from
the time the vessel crosses the VMS
demarcation line at the start of its
fishing trip until the time the vessel
crosses the demarcation line on its
return to port, in accordance with
§ 648.10(b)(2)(iii).
(2) The vessel must comply with the
reporting requirements of the U.S./
Canada Management Area specified
under paragraph (a)(3)(v) of this section
for the duration of the trip.
(3) If the vessel fishes or intends to
fish in one or both of the differential
DAS areas defined under
§ 648.82(e)(4)(i), it must declare its
intent to do so prior to leaving the
Eastern U.S./Canada Area (including at
the time of initial declaration into the
Eastern U.S./Canada Area), and must
not have exceeded the CC/GOM or SNE/
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MA yellowtail flounder trip limits,
specified in § 648.86(g), for the
respective areas.
(4) If a vessel possesses yellowtail
flounder in excess of the trip limits for
CC/GOM yellowtail flounder or SNE/
MA yellowtail flounder, as specified in
§ 648.86(g), the vessel may not fish in
either the CC/GOM or SNE/MA
yellowtail flounder stock area during
that trip (i.e., may not fish outside of the
U.S./Canada Management Area).
(B) A vessel fishing under a NE
multispecies DAS in the Western U.S./
Canada Area may fish inside and
outside the Western U.S./Canada Area
on the same trip, provided it complies
with the most restrictive regulations
applicable to the area fished for the
entire trip (e.g., the possession
restrictions specified in paragraph
(a)(3)(iv)(C)(4) of this section), and the
reporting requirements specified in
paragraph (a)(3)(v) of this section.
(C) For the purposes of selecting
vessels for observer deployment, a
vessel fishing in either of the U.S./
Canada Management Areas specified in
paragraph (a)(1) of this section must
provide notice to NMFS of the vessel
name; contact name for coordination of
observer deployment; telephone number
for contact; and the date, time, and port
of departure, at least 72 hr prior to the
beginning of any trip that it declares
into the U.S./Canada Management Area,
as required under this paragraph
(a)(3)(viii).
(ix) Gear requirements. NE
multispecies vessels fishing with trawl
gear in the Eastern U.S./Canada Area
defined in paragraph (a)(1)(ii) of this
section, unless otherwise provided in
paragraphs (b)(8) and (b)(10) of this
section, must fish with a Ruhle trawl, as
described in paragraph (b)(10)(iv)(J)(1)
of this section, or a haddock separator
trawl or a flounder trawl net, as
described in paragraphs (a)(3)(ix)(A) and
(B) of this section (all three nets may be
onboard the fishing vessel
simultaneously). Gear other than the
Ruhle trawl, haddock separator trawl, or
the flounder trawl net as described in
paragraph (a)(3)(ix) of this section, or
gear authorized under paragraphs (b)(8)
and (b)(10) of this section, may be on
board the vessel during a trip to the
Eastern U.S./Canada Area, provided the
gear is stowed according to the
regulations at § 648.23(b). The
description of the Ruhle trawl, the
haddock separator trawl, and the
flounder trawl net in paragraph
(b)(10)(iv)(J)(1) of this section and in
this paragraph (a)(3)(ix) may be further
specified by the Regional Administrator
through publication of such
specifications in the Federal Register,
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consistent with the requirements of the
Administrative Procedure Act.
(A) Haddock separator trawl. A
haddock separator trawl is defined as a
groundfish trawl modified to a vertically
oriented trouser trawl configuration,
with two extensions arranged one over
the other, where a codend shall be
attached only to the upper extension,
and the bottom extension shall be left
open and have no codend attached. A
horizontal large-mesh separating panel
constructed with a minimum of 6.0-inch
(15.2-cm) diamond mesh must be
installed between the selvedges joining
the upper and lower panels, as
described in this paragraph (a)(3)(ix)(A)
and in paragraph (B) of this section,
extending forward from the front of the
trouser junction to the aft edge of the
first belly behind the fishing circle.
(1) Two-seam bottom trawl nets. For
two-seam nets, the separator panel will
be constructed such that the width of
the forward edge of the panel is 80–85
percent of the width of the after edge of
the first belly of the net where the panel
is attached. For example, if the belly is
200 meshes wide (from selvedge to
selvedge), the separator panel must be
no wider than 160–170 meshes.
(2) Four-seam bottom trawl nets. For
four-seam nets, the separator panel will
be constructed such that the width of
the forward edge of the panel is 90–95
percent of the width of the after edge of
the first belly of the net where the panel
is attached. For example, if the belly is
200 meshes wide (from selvedge to
selvedge), the separator panel must be
no wider than 180–190 meshes. The
separator panel will be attached to both
of the side panels of the net along the
midpoint of the side panels. For
example, if the side panel is 100 meshes
tall, the separator panel must be
attached at the 50th mesh.
(B) Flounder trawl net. A flounder
trawl net is defined as bottom trawl gear
meeting one of the following two net
descriptions:
(1) A two-seam, low-rise net
constructed with mesh size in
compliance with § 648.80(a)(4), where
the maximum footrope length is not
greater than 105 ft (32.0 m) and the
headrope is at least 30-percent longer
than the footrope. The footrope and
headrope lengths shall be measured
from the forward wing end.
(2) A two-seam, low-rise net
constructed with mesh size in
compliance with § 648.80(a)(4), with the
exception that the top panel of the net
contains a section of mesh at least 10 ft
(3.05 m) long and stretching from
selvedge to selvedge, composed of at
least 12-inch (30.5-cm) mesh that is
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20:07 Apr 10, 2009
Jkt 217001
inserted no farther than 4.5 meshes
behind the headrope.
(b) * * *
(8) * * *
(v) * * *
(E) * * *
(3) Approval of additional gear. The
Regional Administrator may authorize
additional gear for use in the Eastern
U.S./Canada Haddock SAP in
accordance with the standards and
requirements specified at paragraph
(b)(10)(iv)(J)(2) of this section.
*
*
*
*
*
(M) Incidental TACs. The maximum
amount of GB cod, and the amount of
GB yellowtail flounder, GB winter
flounder, and pollock, both landings
and discards, that may be caught when
fishing in the Eastern U.S./Canada
Haddock SAP Program in a fishing year
by vessels fishing under a Category B
DAS, as authorized in paragraph
(b)(8)(v)(A) of this section, is the amount
specified in paragraphs (b)(9)(ii), (iii),
and (iv) of this section, respectively.
(N) Mandatory closure of Eastern
U.S./Canada Haddock SAP. When the
Regional Administrator projects that one
or more of the TAC allocations specified
in paragraph (b)(8)(v)(M) of this section
has been caught by vessels fishing under
Category B DAS, NMFS shall prohibit
the use of Category B DAS in the Eastern
U.S./Canada Haddock SAP, through
publication in the Federal Register
consistent with the Administrative
Procedure Act. In addition, the closure
regulations described in paragraph
(a)(3)(iv)(E) of this section shall apply to
the Eastern U.S./Canada Haddock SAP
Program.
(9) Incidental Catch TACs. Unless
otherwise specified in this paragraph
(b)(9), Incidental Catch TACs shall be
specified through the periodic
adjustment process described in
§ 648.90, and allocated as described in
this paragraph (b)(9), for each of the
following stocks: GOM cod, GB cod, GB
yellowtail flounder, GB winter flounder,
GOM winter, white hake, CC/GOM
yellowtail flounder, SNE/MA yellowtail
flounder, witch flounder, and pollock.
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, GB winter flounder,
and pollock. With the exception of GB
cod, GB yellowtail flounder, GB winter
flounder, and pollock, the Incidental
Catch TACs specified under this
paragraph (b)(9) shall be allocated to the
Regular B DAS Program described in
paragraph (b)(10) of this section.
(ii) GB cod. The Incidental TAC for
GB cod specified under this paragraph
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17057
(b)(9) shall be subdivided as follows: 70
percent to the Regular B DAS Program
described in paragraph (b)(10) of this
section; 16 percent to the CA I Hook
Gear Haddock SAP described in
paragraph (b)(7) of this section; and 14
percent to the Eastern U.S./Canada
Haddock SAP described in paragraph
(b)(8) of this section.
(iii) GB yellowtail flounder and GB
winter flounder. Each of the Incidental
Catch TACs for GB yellowtail flounder
and GB winter flounder specified under
this paragraph (b)(9) shall be subdivided
as follows: 80 percent to the Regular B
DAS Program described in paragraph
(b)(10) of this section; and 20 percent to
the Eastern U.S./Canada Haddock SAP
described in paragraph (b)(8) of this
section.
(iv) Pollock. The Incidental TAC for
pollock specified under this paragraph
(b)(9) shall be subdivided as follows: 90
percent to the Regular B DAS Program
described in paragraph (b)(10) of this
section; 5 percent to the CA I Hook Gear
Haddock SAP described in paragraph
(b)(7) of this section; and 5 percent to
the Eastern U.S./Canada Haddock SAP
described in paragraph (b)(8) of this
section.
(10) Regular B DAS Program.—(i)
Eligibility. Vessels issued a valid limited
access NE multispecies DAS permit and
allocated Regular B DAS are eligible to
participate in the Regular B DAS
Program and may elect to fish under a
Regular B DAS, provided they comply
with the requirements and restrictions
of this paragraph (b)(10), and provided
the use of Regular B DAS is not
restricted according to paragraphs
(b)(10)(iv)(G) or (H) of this section, or
paragraph (b)(10)(vi) of this section.
Vessels are required to comply with the
no discarding and DAS flip
requirements specified in paragraph
(b)(10)(iv)(E) of this section and the DAS
balance and accrual requirements
specified in paragraph (b)(10)(iv)(F) of
this section. Vessels may fish under the
B Regular DAS Program and in the U.S./
Canada Management Area on the same
trip, but may not fish under the Regular
B DAS Program and in a SAP on the
same trip.
(ii) [Reserved]
(iii) Quarterly Incidental Catch TACs.
The Incidental Catch TACs specified in
accordance with paragraph (b)(9) of this
section shall be divided into quarterly
catch TACs as follows: The first quarter
shall received 13 percent of the
Incidental Catch TACs and the
remaining three quarters shall each
receive 29 percent of the Incidental
Catch TACs. When the Regional
Administrator projects that there is
uncaught TAC in quarters one, two, or
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three, the uncaught TAC will be added
to the TAC allocated for the subsequent
quarter. Uncaught TAC at the end of the
fishing year will not be added to
allocations in subsequent fishing years.
NMFS shall send letters to all limited
access NE multispecies permit holders
notifying them of such TACs and any
adjustments to such TACs.
(iv) Program requirements.—(A) VMS
requirement. A NE multispecies DAS
vessel fishing in the Regular B DAS
Program described in paragraph
(b)(10)(i) of this section must have
installed on board an operational VMS
unit that meets the minimum
performance criteria specified in
§§ 648.9 and 648.10.
(B) Observer notification. For the
purposes of selecting vessels for
observer deployment, a vessel must
provide notice to NMFS of the vessel
name; contact name for coordination of
observer deployment; telephone number
for contact; the date, time, and port of
departure; and the planned fishing area
or areas (GOM, GB, or SNE/MA) at least
72 hr prior to the beginning of any trip
that it declares into the Regular B DAS
Program, as required under paragraph
(b)(10)(iv)(C) of this section, and in
accordance with instructions provided
by the Regional Administrator.
Providing notice of the area that the
vessel intends to fish does not restrict
the vessel’s activity to only that area on
that trip (i.e., the vessel operator may
change his/her plans regarding planned
fishing area).
(C) VMS declaration. To participate in
the Regular B DAS Program under a
Regular B DAS, a vessel must declare
into the Program via VMS prior to
departure from port, in accordance with
instructions provided by the Regional
Administrator. A vessel declared into
the Regular B DAS Program cannot fish
in an approved SAP described under
this section on the same trip. Mere
declaration of a Regular B DAS Program
trip does not reserve a vessel’s right to
fish under the Program, if the vessel has
not crossed the VMS demarcation line.
(D) Landing limits. Unless otherwise
specified in this paragraph
(b)(10)(iv)(D), a NE multispecies vessel
fishing in the Regular B DAS Program
described in this paragraph (b)(10), and
fishing under a Regular B DAS, may not
land more than 100 lb (45.5 kg) per
DAS, or any part of a DAS, up to a
maximum of 1,000 lb (454 kg) per trip
of any of the following species/stocks
from the areas specified in paragraph
(b)(10)(v) of this section: Cod, pollock,
white hake, witch flounder, GB winter
flounder, GB yellowtail flounder, and
southern windowpane flounder; and
may not land more than 25 lb (11.3 kg)
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20:07 Apr 10, 2009
Jkt 217001
per DAS, or any part of a DAS, up to a
maximum of 250 lb (113 kg) per trip of
CC/GOM or SNE/MA yellowtail
flounder. In addition, trawl vessels that
are required to fish with a haddock
separator trawl or Ruhle trawl, as
specified under paragraph (b)(10)(iv)(J)
of this section, and other gear that may
be required in order to reduce catches
of stocks of concern as described under
paragraph (b)(10)(iv)(J) of this section,
are restricted to the following trip
limits: 500 lb (227 kg) of all flatfish
species (American plaice, witch
flounder, winter flounder (GOM or GB),
windowpane flounder (south), and
yellowtail flounder), combined; 500 lb
(227 kg) of monkfish (whole weight);
500 lb (227 kg) of skates (whole weight);
and zero possession of lobsters, ocean
pout, SNE/MA winter flounder, and
windowpane flounder (north), unless
otherwise restricted by § 648.94(b)(3).
(E) No-discard provision and DAS
flips. A vessel fishing in the Regular B
DAS Program under a Regular B DAS
may not discard legal-sized regulated
species, Atlantic halibut, or monkfish,
unless otherwise specified in this
paragraph (b)(10)(iv)(E). This
prohibition on discarding does not
apply to ocean pout, windowpane
(north), or SNE winter flounder, or in
areas or times where the possession or
landing of regulated species is
prohibited. If such a vessel harvests and
brings on board legal-sized regulated NE
multispecies, or Atlantic halibut unless
exempted, as specified in this paragraph
(b)(10)(iv)(E), in excess of the allowable
landing limits specified in paragraph
(b)(10)(iv)(D) of this section, or § 648.86,
the vessel operator must notify NMFS
immediately via VMS to initiate a DAS
flip from a B DAS to an A DAS. Once
this notification has been received by
NMFS, the vessel shall automatically be
switched by NMFS to fishing under a
Category A DAS for its entire fishing
trip. Thus, any Category B DAS that
accrued between the time the vessel
declared into the Regular B DAS
Program at the beginning of the trip (i.e.,
at the time the vessel crossed the
demarcation line at the beginning of the
trip) and the time the vessel declared its
DAS flip shall be accrued as Category A
DAS, and not Regular B DAS. After
flipping to a Category A DAS, the vessel
is subject to the applicable trip limits
specified under § 648.86 or paragraph
(a) of this section and may discard fish
in excess of the applicable trip limits.
(F) Minimum Category A DAS and B
DAS accrual. For a vessel fishing under
the Regular B DAS Program, the number
of Regular B DAS that may be used on
a trip cannot exceed the number of
Category A DAS that the vessel has at
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Fmt 4701
Sfmt 4700
the start of the trip. If a vessel is fishing
any part of a trip in one or both of the
differential DAS areas, as described in
§ 648.82(e)(4)(i), the number of Regular
B DAS that may be used on a trip cannot
exceed the number of Category A DAS
that the vessel has at the start of the trip
divided by two. For example, if a vessel
plans a trip under the Regular B DAS
Program into the Interim SNE
Differential DAS Area and has 10
Category A DAS available at the start of
the trip, the maximum number of
Regular B DAS that the vessel may fish
under the Regular B DAS Program is 5.
A vessel fishing in the Regular B DAS
Program for its entire trip shall accrue
DAS in accordance with § 648.82(e)(5).
(G) Restrictions when 100 percent of
the incidental catch TAC is harvested.
With the exception of white hake, witch
flounder, and pollock, when the
Regional Administrator provides
notification through methods consistent
with the Administrative Procedure Act
that 100 percent of one or more of
quarterly incidental TACs specified
under paragraph (b)(10)(iii) of this
section have been projected to have
been harvested, the use of Regular B
DAS shall be prohibited in the pertinent
stock area(s) as defined under paragraph
(b)(10)(v) of this section for the duration
of the calendar quarter. The closure of
a stock area to all Regular B DAS use
shall occur even if the quarterly
incidental catch TACs for other stocks
in that stock area have not been
completely harvested. When the
Regional Administrator projects that 100
percent of the quarterly white hake,
witch flounder, or pollock incidental
catch TAC specified under paragraph
(b)(10)(iii) of this section has been
harvested, vessels fishing under a
Regular B DAS, or that complete a trip
under a Regular B DAS, shall be
prohibited from retaining white hake,
witch flounder, or pollock, respectively.
(H) Closure of Regular B DAS Program
and quarterly DAS limits. Unless
otherwise closed as a result of the
harvest of an Incidental Catch TAC as
described in paragraph (b)(10)(iv)(G) of
this section, or as a result of an action
by the Regional Administrator under
paragraph (b)(10)(vi) of this section, the
use of Regular B DAS shall, in a manner
consistent with the Administrative
Procedure Act, be prohibited when 500
Regular B DAS have been used during
the first quarter of the fishing year
(May–July), or when 1,000 Regular B
DAS have been used during any of the
remaining quarters of the fishing year,
in accordance with § 648.82(e)(5).
(I) Reporting requirements. The owner
or operator of a NE multispecies DAS
vessel must submit catch reports via
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VMS in accordance with instructions
provided by the Regional Administrator,
for each day fished when declared into
the Regular B DAS Program. The reports
must be submitted in 24-hr intervals for
each day, beginning at 0000 hr and
ending at 2400 hr. The reports must be
submitted by 0900 hr of the following
day. For vessels that have declared into
the Regular B DAS Program in
accordance with paragraph (b)(10)(iv)(C)
of this section, the reports must include
at least the following information:
Statistical area fished; total pounds of
cod, haddock, yellowtail flounder,
winter flounder, witch flounder,
pollock, and white hake kept; date fish
were caught; and VTR serial number, as
instructed by the Regional
Administrator. Daily reporting must
continue even if the vessel operator is
required to flip, as described under
paragraph (b)(10)(iv)(E) of this section.
(J) Gear requirement.—(1) Vessels
fishing with trawl gear in the Regular B
DAS Program must use a haddock
separator trawl or Ruhle trawl, as
described under paragraphs (a)(3)(iii)(A)
and (b)(10)(iv)(J)(3) of this section,
respectively, or other type of gear, if
approved, as described under this
paragraph (b)(10)(iv)(J). Other gear may
be on board the vessel, provided it is
stowed when the vessel is fishing under
the Regular B DAS Program. Vessels
fishing with gillnet gear in the Regular
B DAS Program may not use a low
profile (‘‘tie-down’’ type) gillnet.
(2) Approval of additional gear. At the
request of the Council or Council’s
Executive Committee, the Regional
Administrator may authorize additional
gear for use in the Regular B DAS
Program, through notice consistent with
the Administrative Procedure Act. The
proposed gear must satisfy standards
specified in paragraphs
(b)(10)(iv)(J)(2)(i) or (ii) of this section in
a completed experiment that has been
reviewed according to the standards
established by the Council’s research
policy before the gear can be considered
and approved by the Regional
Administrator. Comparisons of the
criteria specified in this paragraph
(b)(10)(iv)(J)(2) will be made to an
appropriately selected control gear.
(i) The gear must show a statistically
significant reduction in catch of at least
50 percent (by weight, on a trip-by-trip
basis) of each regulated species stock of
concern, unless otherwise allowed in
this paragraph (b)(10)(iv)(J)(2)(i), or
other non-groundfish stocks that are
overfished or subject to overfishing
identified by the Council. This
requirement does not apply to regulated
species identified by the Council as not
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20:07 Apr 10, 2009
Jkt 217001
being subject to gear performance
standards; or
(ii) The catch of each regulated
species stock of concern, unless
otherwise allowed in this paragraph
(b)(10)(iv)(J)(2)(ii), or other nongroundfish stocks that are overfished or
subject to overfishing identified by the
Council, must be less than 5 percent of
the total catch of regulated groundfish
by weight, on a trip-by-trip basis. This
requirement does not apply to regulated
species identified by the Council as not
being subject to gear performance
standards.
(3) Ruhle Trawl. The Ruhle Trawl is
a four-seam bottom groundfish trawl
designed to reduce the bycatch of cod
while retaining or increasing the catch
of haddock, when compared to
traditional groundfish trawls. A Ruhle
Trawl must be constructed in
accordance with the standards
described and referenced in this
paragraph (b)(10)(iv)(J)(3). The mesh
size of a particular section of the Ruhle
Trawl is measured in accordance with
§ 648.80(f)(2), unless insufficient
numbers of mesh exist, in which case
the maximum total number of meshes in
the section will be measured (between
2 and 20 meshes).
(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 A ‘‘Nomenclature for 4-seam Ruhle
Trawl’’ (this figure is also available from
the Regional Administrator): Top jib,
bottom jib, jib side panels (x 2), top
wing, bottom wing, wing side panels (x
2), square, bunt, square side panels (x
2), first top belly, first bottom belly, first
belly side panels (x 2), second top belly,
second bottom belly, second belly side
panels (x 2), and third bottom belly.
(ii) The first bottom belly, bunt, the
top and bottom wings, and the top and
bottom jibs, jib side panels, and wing
side panels (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 and second top belly,
the first belly side panels, and the third
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Sfmt 4700
17059
bottom belly must be at least 7.9 inches
(20 cm); and 6 inches (15.24 cm) or
larger in sections following the second
top belly and third 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 a fishing
circle of at least 398 ft (121.4 m). This
number is calculated by separately
counting the number of meshes for each
section of the net at the wide, fore end
of the first bottom belly, and then
calculating a stretched length as follows:
For each section of the net (first bottom
belly, two belly side panels and first top
belly) multiply the number of meshes
times the length of each stretched mesh
to get the stretched mesh length for that
section, and then add the sections
together. For example, if the wide, fore
end of the bottom belly of the Ruhle
Trawl is 22 meshes (and the mesh is at
least 7.9 ft (240 cm)), the stretched mesh
length for that section of the net is
derived by multiplying 22 times 7.9 ft
(240 cm) and equals 173.2 ft (52.8 m).
The top and sides (x 2) of the net at this
point in the trawl are 343 meshes (221
+ 61 + 61, respectively) (each 7.9 inches
(20 cm)), which equals 225.1 ft (68.6 m)
stretched length. The stretched lengths
for the different sections of mesh are
added together (173.2 ft + 225.1 ft (52.8
m + 68.6 m)) and result in the length of
the fishing circle, in this case 398.3 ft
(121.4 m).
(v) The trawl must have a single or
multiple kite panels with a total surface
area of at least 29.1 sq. ft. (2.7 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.
(vi) The sweep must include
rockhoppers of various sizes, which are
arranged along the sweep in size order,
graduated from 16-inch (40-cm)
diameter in the sweep center down to
12-inch (30-cm) diameter at the wing
ends. There must be six or fewer 12- to
16-inch (30- to 40-cm) rockhopper discs
over any 10-ft (3.0-m) length of the
sweep. The 12- to 16- inch (30- to 40cm) discs (minimum size) must be
spaced evenly, with one disc placed
approximately every 2 ft (60 cm) along
the sweep. The 12- to 16-inch (30- to 40cm) discs must be separated by smaller
discs, no larger than 3.5 inches (8.8 cm)
in diameter.
(v) Definition of incidental TAC stock
areas. For the purposes of the Regular
B DAS Program, including the stocks
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that may not be retained by vessels as
specified under § 648.86, the species
stock areas are defined in paragraphs
(b)(10)(v)(A) through (I) of this section.
Copies of a chart depicting these areas
are available from the Regional
Administrator upon request.
(A) GOM cod stock area. The GOM
cod stock area for the purposes of the
Regular B DAS Program is the area
defined by straight lines connecting the
following points in the order stated:
GULF OF MAINE COD STOCK AREA
Point
GOM1
GOM2
GOM3
GOM4
GOM5
GOM6
GOM7
GOM8
N. lat.
...............
...............
...............
...............
...............
...............
...............
...............
(1)
42°20′
42°20′
43°50′
43°50′
44°20′
44°20′
(2)
W. long.
70°00′
70°00′
67°40′
67°40′
66°50′
66°50′
67°00′
67°00′
1 Intersection of the north-facing coastline of
Cape Cod, MA, and 70°00′ W. Long.
2 Intersection of the south-facing Maine
coastline and 67°00′ W. Long.
(B) GB cod stock area. The GB cod
stock area for the purposes of the
Regular B DAS Program is the area
defined by straight lines connecting the
following points in the order stated:
GEORGES BANK COD STOCK AREA
Point
N. lat.
GB1 ...................
GB2 ...................
GB3 ...................
GB4 ...................
GB5 ...................
GB6 ...................
GB7 ...................
GB8 ...................
GB9 ...................
GB10 .................
GB11 .................
GB12 .................
(1)
42°20′
42°20′
42°10′
42°10′
42°00′
42°00′
40°30′
39°00′
39°00′
35°00′
35°00′
W. long.
70°00′
70°00′
66°00′
66°00′
65°50′
65°50′
65°40′
65°40′
65°40′
70°00′
70°00′
(2)
1 Intersection of the north-facing coastline of
Cape Cod, MA, and 70°00′ W. Long.
2 Intersection of the east-facing coastline of
Outer Banks, NC, and 35°00′ N. Lat.
(C) CC/GOM yellowtail flounder stock
area. The CC/GOM yellowtail flounder
stock area for the purposes of the
Regular B DAS Program is the area
defined by straight lines connecting the
following points in the order stated:
CC/GOM YELLOWTAIL FLOUNDER
STOCK AREA
Point
N. lat.
CCGOM1 ..........
CCGOM 2 .........
CCGOM 3 .........
CCGOM 4 .........
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43°00′
42°20′
42°20′
42°10′
20:07 Apr 10, 2009
W. long.
(1)
70°00′
66°00′
66°00′
Jkt 217001
CC/GOM YELLOWTAIL FLOUNDER
STOCK AREA—Continued
Point
CCGOM
CCGOM
CCGOM
CCGOM
CCGOM
CCGOM
CCGOM
CCGOM
CCGOM
N. lat.
5 .........
6 .........
7 .........
8 .........
9 .........
10 .......
11 .......
12 .......
13 .......
42°10′
42°00′
42°00′
40°30′
39°00′
(2)
35°00′
35°00′
(3)
W. long.
65°50′
65°50′
65°40′
65°40′
65°40′
....................
(3)
(4)
....................
1 Intersection
with the New Hampshire
coastline.
2 Intersection of the south-facing shoreline of
Cape Cod, MA.
3 Intersection with the east-facing shoreline
of Cape Cod, MA.
4 Intersection with the west-facing shoreline
of Massachusetts.
SOUTHERN NEW ENGLAND/MID-ATLANTIC
WINTER FLOUNDER STOCK
AREA—Continued
Point
SNEW3
SNEW4
SNEW5
SNEW6
SNEW7
SNEW8
SNEW9
.............
.............
.............
.............
.............
.............
.............
N. lat.
42°20′
39°50′
39°50′
39°00′
39°00′
35°00′
35°00′
W. long.
68°50′
68°50′
71°40′
71°40′
70°00′
70°00′
(2)
1 Intersection of the north-facing Coastline of
Cape Cod, MA, and 70°00′ W. Long.
2 The intersection of the east-facing coastline of Outer Banks, NC, and 35°00′ N. Lat.
(D) SNE/MA yellowtail flounder stock
area. The SNE/MA stock area for the
purposes of the Regular B DAS Program
is the area bounded on the north, east,
and south by straight lines connecting
the following points in the order stated:
(F) Windowpane flounder northern
stock area. The windowpane flounder
northern stock area, for the purposes of
prohibition on retention of northern
windowpane flounder specified under
§ 648.86, is the area defined by straight
lines connecting the following points in
the order stated:
SNE/MA YELLOWTAIL FLOUNDER
STOCK AREA
WINDOWPANE FLOUNDER NORTHERN
STOCK AREA
Point
N. lat.
SNEMA1 ...........
SNEMA2 ...........
SNEMA3 ...........
SNEMA4 ...........
SNEMA5 ...........
SNEMA6 ...........
SNEMA7 ...........
SNEMA8 ...........
SNEMA9 ...........
SNEMA10 .........
SNEMA11 .........
SNEMA12 .........
SNEMA13 .........
SNEMA14 .........
SNEMA15 .........
SNEMA16 .........
SNEMA17 .........
40°00′
40°00′
40°30′
40°30′
41°00′
41°00′
41°30′
39°00′
41°00′
41°00′
41°30′
(1)
(2)
(3)
40°30′
40°30′
40°00′
Point
W. long.
74°00′
72°00′
72°00′
69°30′
69°30′
69°00′
70°00′
70°00′
70°00′
70°30′
70°30′
72°00′
72°00′
73°00′
73°00′
74°00′
74°00′
G12 ...................
WIN1 .................
WIN2 .................
WIN3 .................
WIN4 .................
WIN5 .................
WIN6 .................
WIN7 .................
WIN8 .................
WIN9 .................
WIN10 ...............
N. lat.
(1)
41°20′
41°20′
41°10′
41°10′
41°00′
41°00′
39°50′
39°50′
39°00′
39°00′
W. long.
70°00′
70°00′
69°50′
69°50′
69°30′
69°30′
68°50′
68°50′
69°00′
69°00′
(2)
1 South-facing
coastline of Cape Cod, MA.
of 39°00′ N. Lat. and the
boundary of the EEZ.
2 Intersection
(G) GB yellowtail flounder stock area.
The GB yellowtail flounder stock area,
for the purposes of the Regular B DAS
Program, is the area defined as the U.S./
Canada Management Areas, as specified
in paragraphs (a)(1)(i) and (ii) of this
(E) SNE/MA winter flounder stock
section.
area. The SNE winter flounder stock
(H) GB winter flounder stock area.
area, for the purposes of the Regular B
The GB winter flounder stock area, for
DAS Program and the prohibition on
the purposes of the Regular B DAS
retention of winter flounder specified
Program, is the area defined as the U.S./
under § 648.86, is the area defined by
Canada Management Areas, as specified
straight lines connecting the following
in paragraphs (a)(1)(i) and (ii) of this
points in the order stated:
section.
SOUTHERN NEW ENGLAND/MID-ATLAN(I) GOM winter flounder stock area.
TIC WINTER FLOUNDER STOCK AREA
The GOM winter flounder stock area, for
the purposes of the Regular B DAS
Point
N. lat.
W. long.
Program, is the area defined by straight
1)
SNEW1 .............
(
70°00′ lines connecting the following points in
SNEW2 .............
42°20′
70°00′ the order stated:
1 South-facing
shoreline of Connecticut.
2 North-facing shoreline of Long Island, New
York.
3 South-facing shoreline of Long Island, New
York.
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GOM WINTER FLOUNDER STOCK AREA
Point
N. lat.
CA I HOOK GEAR HADDOCK ACCESS
AREA
W. long.
Point
GOM1
GOM2
GOM3
GOM4
GOM5
GOM6
GOM7
GOM8
...............
...............
...............
...............
...............
...............
...............
...............
(1)
42°20′
42°20′
43°50′
43°50′
44°20′
44°20′
(2)
70°00′
70°00′
67°40′
67°40′
66°50′
66°50′
67°00′
67°00′
1 Intersection of the north-facing coastline of
Cape Cod, MA, and 70°00′ W. Long.
2 Intersection of the south-facing Maine
coastline and 67°00′ W. Long.
(vi) Closure and in-season
modification to the Regular B DAS
Program. The Regional Administrator,
based upon information required under
§§ 648.7, 648.9, 648.10, or this
paragraph (b)(10)(vi), and any other
relevant information, in a manner
consistent with the Administrative
Procedure Act, may prohibit the use of
Regular B DAS, modify possession
restrictions, or implement other
measures, including a partial closure for
the Regular B DAS Program, for the
duration of a quarter or fishing year, if
it is projected that continuation of the
Regular B DAS Program would
undermine the achievement of the
objectives of the FMP or Regular B DAS
Program. Reasons for modification or
termination of the program include, but
are not limited to, the following:
Inability to constrain catches to the
Incidental Catch TACs; evidence of
excessive discarding; a significant
difference in flipping rates between
observed and unobserved trips; or
insufficient observer coverage to
adequately monitor the program.
(11) CA I Hook Gear Haddock SAP.—
(i) Eligibility. Vessels issued a valid
limited access NE multispecies DAS
permit are eligible to participate in the
CA I Hook Gear Haddock SAP, and may
fish in the CA I Hook Gear Haddock
Access Area, as described in paragraph
(b)(11)(ii) of this section, for the season
specified in paragraph (b)(11)(iii) of this
section, provided such vessels comply
with the requirements of this section,
and provided the SAP is not closed
according to the provisions specified
under paragraph (b)(11)(iv)(I) or
(b)(11)(vi)(F) of this section. Copies of a
chart depicting this area are available
from the Regional Administrator upon
request.
(ii) CA I Hook Gear Haddock Access
Area. The CA I Hook Gear Haddock
Access Area is the area defined by
straight lines connecting the following
points in the order stated:
VerDate Nov<24>2008
20:07 Apr 10, 2009
Jkt 217001
N. lat.
Hook 1 ..............
CI4 ....................
CI1 ....................
Hook 2 ..............
41°09′
41°30′
41°30′
41°04′
W. long.
68°30′
68°30′
69°23′
69°01′
(iii) Season. The overall season for the
CA I Hook Gear Haddock SAP is May
1 through January 31.
(iv) General program restrictions.
General program restrictions specified
in this paragraph (b)(11)(iv) apply to all
eligible vessels as specified in paragraph
(b)(11)(i) of this section. Further
program restrictions specific to Sector
and non-Sector vessels are specified in
paragraphs (b)(11)(v) and (vi) of this
section.
(A) DAS use restrictions. A vessel
fishing in the CA I Hook Gear Haddock
SAP may not initiate a DAS flip. A
vessel is prohibited from fishing in the
CA I Hook Gear Haddock SAP while
making a trip under the Regular B DAS
Pilot Program described under
paragraph (b)(10) of this section. DAS
will be charged as described in § 648.10.
(B) VMS requirement. An eligible NE
multispecies DAS vessel fishing in the
CA I Hook Gear Haddock SAP specified
in this paragraph (b)(11) must have
installed on board an operational VMS
unit that meets the minimum
performance criteria specified in
§§ 648.9 and 648.10.
(C) Observer notifications. For the
purpose of selecting vessels for observer
deployment, a vessel must provide
notice to NMFS of the vessel name;
contact name for coordination of
observer deployment; telephone number
for contact; and date, time, and port of
departure at least 72 hr prior to the
beginning of any trip that it declares
into the CA I Hook Gear Haddock SAP,
as required in paragraph (b)(11)(iv)(D) of
this section, and in accordance with
instructions provided by the Regional
Administrator.
(D) VMS declaration. Prior to
departure from port, a vessel intending
to participate in the CA I Hook Gear
Haddock SAP must declare into the SAP
via VMS, and indicate the type of DAS
that it intends to fish. A vessel declared
into the CA I Hook Gear Haddock SAP
may fish only on a declared trip in the
CA I Hook Gear Haddock Special Access
Area described under paragraph
(b)(11)(ii) of this section.
(E) Gear restrictions. A vessel
declared into and fishing in the CA I
Hook Gear Haddock SAP may fish with
and possess on board demersal longline
gear or tub trawl gear only, unless
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17061
further restricted as specified under
paragraph (b)(11)(v)(B) of this section.
(F) Haddock TAC.—(1) Allocation
and distribution. The maximum total
amount of haddock that may be caught
(landings and discards) in the CA I
Hook Gear SAP Area in any fishing year
is based upon the size of the TAC
allocated for the 2004 fishing year
(1,130 mt live weight), adjusted
according to the growth or decline of the
western GB (WGB) haddock exploitable
biomass (in relationship to its size in
2004), according to the following
formula: BiomassYEAR X = (1,130 mt
live weight) × (Projected WGB Haddock
ExploitableBiomassYEAR X/WGB
Haddock Exploitable Biomass2004). The
size of the western component of the
stock is considered to be 35 percent of
the total stock size, unless modified by
a stock assessment. The Regional
Administrator shall specify the haddock
TAC for the SAP, in a manner consistent
with applicable law.
(2) [Reserved]
(G) Trip restrictions. A vessel is
prohibited from deploying fishing gear
outside of the CA I Hook Gear Haddock
SAP Area on the same fishing trip on
which it is declared into the CA I Hook
Gear Haddock SAP, and must exit the
SAP if the vessel exceeds the applicable
landing limits described in paragraph
(b)(11)(iv)(H) of this section.
(H) Landing limits. For all eligible
vessels declared into the CA I Hook
Gear Haddock SAP described in
paragraph (b)(11)(i) of this section,
landing limits for NE multispecies other
than cod, which are specified at
paragraphs (b)(11)(v)(C) and
(b)(11)(vi)(C) of this section, are as
specified at § 648.86. Unless otherwise
specified in this part, such vessels are
prohibited from discarding legal-sized
regulated NE multispecies, Atlantic
halibut, and ocean pout, and must exit
the SAP and cease fishing if any trip
limit is achieved or exceeded.
(I) Mandatory closure of CA I Hook
Gear Haddock Access Area. When the
Regional Administrator determines that
the haddock TAC specified in paragraph
(b)(11)(iv)(F) of this section has been
caught, NMFS shall close, through
rulemaking consistent with the
Administrative Procedure Act, the CA I
Hook Gear Haddock SAP Area as
specified in paragraph (b)(11)(ii) of this
section, to all eligible vessels.
(J) Bait restriction. A vessel declared
into and fishing in the CA I Hook Gear
Haddock SAP is prohibited from using
squid as bait when participating in the
CA I Hook Gear Haddock SAP.
(v) Sector vessel program restrictions.
In addition to the general program
restrictions specified at paragraph
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(b)(11)(iv) of this section, the
restrictions specified in this paragraph
(b)(11)(v) apply only to Sector vessels
declared into the CA I Hook Gear
Haddock SAP.
(A) DAS use restrictions. Sector
vessels fishing in the CA I Hook Gear
Haddock SAP may use Category A,
Regular B, or Reserve B DAS, in
accordance with § 648.82(d).
(B) Gear restrictions. A vessel enrolled
in the Sector is subject to the gear
requirements of the Sector Operations
Plan as approved under § 648.87(d).
(C) Landing limits. A Sector vessel
declared into the CA I Hook Gear
Haddock SAP described in paragraph
(b)(11)(i) of this section is subject to the
cod landing limit in effect under the
Sector’s Operations Plan as approved
under § 648.87(d).
(D) Reporting requirements. The
owner or operator of a Sector vessel
declared into the CA I Hook Gear
Haddock SAP must submit reports to
the Sector Manager, with instructions to
be provided by the Sector Manager, for
each day fished in the CA I Hook Gear
Haddock SAP Area. The Sector Manager
shall provide daily reports to NMFS,
including at least the following
information: Total pounds of haddock,
cod, yellowtail flounder, winter
flounder, witch flounder, pollock, and
white hake kept; total pounds of
haddock, cod, yellowtail flounder,
winter flounder, witch flounder,
pollock, and white hake discarded; date
fish were caught; and VTR serial
number, as instructed by the Regional
Administrator. Daily reporting must
continue even if the vessel operator is
required to exit the SAP as required
under paragraph (b)(11)(iv)(F) of this
section.
(E) GB cod incidental catch TAC.
There is no GB cod incidental catch
TAC specified for Sector vessels
declared into the CA I Hook Gear
Haddock SAP. All cod caught by Sector
vessels fishing in the SAP count toward
the Sector’s annual GB cod TAC,
specified in § 648.87(d)(1)(iii).
(vi) Non-Sector vessel program
restrictions. In addition to the general
program restrictions specified in
paragraph (b)(11)(iv) of this section, the
restrictions specified in this paragraph
(b)(11)(vi) apply only to non-Sector
vessels declared into the CA I Hook
Gear Haddock SAP.
(A) DAS use restrictions. Non-Sector
vessels fishing in the CA I Hook Gear
Haddock SAP may use Regular B or
Reserve B DAS, in accordance with
§ 648.82(d)(2)(i)(A) and (d)(2)(ii)(A). A
non-Sector vessel is prohibited from
using A DAS when declared into the
SAP.
VerDate Nov<24>2008
20:07 Apr 10, 2009
Jkt 217001
(B) Gear restrictions. A non-Sector
vessel declared into the CA I Hook Gear
Haddock SAP is exempt from the
maximum number of hooks restriction
specified in § 648.80(a)(4)(v).
(C) Landing limits. A non-Sector
vessel declared into the CA I Hook Gear
Haddock SAP described in paragraph
(b)(11)(i) of this section may not land,
fish for, or possess on board more than
1,000 lb (453.6 kg) of cod per trip. A
non-Sector vessel is not permitted to
discard legal-sized cod prior to reaching
the landing limit, and is required to end
its trip if the cod trip limit is achieved
or exceeded.
(D) VMS declaration. Prior to
departure from port, a vessel intending
to participate in the CA I Hook Gear
Haddock SAP must declare into the SAP
via VMS, and indicate the type of DAS
that it intends to fish. A vessel declared
into the CA I Hook Gear Haddock SAP
may fish only on a declared trip in the
CA I Hook Gear Haddock Special Access
Area described under paragraph
(b)(11)(ii) of this section.
(E) Incidental catch TACs. The
maximum amount of GB cod and
pollock (landings and discards) that
may be cumulatively caught by nonSector vessels from the CA I Hook Gear
Haddock Access Area in a fishing year
is the amount specified under
paragraphs (b)(9)(ii) and (iv) of this
section, respectively.
(F) Mandatory closure of CA I Hook
Gear Haddock Access Area due to catch
of any incidental catch TAC. When the
Regional Administrator determines that
either the GB cod or pollock incidental
catch TAC specified in paragraph
(b)(11)(vi)(E) of this section has been
caught, NMFS shall close, through
rulemaking consistent with the
Administrative Procedure Act, the CA I
Hook Gear Haddock Access Area to all
non-Sector fishing vessels.
*
*
*
*
*
■ 9. In § 648.86, paragraph (b) is
suspended; and paragraphs (l), (m), and
(n) are added to read as follows:
§ 648.86 NE multispecies possession
restrictions
*
*
*
*
*
(l) Cod.—(1) GOM cod landing limit.
(i) Except as provided in paragraphs
(l)(1)(ii) and (l)(4) of this section, or
unless otherwise restricted under
§ 648.85, a vessel fishing under a NE
multispecies DAS may land only up to
800 lb (362.9 kg) of cod during the first
24-hr period after the vessel has started
a trip on which cod were landed (e.g.,
a vessel that starts a trip at 6 a.m. may
call out of the DAS program at 11 a.m.
and land up to 800 lb (362.9 kg), but the
vessel cannot land any more cod on a
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Frm 00034
Fmt 4701
Sfmt 4700
subsequent trip until at least 6 a.m. on
the following day). For each trip longer
than 24 hr, a vessel may land up to an
additional 800 lb (362.9 kg) for each
additional 24-hr block of DAS fished, or
part of an additional 24-hr block of DAS
fished, up to a maximum of 4,000 lb
(1,814.4 kg) per trip (e.g., a vessel that
has been called into the DAS program
for more than 24 hr, but less than 48 hr,
may land up to, but no more than, 1,600
lb (725.7 kg) of cod). A vessel that has
been called into only part of an
additional 24-hr block of a DAS (e.g., a
vessel that has been called into the DAS
program for more than 24 hr, but less
than 48 hr) may land up to an additional
800 lb (362.9 kg) of cod for that trip,
provided the vessel complies with the
provisions of paragraph (l)(1)(ii) of this
section. Cod on board a vessel subject to
this landing limit must be separated
from other species of fish and stored so
as to be readily available for inspection.
(ii) A vessel that has been called into
or declared into only part of an
additional 24-hr block may come into
port with and offload cod up to an
additional 800 lb (362.9 kg), provided
that the vessel operator, with the
exception of vessels fishing in one or
both of the two differential DAS areas
under the restrictions of § 648.82(e)(4),
complies with the following:
(A) For a vessel that is subject to the
VMS provisions specified under
§ 648.10(b), the vessel declares through
VMS that insufficient DAS have elapsed
in order to account for the amount of
cod onboard and, after returning to port,
does not depart from a dock or mooring
in port, unless transiting as allowed
under paragraph (l)(3) of this section,
until the rest of the additional 24-hr
block of the DAS has elapsed, regardless
of whether all of the cod on board is
offloaded (e.g., a vessel that has been in
the DAS program for 25 hr prior to
crossing the VMS demarcation line on
the return to port may land only up to
1,600 lb (725.7 kg) of cod, provided the
vessel does not declare another trip or
leave port until 48 hr have elapsed from
the beginning of the trip).
(B) For a vessel that has been
authorized by the Regional
Administrator to utilize the DAS call-in
system, as specified under § 648.10(c),
in lieu of VMS, the vessel does not call
out of the DAS program as described
under § 648.10(c)(3) and does not depart
from a dock or mooring in port, unless
transiting as allowed in paragraph (l)(3)
of this section, until the rest of the
additional 24-hr block of DAS has
elapsed, regardless of whether all of the
cod on board is offloaded (e.g., a vessel
that has been called into the DAS
program for 25 hr at the time of landing
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may land only up to 1,600 lb (725.6 kg)
of cod, provided the vessel does not call
out of the DAS program or leave port
until 48 hr have elapsed from the
beginning of the trip).
(2) GB cod landing and maximum
possession limits. (i) Unless otherwise
restricted under § 648.85 or the
provisions of paragraph (l)(2)(ii) of this
section, or unless exempt from the
landing limit under paragraph (l)(1) of
this section as authorized under the
Sector provisions of § 648.87, a NE
multispecies DAS vessel may land up to
1,000 lb (453.6 kg) of cod per DAS, or
part of a DAS, provided it complies with
the requirements specified at paragraph
(l)(4) of this section and this paragraph
(l)(2). A NE multispecies DAS vessel
may land up to 1,000 lb (453.6 kg) of
cod during the first 24-hr period after
such vessel has started a trip on which
cod were landed (e.g., a vessel that starts
a trip at 6 a.m. may call out of the DAS
program at 11 a.m. and land up to 1,000
lb (453.6 kg) of cod, but the vessel
cannot land any more cod on a
subsequent trip until at least 6 a.m. on
the following day). For each trip longer
than 24 hr, a vessel may land up to an
additional 1,000 lb (453.6 kg) of cod for
each additional 24-hr block of DAS
fished, or part of an additional 24-hr
block of DAS fished, up to a maximum
of 10,000 lb (4,536 kg) of cod per trip
(e.g., a vessel that has been called into
the DAS program for more than 24 hr,
but less than 48 hr, may land up to, but
no more than, 2,000 lb (907.2 kg) of
cod). A vessel that has been called into
only part of an additional 24-hr block of
a DAS (e.g., a vessel that has been called
into the DAS program for more than 24
hr, but less than 48 hr) may land up to
an additional 1,000 lb (453.6 kg) of cod
for that trip, provided the vessel
complies with the provisions of
paragraph (l)(2)(ii) of this section. Cod
on board a vessel subject to this landing
limit must be separated from other
species of fish and stored so as to be
readily available for inspection.
(ii) A vessel that has been called into
or declared into only part of an
additional 24-hr block may come into
port with and offload cod up to an
additional 1,000 lb (453.6 kg), provided
that the vessel operator, with the
exception of vessels fishing in one or
both of the differential DAS areas under
the restrictions of § 648.82(e)(4),
complies with the following:
(A) For a vessel that has been
authorized by the Regional
Administrator to utilize the DAS call-in
system as specified under § 648.10(c), in
lieu of VMS, the vessel does not call out
of the DAS program as described under
§ 648.10(c)(3) and does not depart from
VerDate Nov<24>2008
20:07 Apr 10, 2009
Jkt 217001
a dock or mooring in port, unless
transiting, as allowed in paragraph (l)(3)
of this section, until the rest of the
additional 24-hr block of DAS has
elapsed, regardless of whether all of the
cod on board is offloaded (e.g., a vessel
that has been called into the DAS
program for 25 hr at the time of landing
may land only up to 2,000 lb (907.2 kg)
of cod, provided the vessel does not call
out of the DAS program or leave port
until 48 hr have elapsed from the
beginning of the trip.)
(B) For a vessel that is subject to the
VMS provisions specified under
§ 648.10(b), the vessel declares through
VMS that insufficient DAS have elapsed
in order to account for the amount of
cod onboard, and after returning to port
does not depart from a dock or mooring
in port, unless transiting, as allowed
under paragraph (l)(3) of this section,
until the rest of the additional 24-hr
block of the DAS has elapsed, regardless
of whether all of the cod on board is
offloaded (e.g., a vessel that has been in
the DAS program for 25 hr prior to
crossing the VMS demarcation line on
the return to port may land only up to
2,000 lb (907.2 kg) of cod, provided the
vessel does not declare another trip or
leave port until 48 hr have elapsed from
the beginning of the trip.)
(3) Transiting. A vessel that has
exceeded the cod landing limit as
specified in paragraphs (l)(1) and (2) of
this section, and that is, therefore,
subject to the requirement to remain in
port for the period of time described in
paragraphs (l)(1)(ii)(A) and (l)(2)(ii)(A)
of this section, may transit to another
port during this time, provided that the
vessel operator notifies the Regional
Administrator, either at the time the
vessel reports its hailed weight of cod,
or at a later time prior to transiting, and
provides the following information:
Vessel name and permit number,
destination port, time of departure, and
estimated time of arrival. A vessel
transiting under this provision must
stow its gear in accordance with one of
the methods specified in § 648.23(b) and
may not have any fish on board the
vessel.
(4) Exemption. A vessel fishing under
a NE multispecies DAS is exempt from
the landing limit described in paragraph
(l)(1) of this section when fishing south
of the Gulf of Maine Regulated Mesh
Area, defined in § 648.80(a)(1), provided
that it complies with the requirement of
this paragraph (l)(4).
(i) Declaration. With the exception of
vessels declared into the U.S./Canada
Management Area, as described under
§ 648.85(a)(3)(viii), a NE multispecies
DAS vessel that fishes or intends to fish
south of the line described in this
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Fmt 4701
Sfmt 4700
17063
paragraph (l)(4)(i) under the cod trip
limits described under paragraph (l)(2)
of this section, must, prior to leaving the
dock, declare its intention to do so
through the VMS, in accordance with
instructions to be provided by the
Regional Administrator. In lieu of a
VMS declaration, the Regional
Administrator may authorize such
vessels to obtain a letter of
authorization. If a letter of authorization
is required, such vessel may not fish
north of the exemption area for a
minimum of 7 consecutive days (when
fishing under the NE multispecies DAS
program), and must carry the
authorization letter on board.
(ii) A vessel exempt from the GOM
cod landing limit may not fish north of
the line specified in this paragraph
(l)(4)(ii) for the duration of the trip, but
may transit the GOM Regulated Mesh
Area, provided that its gear is stowed in
accordance with the provisions of
§ 648.23(b). A vessel fishing north and
south of the line on the same trip is
subject to the most restrictive applicable
cod trip limit.
(m) Witch flounder. Unless otherwise
restricted under this part, a vessel
issued a NE multispecies DAS permit, a
limited access Handgear A permit, an
open access Handgear B permit, or a
monkfish limited access permit and
fishing under the monkfish Category C
or D permit provisions may land up to
1,000 lb (453.6 kg) of witch flounder per
DAS, or any part of a DAS, up to 5,000
lb (2,268.1 kg) per trip.
(n) Zero retention stocks.—(1) SNE
winter flounder. Vessels issued a NE
multispecies permit may not fish for,
possess, or land winter flounder caught
in the SNE/MA winter flounder stock
area, as defined in § 648.85(b)(10)(v)(E).
Vessels may transit this area with GOM
or GB winter flounder on board the
vessel, provided that gear is stowed in
accordance with the provisions of
§ 648.23(b). Vessels fishing for winter
flounder in multiple stock areas are
subject to the most restrictive winter
flounder possession limit.
(2) Northern windowpane flounder.
Vessels issued a NE multispecies permit
may not fish for, possess, or land
windowpane flounder caught in the
northern windowpane flounder stock
area, as defined in § 648.85(b)(10)(v)(F).
Vessels may transit this area with
southern windowpane flounder on
board, provided that gear is stowed in
accordance with the provisions of
§ 648.23(b). Vessels fishing for
windowpane flounder in multiple stock
areas would be subject to the most
restrictive windowpane flounder
possession limit.
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Federal Register / Vol. 74, No. 69 / Monday, April 13, 2009 / Rules and Regulations
(3) Ocean pout. Vessels issued a NE
multispecies permit may not fish for,
possess or land ocean pout.
■ 10. In § 648.89, paragraphs (b)(1),
(c)(1)(v), and (c)(2) are suspended, and
paragraphs (b)(5), (c)(1)(vi), (c)(5), and
(f) are added to read as follows:
§ 648.89 Recreational and charter/party
vessel restrictions.
*
*
*
*
*
(b) * * *
(5) Minimum fish sizes. Unless further
restricted under paragraph (b)(3) of this
section, persons aboard charter or party
vessels permitted under this part and
not fishing under the NE multispecies
DAS program, and recreational fishing
vessels in or possessing fish from the
EEZ, may not possess fish smaller than
the minimum fish sizes, measured in
total length (TL), as follows:
MINIMUM FISH SIZES (TL) FOR CHARTER, PARTY, AND PRIVATE RECREATIONAL VESSELS
Species
Sizes
Cod ....................................
Haddock .............................
Pollock ...............................
Witch flounder (gray sole)
Yellowtail flounder .............
Atlantic halibut ...................
American plaice (dab) .......
Winter flounder (blackback)
Redfish ...............................
22 in (58.4 cm)
18 in (45.7 cm)
19 in (48.3 cm)
14 in (35.6 cm)
13 in (33.0 cm)
36 in (91.4 cm)
14 in (35.6 cm)
12 in (30.5 cm)
9 in (22.9 cm)
(c) * * *
(1) * * *
(vi) Seasonal GOM cod possession
prohibition. Persons aboard private
recreational fishing vessels fishing in
the GOM Regulated Mesh Area specified
under § 648.80(a)(1) may not fish for,
possess, or land any cod from November
1 through April 15. Private recreational
vessels in possession of cod caught
outside the GOM Regulated Mesh Area
may transit this area, provided all bait
and hooks are removed from all fishing
rods, and any cod on board has been
gutted and stored.
*
*
*
*
*
(5) Charter/party vessels. Charter/
party vessels are subject to the following
possession limit restrictions:
(i) Unless further restricted by the
Seasonal GOM Cod Possession
Prohibition, specified under paragraph
(c)(5)(v) of this section, each person on
a charter/party vessel may possess no
more than 10 cod per day in, or
harvested from, the EEZ.
(ii) For purposes of counting fish,
fillets shall be converted to whole fish
at the place of landing by dividing the
number of fillets by two. If fish are
filleted into a single (butterfly) fillet,
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20:07 Apr 10, 2009
Jkt 217001
such fillet shall be deemed to be from
one whole fish.
(iii) Cod harvested by charter/party
vessels with more than one person
aboard may be pooled in one or more
containers. Compliance with the
possession limits will be determined by
dividing the number of fish on board by
the number of persons on board. If there
is a violation of the possession limits on
board a vessel carrying more than one
person, the violation shall be deemed to
have been committed by the owner and
operator of the vessel.
(iv) Cod must be stored so as to be
readily available for inspection.
(v) Seasonal GOM cod possession
prohibition. Persons aboard charter/
party fishing vessels fishing in the GOM
Regulated Mesh Area specified under
§ 648.80(a)(1) may not fish for or possess
any cod from November 1 through April
15. Charter/party vessels in possession
of cod caught outside the GOM
Regulated Mesh Area may transit this
area, provided all bait and hooks are
removed from all fishing rods, and any
cod on board has been gutted and
stored.
*
*
*
*
*
(f) SNE/MA winter flounder retention
prohibition. Private recreational and
charter/party vessels fishing in the SNE/
MA winter flounder stock area, as
defined in § 648.85(b)(10)(v)(E), may not
fish for, possess, or land winter
flounder. Recreational vessels in
possession of winter flounder caught
outside of the SNE/MA winter flounder
may transit this area, provided all bait
and hooks are removed from all fishing
rods, and any winter flounder on board
has been stored.
■ 11. In § 648.92, paragraphs (b)(1)(i),
(b)(1)(iii)(A), (b)(2), and (b)(8)(v) are
suspended; and paragraphs (b)(1)(iii)(C),
(b)(1)(vi), (b)(8)(vi), and (b)(10) are
added to read as follows:
§ 648.92 Effort-control program for
monkfish limited access vessels.
*
*
*
*
*
(b) * * *
(1) * * *
(iii) * * *
(C) Vessels that change their DAS
declaration from a NE multispecies
Category A DAS to a monkfish DAS
during the course of a trip remain
subject to the NE multispecies DAS
usage requirements (i.e., use a NE
multispecies Category A DAS in
conjunction with the monkfish DAS)
described in paragraph (b)(10)(i) of this
section.
*
*
*
*
*
(vi) General provision. Limited access
monkfish permit holders shall be
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Fmt 4701
Sfmt 4700
allocated 31 monkfish DAS each fishing
year to be used in accordance with the
restrictions of this paragraph (b), unless
otherwise restricted by paragraph
(b)(1)(ii) of this section or modified by
§ 648.96(b)(3), or unless the vessel is
enrolled in the Offshore Fishery
Program in the SFMA, as specified in
paragraph (b)(1)(iv) of this section. The
annual allocation of monkfish DAS shall
be reduced by the amount calculated in
paragraph (b)(1)(v) of this section for the
research DAS set-aside. Limited access
NE multispecies and limited access sea
scallop permit holders who also possess
a limited access monkfish permit must
use a NE multispecies or sea scallop
DAS concurrently with each monkfish
DAS utilized, except as provided in
paragraph (b)(10) of this section, unless
otherwise specified under this subpart
F.
*
*
*
*
*
(8) * * *
(vi) Method of counting DAS. A vessel
fishing with gillnet gear under a
monkfish DAS shall accrue 15 hr of
monkfish DAS for all trips less than or
equal to 15 hr in duration. Such vessels
shall accrue monkfish DAS based on
actual time at sea for trips greater than
15 hr in duration. A vessel fishing with
gillnet gear under only a monkfish DAS
is not required to remove gillnet gear
from the water upon returning to the
dock and calling out of the DAS
program, provided the vessel complies
with the requirements and conditions of
paragraphs (b)(8)(i)–(vi) of this section.
A vessel fishing with gillnet gear under
a joint monkfish and NE multispecies
DAS, as required under
§ 648.92(b)(10)(i), that is declared as a
trip gillnet vessel under the NE
Multispecies FMP, must remove its
gillnet gear from the water prior to
calling out of the DAS program, as
specified at § 648.82(j)(2).
*
*
*
*
*
(10) Category C, D, F, G, or H limited
access monkfish permit holders—(i)
Unless otherwise specified in paragraph
(b)(10)(ii) of this section, each monkfish
DAS used by a limited access NE
multispecies or scallop DAS vessel
holding a Category C, D, F, G, or H
limited access monkfish permit shall
also be counted as a NE multispecies or
scallop DAS, as applicable, except when
a Category C, D, F, G, or H vessel with
a limited access NE multispecies DAS
permit has an allocation of NE
multispecies Category A DAS, specified
under § 648.82(d)(1), that is less than
the number of monkfish DAS allocated
for the fishing year May 1 through April
30. Under this circumstance, the vessel
may fish under the monkfish limited
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Federal Register / Vol. 74, No. 69 / Monday, April 13, 2009 / Rules and Regulations
access Category A or B provisions, as
applicable, for the number of DAS that
equal the difference between the
number of its allocated monkfish DAS
and its allocated NE multispecies
Category A DAS. For such vessels, when
the total allocation of NE multispecies
Category A DAS has been used, a
monkfish DAS may be used without
concurrent use of a NE multispecies
DAS, provided that the vessel fishes
under the regulations pertaining to a
Category B vessel and does not retain
any regulated NE multispecies. For
example, if a monkfish Category D
vessel’s NE multispecies Category A
DAS allocation is 20, and the monkfish
allocation is 31, the vessel may use up
to 11 of its monkfish DAS without
concurrently using a groundfish DAS
(31¥20 = 11), after all 20 NE
multispecies Category A DAS are used.
In addition, Category C and D vessels
that are fishing in one or both of the 2:1
differential DAS areas specified in
§ 648.82(e)(4)(i) shall accrue monkfishonly DAS to account for those monkfish
DAS that are ‘‘lost’’ as a result of fishing
in the differential DAS area (resulting
from the use of groundfish DAS at a
higher rate). These vessels shall accrue
monkfish-only DAS at a rate of 1
monkfish DAS for every 2 NE
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20:07 Apr 10, 2009
Jkt 217001
multispecies DAS used in the
differential area (2:1 rate). These
monkfish-only DAS may later be used
without concurrent use of a NE
multispecies DAS, provided that the
vessel fishes under the regulations
pertaining to a Category A or Category
B vessel and does not retain any
regulated NE multispecies. A vessel
holding a Category C, D, F, G, or H
limited access monkfish permit may not
use a NE multispecies Category B
Regular DAS under the NE Multispecies
Regular B DAS Program, as specified
under § 648.85(b)(10), in order to satisfy
the requirement of this paragraph
(b)(10)(i) to use a NE multispecies DAS
concurrently with a monkfish DAS.
(ii) Category C, D, F, G, or H vessels
that lease NE multispecies DAS.—(A) A
monkfish Category C, D, F, G, or H
vessel that has ‘‘monkfish-only’’ DAS, as
specified in paragraph (b)(2)(i) of this
section, and that leases NE multispecies
DAS from another vessel pursuant to
§ 648.82(k), is required to fish its
available ‘‘monkfish-only’’ DAS in
conjunction with its leased NE
multispecies DAS, to the extent that the
vessel has NE multispecies DAS
available.
(B) A monkfish Category C, D, F, G,
or H vessel that leases DAS to another
vessel(s), pursuant to § 648.82(k) must
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Fmt 4701
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17065
forfeit a monkfish DAS for each NE
multispecies DAS that the vessel leases,
equal in number to the difference
between the number of remaining NE
multispecies DAS and the number of
unused monkfish DAS at the time of the
lease. For example, if a lessor vessel that
had 31 unused monkfish DAS and 35
allocated NE multispecies DAS leased
10 of its NE multispecies DAS to
another vessel, the lessor would forfeit
6 of its monkfish DAS (10 ¥ (35 NE
multispecies DAS ¥ 31 monkfish DAS)
= 6).
*
*
*
*
*
■ 12. In § 648.95, paragraph (h) is
suspended and paragraph (i) is added to
read as follows:
§ 648.95
SFMA.
Offshore Fishery Program in the
*
*
*
*
*
(i) DAS usage by NE multispecies or
sea scallop limited access permit
holders. A vessel issued a Category F
permit that also has been issued either
a NE multispecies or sea scallop limited
access permit, and is fishing on a
monkfish DAS, is subject to the DAS
usage requirements specified in
§ 648.92(b)(10).
[FR Doc. E9–8092 Filed 4–10–09; 8:45 am]
BILLING CODE 3510–22–P
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Agencies
[Federal Register Volume 74, Number 69 (Monday, April 13, 2009)]
[Rules and Regulations]
[Pages 17030-17065]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-8092]
[[Page 17029]]
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Part III
Department of Commerce
-----------------------------------------------------------------------
National Oceanic and Atmospheric Administration
-----------------------------------------------------------------------
50 CFR Part 648
Fisheries of the Northeastern United States; Northeast Multispecies
Fishery; Secretarial Interim Action; Final Rule
Federal Register / Vol. 74, No. 69 / Monday, April 13, 2009 / Rules
and Regulations
[[Page 17030]]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 648
[Docket No. 080521698-9067-02]
RIN 0648-AW87
Fisheries of the Northeastern United States; Northeast
Multispecies Fishery; Secretarial Interim Action
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Temporary final rule; interim measures; request for comments.
-----------------------------------------------------------------------
SUMMARY: NMFS implements this final interim rule pursuant to its
authority to issue interim management measures under the authority of
the Magnuson-Stevens Fishery Conservation and Management Act (Magnuson-
Stevens Act). This action is intended to immediately reduce overfishing
on certain stocks managed by the Northeast (NE) Multispecies Fishery
Management Plan (FMP), without jeopardizing the likelihood that
overfished stocks can achieve rebuilding objectives until long-term
measures can be implemented under Amendment 16 to the FMP. Measures for
the commercial fishery include an expanded differential days-at-sea
(DAS) area in Southern New England (SNE), where a vessel will be
charged 2 days for every day fished, and modified groundfish trip
limits. In addition, this action maintains the scheduled fishing year
(FY) 2009 DAS reduction included in the FMP, which results in an
approximate 18-percent reduction in Category A DAS. For private
recreational vessels fishing in the Exclusive Economic Zone (EEZ), and
for federally permitted charter/party vessels, this action extends in
time a seasonal prohibition on the possession of Gulf of Maine (GOM)
cod, and prohibits the possession of SNE/Mid-Atlantic (MA) winter
flounder. For federally permitted charter/party vessels, this action
implements a trip limit for Georges Bank (GB) cod. In addition, this
action implements measures to mitigate some of the negative, short-term
economic impacts of the FMP by expanding the Closed Area I (CA I) Hook
Gear Haddock Special Access Program (SAP); modifying the DAS Leasing
Program, the Regular B DAS Program, and the DAS Transfer Program;
continuing the Eastern U.S./Canada Haddock SAP; and implementing a
reduction in the haddock minimum size to 18 inches (45 cm) for both
commercial and recreational vessels. This action also specifies
management measures for the U.S./Canada Management Area for FY 2009.
NMFS anticipates that the interim measures will need to be renewed upon
the rule's expiration for an additional 185 days. Therefore, NMFS is
requesting public comments on these measures; comments received will be
considered during any subsequent action to extend this final interim
rule.
DATES: Effective May 1, 2009, through October 28, 2009. Comments must
be received by June 12, 2009.
ADDRESSES: You may submit comments, identified by 0648-AW87, by any one
of the following methods:
Electronic Submissions: Submit all electronic public
comments via the Federal e-rulemaking portal: https://www.regulations.gov.
Mail: Paper, disk, or CD-ROM comments should be sent to
Patricia A. Kurkul, Regional Administrator, National Marine Fisheries
Service, 55 Great Republic Drive, Gloucester, MA 01930-2276. Mark the
outside of the envelope: ``Comments on NE Multispecies Final Interim
Rule.''
Fax: (978) 281-9135.
Instructions: All comments received are part of the public record
and will generally be posted to https://www.regulations.gov without
change. All Personal Identifying Information (for example, name,
address, etc.) voluntarily submitted by the commenter may be publicly
accessible. Do not submit confidential business information or
otherwise sensitive or protected information.
NMFS will accept anonymous comments (enter ``N/A'' in the required
fields, if you wish to remain anonymous). Attachments to electronic
comments will be accepted in Microsoft Word, Excel, WordPerfect, or
Adobe PDF formats only.
NMFS prepared a Final Regulatory Flexibility Analysis (FRFA), which
consists of the Initial Regulatory Flexibility Analysis (IRFA), public
comments and responses, and the summary of impacts and alternatives
contained in the Classification section of the preamble of this final
rule. Copies of the small entity compliance guide are available from
the Regional Administrator, NMFS, Northeast Regional Office, at the
address noted above. Copies of the Environmental Assessment (EA)
prepared for this rule may be found at the following Internet address:
https://www.nero.noaa.gov/nero/regs/frdoc/08/08MultiInterimEA.pdf.
Written comments regarding the burden-hour estimates or other
aspects of the collection-of-information requirements contained in this
rule may be submitted to the Northeast Regional Office and by e-mail to
David_Rostker@omb.eop.gov, or fax to (202) 395-7285.
FOR FURTHER INFORMATION CONTACT: Thomas Warren, Fishery Policy Analyst,
(978) 281-9347, fax (978) 281-9135.
SUPPLEMENTARY INFORMATION: A proposed interim rule was published in the
Federal Register on January 16, 2009 (74 FR 2959), which includes
detailed information on the background and reasons pertinent to the
need to reduce fishing effort in the NE multispecies fishery for FY
2009. Comments on the proposed rule were accepted through February 17,
2009, which are summarized and responded to below. The FMP specifies
the management measures for 12 species, and a total of 19 stocks of
groundfish in Federal waters off the New England and Mid-Atlantic
coasts. Species managed by the FMP are Atlantic cod, haddock,
yellowtail flounder, pollock, American plaice, witch flounder, white
hake, windowpane flounder, Atlantic halibut, winter flounder, ocean
pout, and redfish. In 2008, the effectiveness of the management
measures and the validity of the status determination criteria
(biological reference points) were fully evaluated. This planned
assessment of the biological reference points (Groundfish Assessment
Review Meeting (GARM III)) was part of the FMP's biennial adjustment
process to be used for setting fishery measures for FY 2009 (May 1,
2009-April 30, 2010), and was also part of the rebuilding strategy,
which sought to evaluate the more fundamental scientific information
mid-way through the rebuilding period for most stocks. Although the
Council intended to meet a required May 1, 2009, implementation date
for Amendment 16, due to the timing and the somewhat unanticipated
results from GARM III (September 2008), the Council developed a revised
Amendment 16 schedule, which, if approved, is now expected to be
implemented on May 1, 2010. In addition, the Council voted on September
4, 2008, to request that NMFS implement an interim action for the
duration of FY 2009, and recommended a specific suite of management
measures for the interim action. As explained fully in Measure 12 under
``Proposed Commercial Measures'' of the proposed rule, NMFS did not
propose the Council's recommendations in the proposed rule
[[Page 17031]]
because NMFS believed that the Council's recommended alternative would
allow overfishing to continue for several stocks and not achieve
rebuilding objectives.
A summary of the GARM III results that formed the basis for the
proposed interim rule is in Table 1 below. Overfishing is occurring on
stocks when the ratio of the fishing mortality rate (F) to the F that
results in the maximum sustainable yield (MSY) (Fmsy) is greater than
1.0, and a stock is overfished if the ratio of the biomass level (B) to
the B that produces MSY (Bmsy) is equal to or less than 0.5.
Table 1--GARM III Stock Status Determination Criteria and 2007 Status
--------------------------------------------------------------------------------------------------------------------------------------------------------
2007
Fishing 2007 Estimated
Species Stock Fmsy Bmsy (mt) mortality Biomass 2008
(2007 F/ (2007 B/ fishing
Fmsy) Bmsy) mortality
--------------------------------------------------------------------------------------------------------------------------------------------------------
Cod............................................ GB.................................... 0.2466 148,084 1.2 0.12 0.41
GOM................................... 0.237 58,248 1.9 0.58 0.300
Haddock........................................ GB.................................... 0.350 158,873 0.49 2.05 0.083
GOM................................... 0.430 5,900 0.8 0.99 0.250
Yellowtail flounder............................ GB.................................... 0.254 43,200 1.1 0.22 0.130
SNE/MA................................ 0.254 27,400 1.6 0.13 0.120
CC/GOM................................ 0.239 7,790 1.7 0.25 0.289
American plaice................................ ...................................... 0.190 21,940 0.5 0.51 0.099
Witch flounder................................. ...................................... 0.200 11,447 1.5 0.30 0.296
Winter flounder................................ GB.................................... 0.260 16,000 1.1 0.31 0.131
GOM................................... 0.283 3,792 1.5 0.29 0.317
SNE/MA................................ 0.248 38,761 2.6 0.09 0.265
Redfish........................................ ...................................... 0.038 271,000 0.1 0.64 0.008
White hake..................................... ...................................... 0.125 56,254 1.2 0.35 0.065
Pollock*....................................... ...................................... 5.660 2.0 1.9 0.45 10.975
Windowpane*.................................... North................................. 0.500 1.4 3.9 0.38 1.96
South................................. 1.470 0.34 1.3 0.62 1.85
Ocean pout..................................... ...................................... 0.760 4.94 0.5 0.10 N/A
Atlantic halibut............................... ...................................... 0.073 49,000 0.9 0.03 0.06
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Pollock and windowpane flounder information was revised subsequent to GARM III in order to utilize 3-yr averages, and incorporate the fall survey data
for pollock; pollock Fmsy is listed in terms of relative exploitation index (catch per centered 3-yr survey index).
N/A indicates an estimate of F in 2008 was unavailable for this stock.
Although NMFS' initial fishing mortality rate goals for the FY 2009
interim period are unchanged, based on public comment, NMFS is
modifying several of the measures proposed in the proposed interim
rule, and asking for public comment on the modified final rule. This
decision to modify measures means that, even though substantial
reductions in F will be achieved by this rule, overfishing will
continue on certain stocks--notably GB cod, witch flounder, pollock,
and northern windowpane flounder--during the duration of this interim
action. Under section 305(c) of the Magnuson-Stevens Act, NMFS may
implement an interim rule that reduces overfishing on overfished
stocks, without necessarily ending overfishing. In this instance, the
purpose of the interim rule is to reduce or end overfishing and help
ensure that stocks rebuild consistent with Amendment 13 objectives for
FY 2009, and to reduce overfishing on the three other stocks, which
were recently identified as being overfished. The measures implemented
through this rule will satisfy these objectives, while at the same time
mitigating, to the extent practicable, the impacts on the fishing
community. As indicated by the EA and the comments received on the
proposed rule, ending overfishing on all multispecies stocks in this
interim rule would result in substantial negative consequences to the
fishing industry. The Council is developing mitigating measures in
Amendment 16, primarily through sector proposals, that should help to
offset these negative consequences. The full range of possible
mitigation measures cannot be implemented in this interim rule because
they have not been fully developed and analyzed. While there is some
decrease in the likelihood that GB cod and other stocks will rebuild
within the time prescribed by the Amendment 13 rebuilding plan as a
result of this final rule, the action should not significantly
jeopardize the likelihood that Amendment 13's rebuilding objectives
will be met, particularly given the short-term nature of this interim
rule and the fact that additional measures will be implemented through
Amendment 16. Therefore, in exercising the flexibility provided by
section 305(c) of the Magnuson-Stevens Act, NMFS has determined that
the modifications to the proposed rule as described below are
justifiable because they are necessary to mitigate impacts on the
fishing industry to the extent practicable, without fatally
jeopardizing the likelihood that overfished multispecies stocks will
achieve their rebuilding objectives through Amendment 16 measures. The
rationale for determining the extent of acceptable changes to the
proposed rule follows.
Generally speaking, these final interim measures reduce overfishing
to a lesser degree than the proposed interim action, as explained later
in this preamble. This action includes several elements of the
Council's proposed alternative, but contains additional measures to
further protect stocks that are in the most critical condition, such as
SNE/MA winter flounder. Management measures implemented under this
action include: An expansion of the status quo 2:1 SNE Differential DAS
Area measures; a witch flounder trip limit of 1,000 lb (453.6 kg) per
DAS, up to 5,000 lb (2,268 kg) per trip; zero retention limits for SNE
winter flounder (for both commercial and recreational vessels),
northern windowpane flounder, and ocean pout; a 2-week extension of the
seasonal prohibition on the retention of GOM cod for both private
recreational and party/charter vessels, (i.e., revised to encompass
[[Page 17032]]
November through April 15); a bag limit of 10 GB cod per person per day
for party/charter vessels operating in all areas; and mitigation
measures that include modifications to the DAS Leasing, Transfer, and
Regular B DAS Programs, expansion in area and season of the CA I Hook
Gear Haddock SAP, renewal of the Eastern U.S./Canada Haddock SAP, and
reduction of the haddock minimum fish size from 19 inches (48.3 cm) to
18 inches (45.7 cm) for both commercial and recreational vessels. This
action does not implement the proposed expansion of the GOM
Differential DAS Area (i.e., the Interim Differential DAS Area), or the
proposed SNE Closure Area. In addition, this action maintains the
Amendment 13 default measure for FY 2009, whereby Category A DAS are
reduced by 18.2 percent, and maintains the status quo 2:1 GOM
Differential DAS Area measures.
For reasons explained in the preamble to the proposed interim rule,
the proposed fishing mortality targets were either Fmsy (for windowpane
flounder, GOM winter flounder, GB winter flounder, witch flounder,
pollock, GB haddock, GOM haddock, GOM cod, GB cod, American plaice,
redfish, and ocean pout), or Frebuild (GB cod, GB yellowtail flounder,
SNE/MA yellowtail flounder, Cape Cod (CC)/GOM yellowtail flounder, SNE/
MA winter flounder, white hake, and Atlantic halibut). The proposed
interim measures would not have achieved Frebuild for GB cod; however,
they would have achieved Fmsy for this stock. The proposed measures
also would not have achieved the Fmsy target for northern windowpane
flounder, or the Frebuild target for SNE/MA winter flounder.
GARM III provided example estimates of Frebuild for overfished
stocks, making assumptions about the rebuild period end-dates and the
starting stock conditions at the beginning of the rebuilding periods.
In doing so, GARM III assumed that the catch in FY 2008 will be the
same as the catch in FY 2007. In contrast, for this interim action, an
estimated catch in FY 2008 was used to recalculate the starting stock
conditions in FY 2008, and the associated Frebuilds. For Amendment 16,
the Council's Plan Development Team (PDT) estimated catch for the
entire FY 2008 based upon an extrapolation of landings data for
calendar year (CY) 2008 through June 2008. As explained further in the
proposed interim rule preamble, this interim action relies on the PDT's
estimated landings for FY 2008, and derived estimates of fishing
mortality rates for CY 2008 and the recalculated Frebuilds. Because the
measures implemented by this action will be effective in FY 2009, an
estimate of fishing mortality in CY 2008 more closely represents the
starting conditions of the remainder of the rebuilding periods. For GB
yellowtail flounder, Frebuild was calculated utilizing an assumed catch
in CY 2008 of 2,500 mt.
The target reductions for pollock and the two windowpane flounder
stocks were revised from the proposed rule in order to be consistent
with the other stocks. In the proposed rule, the target reductions for
all stocks except these three were based upon an estimate of fishing
mortality in 2008. In contrast, the target reductions for pollock and
the two stocks of windowpane flounder were based upon the fishing
mortality in 2007. Thus, this final rule utilizes a starting fishing
mortality estimate in 2008 for all stocks. Because the estimate of
fishing mortality in 2008 was greater than that observed in 2007 for
these three stocks, the effect of this change is an increase in the
percentage reduction necessary to reduce fishing mortality to Fmsy. For
the calculation of F in 2008, for pollock, the PDT calculated an
assumed catch in 2008 and for the windowpane flounder stocks, catch in
2008 was assumed to be equal to the catch in 2007.
In contrast to the proposed interim rule, which would not have
attained the proposed interim goals for two stocks (i.e., SNE/MA winter
flounder and Northern windowpane flounder), nor the updated Fmsy goal
for pollock (which was updated after the proposed interim rule was
published), management measures implemented through this final rule do
not attain the stated goals for five stocks (SNE/MA winter flounder,
Northern windowpane flounder, pollock, GB cod, and witch flounder).
However, for four of these five stocks, the rebuilding timeline extends
beyond 2014 (a 2026 Amendment 13 end date for GB cod; and a 2017
Amendment 16 proposed end date for Northern windowpane flounder, witch
flounder, and pollock). Because these four stocks have longer
rebuilding timelines associated with them, additional time is available
to ensure that the rebuilding goals of the FMP are met. However, to
maintain the FMP rebuilding trajectories and to meet the statutory
rebuild dates, the Council will need to consider whether further
adjustments in fishing mortality are needed. If further adjustments are
needed, the Council will need to account for this in future actions,
possibly even in Amendment 16. Given the likely rebuilding schedules
and the original justification for the expanded differential DAS
counting area in the GOM and northern GB in the proposed interim rule
(primarily to protect pollock and witch flounder), NMFS is not
implementing the proposed expanded differential DAS counting area in
this final rule, and is maintaining the status quo inshore GOM
Differential DAS Area. The SNE Closure Area was included in the
proposed interim rule primarily to protect SNE/MA winter flounder.
Although this stock has a rebuilding timeline of 2014, given the
concern raised by the public regarding the severe economic impacts that
would be imposed by this closure area and the potential for this
closure to lead to shifts in effort to other areas and other stocks,
NMFS is instead implementing in this same area, slightly modified, a
requirement for 2:1 differential DAS counting. To strictly control
effort on SNE/MA winter flounder, NMFS is implementing a zero landing
limit for SNE/MA winter flounder for both commercial and recreational
vessels throughout the range of the stock. Table 2 identifies the 2009
target Fs as published in the proposed interim rule, and provides a
comparison of the estimated fishing mortality reductions achieved for
measures proposed in the proposed interim rule, and the measures
implemented by this final interim rule.
Table 2--Comparison of Fishing Mortality Reductions for the Proposed and Final Interim Rules
--------------------------------------------------------------------------------------------------------------------------------------------------------
F value for F value for
2009 F reduction proposed F reduction final F reduction
Species Stock proposed F objective interim achieved interim achieved
target action action
--------------------------------------------------------------------------------------------------------------------------------------------------------
Cod..................................... GB.............................. 0.247 -40% 0.208 -49% 0.295 -28%
(Fmsy)
[[Page 17033]]
GOM............................. 0.237 -21% 0.203 -32% 0.247 -18%
(Fmsy)
Haddock................................. GB.............................. 0.350 322% 0.049 -38% 0.062 -25%
(Fmsy)
GOM............................. 0.430 72% 0.159 -36% 0.205 -18%
(Fmsy)
Yellowtail Flounder..................... GB.............................. 0.109 -16% 0.109 -16% 0.109 -16%
(Freb)
SNE/MA.......................... 0.072 -38% 0.017 -86% 0.073 -39%
(Freb)
CC/GOM.......................... 0.238 -18% 0.174 -40% 0.167 -42%
(Freb)
American Plaice......................... ................................ 0.190 92% 0.056 -43% 0.084 -15%
(Fmsy)
Witch Flounder.......................... ................................ 0.200 -32% 0.167 -44% 0.247 -17%
(Fmsy)
Winter Flounder......................... GB.............................. 0.260 98% 0.108 -18% 0.114 -13%
(Fmsy)
GOM............................. 0.283 -11% 0.286 -10% 0.265 -16%
(Fmsy)
SNE/MA.......................... 0.000 -100% 0.052 -80% 0.100 -62%
(Freb)
Redfish................................. ................................ 0.038 375% 0.004 -50% 0.007 -13%
(Fmsy)
White Hake.............................. ................................ 0.084 29% 0.033 -49% 0.054 -17%
(Freb)
Pollock................................. ................................ 5.660 -51% 6.520 NA 9.342 -19%
(Fmsy)
Windowpane Flounder..................... North........................... 0.500 -83% ........... NA 2.229 -22%
(Fmsy)
South........................... 1.470 -29% ........... NA 1.392 -32%
(Fmsy)
Ocean Pout.............................. ................................ 7.600 NA ........... NA ........... ...........
(Fmsy)
Atlantic halibut........................ ................................ 0.044 -27% ........... NA ........... ...........
(Freb)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Because of the substantial changes made to the proposed interim
measures, and the resulting changes in the expected Fs as a consequence
of these changes, this final rule also implements revised target TACs
and Incidental Catch TACs. The target TACs, and the Incidental TACs
that are based on these targets, are specified as follows: For those
stocks where the measures implemented by this rule are expected to
reduce F to below the F target, the target TACs are set based on the
estimated F achieved from the management measures in this action; for
those stocks with Fs that are less than the proposed rule F targets,
the target TACs will be set based on the proposed F targets. See
Measure 3 under ``Approved Commercial Measures'' for further details on
these final target TACs.
Management Measures
All measures in effect prior to May 1, 2009, including the
scheduled default DAS reduction measures, that are not amended by this
final interim rule, will remain in effect on and after May 1, 2009.
This interim action implements management measures to reduce fishing
mortality on the commercial and recreational fisheries without
compromising rebuilding objectives, and revises several management
programs to mitigate the negative economic and social impacts. The
interim action is intended to ensure consistency, to the extent
practicable in an interim rule, with the national standards and
required provisions of the Magnuson-Stevens Act. This action also
specifies target TACs for all managed stocks, and annual specifications
for stocks managed by the U.S./Canada Resource Sharing Understanding
(Understanding). As is more fully discussed later in this document,
these measures will result in both quantifiable and non-quantifiable
reductions in fishing mortality for all of the NE multispecies stocks
managed under the FMP.
The interim measures are designed to work in conjunction with the
FMP to reduce fishing mortality and continue to maintain progress
toward achieving the rebuilding requirements of the FMP. The analysis
of this action presumes that the measures will be in effect throughout
FY 2009, and that a subsequent management action (Amendment 16) will be
implemented on May 1, 2010. The FMP management measures include an FY
2009 default measure that will change the allocation ratio of Category
A:B DAS from 55:45 to 45:55. This measure, because it is not an action
implemented by this interim action, is not discussed specifically in
the description of the interim measures that follow. In addition, this
action continues existing measures in the FMP associated with the GOM
Differential DAS Area, as discussed further below. NMFS anticipates
that this interim action will be renewed upon its expiration for an
additional 185 days, given that the Council does not anticipate the
implementation of Amendment 16 until May 2010 and that the Council
recommended that any interim action implemented by NMFS should be in
effect for all of FY 2009. Several measures were modified from the
proposed to the final rule based upon public comments received and
further analysis of proposed measures, to mitigate the negative
economic impacts of the management measures on the fishing industry and
fishing communities without compromising long-term rebuilding of
overfished stocks. Although these revisions will
[[Page 17034]]
result in less reduction to fishing mortality than the measures
proposed, such changes should not undermine efforts to rebuild stocks
within the established timeframes. Such measures will continue to
reduce F on all stocks and eliminate overfishing on all but four stocks
(pollock, GB cod, witch flounder, and northern windowpane flounder).
Three of these stocks are newly classified as overfished (pollock,
witch flounder, and northern windowpane flounder), and the rebuilding
programs developed by the Council in draft Amendment 16 include
rebuilding timelines extending to 2017. The rebuilding timeline for GB
cod extends through 2026. Given this, there should be sufficient
opportunity for future management actions to end overfishing and
rebuild these stocks, as necessary. The following describes the
measures implemented by this final interim rule.
Approved Commercial Measures
1. Differential DAS Counting
This action maintains the existing differential DAS counting area
in the GOM, as established in the FMP. However, in SNE, the existing
SNE Differential DAS Area is replaced by the Interim SNE Differential
DAS Area. This area includes waters between 40[deg]30' and 41[deg]30'
N. lat., and west of 68[deg]50' W. long. (i.e., west of the border of
the Western U.S./Canada Area) to the shore, including all of Nantucket
Sound and the Great South Channel. The Interim SNE Differential DAS
Area is being implemented primarily as a means to reduce F on SNE
winter flounder and SNE/MA yellowtail flounder.
With the exception of vessels fishing with hook gear in the Interim
SNE Differential DAS Area, all NE multispecies vessels declared into
and fishing under a NE multispecies Category A DAS within either the
GOM or Interim SNE Differential DAS Areas for any portion of a trip
will be charged at a rate of 2:1 for the entire trip. In other words,
with the exception noted above, if a vessel declares into, and fishes
in, either the GOM or Interim SNE Differential DAS Area for 10 hr, the
vessel's DAS balance would be charged 20 hr. NE multispecies vessels
declared into and fishing under a Category A DAS in the Interim SNE
Differential DAS Area using hook gear will be charged DAS at a rate of
1:1, provided such vessels have only hook gear on board. The hook gear
exception to the differential DAS counting rate is based upon data that
indicate that the catch rate of winter flounder and yellowtail
flounder, the primary species targeted by this measure, by hook gear is
likely to be very low and, in conjunction with a zero retention limit
for SNE winter flounder, will not substantially affect F reductions
achieved by this action.
A vessel will not be charged at the differential DAS rate if it
declares into and transits to another area outside of one of the
differential DAS areas. For example, if a vessel steams through the GOM
Differential DAS Area on its way to and from the fishing grounds in the
U.S./Canada Management Area, where DAS are not counted differentially,
it will not be charged at the 2:1 rate for the parts of the trip spent
steaming through the GOM Differential DAS Area. If a vessel declares
and fishes both inside and outside of the GOM Differential DAS Area or
the Interim SNE Differential DAS Area on the same trip, it will be
charged differential DAS at a rate of 2:1 for the entire trip. This
does not change the way that DAS are charged for vessels fishing in the
GOM Differential DAS Area. However, charging differential DAS at a rate
of 2:1 for the entire trip does represent a change in the way DAS are
currently charged under the existing SNE Differential DAS Area
implemented under FW 42. This change is based upon the revised area
encompassed by the Interim Differential DAS Area, as further explained
in the response to Comment 15.
Consistent with current regulations, vessels are required to
declare their intent to fish in one or both of the differential DAS
areas via the vessel monitoring system (VMS) prior to leaving port.
However, the Administrator, Northeast Region, NMFS (Regional
Administrator) currently has the authority to require the fishery to
utilize the ``call-in system'' on a temporary basis instead of the VMS
for DAS accounting if the vessel fishes inside/outside of the VMS
demarcation line on the same trip, if the VMS system was down for an
extended period of time, or for some other unforeseen circumstance. In
such a circumstance, vessels fishing any portion of a trip inside one
or both of the differential DAS areas will be charged at the rate of
2:1 for the entire trip.
The interaction of current groundfish and non-groundfish regulatory
programs and the different DAS counting rules remain unchanged under
this action (e.g., the cod running clock, DAS charging rules for Day
gillnet vessels, the application of daily possession limits for certain
stocks, the Eastern U.S./Canada Area rules, use of Regular B DAS, and
monkfish/groundfish permitted vessels fishing under a NE multispecies
DAS). For example, a vessel fishing in the GOM Differential DAS Area
for 25 hr that caught 1,600 lb (726 kg) of GOM cod (i.e., 2 day's
worth) would not be required to submit the cod running clock form via
VMS in order to account for the additional day's worth of cod
harvested. In addition, a Day gillnet vessel declared into and fishing
in the GOM Differential DAS Area would be charged DAS at a rate of 2:1
for any trip less than or equal to 3 hr in duration, or greater than
7.5 hr in duration and 15 hr for any trip greater than 3 hr, or less
than or equal to 7.5 hr in duration. For vessels fishing in multiple
geographic areas in which different rules apply (such as differential
DAS counting and trip limits), the most restrictive rule would apply
for the entire trip. The current regulations that allow monkfish
Category C and D vessels to fish as a monkfish Category A or B vessel,
and land monkfish under certain conditions, will still apply. As
described in detail below under Item 9 ``Mitigating Measures,'' the DAS
rules that apply to monkfish Category C and D vessels fishing in the
GOM Differential DAS Area are modified by this action to minimize any
impact these measures may have on the ability of such vessels to fish
for monkfish.
2. Modified Trip Limits
Under this interim rule, NE multispecies vessels are not allowed to
fish for, possess, or land more than 1,000 lb (453.6 kg) per DAS, up to
5,000 lb (2,268 kg) per trip of witch flounder. In addition, no
retention of SNE winter flounder, northern windowpane flounder, or
ocean pout is allowed. Vessels fishing for winter flounder or
windowpane flounder in multiple stock areas are subject to the most
restrictive possession limit for the pertinent species. In other words,
if a vessel fishes in the SNE winter flounder stock area and the GB
winter flounder stock area on the same trip, the vessel will be subject
to the prohibition on retention of winter flounder for that trip.
Lastly, as explained further under Measure 6 under ``Approved
Commercial Measures'' of the preamble (``Annual Specifications for
U.S./Canada Management Area''), a limit of 5,000 lb (2,268 kg) of GB
yellowtail flounder per trip is specified. Modifications to trip limits
are implemented as a means to reduce fishing mortality or increase
yield because they are a management tool that can target particular
stocks and are an important component of the current FMP.
3. Specification of Target TACs
Target TACs are utilized in the FMP as one method of evaluating the
success
[[Page 17035]]
of management measures and providing a way to make simple comparisons
between different fishing years. Secondly, target TACs form the basis
of calculating allocations of GB cod to sectors and the incidental
catch TACs for the Special Management Programs. This final interim rule
implements target TACs for FY 2009. The proposed rule indicated that
the target TACs would be based upon either Fmsy or Frebuild for each
stock. For stocks that were previously considered overfished, target
TACs were proposed to be based upon Frebuild, with one exception for GB
cod. For GB cod, the target TAC was proposed to be based upon Fmsy, for
reasons specified in the proposed interim rule. In contrast, for stocks
that have been newly classified as overfished based upon the results of
GARM III, the target TACs were proposed to be based upon Fmsy. However,
this final interim rule specifies target TACs based upon either the
Ftarget for each stock (i.e., Fmsy or Frebuild) or the F resulting from
measures implemented by this action (i.e., estimated F), whichever is
higher. For stocks where the estimated F is lower than the Ftarget,
implementing target TACs based upon the Ftarget allows for increased
yield. For stocks where the estimated F is higher than the Ftarget,
implementing target TACs based upon the estimated F more accurately
reflects catch anticipated from measures implemented by this action.
Table 3 lists the target TACs for FY 2009, based upon GARM III data,
and an estimate of F for each stock during CY 2008.
Table 3--Target TACs (mt) for FY 2009
------------------------------------------------------------------------
Target
Species Stock TAC
------------------------------------------------------------------------
Cod................................... GB.................... 5,501
Cod................................... GOM................... 10,724
Haddock............................... GB.................... 89,055
Haddock............................... GOM................... 1,564
Yellowtail flounder................... GB.................... *1,617
Yellowtail flounder................... SNE/MA................ 389
Yellowtail flounder................... CC/GOM................ 860
Plaice................................ ...................... 3,214
Witch flounder........................ ...................... 1,129
Winter flounder....................... GB.................... 2,004
Winter flounder....................... GOM................... 379
Winter flounder....................... SNE................... 0
Redfish............................... ...................... 8,614
White hake............................ ...................... 2,376
Pollock............................... ...................... 6,346
Windowpane flounder................... North................. 581
Windowpane flounder................... South................. 279
Halibut............................... ...................... 68
------------------------------------------------------------------------
* A hard TAC, set through a separate process described in Measure 5 of
this preamble.
4. Revisions to Incidental Catch TACs and Allocations to Special
Management Programs
This final rule revises the specification of incidental catch TACs
applicable to the Special Management Programs of the FMP for FY 2009,
based upon the most recent scientific information. Incidental catch
TACs are specified for certain stocks of concern for Special Management
Programs in order to limit the amount of catch of stocks of concern
that can be caught under such programs, and to fully account for
fishing mortality. The incidental catch TACs apply to catch (landings
and discards) caught under Category B DAS (either Regular or Reserve B
DAS) on trips that end on a Category B DAS. The catch of stocks for
which incidental catch TACs are specified on trips that start under a
Category B DAS and then flip to a Category A DAS do not accrue toward
such TACs.
A stock of concern is defined as a stock that is in an overfished
condition or subject to overfishing. Due to the revised status of
stocks (GARM III) that is adopted under this action, an incidental
catch TAC is no longer appropriate for American plaice, because it is
no longer considered a stock of concern. Further, new incidental catch
TACs are required for GOM winter flounder and pollock because they are
now considered stocks of concern. The percentages that the TACs are
based on remain unchanged, with the exception of witch flounder, which
is reduced from 5 percent to 2 percent, due to its overfished status
and the fact that the F and total catch need to be reduced. The
incidental catch TACs for GOM winter flounder are set at 5 percent,
based on the rationale described in Framework (FW) 40A to the FMP: If
the recent catch levels are less than the expected future catch levels,
and 2009 management measures are likely to achieve more than the
required reduction in F, then the size of an incidental catch TAC
relative to the size of the overall TAC is larger (set as a larger
percent). The incidental catch TAC for pollock is set at 5 percent
because of the prevalence of pollock catch in the Special Management
Programs, and based upon the rationale cited above. The utility of the
Special Management Programs would be severely constrained if the
incidental catch TAC is set too low. The number of total incidental
catch TACs is increased from the current number (8), to 10. Due to the
severe F reduction necessary for the SNE/MA stock of winter flounder,
no retention of this stock is allowed, and there is no incidental catch
TAC specified (see additional discussion under Section 9 of this
preamble, Mitigating Measures). The calculation of incidental catch
TACs by stock based on the target TACs is shown in Table 4.
Table 4--Incidental Catch TACs for FY 2009 (mt)
------------------------------------------------------------------------
Percentage
Stock of total Target TAC Incidental
TAC TAC
------------------------------------------------------------------------
GB cod.......................... 2 5,501 110
GOM cod......................... 1 10,724 107.2
GB yellowtail................... 2 1,617 32.3
CC/GOM yellowtail............... 1 860 8.6
SNE/MA yellowtail............... 1 389 3.9
Pollock......................... 5 6,346 317.3
Witch flounder.................. 2 1,129 22.6
GB winter flounder.............. 2 2,004 40.1
White hake...................... 2 2,376 47.5
GOM winter...................... 5 379 19.0
------------------------------------------------------------------------
[[Page 17036]]
This final interim rule also modifies the allocation of the
incidental catch TACs to the various Special Management Programs due to
the changes in status of stocks, and to optimize the design of the
programs based on the operation of the programs since their inception.
For example, the Eastern U.S./Canada Haddock SAP was not used at all in
FY 2007, and only two trips were taken in the area in FY 2006.
Therefore, the percent allocations to this SAP are reduced for GB cod,
GB yellowtail, and GB winter flounder, and the percent allocation to
the Regular B DAS Program is increased due to higher participation in
that program historically. Secondly, this rule provides the Regional
Administrator the authority to modify the allocations among programs
in-season, or prior to the beginning of the season, because it is
difficult to estimate the appropriate TAC, since the level of
participation and catch rates of stocks of concern in the various
programs is highly variable. The changes to the allocations are
summarized in Table 5. Table 6 contains the incidental catch TACs that
result from applying the percentages in Table 5 to the incidental TACs
in Table 4.
Table 5--Modifications to the Incidental Catch TAC Allocations for FY 2009
----------------------------------------------------------------------------------------------------------------
Regular B DAS Program Eastern U.S./Canada Closed Area I Hook Gear
-------------------------- Haddock SAP Haddock SAP
Stock ---------------------------------------------------
Current New Current New Current New
----------------------------------------------------------------------------------------------------------------
GB Cod............................ 50% 70% 34% 14% 16% No change
GB Yellowtail flounder............ 50% 80% 50% 20% ........... ...........
GB Winter flounder................ 50% 80% 50% 20% ........... ...........
Pollock........................... None 90% None 5% None 5%
GOM Winter flounder............... None 100% ........... ........... ........... ...........
GOM Cod........................... 100% 100% ........... ........... ........... ...........
White hake........................ 100% 100% ........... ........... ........... ...........
CC/GOM Yellowtail flounder........ 100% 100% ........... ........... ........... ...........
SNE/MA Yellowtail flounder........ 100% 100% ........... ........... ........... ...........
Witch flounder.................... 100% 100% ........... ........... ........... ...........
Plaice............................ 100% None ........... ........... ........... ...........
----------------------------------------------------------------------------------------------------------------
Table 6--Specification of Incidental Catch TACs for Special Management Programs (mt) for FY 2009
----------------------------------------------------------------------------------------------------------------
Eastern U.S./ Closed Area I
Stock Regular B DAS Canada Haddock Hook Gear
Program SAP Haddock SAP
----------------------------------------------------------------------------------------------------------------
GB Cod.......................................................... 77 15.4 17.6
GOM Cod......................................................... 107.2 na na
GB Yellowtail flounder.......................................... 25.8 6.5 na
CC/GOM Yellowtail flounder...................................... 8.6 na na
SNE/MA Yellowtail flounder...................................... 3.9 na na
Pollock......................................................... 285.6 15.9 15.9
Witch flounder.................................................. 22.6 na na
GB Winter flounder.............................................. 32.1 8.0 na
White hake...................................................... 47.5 na na
GOM Winter flounder............................................. 19.0 na na
----------------------------------------------------------------------------------------------------------------
5. Annual Specifications for U.S./Canada Management Area
In consultation with the Council, NMFS annually implements
management measures for the U.S./Canada Management Area through
proposed and final rules. For FY 2009, because NMFS is implementing
management measures for the entire fishery to reduce fishing mortality
as described above, NMFS is including the specification of the TACs and
other measures for the U.S./Canada Management Area in this final
interim rule in order to streamline the regulatory process.
The FMP specifies a procedure for setting annual hard TAC levels
(i.e., the fishery or area closes when a TAC is reached) for Eastern GB
cod, Eastern GB haddock, and GB yellowtail flounder in the U.S./Canada
Management Area, which is described in the proposed interim rule. The
specific justification for the FY 2009 TACs, which were based upon the
most recent stock assessments, is also described in the proposed rule.
On October 8, 2008, the Council approved, consistent with the 2008
Guidance Document, the following U.S./TACs recommended by the
Transboundary Management Guidance Committee: 527 mt of Eastern GB cod;
11,100 mt of Eastern GB haddock; and 1,617 mt of GB yellowtail
flounder. The FY 2009 TACs for the U.S./Canada Management Area
represent a decrease for cod and yellowtail flounder, and an increase
for haddock compared to those specified for FY 2008 (Tables 7 and 8).
Table 7--FY 2009 U.S./Canada TACs (mt) and Percentage Shares (in Parentheses)
----------------------------------------------------------------------------------------------------------------
GB Yellowtail
GB Cod GB Haddock Flounder
----------------------------------------------------------------------------------------------------------------
Total Shared TAC................................................ 1,700 30,000 2,100
U.S. TAC........................................................ 527 (31) 11,100 (37) 1,617 (77)
[[Page 17037]]
Canada TAC...................................................... 1,173 (69) 18,900 (63) 483 (23)
----------------------------------------------------------------------------------------------------------------
Table 8--FY 2008 U.S./Canada TACs (mt) and Percentage Shares (in Parentheses)
----------------------------------------------------------------------------------------------------------------
GB Yellowtail
GB Cod GB Haddock Flounder
----------------------------------------------------------------------------------------------------------------
Total Shared TAC................................................ 2,300 23,000 2,500
U.S. TAC........................................................ 667 (29) 8,050 (35) * 1,950 (78)
Canada TAC...................................................... 1,633 (71) 14,950 (65) 550 (22)
----------------------------------------------------------------------------------------------------------------
* Adjusted downward to 1,868.7 mt due to overharvest of FY 2007 TAC.
The regulations for the Understanding, promulgated by the final
rule implementing Amendment 13, state that any overages of the GB cod,
haddock, or yellowtail flounder TACs that occur in a given fishing year
will be subtracted from the respective TAC in the following fishing
year.
Therefore, should an analysis of the catch of the shared stocks by
U.S. vessels indicate that an over-harvest occurred during FY 2008, the
pertinent TAC will be adjusted downward in order to be consistent with
the FMP and Understanding. Although it is very unlikely, it is possible
that a very large over-harvest could result in an adjusted TAC of zero.
If an adjustment to one of the FY 2008 TACs of cod, haddock, or
yellowtail flounder is necessary, the public will be notified through
publication in the Federal Register and through a letter to permit
holders.
NMFS is also implementing, through the authority granted to the
Regional Administrator by the FMP, measures to optimize the harvest of
the shared resources. The regulations under Sec. 648.85(a)(3)(iv)(D)
provide the Regional Administrator the authority to implement in-season
adjustments to various measures in order to prevent over-harvesting, or
to facilitate achieving the TAC.
Based on the Council's vote to postpone the opening of the Eastern
U.S./Canada Area for vessels fishing with trawl gear in FY 2008 from
May 1, 2008, to August 1, 2008, and the success of this management
measure in slowing the annual catch rate of cod during the early part
of the year, NMFS is implementing this same measure for FY 2009. Thus,
the FY 2009 opening of the Eastern U.S./Canada Area for trawl vessels
will be August 1, 2009; more selective longline gear is allowed access
during May through July. Such vessels will be limited to a cod catch of
5 percent of the cod TAC, or 26.4 mt. The objective of this action is
to prevent trawl fishing in the Eastern U.S./Canada Area during the
time period when cod bycatch is likely to be very high. The goal of
this measure is to prolong access to this area in order to maximize the
catch of available cod, haddock, and yellowtail flounder.
Secondly, the Regional Administrator is implementing a possession
limit of 5,000 lb (2,268 kg) per trip for GB yellowtail flounder.
Although the regulations under Sec. 648.86(a)(3)(iv)(C) indicate an
initial trip limit of 10,000 lb (4,536 kg) at the beginning of a
fishing year for GB yellowtail flounder, based on the yellowtail
flounder catch rate from the U.S./Canada Management Area under a 5,000-
lb (2,268-kg) trip limit during FY 2008, and analyses conducted by NMFS
during FY 2007, a 5,000-lb (2,268-kg) trip limit is an appropriate trip
limit to allow harvesting of the TAC, and to increase the likelihood
that further restrictions during the fishing year to slow the catch
rate will be unnecessary.
Third, the Regional Administrator is allowing the use of the Ruhle
Trawl in the Eastern U.S./Canada Area. Under permanent regulations,
only a flounder net and the haddock separator trawl are permanently
authorized for such use. The Ruhle trawl, which is a modified trawl
that substantially reduces the catch rate of most stocks of concern,
was approved for use in the Regular B DAS Program and the Eastern U.S./
Canada Haddock SAP (73 FR 40186, July 14, 2008). Approval of the use of
the Ruhle trawl in the Eastern U.S./Canada Area through this interim
rule will provide another alternative for trawl vessel operators and,
therefore, provide additional flexibility. As detailed in the July 14,
2008 final rule, the Ruhle trawl has been demonstrated to substantially
reduce catch of many species of groundfish, and therefore its use is
consistent with the management objectives for the Eastern U.S./Canada
Area.
Lastly, the Regional Administrator is implementing zero trips into
the CA II Yellowtail Flounder SAP during FY 2009, based on a
determination that the available TAC of GB yellowtail flounder is
insufficient to support a minimum level of fishing activity within the
CA II Yellowtail Flounder SAP. The Regional Administrator has the
authority to determine the allocation of the total number of trips into
the CA II Yellowtail Flounder SAP based upon several criteria,
including GB yellowtail flounder TAC level and the amount of GB
yellowtail flounder caught outside of the SAP. As implemented by FW
40B, zero trips to this SAP should be allocated if the available GB
yellowtail flounder catch is not sufficient to support 150 trips with a
15,000-lb (6,804-kg) trip limit (i.e., if the available GB yellowtail
flounder catch is less than 1,021 mt). This calculation takes into
account the projected catch from the area outside of the SAP. Based on
the estimate for catch outside of the SAP utilized for FY 2008 (1,376
mt), and the proposed GB yellowtail flounder TAC for FY 2009 (1,617
mt), there is insufficient available catch to allow the SAP to proceed
(i.e., 1,617 - 1,376 = 241; 241 < 1,021 mt).
6. Haddock TAC for the CA I Hook Gear Haddock SAP
Under this action, a haddock TAC for the CA I Hook Gear Haddock SAP
is set based upon the GARM III stock assessment and a formula
implemented in FW 42. The haddock TAC in a particular year is based
upon the TAC that was specified for the SAP in 2004 (1,130 mt), scaled
according to the size of the exploitable biomass of western GB haddock
compared to the biomass size in 2004 (35,317 mt). The size of the
western component of the GB haddock stock is estimated at 35 percent of
the size of the total GB haddock stock. Because the 2009 exploitable
biomass of haddock is 321,870 mt, the formula and
[[Page 17038]]
resultant TAC is as follows: ((.35)(321,870)/35,317) x 1,130 = 3,604.5
mt. This action implements further modifications to this SAP, as
discussed in Item 9 below.
7. Elimination of the SNE/MA Winter Flounder SAP
The SNE/MA Winter Flounder SAP regulations allow a limited access
NE multispecies vessel fishing for summer flounder west of 72[deg]30'
W. long. to retain up to 200 lb (91 kg) of winter flounder while not
under a NE multispecies DAS, provided the vessel complies with various
restrictions. Due to the severely depleted status of SNE/MA winter
flounder, and the goal of reducing F to as close to zero as
practicable, this final rule eliminates this SAP. Because the SAP could
enable limited targeting of winter flounder, elimination of the SAP may
prevent some catch of winter flounder from occurring.
8. Elimination of the State Waters Winter Flounder Exemption
The State Waters Winter Flounder Exemption allows vessels issued a
NE multispecies permit to fish in state waters for winter flounder
using gear with mesh smaller than required for other vessels in the
fishery (provided various requirements and criteria are met). Due to
the severely depleted status of the SNE/MA winter flounder stock, and
the goal of reducing F to as close to zero as practicable, this final
rule eliminates this SAP. Because the SAP could enable limited
targeting of winter flounder, elimination of the SAP may prevent some
catch of winter flounder from occurring.
9. Mitigating Measures
CA I Hook Gear Haddock SAP Expansion. For reasons explained in the
Comments section below, this final rule implements modifications to the
CA I Hook Gear Haddock SAP to expand its scope and change some of the
restrictions in order to increase opportunity to access GB haddock and
provide additional flexibility to vessels. The expansion has been
determined to be consistent with the goals of the FMP. Specifically,
this rule modifies the time period for the SAP from October through
December, to May through January, and expands the area within CA I
where vessels may fish to the east and south, to encompass the entire
northern half of CA I. This rule eliminates the division of the SAP
into two time periods, as well as the allocation of the haddock TAC to
the two time periods. All limited access NE multispecies DAS vessels
fishing with hook gear may fish in the SAP at any time (provided the
SAP is open), regardless of whether the vessel is enrolled in a sector
or is in the ``common pool.'' This final rule also implements a
provision that was not included in the Council's alternative, which is
a prohibition on the use of squid as bait when fishing in this SAP, in
order to allow haddock to be targeted with increased likelihood that
the catch rate of cod will be low. This prohibition is based upon
analysis of experimental fishery data during the comment period for
this action that indicated high bycatch of cod may occur when using
squid as bait. This final rule also eliminates the requirement that
vessels intending to participate in the SAP provide a yearly
notification to the observer program in advance of the SAP season,
because the removal of the sector and non-sector seasons for this SAP
no longer make this notification necessary to assist in the deployment
of observers. The requirement to notify the observer program 72 hr in
advance of each trip is maintained. These measures were not included in
the proposed rule and NMFS