Fisheries of the Northeastern United States; Northeast Multispecies Fishery; Secretarial Interim Action, 2959-2984 [E9-846]
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Federal Register / Vol. 74, No. 11 / Friday, January 16, 2009 / Proposed Rules
subject to EO 13045 because it
implements Section 604(d)(2) of the
Clean Air Act which states that the
Agency shall authorize essential use
exemptions should the Food and Drug
Administration determine that such
exemptions are necessary.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not subject to Executive
Order 13211 (66 FR 28355 (May 22,
2001)), because it is not a significant
regulatory action under Executive Order
12866.
hsrobinson on PROD1PC76 with PROPOSALS
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, 12(d) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
with applicable law or otherwise
impractical. Voluntary consensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, and business
practices) that are developed or adopted
by voluntary consensus standards
bodies. The NTTAA directs EPA to
provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards. This
proposed rule does not involve
technical standards. Therefore, EPA did
not consider the use of any voluntary
consensus standards.
J. Executive Order 12898: Federal
Actions to Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order (EO) 12898 (59 FR
7629 (Feb. 16, 1994)) establishes federal
executive policy on environmental
justice. Its main provision directs
federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
EPA has concluded that it is not
practicable to determine whether there
would be disproportionately high and
adverse human health or environmental
effects on minority and/or low income
populations from this proposed rule.
EPA believes, however, that this action
affects the level of environmental
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protection equally for all affected
populations without having any
disproportionately high and adverse
human health or environmental effects
on any population, including any
minority or low-income population.
Any ozone depletion that results from
this proposed rule will impact all
affected populations equally because
ozone depletion is a global
environmental problem with
environmental and human effects that
are, in general, equally distributed
across geographical regions.
List of Subjects in 40 CFR Part 82
Environmental protection,
Administrative practice and procedure,
Air pollution control, Chemicals,
Chlorofluorocarbons, Imports, Methyl
Chloroform, Ozone, Reporting and
recordkeeping requirements.
2959
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 080521698–8699–01]
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: Proposed rule; request for
comment.
SUMMARY: NMFS proposes a temporary
Secretarial interim action under the
Magnuson-Stevens Fishery
Dated: January 12, 2009.
Conservation and Management Act
Stephen L. Johnson,
(Magnuson-Stevens Act) to implement
Administrator.
measures intended to immediately
40 CFR Part 82 is proposed to be
reduce overfishing in the Northeast (NE)
multispecies fishery, while addressing
amended as follows:
the need to help sustain fishing
PART 82–PROTECTION OF
communities, without compromising
STRATOSPHERIC OZONE
rebuilding objectives. Measures
proposed for the commercial fishery
1. The authority citation for part 82
include the following: A differential
continues to read as follows:
days-at-sea (DAS) area north of 41°30′ N.
lat., whereby a vessel would be charged
Authority: 42 U.S.C. 7414, 7601, 7671–
2 days for every day fished; a large
7671q.
Southern New England (SNE) Closure
Area; and modified groundfish trip
Subpart A—Production and
limits. This action does not change the
Consumption Controls
scheduled DAS reduction in the NE
2. Section 82.8 is amended by revising Multispecies Fishery Management Plan
(FMP), which would result in an
the table in paragraph (a) to read as
approximate 18–percent reduction in
follows:
DAS. For private recreational vessels
§ 82.8 Grant of essential use allowances
fishing in the Exclusive Economic Zone
and critical use allowances.
(EEZ) and for federally permitted
charter/party vessels, this action would
(a) * * *
extend in time a seasonal prohibition on
the possession of Gulf of Maine (GOM)
TABLE I.—ESSENTIAL USE ALLOWcod, and prohibit the possession of SNE
ANCES FOR CALENDAR YEAR 2009
winter flounder. For federally permitted
charter/party vessels, this action would
2009 Quantity
Company
Chemical
implement a trip limit for Georges Bank
(metric tons)
(GB) cod. In addition, this action
proposes to mitigate some of the
(i) Metered Dose Inhalers (for oral inhalation)
negative short-term economic impacts of
for Treatment of Asthma and Chronic Obstructive Pulmonary Disease
the FMP by making modifications to the
DAS Leasing Program, the Regular B
Armstrong
CFC–11 or
63.0 DAS Program, and the DAS Transfer
CFC–12 or
Program; continuing the Eastern U.S./
CFC–114.
Canada Haddock Special Access
Program (SAP); and implementing a
*
*
*
*
*
reduction in the haddock minimum size
[FR Doc. E9–945 Filed 1–15–09; 8:45 am]
to 18 inches (45 cm). Finally, this action
BILLING CODE 6560–50–P
would specify management measures
for the U.S./Canada Management Area
for fishing year (FY) 2009.
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DATES: Comments must be received by
February 17, 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 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 an Initial Regulatory
Flexibility Analysis (IRFA), which is
contained in the Classification section
of this proposed rule. 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.
FOR FURTHER INFORMATION CONTACT:
Thomas Warren, Fishery Policy Analyst,
(978) 281–9347, fax (978) 281–9135.
SUPPLEMENTARY INFORMATION: The FMP
specifies the management measures for
12 species in Federal waters off the New
England and Mid-Atlantic coasts, which
are Atlantic cod, haddock, yellowtail
flounder, pollock, American plaice,
witch flounder, white hake,
windowpane flounder, Atlantic halibut,
winter flounder, ocean pout, and
redfish, comprising a total of 19
individual stocks (groundfish). A major
overhaul of the FMP occurred in 2004
with implementation of Amendment 13
and the establishment of rebuilding
programs for all stocks managed by the
FMP, including specification of status
determination criteria for each stock.
Amendment 13 established two
different strategies for rebuilding (an
adaptive and a phased rebuilding
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strategy), and a rebuilding plan for each
overfished stock was developed in
accordance with one of the two
strategies. Under the ‘‘adaptive’’
rebuilding strategy, fishing mortality is
held at Fmsy from 2004 through 2008,
and then subsequently reduced to the
level required to rebuild by the selected
end-date of the rebuilding period. In
2008, the effectiveness of the
management measures and the validity
of the status determination criteria
(biological reference points) were fully
evaluated. Eight stocks (GOM cod, GB
haddock, GOM haddock, SNE/Mid
Atlantic (MA) winter flounder, GB
yellowtail flounder, redfish,
windowpane flounder (southern stock),
and ocean pout) are managed under the
adaptive rebuilding strategy. In contrast,
under the ‘‘phased’’ rebuilding strategy,
fishing mortality is allowed to remain
above Fmsy at the start of the rebuilding
period in 2004, and then reduced
sequentially in 2006 and 2009. Five
stocks (GB cod, Cape Cod (CC)/GOM
yellowtail flounder, SNE/MA yellowtail
flounder, American plaice, and white
hake) are managed under the phased
rebuilding strategy. The end of the
rebuilding period for all stocks is 2014,
with the exception of GB cod (2026),
CC/GOM yellowtail flounder (2023),
and redfish (2051).
Amendment 13 also implemented a
process whereby the NE multispecies
complex is routinely evaluated through
a biennial adjustment. This adjustment
process provides an update of the
scientific information regarding the
status of the stocks, and an evaluation
of the effectiveness of the regulations.
The biennial adjustment provides the
New England Fishery Management
Council (Council) with information to
make adjustments to management
measures necessary to modify fishing
mortality to comply with the rebuilding
schedules and approach optimum yield.
The FMP further specified a benchmark
stock assessment and review of the
biological reference points (stock status
determination criteria) in 2008. This
planned assessment of the biological
reference points (Groundfish
Assessment Review Meeting, (GARM III)
in 2008) was part of the biennial
adjustment process, but was also part of
the adaptive rebuilding strategy
described above, which sought to
evaluate the more fundamental
scientific information mid-way through
the rebuilding period for most stocks.
Although, strictly speaking, the adaptive
rebuilding strategy applies to only five
stocks, the intent of the Council in
scheduling a benchmark assessment in
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2008 was an evaluation of the biological
reference points for all stocks.
In order to implement these
rebuilding strategies, Amendment 13
included default management measures
for implementation in FY 2006 and FY
2009, which were designed to reduce
fishing mortality on certain stocks, and
established criteria to determine
conditions under which the default
measures would not be triggered. The
default measure developed for FY 2009
is a modification to the Category A DAS
and Category B DAS ratio from 55:45 to
45:55 (respectively). This decrease in
the amount of A DAS represents an
18.2–percent decrease in the number of
A DAS a vessel may fish. Amendment
13 noted the challenge of implementing
the rebuilding program due to the
difficulty of designing effort controls
that would precisely achieve the desired
fishing mortality reductions for all
stocks.
The Council began development of
Amendment 16 in 2006 to meet a
required May 1, 2009, implementation
date because it anticipated that new
scientific information from the
scheduled 2008 biennial review and
benchmark assessment (GARM III)
would indicate that additional fishing
mortality reductions may be necessary
for FY 2009 in order to continue
rebuilding at the required rate. At the
Council meeting on June 3, 2008, the
Northeast Fisheries Science Center
(NEFSC) presented preliminary
estimates of stock size and fishing
mortality in 2006, which indicated that
draft effort control measures under
development for Amendment 16 were
not targeting the correct stocks. Based
on this information, the Council
decided to wait until receipt of the final
GARM III assessment results in
September 2008 to design appropriate
management measures and hold public
hearings.
The Council subsequently developed
a revised schedule of development for
Amendment 16, which, if approved,
would be implemented on May 1, 2010.
The Council voted on September 4,
2008, to request that NMFS implement
an interim action for the duration of FY
2009 (May 1, 2009–April 30, 2010), and
recommended a specific suite of
management measures for the interim
action. As explained fully under section
12 below, NMFS did not adopt the
Council’s recommendations for this
proposed interim action because it was
determined that the Council’s
recommended alternative was
insufficient to end overfishing.
GARM III, completed in August 2008,
was an extensive benchmark
assessment. GARM III evaluated the
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underlying data and models utilized for
assessment of the groundfish stocks,
evaluated the biological reference
points, established new reference
points, assessed the biomass and fishing
mortality status of the groundfish stocks
in 2007, and provided examples of
fishing mortality rates that would be
expected to rebuild overfished stocks.
Incorporation of new scientific
information and revisions to
management measures in the FMP,
effective May 1, 2009, are necessary to
continue rebuilding to comply the
intent of the FMP. However, due to the
Council’s revised Amendment 16
schedule, such revisions to the FMP
would not be implemented, without this
interim action.
Section 305(c) of the MagnusonStevens Act authorizes the Secretary of
Commerce (Secretary) to amend an FMP
if the appropriate Council fails to
develop and submit to the Secretary any
necessary amendment to an FMP if the
fishery requires conservation and
management. NMFS promulgated
guidelines to further clarify how this
authority to amend an FMP should be
interpreted (63 FR 24212; May 1, 1998).
The Secretary, on his/her own initiative,
or in response to a Council request, may
implement interim measures to reduce
overfishing under section 305(c), until
such measures can be replaced by an
FMP amendment or regulations taking
remedial action. The measures may
remain in place for 180 days, but may
be extended for an additional 186 days
if the public has had an opportunity to
comment on the measures.
Because of the need to eliminate and
reduce overfishing, as well as to reduce
fishing mortality to more closely comply
with the FMP rebuilding schedules,
NMFS is proposing this interim action.
To that end, this action would
implement management measures that,
as much as practicable, build upon the
Amendment 13 default measures and
include major elements of the Council’s
Amendment 16 alternatives, such as
differential DAS. Measures that are
similar to Amendment 16 would
facilitate industry understanding, enable
NMFS to administer such short-term
measures, and allow vessels to adapt
any measures implemented by
Amendment 16 if they are adopted.
Further, it is important that NMFS can
enforce and administer the interim
measures, and that such measures are
fair and simple. The proposed interim
action management measures are more
narrowly focused than what is currently
under consideration in the Council’s
Amendment 16 draft document, which
contains measures beyond those
designed to reduce fishing mortality,
such as inclusion of many new sectors
and measures to address new
Magnuson-Stevens Act requirements
(e.g., annual catch limits and
accountability measures). Failure to
reduce or prevent overfishing by May 1,
2009, while the Council completes
Amendment 16, would likely lead to
continued overfishing of several
groundfish stocks, resulting in slower
rebuilding that would likely require
more stringent future measures, with
additional economic and social
consequences.
A summary of the GARM III results
that form the basis for this proposed
interim rule is in Table 1 below.
Overfishing is occurring on stocks when
the fishing mortality to Fmsy ratio (F/
Fmsy) is greater than 1.0, and a stock is
overfished if the biomass level to Bmsy
ratio (B/Bmsy) is equal to or less than
0.5.
TABLE 1. GARM III STOCK STATUS DETERMINATION CRITERIA AND 2007 STATUS
Species
Cod
Stock
Fmsy
Bmsy
2007 Fishing Mortality
(2007 F/ Fmsy)
2007 Biomass (2007 B/
Bmsy)
GB
0.2466
148,084
1.2
0.12
GOM
0.237
58,248
1.9
0.58
GB
0.350
158,873
0.49
2.05
GOM
0.430
5,900
0.8.
0.99
GB
0.254
43,200
1.1
0.22
SNE/MA
0.254
27,400
1.6
0.13
CC/GOM
0.239
7,790
1.7
0.25
American plaice
0.190
21,940
0.5
0.51
Witch flounder
0.200
11,447
1.5
0.30
GB
0.260
16,000
1.1
0.31
GOM
0.283
3,792
1.5
0.29
SNE/MA
0.248
38,761
2.6
0.09
Redfish
0.038
271,000
0.1
0.64
White hake
0.125
56,254
1.2
0.35
Pollock
5.660
2.0
* 1.2
* 0.71
North
0.500
1.4
* 3.9
* 0.38
South
1.470
0.34
* 1.3
* 0.62
0.760
4.94
0.5
0.10
Haddock
Yellowtail flounder
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Winter flounder
Windowpane
Ocean pout
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TABLE 1. GARM III STOCK STATUS DETERMINATION CRITERIA AND 2007 STATUS—Continued
Species
Stock
Fmsy
Atlantic halibut
0.073
2007 Fishing Mortality
(2007 F/ Fmsy)
2007 Biomass (2007 B/
Bmsy)
0.9
Bmsy
0.03
49,000
* Pollock and windowpane flounder information was revised subsequent to GARM III in order to utilize 3 yr averages. Pollock is approaching
an overfished condition.
Because GARM III revised the
biological reference points and the 2007
stock status determination, and the
current status of stocks is different from
the understanding of stock status based
on GARM I and II, it is necessary to
utilize new fishing mortality targets that
are appropriate to the revised stock
status. Therefore, this interim action
would utilize the GARM III revised
stock status determination as the basis
for developing fishing mortality targets
in order to be consistent with National
Standard 2, which requires that
conservation and management measures
shall be based upon the best scientific
information available.
New rebuilding plans for those stocks
recently determined to be overfished or
approaching an overfished condition,
based on results from GARM III
(windowpane flounder (northern stock),
GOM and GB winter flounder, witch
flounder, and pollock), are not proposed
in this interim action, but rather are
being considered by the Council in
Amendment 16. For these five stocks,
the fishing mortality target of the
interim action is proposed to be Fmsy,
although, as explained later in this
preamble, the proposed measures would
not achieve this objective for
windowpane north.
For those stocks that are either rebuilt
(GB haddock) or for stocks where Fmsy
would rebuild the stock (GOM haddock,
GOM cod, American plaice, redfish), the
fishing mortality target for the interim
action would be Fmsy. For these stocks,
which are currently in rebuilding
programs, Fmsy is the appropriate target
fishing mortality rate because Fmsy is
lower than Frebuild, and the stocks are
projected to rebuild to Bmsy within
their rebuilding periods.
For stocks currently under rebuilding
programs and for which the fishing
mortality rate required to rebuild the
stock (Frebuild) is less than Fmsy (GB
cod, GB yellowtail, SNE yellowtail, CC
yellowtail, SNE winter flounder, white
hake), the fishing mortality target under
this interim action would be Frebuild,
with one exception (noted below).
For GB cod, fishing mortality under
this interim action would be reduced to
a level less than Fmsy, but would not
achieve Frebuild. The two recent stock
assessments that pertain to GB cod
(GARM III for the entire stock;
Transboundary Resource Assessment
Committee 2008 for the eastern portion
of the stock) were unable to be
reconciled with each other, with the
assessment of the size of the overall
stock relatively low and the assessment
of the size of the eastern portion of the
stock relatively high. Given the
scientific uncertainty, the fact that the
fishing mortality of the eastern portion
of the stock is strictly controlled
through a hard total allowable catch
(TAC), and the limited scope of this
action, Fmsy is being proposed as the
fishing mortality rate target for this
stock. However, the fishing mortality
rate that would be achieved by the
proposed interim action is estimated to
be between Fsmy and Frebuild.
GARM III provided example estimates
of Frebuild for overfished stocks,
making assumptions about the rebuild
period end-dates and the starting
conditions at the beginning of the
rebuilding periods. In doing so, GARM
III assumed that the catch in FY 2008
will equal the catch in FY 2007. In
contrast, for this interim action, an
estimated catch in FY 2008 was used to
recalculate the starting conditions in FY
2008, and the Frebuilds. For
Amendment 16, the Plan Development
Team (PDT) estimated catch for the
entire FY 2008 year based upon an
extrapolation of landings data for
calendar year 2008 through June 2008.
This interim action relies on the PDT’s
estimated landings for FY 2008 and a
derived estimate of fishing mortality for
Calendar Year (CY) 2008 and the
recalculated Frebuilds. The probabilities
associated with the Frebuilds and
rebuilding end dates are consistent with
the current FMP. Stocks would rebuild
with a 50–percent probability, with the
exception of GB yellowtail flounder,
which has a 75–percent probability of
rebuilding by the end of the rebuilding
period. The end of the rebuilding period
for all stocks with rebuilding plans is
2014, with the exception of GB cod
(2026), CC/GOM yellowtail flounder
(2023), and redfish (2051). Because the
measures to be implemented by this
action would begin 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.
In a similar manner, in order to
calculate the amount of reduction in
fishing mortality required for pertinent
stocks, the estimated fishing mortality
in CY 2008 was considered as the
starting condition. For example, in order
to calculate the required fishing
mortality reduction for the CC/GOM
stock of yellowtail flounder, Frebuild
(0.238) was compared to F 2008 (0.289).
An 18–percent reduction in fishing
mortality is required to reduce F from
0.289 in CY 2008 to achieve an Frebuild
of 0.238 in CY 2009. Table 2 below
summarizes information on the CY 2008
fishing mortality, the fishing mortality
goal of the interim action, and the
percentage fishing reduction objective to
reduce fishing mortality from the
starting conditions (F 2008) to the
fishing mortality rate goal.
hsrobinson on PROD1PC76 with PROPOSALS
TABLE 2. FISHING MORTALITY REDUCTION OBJECTIVES FOR THE PROPOSED INTERIM ACTION
2008 F
Fishing Mortality Rate
Goal
Value Associated with
Fishing Mortality Rate
Goal
Fishing Mortality Rate
Reduction Objective
GB
0.410
Fmsy
0.2466
- 40 %
GOM
0.300
Fmsy
0.237
- 21 %
Species
Cod
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TABLE 2. FISHING MORTALITY REDUCTION OBJECTIVES FOR THE PROPOSED INTERIM ACTION—Continued
2008 F
Fishing Mortality Rate
Goal
Value Associated with
Fishing Mortality Rate
Goal
Fishing Mortality Rate
Reduction Objective
GB
0.083
Fmsy
0.350
322 %
GOM
0.250
Fmsy
0.430
72 %
GB
0.130
Frebuild
0.109
- 16 %
SNE/MA
0.120
Frebuild
0.075
-386%
CC/GOM
0.289
Frebuild
0.238
- 18 %
American plaice
0.099
Fmsy
0.190
92 %
Witch flounder
0.296
Fmsy
0.200
- 32 %
GB
0.131
Fmsy
0.260
98 %
GOM
0.317
Fmsy
0.283
- 11 %
SNE/MA
0.265
Frebuild
0.000
- 100 %
Redfish
0.008
Fmsy
0.038
375 %
White hake
0.065
Frebuild
0.084
29 %
Pollock
NA
Fmsy
5.66
- 48 %
Windowpane
NA
Fmsy
0.50
- 74 %
NA
Fmsy
1.47
- 21 %
NA
Fmsy
0.760
NA
0.060
Frebuild
0.044
- 27 %
Species
Haddock
Yellowtail flounder
Winter flounder
Stock
Ocean pout
Atlantic halibut
NA - not available
hsrobinson on PROD1PC76 with PROPOSALS
Proposed Management Measures
All measures in effect prior to May 1,
2009, including the default measures
relating to DAS reductions scheduled to
go into place and not amended by this
proposed interim rule, would remain in
effect on and after May 1, 2009. This
proposed interim action would
implement management measures to
reduce fishing mortality on the
commercial and recreational fisheries,
without compromising rebuilding
objectives, as well as revise various
management programs in order to
mitigate the negative economic and
social impacts of the FMP to ensure
consistency with National Standards
and required provisions of the
Magnuson-Stevens Act and to enhance
the likelihood of compliance with the
measures. Routine specification of TAC
and annual specifications for the U.S./
Canada Management Area are also
proposed. As is more fully discussed
later in this document, these measures
would result in both quantifiable and
non-quantifiable reductions in fishing
mortality for virtually all of the NE
multispecies stocks managed under the
FMP.
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The proposed interim measures are
designed to work in conjunction with
the current FMP to achieve the fishing
mortality requirements of the FMP. The
analysis of this action presumes that the
proposed measures would be in effect
throughout FY 2009, and that a
subsequent management action
(Amendment 16) will be implemented
on May 1, 2010. The current FMP
management measures include a FY
2009 default measure that will change
the allocation ratio of Category A:B DAS
from 60:40 to 55:45. This measure,
therefore, is not discussed specifically
in the description of the proposed
interim measures that follows. NMFS
anticipates that, if approved and
implemented, this interim action may
be renewed upon expiration for an
additional 185 days, given that the
Council does not anticipate the
implementation of Amendment 16 until
May 2010. The Council also
recommended to NMFS that any interim
action should be in effect for all of FY
2009. The following measures are
proposed to be implemented on May 1,
2009, to reduce overfishing.
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Commercial Measures
1. Differential DAS Counting
Under this proposed interim action,
the existing differential DAS areas in the
GOM and SNE would no longer apply,
and a single, larger differential DAS area
would be implemented in the entire
GOM and in the northern portion of GB,
north of 41o 30’N. lat. For the revised
Interim Differential DAS Area, the DAS
accrual rate would be 2:1. In other
words, under this action, if a vessel
declares into the Interim Differential
DAS Area for 10 hr, the vessel’s DAS
balance would be debited 20 hr. A
vessel would not be charged at the
differential DAS rate if it declared and
transited to another area outside of the
Interim Differential DAS Area. For
example, if a vessel steams through the
Interim Differential DAS Area on its
way to and from the fishing grounds in
the southern portion of the U.S./Canada
Management Area, where DAS are not
counted differentially, it would not be
charged at the 2:1 rate for part of the trip
spend steaming through the Interim
Differential DAS Area. If a vessel
declared and fished both inside the
Interim Differential DAS Area and
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hsrobinson on PROD1PC76 with PROPOSALS
outside that area on the same trip, it
would be charged differential DAS (2:1)
for all the DAS accrued on that trip.
The interaction of current groundfish
and non-groundfish regulatory programs
and the different DAS counting rules
would remain unchanged under this
action (e.g., the cod running clock, Day
Gillnet Category rules, the application of
per DAS possession limits, 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, vessels
fishing in the Interim Differential DAS
Area and the Eastern U.S./Canada
Management Area (exclusively) would
be charged at the differential DAS rate
of 2:1, but would not be charged
steaming time to or from the area. For
vessels fishing in multiple geographic
areas where different rules apply to each
area (such as differential DAS 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,
would still apply.
As under the current regulations,
vessels would be required to declare,
prior to leaving port, their intent to fish
in the Interim Differential DAS Area, via
Vessel Monitoring System (VMS). The
VMS declaration screens would be
modified slightly to accommodate the
fact that the southern border of the
Interim Differential DAS Area divides
the U.S./Canada Management Area into
two portions. For example, a vessel
intending to fish in the Eastern U.S./
Canada Area would also have to specify
whether it would also fish in the Interim
Differential DAS Area.
The Interim Differential DAS Area is
proposed as a means to reduce fishing
mortality on multiple stocks instead of
further reductions in DAS allocations in
order to provide flexibility for vessel
owners.
2. SNE Closure Area
The area in SNE between 40° 30’ and
41° 30’ N. lat., and west of 68° 30’ W.
long. to the shore, including Nantucket
Sound (30-minute square blocks of 97–
107 and 80–90) would be closed to
federally permitted groundfish vessels
(both open access and limited access)
when fishing on groundfish, with the
exception of NE multispecies vessels
using hook gear, provided such vessels
do not retain winter flounder, and
provided the vessels have only hook
gear on board. This interim rule
proposes that groundfish vessels using
only hook gear on a particular trip may
fish in the SNE Closure Area because
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the catch rate of winter flounder is
likely to be very low. Non-groundfish
commercial trips fishing in exempted
fisheries (e.g., summer flounder, scallop,
and skate exemptions), or using
exempted gear, could also fish in the
SNE Closure Area. NE multispecies
vessels not fishing in the SNE Closure
Area would be allowed to transit
through the area, provided all fishing
gear is properly stowed. The SNE
Closure Area is proposed as a means to
reduce fishing mortality on SNE winter
flounder primarily, but would also
reduce fishing mortality on other stocks
such as SNE/MA yellowtail flounder.
TABLE 3. TARGET TACS (MT) FOR FY
2009
3. Modified Trip Limits
4. Specification of Target TACs
Target TACs are utilized in the FMP
as one method of evaluating the success
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 basis of calculating the
incidental catch TACs for the Special
Management Programs. Table 3 lists the
target TACs for FY 2009, based upon
GARM III data and estimated CY 2008
fishing mortalities.
Frm 00062
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Sfmt 4702
Stock
Target TAC
Cod
GB
3,506
Cod
GOM
10,327
Haddock
GB
86,520
Haddock
GOM
1,564
Yellowtail
flounder
GB
1,617
Yellowtail
flounder
SNE/MA
389
Yellowtail
flounder
Under this interim rule, the current
white hake possession limit of 1,000 lb
(454 kg) per DAS would be increased to
2,000 lb (907 kg) per DAS, with the
same maximum of 10,000 lb (4,536 kg)
per trip, and the trip limit for GB winter
flounder, currently 5,000 lb (2.268 kg)
per trip, would be removed. No
retention of any fish would be allowed
for SNE winter flounder, northern
windowpane flounder, or ocean pout.
Vessels fishing for winter flounder or
windowpane flounder in multiple stock
areas would be 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
would be subject to the prohibition on
retention for that trip. Lastly, as
explained further under item 7
(‘‘Annual Specifications for U.S./Canada
Management Area’’), a limit of 5,000 lb
(2,268 kg) of GB yellowtail flounder per
trip would be specified. Modifications
to trip limits are proposed as a means
to reduce fishing mortality or increase
yield because they are a management
tool that can effectively target particular
stocks and are an important component
of the current FMP.
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Species
CC/GOM
860
Plaice
3,214
Witch flounder
928
Winter flounder
GB
Winter flounder
GOM
2,004
379
Redfish
8,614
White hake
2,376
Pollock
6,486
Windowpane
flounder N.
299
Windowpane
flounder S.
338
Halibut
68
* A hard TAC, set through a separate process described in item 6.
5. Revisions to Incidental Catch TACs
and Allocations to Special Management
Programs
This proposed interim action would
revise the specification of incidental
catch TACs applicable to the Special
Management Programs of the FMP 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.
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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
would be adopted under this action, an
incidental catch TAC would no longer
be appropriate for American plaice,
because it would no longer be
considered a stock of concern. Further,
new incidental catch TACs would be
required for GOM winter flounder and
pollock, because they would now be
considered stocks of concern. The
percentages that the TACs are currently
based on would remain unchanged,
with the exception of witch flounder,
which would be reduced from 5–
percent to 2–percent, due to its new
proposed status and the fact that the
fishing mortality rate and total catch
need to be reduced. The incidental
catch TACs for GOM winter flounder
would be 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 proposed management
measures are likely to achieve more
than the required reduction in fishing
mortality, 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 would be 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 would
increase from the current number (8), to
10. Due to the severe fishing mortality
reduction necessary for the SNE/MA
stock of winter flounder, no retention of
this stock would be allowed under this
alternative, and there would be no
incidental catch TAC specified (see
additional discussion under item 10,
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
Stock
Percentage of Total TAC
Initial TAC
Incidental TAC
GB cod
2
3,506
70.1
GOM cod
1
10,327
103.3
GB yellowtail
2
1,617
32.3
CC/GOM yellowtail
1
860
8.6
SNE/MA yellowtail
1
389
3.9
Pollock
5
6,486
324.3
Witch flounder
2
928
18.6
GB winter flounder
2
2,004
40.1
White hake
2
2,376
47.5
GOM winter
5
379
19.0
This proposed rule would also modify
the allocation of the incidental catch
TACs to the various Special
Management Programs due to the
change in status of stocks, as well as 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 would be reduced for GB cod, GB
yellowtail, and GB winter flounder, and
the percent allocation to the Regular B
DAS Program would be increased due to
higher participation in that program
historically. Secondly, this rule would
provide the Administrator, Northeast
Region, NMFS (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
rate of catch of stocks of concern in the
various programs is highly variable. The
proposed 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
Closed Area I Hook Gear Haddock
SAP
Current
New
Current
New
Current
New
GB Cod
hsrobinson on PROD1PC76 with PROPOSALS
Stock
Eastern U.S./Canada Haddock SAP
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%
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Federal Register / Vol. 74, No. 11 / Friday, January 16, 2009 / Proposed Rules
TABLE 5. MODIFICATIONS TO THE INCIDENTAL CATCH TAC ALLOCATIONS FOR FY 2009—Continued
Regular B DAS Program
Eastern U.S./Canada Haddock SAP
Stock
Current
New
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 %
Current
Closed Area I Hook Gear Haddock
SAP
New
none
Current
New
TABLE 6. SPECIFICATION OF INCIDENTAL CATCH TACS FOR SPECIAL MANAGEMENT PROGRAMS (MT) FOR FY 2009
Regular B DAS Program
Eastern U.S./Canada Haddock
SAP
Closed Area I Hook Gear Haddock SAP
GB Cod
49.1
9.8
11.2
GOM Cod
103.3
na
na
GB Yellowtail flounder
25.9
6.5
na
CC/GOM Yellowtail flounder
8.6
na
na
SNE/MA Yellowtail flounder
3.9
na
na
Pollock
291.9
16.2
16.2
Witch flounder
18.6
na
na
GB Winter flounder
32.1
8.0
na
White hake
47.5
na
na
GOM Winter flounder
19.0
na
na
Stock
hsrobinson on PROD1PC76 with PROPOSALS
6. 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 will also be proposing
management measures for the entire
fishery to reduce fishing mortality as
described above and expects to
implement measures for the entire FY
2009, NMFS is including the
specification of the TACs and other
measures for the U.S./Canada
Management Area in this proposed 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
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17:46 Jan 15, 2009
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haddock, and GB yellowtail flounder in
the U.S./Canada Management Area. The
regulations governing the annual
development of TACs were
implemented by Amendment 13 to the
FMP in order to be consistent with the
U.S./Canada Resource Sharing
Understanding (Understanding), which
is an informal (i.e., non-binding)
understanding between the Northeast
Region of NMFS and the Maritimes
Region of the Department of Fisheries
and Ocean of Canada (DFO) that
outlines a process for the management
of the shared GB groundfish resources.
The Understanding specifies an
allocation of TAC for these three stocks
for each country, based on a formula
that considers historical catch
percentages and current resource
distribution.
Annual TACs are determined through
a process involving the Council, the
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Transboundary Management Guidance
Committee (TMGC), and the U.S./
Canada Transboundary Resources
Steering Committee. In September 2008,
the TMGC approved the 2008 Guidance
Document for Eastern GB cod, Eastern
GB haddock, and GB yellowtail
flounder, which included recommended
U.S. TACs for these stocks. The
recommended FY 2008 TACs were
based upon the most recent stock
assessments TRAC Status Reports for
2008), and the fishing mortality strategy
shared by both NMFS and DFO. The
strategy is to maintain a low to neutral
(less than 50–percent) risk of exceeding
the fishing mortality limit reference
(Fref = 0.18, 0.26, and 0.25 for cod,
haddock, and yellowtail flounder,
respectively). When stock conditions are
poor, fishing mortality rates should be
further reduced to promote rebuilding.
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Federal Register / Vol. 74, No. 11 / Friday, January 16, 2009 / Proposed Rules
The TMGC concluded that the most
appropriate combined U.S./Canada TAC
for Eastern GB cod for FY 2009 is 1,700
mt. This corresponds to a low risk (less
than 25- percent) of exceeding the Fref
of 0.18 (i.e., Fmsy) in 2009. However,
due to poor recruitment, there is a high
risk (greater than 75–percent) that stock
biomass will not increase from CY 2009
to CY 2010. The annual allocation
shares between countries for FY 2009
are based on a combination of historical
catches (15–percent weighting) and
resource distribution based on trawl
surveys (85–percent weighting).
Combining these factors entitles the
United States to 31–percent of the
shared TAC and Canada to 69- percent,
resulting in a national quota of 527 mt
for the United States and 1,173 mt for
Canada.
For Eastern GB haddock, the TMGC
concluded that the most appropriate
combined U.S./Canada TAC for FY 2009
fishing year is 30,000 mt. This
represents a low to neutral risk (greater
than 25–percent but less than 50–
percent) of exceeding the Fref of 0.26.
Adult biomass is projected to peak at
158,000 mt in CY 2008 (reflecting the
recruitment and growth of the
exceptional 2003 year class), and
decline to 131,000 mt in 2010. The
annual allocation shares between
countries for FY 2009 are based on a
combination of historical catches (15–
percent weighting) and resource
distribution based on trawl surveys (85–
percent weighting). Combining these
factors entitles the United States to 37–
percent of the shared TAC and Canada
to 63–percent, resulting in a national
quota of 11,100 mt for the United States
and 18,900 mt for Canada.
For GB yellowtail flounder, the TMGC
concluded that the most appropriate
combined U.S./Canada TAC for the
2009 fishing year is 2,100 mt. This
corresponds to an F of 0.11, lower than
the Fref of 0.25, and is consistent with
the fishing mortality required to rebuild
GB yellowtail flounder by 2014. With a
2967
catch of 2,100 mt in 2009, the age 3+
biomass is expected to increase by about
21–percent. The annual allocation
shares between countries for 2008 are
based on a combination of historical
catches (15–percent weighting) and
resource distribution based on trawl
surveys (85–percent weighting).
Combining these factors entitles the U.S.
to 77–percent of the shared TAC and
Canada to 23–percent, resulting in a
national quota of 1,617 mt for the U.S.
and 483 mt for Canada.
On October 8, 2009, the Council
approved, consistent with the 2008
Guidance Document, the following U.S./
TACs recommended by the TMGC: 527
mt of Eastern GB cod; 11,100 mt of
Eastern GB haddock; and 1,617 mt of GB
yellowtail flounder. The proposed 2009
fishing year TACs for the U.S./Canada
Management Area represent a decrease
for cod and yellowtail flounder, and an
increase for haddock compared with
those specified for the 2008 fishing year
(Tables 7 and 8).
TABLE 7. 2009 U.S./CANADA TACS (MT) AND PERCENTAGE SHARES (IN PARENTHESES)
GB Cod
GB Yellowtail Flounder
1,700
527 (31%)
1,173 (69%)
Total Shared TAC
U.S. TAC
Canada TAC
GB Haddock
30,000
11,100 (37%)
18,900 (63%)
2,100
1,617 (77%)
483 (23%)
TABLE 8. 2008 U.S./CANADA TACS (MT) AND PERCENTAGE SHARES (IN PARENTHESES)
GB Cod
GB Yellowtail Flounder
2,300
667 (29%)
1,633 (71%)
Total Shared TAC
U.S. TAC
Canada TAC
GB Haddock
23,000
8,050 (35%)
14,950 (65%)
2,500
* 1,950 (78%)
550 (22%)
hsrobinson on PROD1PC76 with PROPOSALS
* Adjusted downward to 1,868.7 mt due to overharvest of 2007 TAC
The 2009 TACs are based upon stock
assessments conducted in June 2008 by
the TRAC. The proposed TACs are
consistent with the results of the TRAC
and the TMGC’s harvest strategy, as well
as the GB yellowtail flounder rebuilding
plan implemented by FW 42. 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 would 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
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17:46 Jan 15, 2009
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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 proposing, 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
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Sfmt 4702
early part of the year, NMFS is
proposing this same measure for FY
2009. Thus, the FY 2009 opening of the
Eastern U.S./Canada Area for trawl
vessels would be postponed from May
1, 2009, until August 1, 2009, while
allowing more selective longline gear
access during May through July. Such
vessels would be limited to a cod catch
of 5–percent of the cod TAC, or 26.4 mt
of cod. The objective of the proposed
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 proposing implementation of 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
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Federal Register / Vol. 74, No. 11 / Friday, January 16, 2009 / Proposed Rules
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 would be an appropriate trip
limit to allow harvesting of the TAC and
increase the likelihood that further
restrictions will not be necessary during
the fishing year to slow the catch rate.
Third, the Regional Administrator is
proposing to allow the use of the Ruhle
Trawl in the Eastern U.S./Canada Area.
Under current regulations, only a
flounder net and the haddock separator
trawl are permanently authorized for
such use. The 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 would provide
another alternative for trawl vessel
operators and, therefore, provide
additional flexibility. As detailed in the
July 14, 2008 rule, the Ruhle trawl has
been demonstrated to substantially
reduce catch of many species of
groundfish, and therefore its use would
be consistent with the management
objectives for the Eastern U.S./Canada
Area.
Lastly, the Regional Administrator is
proposing zero trips into the Closed
Area (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 SAP. The
Regional Administrator has the
authority to determine the allocation of
the total number of trips into the CA II
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).
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17:46 Jan 15, 2009
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7. Haddock TAC for CA I Hook Gear
Haddock SAP
Under this action, a haddock TAC for
the CA I Hook Gear Haddock SAP
would be specified 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), and
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 as 35–percent of the
size of the total GB haddock stock.
Therefore, if the 2007 exploitable
biomass of haddock is 321,870 mt, the
formula and resultant TAC would be as
follows: ((.35)(321,870)/35,317) x 1,130
= 3,604.5 mt.
8. Elimination of the SNE/MA Winter
Flounder SAP
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 fishing mortality to as close to
zero as practicable, this SAP would be
eliminated. Because the SAP could
enable limited targeting of winter
flounder, elimination of the SAP may
prevent some catch of winter flounder
from occurring.
9. Elimination of the State Waters
Winter Flounder Exemption
The State Waters Winter Flounder
Exemption currently 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 fishing
mortality to as close to zero as
practicable, this SAP would be
eliminated. Because the SAP could
enable limited targeting of winter
flounder, elimination of the SAP may
prevent some catch of winter flounder
from occurring.
10. Mitigating Measures
Reduction of Haddock Minimum Size.
Under this interim action, the haddock
minimum size would be reduced to 18
inches (45 cm) for both the commercial
and recreational fisheries in order to
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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 99–
percent 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 would allow
vessels to retain additional haddock,
thereby increasing yield for this species.
Other recreational measures are
described under item 11.
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,
would be extended through this
proposed 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’’ that is not otherwise
accessible. The geographic area would
remain unchanged, and the rules that
apply would remain unchanged, with
the exception of the reallocation of the
incidental catch TACs (see Table 5).
When fishing in this SAP, vessels
must currently 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 are required 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,
provided the Program requirements
designed to minimize impacts of stocks
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of concern are met. Under this proposed
rule, in addition to the modifications
proposed under item 5 (Revisions to
Incidental Catch TACs and Allocations
to Special Management Programs),
several revisions would be made to the
Regular B DAS Program in order to
address the current status of stocks and
necessary reductions to fishing
mortality, 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 item 5,
NMFS would closely monitor the level
of discarding of stocks that are proposed
to have zero retention, but for which
there is no incidental TAC proposed
(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
incidental catch TAC that remains
uncaught from quarters one, two, and
three would roll over into the
subsequent quarter.
Due to the number of flatfish stocks
that need reductions in fishing
mortality, the use of low profile (tiedown) gillnets under this interim action
would be 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 bottomset 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 would be prohibited under
this Program. The use of gillnet gear to
catch haddock would still be 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
are prohibited in the pertinent stock
area for the duration of the quarter. This
proposed interim rule would treat
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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 has been harvested, vessels
fishing under a Regular B DAS would 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 would be 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 proposed rule, the current
prohibition on leasing DAS between
sector and common pool vessels would
be 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 vessels
may lease would be eliminated.
Amendment 13 implemented a
restriction that a lessee may lease
Category A DAS in an amount 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 would be removed in order to
increase flexibility and efficiency in the
DAS leasing market. These mitigation
measures, including the DAS Transfer
Program modifications described below,
would also enhance the likelihood of
compliance with the measures by
providing additional fishing
opportunities.
DAS Transfer Program Modifications.
Under this proposed rule, the DAS
conservation tax would be removed
from the DAS Transfer Program.
Specifically, the mandatory reduction of
Category A and B DAS (20 percent), and
Category C DAS (90 percent), would 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
proposing this temporary modification
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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)
would limit the amount of any effect the
change may have on increasing the
overall DAS use rate. NMFS is not
proposing a DAS tax refund, because it
would be counter to the regulations that
have been in place.
11. Recreational Measures
This action proposes to reduce 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. Following are the
recreational measures proposed under
this action: The current seasonal
prohibition on the possession of GOM
cod for both private recreational and
charter/party vessels would be extended
from its current duration of November
through March, to November through
April 15. Secondly, this action would
implement a GB cod trip limit of 10 cod
per person per day for charter/party
vessels, consistent with the GB cod trip
limit for private recreational vessels.
Retention of winter flounder caught in
the SNE/MA stock area would be
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 could 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 would be reduced to 18–inches
(45.7–cm).
12. Council’s Recommended Measures
for Interim Action Considered, but
Rejected
At it’s September 4, 2008, meeting,
the Council recommended that NMFS
implement an interim action for the
duration of FY 2009 and proposed
specific management measures. The
Council’s alternative proposed an 18–
percent default DAS reduction; and
target TACs for GB yellowtail flounder,
SNE/MA yellowtail flounder, CC/GOM
yellowtail flounder, American plaice,
witch flounder, GB winter flounder,
GOM winter flounder, redfish, white
hake, pollock, GB cod, and GOM cod.
The Council’s proposed TACs were
those associated with Frebuild for all
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stocks except for the two cod stocks,
which would be the TACs associated
with Fmsy, and the TAC for SNE/MA
winter flounder, which would be lower
than that associated with Fmsy. The
Council’s proposal also included a
5,000–lb (2,268–kg) trip limit for SNE/
MA winter flounder, and a 1,000–lb
(454–kg)/DAS and 5,000–lb (2,268–kg)/
trip limit for witch flounder. TAC
overharvests in FY 2009 would be
deducted from the FY 2010 TACs, and
sectors would not be held responsible
for FY 2009 over-harvests that they were
not responsible for. Amendment 16 was
proposed as the means by which the FY
2009 TAC overharvests would be
reconciled in FY 2010.
In addition, the Council
recommended mitigation measures, as
follows: An 18–inch (45–cm) haddock
minimum fish size; extension of the
Eastern U.S./Canada Haddock SAP;
expansion of the CA I Hook Gear
Haddock SAP; removal of the DAS
Transfer Program’s conservation tax;
and removal of the restriction that
prohibits sector members from leasing
to and from common pool vessels.
Although, for some stocks, the
appropriate amount of catches in FY
2009 (i.e., the projected TACs associated
with Fmsy or F rebuild) would be
similar to or larger than recent catch
levels, because of the large fishing
mortality reductions necessary to end
overfishing NMFS has determined that
the Council’s recommended measures to
reduce fishing mortality are insufficient
to meet NMFS’ objectives.
To estimate the amount of fishing
mortality that can be expected from a
given allocation of DAS, NMFS utilizes
the Closed Area Model (CAM), which
incorporates multiple factors, and
provides indications of relative changes
in fishing exploitation. NMFS could not
adopt the Council’s alternative because
CAM analyses of a similar alternative
(i.e., the no action alternative), indicated
that fishing mortality reductions would
be insufficient for a number of stocks (7
of 11 requiring fishing mortality
reductions). Even if the trip limits
associated with the Council’s alternative
achieved the witch flounder objective,
the fishing mortality associated with six
stocks would have been excessive.
Further, deductions of TAC
overharvests in the subsequent fishing
year would compound the challenge of
rebuilding stocks (depending upon the
biomass trend, stock structure, and
recruitment) in the time required by the
Magnuson-Stevens Act and the FMP.
Finally, an interim action cannot
implement measures that would go into
place in a subsequent fishing year, such
as a TAC deduction for over-harvest that
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could occur in 2009, because of the
statutory limitations on its duration.
NMFS explored whether the Council’s
recommended measures could be
modified to meet the objectives of the
interim action, and developed a hard
TAC alternative in order to reduce the
risk that appropriate catch levels would
be exceeded. As detailed in the EA
developed for this proposed action,
NMFS ultimately rejected the hard TAC
alternative for two principal reasons: 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, thereby causing
severe economic costs to the industry;
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 to successfully implement
in the short period of an interim action
and possibly inconsistent with
Magnuson-Stevens Act National
Standards and required provisions.
This proposed interim action would
adopt the following mitigation measures
proposed by the Council: Extension of
the Eastern U.S./Canada Haddock SAP;
revision of the DAS Leasing Program;
revision of the DAS Transfer Program;
and reduction of the haddock minimum
size limit.
NMFS considered but rejected the
Council’s Amendment 16 proposed
mitigating measures that would modify
the CA I Hook Gear Haddock SAP, and
the extension of the CA II Yellowtail
Flounder SAP to include haddock. The
Amendment 16 proposal to modify the
CA I Hook Gear Haddock SAP would
expand the geographic and temporal
scope of the SAP. The expansion of the
CA I Hook Gear Haddock SAP is not
supported by relevant research. The
data relied upon for the approval of the
CA I Hook Gear Haddock SAP in FW
40A were from the months of October
through December. These data
supported the determination that the
SAP would have minimal impacts on
stocks of concern (notably cod). In
contrast, the SAP, as expected to be
proposed in Amendment 16, would be
open for a 9-month period from May
through January. NMFS is unaware of
pertinent research that would support
the conclusion that the expansion
would have minimal impacts on stocks
of concern. Although the expansion of
the SAP may provide some mitigating
effect for some members of the fishery,
only one gear type would be affected
and the measures would represent an
expansion of effort into a closed area.
Such an expansion may not be fully
consistent with the intent of this action.
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Similarly, the Council’s proposal for
the CA II Yellowtail Flounder SAP,
which would allow targeting of either
haddock or yellowtail flounder in this
area, would represent a major
modification to this SAP. NMFS is
unaware of pertinent research that
would support the conclusion that the
expansion would have minimal impacts
on stocks of concern. Therefore, the
Council’s proposed SAP modification
may have potential adverse impacts on
stocks of concern, and could undermine
the utility of CA II.
Classification
Because this action is a proposed rule,
at this time, NMFS has not made a final
determination that the interim measures
that this proposed rule would
implement are consistent with the
national standards of the MagnusonStevens Act and other applicable laws.
NMFS, in making this final
determination, will take into account
the data, views, and comments received
during the comment period.
This proposed rule has been
determined to be significant for the
purposes of Executive Order (E.O.)
12866.
This proposed rule does not contain
policies with Federalism or ‘‘takings’’
implications as those terms are defined
in E.O. 13132 and E.O. 12630,
respectively. This proposed rule does
not contain any new recordkeeping or
reporting requirements.
NMFS prepared an IRFA as required
by section 603 of the Regulatory
Flexibility Act (RFA). The IRFA
describes the economic impact this
proposed rule, if adopted, would have
on small entities. A description of the
action, why it is being considered, and
the legal basis for this action are
contained in the preamble to this
proposed rule and in the Executive
Summary and Background (Section 3.0)
of the EA prepared for this action.
As described above, this action is
necessary to comply with the fish stock
rebuilding requirements of the FMP and
the Magnuson-Stevens Act. In response
to new scientific information, this
action would reduce fishing mortality
on all groundfish stocks and provide
flexibility to the fishing industry to
adapt to the new regulations and help
mitigate negative economic impacts.
The principal goal of this interim action
is to eliminate or reduce overfishing and
achieve the rebuilding fishing mortality
rates to the extent practicable for an
interim period, while the Council
develops more comprehensive,
permanent measures. The Preferred
Alternative would achieve an
appropriate balance of short-term costs
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and benefits that would strictly
maintain adherence to rebuilding plans
for most stocks, and reduce fishing
mortality to Fmsy or below for all stocks
except northern windowpane flounder.
NMFS fully analyzed and considered
three principal alternatives (plus the No
Action Alternative), and considered, but
did not fully analyze, several additional
alternatives characterized as considered
but rejected. Alternative 1 relies upon
an 18–percent DAS reduction combined
with two different configurations of
differential DAS areas; Alternative 2 is
based upon a 40–percent DAS
reduction; and Alternative 3, the
Preferred Alternative relies on an 18–
percent DAS reduction and one large
differential DAS area. Fishing mortality
reductions for all three alternatives
include management measures for the
commercial and recreational portions of
the fishery. The No Action Alternative
consists of the management measures
currently in effect for the FMP, as well
as the May 1, 2009, default measures
specified under Amendment 13. Under
the default measures, Category A DAS
would be reduced by approximately 18–
percent, and all other management
measures would remain the same.
Under all alternatives (except the No
Action Alternative) the trip limit for
white hake would be modified from
1,000–lb (454- kg) per DAS, to 2,000–lb
(907–kg) per DAS (with the maximum
per trip remaining at 10,000–lb (4,536–
kg)); the current trip limit of 5,000–lb
(2,268–kg)/trip for GB winter flounder
would be removed; and the retention of
ocean pout, SNE winter flounder, and
the northern stock of windowpane
flounder would be prohibited. Also,
under all alternatives, a SNE Closure
Area is being proposed to protect SNE
winter flounder. Furthermore, the two
current regulatory programs that allow
vessels to retain winter flounder (that
would otherwise be prohibited from
retaining winter flounder) would be
eliminated, i.e., the SNE Winter
Flounder SAP and the State Waters
Winter Flounder Exemption.
The following measures for the
recreational sector would be
implemented under the Preferred
Alternative, as well as the other two
principal alternatives considered: The
current seasonal prohibition on the
retention of GOM cod (for both private
recreational vessels fishing in the EEZ
and federally permitted party/charter
vessels) would be lengthened by 2
weeks, with the resulting seasonal
closure of November through April 15;
persons fishing on federally permitted
party/charter vessels would be
prohibited from possessing more than
10 cod per day (caught anywhere), a
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more restrictive limit than the current
limit of 10 cod per day when fishing
only in the GOM; and private
recreational vessels fishing in the EEZ
and federally permitted party/charter
vessels would not be allowed to retain
SNE winter flounder.
In addition, the following mitigation
measures would be implemented under
the proposed rule and other alternatives
considered: The DAS Transfer Program
would be modified to remove the DAS
tax on transferred DAS; the Eastern
U.S./Canada Haddock SAP, which is
scheduled to expire, would be renewed;
the DAS Leasing Program rules would
be modified to remove the cap on the
number of DAS that can be leased and
to allow leasing between sector and
common pool vessels; the minimum
size for haddock would be reduced from
19 inches (47.5 cm) to 18 inches (45 cm)
for both the recreational and
commercial fisheries; and modifications
would be made to the Regular B DAS
Program, including roll-over of quarterly
incidental catch TACs. A more detailed
description of the proposed and other
two principal alternatives analyzed and
considered may be found in the
preamble of this proposed rule and in
the EA, respectively.
Description of and Estimate of the
Number of Small Entities to Which the
Proposed 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. The size
standard for commercial fishing entities
is $4 million in sales, while the size
standard for party/charter 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 his proposed rule. The remaining
discussion describes the number of
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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.
Economic Impacts of the Proposed
Action
The Preferred Alternative contains
several different measures that may
affect regulated vessels holding either
an open access or limited access NE
multispecies permit. During FY 2007,
there were a total of 1,292 commercial
open access permits (Handgear B) and a
total of 1,530 limited access permits
issued. Of these permits, 664 limited
access permit holders and 123 open
access permit holders participated in
the groundfish fishery during FY 2007.
The principal proposed management
measures include a reduction in DAS;
specification of differential DAS in the
entire GOM, as well as a portion of GB;
a SNE Closure Area; and modifications
to trip limits. Because of statutory and
regulatory requirements to meet certain
conservation objectives, the overall
short term economic impact of the
proposed action and any alternative
considered would be negative.
Region-wide, the impact on revenue
received on trips where groundfish were
landed was estimated to fall by 31
percent, while sales of all species was
estimated to be reduced by 20 percent
(from $156 million to $126 million).
Among individual vessels, a small
number of regulated entities, primarily
from NJ, may be able to increase sales
due to the location of the SNE Closure
Area relative to taking no action (i.e.,
the SNE Differential DAS Area would
remain in place under the No Action
Alternative). That is, fishing
opportunities in the area that would
now be opened to these vessels would
more than offset the changes in trip
limits and DAS reduction. However, for
the overwhelming majority of regulated
small entities, the economic impacts
would be negative. The impact on total
revenue would vary depending on a
port’s dependence on groundfish, with
the greatest reductions for ME and MA
(34 percent and 27 percent,
respectively). For vessels that fish
exclusively in the GOM, the 2:1
differential DAS counting, coupled with
the default 18–percent reduction in
DAS, is equivalent to a 36–percent
reduction in DAS. For vessels with a
low dependence on groundfish, even
this reduction in DAS may not result in
a large reduction in total catch. The
combination of where vessels fish, and
higher dependence on groundfish trip
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income, results in the highest impacts
on fishing revenue.
The estimated reduction in total
revenue to NH and CT home port
vessels was 16 percent, and 17 percent,
respectively. For the other states, the
expected reduction ranged from 6
percent in NY to 8 percent in RI.
In relative terms, the proposed
measures would have similar impacts
among vessels of different sizes. Among
the most affected vessels (the 20 percent
that would experience the greatest
impacts), the adverse impact on small
vessels was less (39 percent) than for
either medium or large vessels. For
those vessels least affected by the
Preferred Alternative, with respect to
impacts by primary fishing gear, the
reduction in total revenue was similar
for vessels using gillnet or trawl gear.
However, for those vessels more highly
impacted by the Preferred Alternative,
trawl gear impacts were higher than for
either gillnet or hook gear vessels. For
trawl vessels, an average to above
average level of severity of impacts
would mean a 30 percent reduction in
total revenue, whereas gillnet and hook
gear vessels would experience a 19
percent and 12 percent reduction,
respectively.
Although analyses of the anticipated
impacts of past management actions and
subsequent comparison with the
realized impacts of such actions
suggests that realized revenue losses
have been lower than estimated, the
proposed restrictions would make it
more difficult for vessels to cover fixed
costs on available groundfish trips and
would place greater pressure on vessels
to earn additional income from nongroundfish fishing opportunities. The
proposed action would implement some
mitigating measures, but not all vessels
would be able to take advantage of these
opportunities; some would still require
financial outlays that may not be
supportable, given the reduced fishing
opportunities that would be available.
The proposed measures would affect
not only regulated entities engaged in
commercial fishing for groundfish, but
also entities that provide recreational
fishing services to anglers. Available
data indicate that, of the 92 federally
permitted charter/party vessels that
reported keeping cod, haddock, or
winter flounder, approximately onethird would be adversely affected by
one or more of the proposed measures,
and about two-thirds of participating
party/charter operators would not be
adversely affected. Party/charter
receipts may be expected to be reduced
by approximately 6 percent. The impact
of extending the closed season for
recreationally caught GOM cod is
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difficult to predict due to the highly
variable catch during the month of
April. Reducing the size limit for
haddock would increase the number of
opportunities to keep haddock on all
fishing trips.
The overall economic impact of the
FY 2009 U.S./Canada TACs would
likely be similar or slightly negative,
compared to the economic impacts of
the TACs specified for FY 2008. The
specification of the proposed U.S./
Canada TACs would result in a similar,
or slightly reduced level of income from
trips into the U.S./Canada Management
Area. The FY 2009 cod and yellowtail
flounder TACs would represent a
decrease from the FY 2008 TAC levels.
The changes in TAC reflect changes in
stock size and the U.S. percentage share.
The principal effort reduction
measures may reduce monkfish fishing
effort due to the requirement that
limited access monkfish Category C and
D vessels that also hold a NE
multispecies DAS permit use a NE
multispecies DAS in conjunction with a
monkfish DAS. The proposed measures
would particularly impact those vessels
with relatively few multispecies DAS.
Monkfish vessels with a Category C or
D permit may experience revenue loss if
they previously fished in the proposed
SNE Closure Area and cannot catch a
similar amount of monkfish from
outside of this area. The current
regulations that allow limited access
monkfish Category C and D vessels with
fewer allocated NE multispecies DAS
than allocated monkfish DAS to fish the
difference between these two
allocations, as monkfish-only DAS
would still apply and would help
mitigate the impact of the proposed
measures (in particular, the reduction in
NE multispecies DAS and the SNE
Closure Area) on monkfish fishing
effort.
The two primary skate fisheries, a
wing fishery and a lobster bait fishery,
are largely interwoven with the NE
multispecies fishery. The regulations
require that vessels must be fishing on
a NE multispecies, monkfish, or scallop
DAS, or fish in an exempted fishery, in
order to possess skates. The vast
majority of skate landings are landed on
NE multispecies Category A DAS, and
the DAS restrictions and SNE Closure
Area of the Preferred Alternative would
reduce fishing effort on skates. Thus, the
proposed measures would have a
negative economic impact on the skate
fishery. The SNE Closure Area may have
a greater negative impact on the skate
bait fishery than the skate wing fishery,
because the SNE Closure Area
encompasses the bulk of the area fished
in the skate bait fishery. If vessels were
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able to catch skate outside of the SNE
Closure Area, the impacts would be
mitigated.
Economic Impact of Alternatives to the
Proposed Action
Under the No Action Alternative the
estimated groundfish trip revenue
would decline by 12.1 percent to $89
million, and total fishing revenue would
decline by 7.7 percent to $145 million.
The relative reduction in groundfish trip
revenue varied little by home port state
ranging from 10.3 percent to 12.8
percent. However, the change in total
trip revenue varied among home port
states primarily based on the relative
contribution of groundfish trip revenue
to total revenue. For example, total trip
revenue declined by approximately 10
percent in ME, NH, and MA, but
declined by no more than 6 percent in
any other state. The change in revenue
for individual vessels depends upon
DAS use rate, as well as dependence
upon groundfish. Under No Action, any
vessel whose current DAS use rate was
low would be unaffected, since their
allocated A DAS under No Action
would still be greater than the DAS they
used. In relative terms, the No Action
alternative would have similar impacts
among vessels of different sizes. Among
primary gears, the relative distribution
of adverse impact on total revenue was
nearly identical for vessels using gillnet
or trawl gear, and less for most hook
vessels.
Under Alternative 1 (inshore and
offshore GOM differential DAS areas,
with a relative high rate), the estimated
groundfish trip revenue would decline
by 28 percent to $72 million, and total
fishing revenue would decline by 18
percent to $129 million. Alternative 1
would have an adverse impact on 477
of the 509 vessels included in the
analysis. With a few exceptions,
Alternative 1 would have similar
impacts among vessels of different sizes.
Compared to all other states, adverse
impact on fishing revenue for ME home
port vessels was much higher for vessels
up to the 20th percentile (12 percent),
and was higher for vessels between the
20th percentile and the median (21
percent). At intervals above the median,
the impacts on ME home port vessels
were similar to those on MA home port
vessels. Vessels with high dependence
on groundfish trip revenue may be
expected to be more adversely affected
by Alternative 1 than less dependent
vessels.
Alternative 1 reduces fishing effort,
and therefore reduces opportunities to
catch and land skates. Compared to the
No Action alternative, Alternative 1
would have negative economic impacts
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on skate fishing vessels. The SNE
Closure Area may have greater negative
economic impacts on the skate bait
fishery than on the skate wing fishery.
Skate vessels potentially impacted by
the SNE Closure Area may be able to
mitigate some of their revenue losses by
fishing in exempted fisheries. In general
terms, Alternative 1 could have greater
negative economic impacts on skate
vessels than the other alternatives due
to the 2.25:1 differential DAS area in the
western GOM, where a great deal of
skate fishing occurs.
Under Alternative 1, the 18–percent
DAS reduction may reduce monkfish
fishing effort, due to the requirement
that limited access monkfish Category C
and D vessels that also hold a NE
multispecies DAS permit use a NE
multispecies DAS in conjunction with a
monkfish DAS. However, the existing
regulation that allows limited access
monkfish Category C and D vessels with
fewer allocated NE multispecies DAS
than allocate monkfish DAS to use the
difference between these two allocations
as monkfish-only DAS will help
mitigate such impact on monkfish
fishing effort. The SNE year-round
closure, although smaller in size than
the SNE Differential DAS Area currently
in effect, would likely impact inshore
monkfish gillnet vessels that fish in this
region, reducing monkfish fishing effort
overall in this area with a subsequent
negative economic impact to the
monkfish fishery. The extent of this
potential negative social and economic
impact would depend on the number of
limited access monkfish Category C and
D vessels actively fishing in the
statistical areas encompassed by the
closure, how much monkfish is landed
from these areas, and whether or not
these vessels could move their fishing
operations into an open area in an effort
to mitigate the impacts of the closure.
Under Alternative 2 (40–percent DAS
reduction), the estimated groundfish
trip revenue would decline by 33
percent to $68 million and total fishing
revenue would decline by 21 percent to
$124 million. Reflecting the relatively
larger share of groundfish trip income in
total revenue, the expected reduction in
total fishing revenue was estimated to
be at least 25 percent in ME (27
percent), and MA (27 percent). Across
all vessels, gross revenues for only eight
of the vessels included in the analysis
would not change relative to status quo
conditions, while for the remaining
vessels the estimated reduction in total
revenue ranged from 3 percent to 37
percent. In relative terms, Alternative 2
would have somewhat similar impacts
among vessels of different sizes. Among
primary gears the relative distribution of
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adverse impact on total revenue was
similar for vessels using gillnet or trawl
gear. The relative distribution of adverse
impacts differed between states that
border the GOM (ME, NH, and MA) and
those that do not. Vessels with high
dependence on groundfish trip revenue
may be expected to be more adversely
affected by Alternative 2 than less
dependent vessels.
Alternative 2 reduces fishing effort,
and therefore reduces opportunities to
catch and land skates. Compared to the
No Action alternative, Alternative 2
would be expected to have negative
economic impacts on skate fishing
vessels. The SNE Closure Area may
have greater negative economic impacts
on the skate bait fishery than on the
skate wing fishery. Skate vessels
potentially impacted by the SNE closure
area may be able to mitigate some of
their revenue losses by fishing in
exempted fisheries. Alternatives 2 and 3
are difficult to differentiate from an
economic impact standpoint.
Under Alternative 2, the 40–percent
DAS reduction may reduce monkfish
fishing effort due to the requirement
that limited access monkfish Category C
and D vessels that also hold a NE
multispecies DAS permit use a NE
multispecies DAS in conjunction with a
monkfish DAS. However, the existing
regulation that allows limited access
monkfish Category C and D vessels with
fewer allocated NE multispecies DAS
than allocate monkfish DAS to use the
difference between these two allocations
as monkfish-only DAS will help
mitigate such impact on monkfish
fishing effort. The SNE year-round
closure, although smaller in size than
the SNE Differential DAS Area currently
in effect, would likely impact inshore
monkfish gillnet vessels that fish in this
region, reducing monkfish fishing effort
overall in this area with a subsequent
negative economic impact to the
monkfish fishery. The extent of this
potential negative social and economic
impact would depend on the number of
limited access monkfish Category C and
D vessels actively fishing in the
statistical areas encompassed by the
closure, how much monkfish is landed
from these areas, and whether or not
these vessels could move their fishing
operations into an open area in an effort
to mitigate the impacts of the closure.
List of Subjects in 50 CFR part 648
Fisheries, Fishing, Reporting and
recordkeeping requirements.
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2973
Dated: January 9, 2009
Samuel D. Rauch III,
Deputy Assistant Administrator For
RegulatoryPrograms, National Marine
Fisheries Service.
For the reasons stated in the
preamble, 50 CFR part 648 is proposed
to be 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 § 648.2, a new definition for
‘‘low profile gillnet’’ is added, in
alphabetical order, to read as follows:
§ 648.2
Definitions.
*
*
*
*
*
Low profile gillnet, with respect to the
NE multispecies fishery, means a
bottom-set gillnet with reduced vertical
height achieved by tying the floatline to
the leadline or by modifying the
construction of the floatline, or through
other means, to reduce or eliminate its
buoyancy.
*
*
*
*
*
3. In § 648.10, paragraph (b)(5) is
suspended, and paragraph (b)(6) is
added to read as follows:
§ 648.10 DAS and VMS notification
requirements.
*
*
*
*
*
(b) * * *
(6) VMS notification requirements for
other fisheries. Unless otherwise
specified in this part, or via letters sent
to affected permit holders under
paragraph (b)(2) of this section, the
owner or authorized representative of a
vessel that is required to use VMS, as
specified in paragraph (b)(1) of this
section, must notify the Regional
Administrator of the vessel’s intended
fishing activity by entering the
appropriate VMS code prior to leaving
port at the start of each fishing trip.
Notification of a vessel’s intended
fishing activity includes, but is not
limited to, gear and DAS type to be
used; area to be fished; and whether the
vessel will be declared out of the DAS
fishery, or will participate in the NE
multispecies and monkfish DAS
fisheries, including approved special
management programs. A vessel cannot
change any aspect of its VMS activity
code outside of port, except that a NE
multispecies vessel is authorized to
change the category of DAS used (i.e.,
flip its DAS), as provided at § 648.85(b),
or change the area declared to be fished
so that the vessel may fish both inside
and outside of the Eastern U.S./Canada
Area on the same trip, as provided
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at§ 648.85(a)(3)(viii)(A). VMS activity
codes and declaration instructions are
available from the Regional
Administrator upon request.
*
*
*
*
*
4. 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 (60),
(62) through (66), (70), (76), (81) through
(83), and (85) through (89) are
suspended.
C. Paragraphs (g)(4) and (5) are
suspended.
D. Paragraphs (a)(183) through (192),
(c)(90) through (122), and (g)(6) and (7)
are added.
The additions read as follows:
§ 648.14
Prohibitions.
hsrobinson on PROD1PC76 with PROPOSALS
*
*
*
*
*
(a) * * *
(183) Enter, or be on a fishing vessel
with a NE multispecies permit in the
area described in § 648.81(n), except as
provided for in § 648.81(n).
(184) Fish for, harvest, possess, or
land regulated species in or from the
closed area specified in § 648.81(n),
unless otherwise allowed under
§ 648.81(n).
(185) 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).
(186) 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).
(187) 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).
(188) 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).
(189) If fishing inside the Eastern
U.S./Canada Area and in possession of
fish in excess of what is allowed under
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).
(190) Fail to comply with the
reporting requirements under
§ 648.85(a)(3)(viii)(A)(2) when fishing
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inside and outside of the Eastern U.S./
Canada Area on a trip.
(191) 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
§ 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).
(192) 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), (g), (h), and
(l), 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
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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
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) If fishing under the party/charter
or private recreational regulations in the
SNE Closure Area defined under
§ 648.81(n)(1), fish for or retain winter
flounder.
(99) 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).
(100) 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.
(101) 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).
(102) If fishing in the Regular B DAS
Program specified in § 648.85(b)(6), fail
to comply with the VMS requirement
specified in § 648.85(b)(6)(iv)(A).
(103) 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).
(104) If fishing in the Regular B DAS
Program specified in § 648.85(b)(10), fail
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to comply with the VMS declaration
requirement specified in
§ 648.85(b)(10)(iv)(C).
(105) 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).
(106) 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).
(107) 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).
(108) 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).
(109) 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).
(110) 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).
(111) If fishing in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(7), fail to comply with the
DAS use restrictions specified in
§ 648.85(b)(7)(iv)(J), and (b)(7)(v)(A) or
(b)(7)(vi)(A), whichever is applicable.
(112) If fishing in the CA I Hook Gear
Haddock SAP specified in
§ 648.85(b)(7), fail to comply with the
reporting requirement specified in
§ 648.85(b)(7)(v)(F) or (b)(7)(vi)(D),
whichever is applicable.
(113) 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).
(114) If fishing under a NE
multispecies Category A DAS in the
Interim Differential DAS Area, defined
under § 648.82(e)(4)(i), fail to declare
into the area through VMS as required
under § 648.82(e)(4)(ii).
(115) If fishing under a NE
multispecies Category A DAS in the
Interim Differential DAS Area 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.
(116) Possess or land more white hake
than allowed under § 648.86(m).
(117) Retain or land zero retention
stocks as specified under § 648.86(n).
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(118) 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).
(119) 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.
(120) 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)(ix)(A), or
other approved gear as described under
§ 648.85(b)(10)(iv)(J).
(121) 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).
(122) 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).
*****
(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]
5. In § 648.80, paragraph (i) is
suspended.
6. In § 648.81, paragraph (b)(2)(iv)(B)
is suspended, and paragraphs
(b)(2)(iv)(C) and (n) are added to read as
follows:
§ 648.81 NE multispecies closed areas and
measures to protect EFH.
*
*
*
(b) * * *
(2) * * *
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*
Fmt 4702
*
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(iv) * * *
(C) The vessel has declared into the
Eastern U.S./Canada Area as specified
in § 648.85(a)(3)(viii) and is transiting
CA II in accordance with the provisions
of § 648.85(a)(3)(vii).
*
*
*
*
*
(n) Southern New England (SNE)
Closure Area. (1) No fishing vessel, or
person on such vessel, may enter, fish
in, or be in; and no fishing gear capable
of catching NE multispecies, unless
otherwise allowed in this part, may be
in, or on board a vessel, in the area
known as the SNE Closure Area, as
defined by straight lines connecting the
following points in the order stated,
except as specified in paragraphs (n)(2)
and (3) of this section (a chart depicting
this area is available from the Regional
Administrator upon request).
SNE CLOSURE AREA
Point
SNECA1
SNECA2
SNECA3
SNECA4
SNECA5
N. lat.
W. long.
(1)
41°30’
41°30’
40°30’
40°30’
70°00’
70°00’
68°30’
68°30’
(2)
(1) Intersection of the shoreline of Cape
Cod, Massachusetts and 70°00’ W. long.
(2) Intersection of the shoreline of Staten Island, New York, and 40°30’ N. lat.
(2) Paragraph (n)(1) of this section
does not apply to persons on fishing
vessels or fishing vessels:
(i) Fishing with exempted gear, as
defined in this part, or under the
exemptions specified in
§ 648.80(b)(2)(vi) and (b)(3);
(ii) Fishing with hook gear, provided
that no gear other than hook gear is on
board, and the vessel abides by the NE
multispecies possession restrictions
under § 648.86; or
(iii) Fishing under the charter/party or
private recreational regulations,
provided that vessel abides by the
recreational restrictions under § 648.89,
and:
(A) With the except of tuna, fish
harvested or possessed by the vessel are
not sold or intended for trade, barter or
sale, regardless of where the regulated
species are caught; and
(B) The vessel has no gear other than
rod and reel or handline on board.
(3) NE multispecies permitted vessels
possessing NE multispecies on board
the vessel and transiting through the
SNE Closure Area, provided gear other
than hook gear is stowed in accordance
with § 648.23(b).
7. 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.
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Federal Register / Vol. 74, No. 11 / Friday, January 16, 2009 / Proposed Rules
Category A DAS, or part thereof, shall be
counted at the ratio of 2 to 1 for the
entire trip, even if only a portion of the
trip is spent fishing in the Interim
§ 648.82 Effort-control program for NE
Differential DAS Area. A vessel that has
multispecies limited access vessels.
not declared its intent to fish in the
*
*
*
*
*
Interim Differential DAS Area and that
(e) * * *
is not transiting, as specified in
(4) Differential DAS. For a NE
paragraph (e)(4)(v) of this section, may
multispecies DAS vessel that intends to be in the Interim Differential DAS Area,
fish some or all of its trip, or fishes some provided the vessel’s fishing gear is
or all of its trip other than for transiting
stowed in accordance with the
purposes, under a Category A DAS in
provisions of§ 648.23(b) for the entire
the Interim Differential DAS Area, as
time the vessel is in the area, and the
defined in paragraph (e)(4)(i) of this
vessel declares immediately upon
section, with the exception of Day
entering the Interim Differential DAS
gillnet vessels, which accrue DAS in
Area, via VMS, that it is in the area.
accordance with paragraph (j)(1)(iii) of
(iv) Restrictions. A NE multispecies
this section, each Category A DAS, or
vessel fishing under a Category A DAS
part thereof, shall be counted at the
in the Interim Differential DAS Area
differential DAS rate described in
defined in paragraph (e)(4)(i) of this
paragraph (e)(4)(iii) of this section, and
section, under the restrictions of this
be subject to the restrictions defined in
paragraph (e)(4) and under the
this paragraph (e).
restrictions of one or more of the Special
(i) Interim Differential DAS Area. The Management Programs under§ 648.85,
Interim Differential DAS Area is defined must comply with the most restrictive
as that area bounded on the west by the
DAS counting, trip limits, and reporting
coast of Massachusetts, New Hampshire, requirements, specified in this
and Maine, on the east by the U.S.paragraph (e)(4) and in § 648.85, under
Canada maritime boundary, and by
the pertinent Special Management
straight lines connecting the following
Program.
points in the order stated (a chart
(v) Transiting. A vessel may transit
depicting this area is available from the
the Interim Differential DAS Area, as
Regional Administrator upon request):
defined in paragraph (e)(4)(i) of this
section, provided the gear is stowed in
Point
N. lat.
W. long.
accordance with the provisions of
§ 648.23(b).
ID10
41°30’
66°35’(1)
(5) Regular B DAS Program 24–hr
ID8
41°30’
70°00’
clock. For a vessel electing to fish in the
2)
ID9
(
70°00’
Regular B DAS Program, as specified at
(1) The U.S.-Canada Maritime Boundary.
§ 648.85(b)(10), and that remains fishing
(2) The intersection of the Cape Cod, Mas- under a Regular B DAS for the entire
sachusetts, shoreline and 70°00’ W. long.
fishing trip (without a DAS flip), DAS
(ii) Declaration. A NE multispecies
used shall accrue at the rate of 1 full
DAS vessel that intends to fish, or fishes DAS for each calendar day, or part of a
under a Category A DAS in the Interim
calendar day fished. For example, a
Differential DAS Area, as described in
vessel that fished on one calendar day
paragraph (e)(4)(i) of this section, must,
from 6 a.m. to 10 p.m. would be charged
prior to leaving the dock, declare
24 hr of Regular B DAS, not 16 hr; a
through the VMS, in accordance with
vessel that left on a trip at 11 p.m on
instructions to be provided by the
the first calendar day and returned at 10
Regional Administrator, that the vessel
p.m. on the second calendar day would
will fish in the Interim Differential DAS be charged 48 hr of Regular B DAS
Area. A DAS vessel that fishes in the
instead of 23 hr, because the fishing trip
Eastern U.S./Canada Area and intends
would have spanned 2 calendar days.
to fish, or fishes, subsequently in the
For the purpose of calculating trip limits
specified under § 648.86, the amount of
Interim Differential DAS Area under a
DAS deducted from a vessel’s DAS
Category A DAS, must declare its
intention to do so through its VMS prior allocation shall determine the amount of
to leaving the dock at the start of the trip fish the vessel can legally land. For a
vessel electing to fish in the Regular B
or prior to leaving the Eastern U.S./
DAS Program, as specified at
Canada Area, as specified
§ 648.85(b)(10), while also fishing in the
in§ 648.85(a)(3)(viii)(A)(3).
(iii) Differential DAS counting. For a
Interim Differential DAS Area, defined
NE multispecies DAS vessel that
in paragraph (e)(4)(i) of this section,
intends to fish, or fishes for some or all
Category B DAS shall accrue at the rate
of its trip other than for transiting
described in this paragraph (e)(5),
purposes under a Category A DAS in the unless the vessel flips to a Category A
Interim Differential DAS Area, each
DAS, in which case the vessel is subject
hsrobinson on PROD1PC76 with PROPOSALS
B. Paragraphs (e)(4) and (5), and
(j)(1)(iii)(E), (F), and (G) are added.
The additions read as follows:
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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 the
Interim Differential DAS Area 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 vessel fishing in the Interim
Differential DAS Area for 8 actual hr
would be charged 16 hours of DAS, or
if fishing for 5 actual hr, would be
charged 15 hours of DAS.
*
*
*
*
*
8. In § 648.83, paragraph (a)(1) is
suspended and paragraph (a)(3) is
revised to read as follows:
§ 648.83
Multispecies minimum fish sizes.
(a) * * *
(3) Minimum fish sizes for
recreational vessels and charter/party
vessels that are not fishing under a NE
multispecis 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):
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Federal Register / Vol. 74, No. 11 / Friday, January 16, 2009 / Proposed Rules
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
18
19
14
(55.9
(45.7
(48.3
(35.6
cm)
cm)
cm)
cm)
13
14
36
12
(33.0
(35.6
(91.4
(30.5
cm)
cm)
cm)
cm)
9 (22.9 cm)
*
*
*
*
*
9. 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), and (6);
(b)(7)(iv)(A); (b)(7)(v)(D); (b)(7)(vi)(E);
(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)(7)(iv)(J);
(b)(7)(v)(F); and (b)(7)(vi)(G);
(b)(8)(v)(E)(3); (b)(8)(v)(M); and (b)(9)
and (10) are added.
The additions read as follows:
§ 648.85
Special management programs.
hsrobinson on PROD1PC76 with PROPOSALS
*
*
*
*
*
(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
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
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17:46 Jan 15, 2009
Jkt 217001
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 the Interim Differential DAS Area
defined under § 648.82(e)(4)(i), it must
declare its intent to fish in the Interim
Differential DAS Area 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/
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
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2977
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 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, 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 6.0inch (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,
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Federal Register / Vol. 74, No. 11 / Friday, January 16, 2009 / Proposed Rules
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
inserted no farther than 4.5 meshes
behind the headrope.
(b) * * *
(7) * * *
(iv) * * *
(J) 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
Program described under paragraph
(b)(10) of this section. DAS will be
charged as described in § 648.10.
(v) * * *
(F) Reporting requirements. The
owner or operator of a Sector vessel
declared into the CA I Hook Gear
Haddock SAP must submit reports to
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Jkt 217001
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 cod,
haddock, yellowtail flounder, winter
flounder, witch flounder, pollock,
windowpane flounder, 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 exit the SAP as
required under paragraph (b)(7)(iv)(F) of
this section.
(vi) * * *
(G) GB cod incidental catch TAC. The
maximum amount of GB cod (landings
and discards) that may be cumulatively
caught by non-Sector vessels from the
CA I Hook Gear Haddock Access Area
in a fishing year is the amount specified
under paragraph (b)(9)(ii) of this section.
(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.
(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 sent 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
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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
(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
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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
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 multipecies 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
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17:46 Jan 15, 2009
Jkt 217001
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)
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 (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 above) 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.
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2979
(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
the start of the trip. If a vessel is fishing
in the Interim Differential DAS area, 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 2. For example, if a vessel plans a
trip under the Regular B DAS Program
into the Interim 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)(4).
(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 has 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 (MayJuly), or when 1,000 Regular B DAS
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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
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
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17:46 Jan 15, 2009
Jkt 217001
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
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 Administrator, Northeast Region):
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
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Sfmt 4702
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
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
+ 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 12to16–inch (30- to 40–cm) rockhopper
discs over any 10–ft (3.0–m) length of
the sweep. The 12- to16- inch (30- to
40–cm) 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
40–cm) discs must be separated by
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smaller discs, no larger than 3.5 inches
(8.8 cm) in diameter.
(vii) Definition of incidental TAC
stock areas. For the purposes of the
Regular B DAS Program, including the
stocks that may not be retained by
vessels as specified under § 648.86, the
species stock areas are defined below.
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.
W. long.
(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.
(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
GB1
GB2
GB3
GB4
GB5
GB6
GB7
GB8
GB9
GB10
GB11
GB12
N. lat.
W. long.
(1)
42°20’
42°20’
42°10’
42°10’
42°00’
42°00’
40°30’
39°00’
39°00’
35°00’
35°00’
70°00’
70°00’
66°00’
66°00’
65°50’
65°50’
65°40’
65°40’
65°40’
70°00’
70°00’
(2)
hsrobinson on PROD1PC76 with PROPOSALS
(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:
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17:46 Jan 15, 2009
Jkt 217001
CC/GOM YELLOWTAIL FLOUNDER
STOCK AREA
Point
CCGOM1
CCGOM2
CCGOM3
CCGOM4
CCGOM5
CCGOM6
CCGOM7
CCGOM8
CCGOM9
CCGOM10
CCGOM11
CCGOM12
CCGOM13
1 Intersection
N. lat.
(1)
70°00’
66°00’
66°00’
65°50’
65°50’
65°40’
65°40’
65°40’
SOUTHERN NEW ENGLAND/MID-ATLANTIC WINTER FLOUNDER STOCK AREA
Point
W. long.
43°00’
42°20’
42°20’
42°10’
42°10’
42°00’
42°00’
40°30’
39°00’
(2)
35°00’)
35°00’)
(3)
with
the
(3)
(4)
New
Hampshire
coastline.
2 Intersection of the south-facing shoreline of
Cape Cod, Massachusetts.
3 Intersection with the east-facing shoreline
of Cape Cod, Massachusetts.
4 Intersection with the west-facing shoreline
of Massachusetts
(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:
SNE/MA YELLOWTAIL FLOUNDER
STOCK AREA
Point
N. lat.
W. long.
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’
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’
2981
SNEW1
SNEW2
SNEW3
SNEW4
SNEW5
SNEW6
SNEW7
SNEW8
SNEW9
N. lat.
W. long.
(1)
42°20’
42°20’
39°50’
39°50’
39°00’
39°00’
35°00’
35°00’
70°00’
70°00’
68°50’
68°50’
71°40’
71°40’
70°40’
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.
(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:
WINDOWPANE FLOUNDER NORTHERN
STOCK AREA:
Point
G12
WIN1
WIN2
WIN3
WIN4
WIN5
WIN6
WIN7
WIN8
WIN9
WIN10
N. lat.
W. long.
(1)
41°20’
41°20’
41°10’
41°10’
41°00’
41°00’
39°50’
39°50’
39°00’
39°00’
70°00’
70°00’
69°50’
69°50’
69°50’
69°30’
68°50’
68°50’
69°00’
69°00’
(2)
(1) South-facing coastline of Cape Cod, MA.
(2) Intersection of 39° 00’ N. Lat. and the
boundary of the EEZ.
(viii) 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 648.85, and any other
relevant information, may, in a manner
consistent with the Administrative
Procedure Act, may prohibit the use of
Regular B DAS, modify possession
restrictions, or implement other
(1) South-facing shoreline of Connecticut.
measures, including a partial closure for
(2) North-facing shoreline of Long Island, the Regular B DAS Program, for the
New York.
duration of a quarter or fishing year, if
(3) South-facing shoreline of Long Island,
it is projected that continuation of the
New York.
Regular B DAS Program would
undermine the achievement of the
(E) SNE/MA winter flounder stock
objectives of the FMP or Regular B DAS
area. The SNE winter flounder stock
Program. Reasons for modification or
area, for the purposes of the Regular B
termination of the program include, but
DAS Program and the prohibition on
are not limited to, the following:
retention of winter flounder specified
Inability to constrain catches to the
under § 648.86, is the area defined by
Incidental Catch TACs; evidence of
straight lines connecting the following
excessive discarding; a significant
points in the order stated:
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difference in flipping rates between
observed and unobserved trips; or
insufficient observer coverage to
adequately monitor the program.
*
*
*
*
*
10. In § 648.86, paragraphs (b), (e),
and (j) are suspended, and paragraphs
(l), (m), and (n) are added to read as
follows:
§ 648.86 NE multispecies possession
restrictions.
hsrobinson on PROD1PC76 with PROPOSALS
*
*
*
*
*
(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
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 the
Interim Differential DAS Area under the
restrictions of § 648.82(e)(4)(i), 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,
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17:46 Jan 15, 2009
Jkt 217001
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
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
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Sfmt 4702
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 the
Interim Differential DAS Area under the
restrictions of § 648.82(e)(4)(i), 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
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
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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)(ii), a NE multispecies
DAS vessel that fishes or intends to fish
south of the line described in this
paragraph (l)(4), 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)
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) White hake. 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
2,000 lb (907.2 kg) of white hake per
DAS, or any part of a DAS, up to 10,000
lb (4,536 kg) per trip.
(n) Zero retention stocks—(1) SNE
winter flounder. Private recreational
vessels fishing in the EEZ, and vessels
issued a NE multispecies permit, may
not fish for, possess, or land winter
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18:32 Jan 15, 2009
Jkt 217001
flounder caught in the SNE/MA winter
flounder stock area, 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 would be subject to the most
restrictive 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, 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) or § 648.89(f), as appropriate.
Vessels fishing for windowpane
flounder in multiple stock areas would
be subject to the most restrictive
possession limit.
(3) Ocean pout. Vessels issued a NE
multispecies permit may not fish for,
possess or land ocean pout.
11. 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
Winter flounder
(blackback)
Redfish
22in
18in
19in
14in
(58.4
(45.7
(48.3
(35.6
cm)
cm)
cm)
cm)
13in
36in
14in
12in
(33.0
(91.4
(35.6
(30.5
cm)
cm)
cm)
cm)
9in (22.9 cm)
(c) * * *
(1) * * *
(vi) Seasonal GOM cod possession
prohibition. Persons aboard private
recreational fishing vessels fishing in
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Fmt 4702
Sfmt 4702
2983
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 fishing
rods and any cod on board has been
gutted and stored.
*
*
*
*
*
(5) Charter/party vessels. Charter/
party vessels fishing any part of a trip
in the GOM Regulated Mesh Area, as
defined in § 648.80(a)(1), 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,
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 or
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 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, posses, or land winter flounder.
Recreational vessels in possession of
winter flounder caught outside of the
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SNE/MA winter flounder may transit
this area, provided all bait and hooks
are removed from fishing rods and any
winter flounder on board has been
stored.
[FR Doc. E9–846 Filed 1–15–09; 8:45 am]
BILLING CODE 3510–22–S
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 679
[Docket No. 080612764–8801–01]
RIN 0648–AW94
Fisheries of the Exclusive Economic
Zone Off Alaska; Groundfish Fisheries
of the Bering Sea and Aleutian Islands
Management Area and Gulf of Alaska,
Seabird Avoidance Requirements
Revisions for International Pacific
Halibut Commission Regulatory Area
4E
hsrobinson on PROD1PC76 with PROPOSALS
AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Proposed rule; request for
comments.
SUMMARY: NMFS issues a proposed rule
that would revise the seabird avoidance
requirements for the hook–and–line
groundfish and halibut fisheries in
International Pacific Halibut
Commission Area 4E. The proposed rule
would eliminate seabird avoidance
requirements for hook–and–line vessels
less than or equal to 55 ft (16.8 m)
length overall in portions of Area 4E in
the eastern Bering Sea. This action is
necessary to revise seabird avoidance
measures based on the latest scientific
information and to reduce unnecessary
regulatory burdens and associated costs.
DATES: Written comments must be
received by February 17, 2009.
ADDRESSES: Send comments to Sue
Salveson, Assistant Regional
Administrator, Sustainable Fisheries
Division, Alaska Region, NMFS, Attn:
Ellen Sebastian. You may submit
comments, identified by 0648–AW94,
by any one of the following methods:
• Electronic Submissions: Submit all
electronic public comments via the
Federal eRulemaking Portal website at
https://www.regulations.gov.
• Mail: P. O. Box 21668, Juneau, AK
99802.
• Fax: (907) 586–7557.
• Hand delivery to the Federal
Building: 709 West 9th Street, Room
420A, Juneau, AK.
VerDate Nov<24>2008
17:46 Jan 15, 2009
Jkt 217001
All comments received are a part of
the public record and will generally be
posted to https://www.regulations.gov
without change. All Personal Identifying
Information (e.g., name, address)
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
portable document file (pdf) formats
only.
Copies of the map of the seabird
avoidance measures in Area 4E, and the
Environmental Assessment/Regulatory
Impact Review/Initial Regulatory
Flexibility Analysis (EA/RIR/IRFA) for
this action may be obtained from the
Alaska Region NMFS address above or
from the Alaska Region NMFS website
at https://www.alaskafisheries.noaa.gov.
FOR FURTHER INFORMATION CONTACT:
Melanie Brown, 907–586–7228.
SUPPLEMENTARY INFORMATION: The
groundfish fisheries in the exclusive
economic zone (EEZ) off Alaska are
managed under the Fishery
Management Plan for Groundfish of the
Bering Sea and Aleutian Islands
Management Area and the Fishery
Management Plan for Groundfish of the
Gulf of Alaska (FMPs). The North
Pacific Fishery Management Council
(Council) prepared the FMPs under the
authority of the Magnuson–Stevens
Fishery Conservation and Management
Act (Magnuson–Stevens Act), 16 U.S.C.
1801, et seq. Regulations implementing
the FMPs appear at 50 CFR part 679.
General regulations governing U.S.
fisheries also appear at 50 CFR part 600.
Management of the Pacific halibut
fisheries in and off Alaska is governed
by an international agreement between
Canada and the United States. This
agreement, entitled the ‘‘Convention
Between the United States of America
and Canada for the Preservation of the
Halibut Fishery of the Northern Pacific
Ocean and Bering Sea’’ (Convention),
was signed at Ottawa, Canada, on March
2, 1953, and was amended by the
‘‘Protocol Amending the Convention,’’
signed at Washington, D.C., March 29,
1979. The Convention is implemented
in the United States by the Northern
Pacific Halibut Act of 1982 (Halibut
Act). The directed commercial Pacific
halibut fishery in Alaska is managed
under an individual fishing quota (IFQ)
program, as is the fixed gear sablefish
fishery. The IFQ Program is a limited
PO 00000
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Fmt 4702
Sfmt 4702
access management system. This
program is codified at 50 CFR part 679.
Background
The purpose of this proposed action
is to revise the seabird avoidance
measures currently implemented for the
hook–and–line groundfish and halibut
fisheries based on the best available
information regarding seabird
occurrence and potential fishing vessel
interactions. Seabird avoidance
measures reduce the incidental
mortality of seabirds in the hook–and–
line fisheries off Alaska. Since 1997,
NMFS has implemented and revised
seabird avoidance measures to mitigate
interactions between the federal hook–
and–line fisheries and seabirds (62 FR
23176, April 29, 1997; 63 FR 11161,
March 6, 1998; 69 FR 1930, January 13,
2004; and 72 FR 71601, December 18,
2007).
NMFS compiled seabird sightings
data from the following sources: from
1988–2004 records from seabird
observers on the U.S. Fish and Wildlife
Service’s (FWS) research vessel M/V
TIGLAX; from incidental sightings by
biologists, fishermen, seamen, fisheries
observers, and birdwatchers provided to
the FWS; from the International Pacific
Halibut Commission (IPHC); from the
Alaska Natural Heritage Program; from
historical sightings documented in
published literature; from satellite
tagging data; and from the North Pacific
Pelagic Seabird Database. The EA/RIR/
IRFA for this action describes this
information (see ADDRESSES). This
information showed that seabird species
of concern are not likely to occur in
portions of Area 4E where fishing
vessels using hook–and–line gear may
operate; and therefore, it is not likely
that interactions between the fishing
vessels and these seabird species of
concern would occur in those portions
of Area 4E. Thus, the Council
recommended revisions to the seabird
avoidance measures in a portion of Area
4E. These revisions would eliminate
seabird avoidance measures in the
portion of Area 4E where seabird
species of concern are not likely to
occur. The revisions would apply to
vessels greater than 26 ft (7.9 m) to less
than or equal to 55 ft (16.8 m) length
overall (LOA) fishing in the EEZ.
Vessels less than or equal to 26 ft (7.9
m) LOA are not required to use seabird
avoidance measures. Vessels greater
than 55 ft (16.8 m) LOA would continue
to be required to use seabird avoidance
measures in all of Area 4E. Vessels this
size and larger are more likely to
interact with other seabirds because of
the greater amount of offal discharge
and greater number of hooks fished
E:\FR\FM\16JAP1.SGM
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Agencies
[Federal Register Volume 74, Number 11 (Friday, January 16, 2009)]
[Proposed Rules]
[Pages 2959-2984]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-846]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 648
[Docket No. 080521698-8699-01]
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: Proposed rule; request for comment.
-----------------------------------------------------------------------
SUMMARY: NMFS proposes a temporary Secretarial interim action under the
Magnuson-Stevens Fishery Conservation and Management Act (Magnuson-
Stevens Act) to implement measures intended to immediately reduce
overfishing in the Northeast (NE) multispecies fishery, while
addressing the need to help sustain fishing communities, without
compromising rebuilding objectives. Measures proposed for the
commercial fishery include the following: A differential days-at-sea
(DAS) area north of 41[deg]30' N. lat., whereby a vessel would be
charged 2 days for every day fished; a large Southern New England (SNE)
Closure Area; and modified groundfish trip limits. This action does not
change the scheduled DAS reduction in the NE Multispecies Fishery
Management Plan (FMP), which would result in an approximate 18-percent
reduction in DAS. For private recreational vessels fishing in the
Exclusive Economic Zone (EEZ) and for federally permitted charter/party
vessels, this action would extend in time a seasonal prohibition on the
possession of Gulf of Maine (GOM) cod, and prohibit the possession of
SNE winter flounder. For federally permitted charter/party vessels,
this action would implement a trip limit for Georges Bank (GB) cod. In
addition, this action proposes to mitigate some of the negative short-
term economic impacts of the FMP by making modifications to the DAS
Leasing Program, the Regular B DAS Program, and the DAS Transfer
Program; continuing the Eastern U.S./Canada Haddock Special Access
Program (SAP); and implementing a reduction in the haddock minimum size
to 18 inches (45 cm). Finally, this action would specify management
measures for the U.S./Canada Management Area for fishing year (FY)
2009.
[[Page 2960]]
DATES: Comments must be received by February 17, 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 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 an Initial Regulatory Flexibility Analysis (IRFA),
which is contained in the Classification section of this proposed rule.
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.
FOR FURTHER INFORMATION CONTACT: Thomas Warren, Fishery Policy Analyst,
(978) 281-9347, fax (978) 281-9135.
SUPPLEMENTARY INFORMATION: The FMP specifies the management measures
for 12 species in Federal waters off the New England and Mid-Atlantic
coasts, which are Atlantic cod, haddock, yellowtail flounder, pollock,
American plaice, witch flounder, white hake, windowpane flounder,
Atlantic halibut, winter flounder, ocean pout, and redfish, comprising
a total of 19 individual stocks (groundfish). A major overhaul of the
FMP occurred in 2004 with implementation of Amendment 13 and the
establishment of rebuilding programs for all stocks managed by the FMP,
including specification of status determination criteria for each
stock.
Amendment 13 established two different strategies for rebuilding
(an adaptive and a phased rebuilding strategy), and a rebuilding plan
for each overfished stock was developed in accordance with one of the
two strategies. Under the ``adaptive'' rebuilding strategy, fishing
mortality is held at Fmsy from 2004 through 2008, and then subsequently
reduced to the level required to rebuild by the selected end-date of
the rebuilding period. In 2008, the effectiveness of the management
measures and the validity of the status determination criteria
(biological reference points) were fully evaluated. Eight stocks (GOM
cod, GB haddock, GOM haddock, SNE/Mid Atlantic (MA) winter flounder, GB
yellowtail flounder, redfish, windowpane flounder (southern stock), and
ocean pout) are managed under the adaptive rebuilding strategy. In
contrast, under the ``phased'' rebuilding strategy, fishing mortality
is allowed to remain above Fmsy at the start of the rebuilding period
in 2004, and then reduced sequentially in 2006 and 2009. Five stocks
(GB cod, Cape Cod (CC)/GOM yellowtail flounder, SNE/MA yellowtail
flounder, American plaice, and white hake) are managed under the phased
rebuilding strategy. The end of the rebuilding period for all stocks is
2014, with the exception of GB cod (2026), CC/GOM yellowtail flounder
(2023), and redfish (2051).
Amendment 13 also implemented a process whereby the NE multispecies
complex is routinely evaluated through a biennial adjustment. This
adjustment process provides an update of the scientific information
regarding the status of the stocks, and an evaluation of the
effectiveness of the regulations. The biennial adjustment provides the
New England Fishery Management Council (Council) with information to
make adjustments to management measures necessary to modify fishing
mortality to comply with the rebuilding schedules and approach optimum
yield. The FMP further specified a benchmark stock assessment and
review of the biological reference points (stock status determination
criteria) in 2008. This planned assessment of the biological reference
points (Groundfish Assessment Review Meeting, (GARM III) in 2008) was
part of the biennial adjustment process, but was also part of the
adaptive rebuilding strategy described above, which sought to evaluate
the more fundamental scientific information mid-way through the
rebuilding period for most stocks. Although, strictly speaking, the
adaptive rebuilding strategy applies to only five stocks, the intent of
the Council in scheduling a benchmark assessment in 2008 was an
evaluation of the biological reference points for all stocks.
In order to implement these rebuilding strategies, Amendment 13
included default management measures for implementation in FY 2006 and
FY 2009, which were designed to reduce fishing mortality on certain
stocks, and established criteria to determine conditions under which
the default measures would not be triggered. The default measure
developed for FY 2009 is a modification to the Category A DAS and
Category B DAS ratio from 55:45 to 45:55 (respectively). This decrease
in the amount of A DAS represents an 18.2-percent decrease in the
number of A DAS a vessel may fish. Amendment 13 noted the challenge of
implementing the rebuilding program due to the difficulty of designing
effort controls that would precisely achieve the desired fishing
mortality reductions for all stocks.
The Council began development of Amendment 16 in 2006 to meet a
required May 1, 2009, implementation date because it anticipated that
new scientific information from the scheduled 2008 biennial review and
benchmark assessment (GARM III) would indicate that additional fishing
mortality reductions may be necessary for FY 2009 in order to continue
rebuilding at the required rate. At the Council meeting on June 3,
2008, the Northeast Fisheries Science Center (NEFSC) presented
preliminary estimates of stock size and fishing mortality in 2006,
which indicated that draft effort control measures under development
for Amendment 16 were not targeting the correct stocks. Based on this
information, the Council decided to wait until receipt of the final
GARM III assessment results in September 2008 to design appropriate
management measures and hold public hearings.
The Council subsequently developed a revised schedule of
development for Amendment 16, which, if approved, would be implemented
on May 1, 2010. The Council voted on September 4, 2008, to request that
NMFS implement an interim action for the duration of FY 2009 (May 1,
2009-April 30, 2010), and recommended a specific suite of management
measures for the interim action. As explained fully under section 12
below, NMFS did not adopt the Council's recommendations for this
proposed interim action because it was determined that the Council's
recommended alternative was insufficient to end overfishing.
GARM III, completed in August 2008, was an extensive benchmark
assessment. GARM III evaluated the
[[Page 2961]]
underlying data and models utilized for assessment of the groundfish
stocks, evaluated the biological reference points, established new
reference points, assessed the biomass and fishing mortality status of
the groundfish stocks in 2007, and provided examples of fishing
mortality rates that would be expected to rebuild overfished stocks.
Incorporation of new scientific information and revisions to
management measures in the FMP, effective May 1, 2009, are necessary to
continue rebuilding to comply the intent of the FMP. However, due to
the Council's revised Amendment 16 schedule, such revisions to the FMP
would not be implemented, without this interim action.
Section 305(c) of the Magnuson-Stevens Act authorizes the Secretary
of Commerce (Secretary) to amend an FMP if the appropriate Council
fails to develop and submit to the Secretary any necessary amendment to
an FMP if the fishery requires conservation and management. NMFS
promulgated guidelines to further clarify how this authority to amend
an FMP should be interpreted (63 FR 24212; May 1, 1998). The Secretary,
on his/her own initiative, or in response to a Council request, may
implement interim measures to reduce overfishing under section 305(c),
until such measures can be replaced by an FMP amendment or regulations
taking remedial action. The measures may remain in place for 180 days,
but may be extended for an additional 186 days if the public has had an
opportunity to comment on the measures.
Because of the need to eliminate and reduce overfishing, as well as
to reduce fishing mortality to more closely comply with the FMP
rebuilding schedules, NMFS is proposing this interim action. To that
end, this action would implement management measures that, as much as
practicable, build upon the Amendment 13 default measures and include
major elements of the Council's Amendment 16 alternatives, such as
differential DAS. Measures that are similar to Amendment 16 would
facilitate industry understanding, enable NMFS to administer such
short-term measures, and allow vessels to adapt any measures
implemented by Amendment 16 if they are adopted. Further, it is
important that NMFS can enforce and administer the interim measures,
and that such measures are fair and simple. The proposed interim action
management measures are more narrowly focused than what is currently
under consideration in the Council's Amendment 16 draft document, which
contains measures beyond those designed to reduce fishing mortality,
such as inclusion of many new sectors and measures to address new
Magnuson-Stevens Act requirements (e.g., annual catch limits and
accountability measures). Failure to reduce or prevent overfishing by
May 1, 2009, while the Council completes Amendment 16, would likely
lead to continued overfishing of several groundfish stocks, resulting
in slower rebuilding that would likely require more stringent future
measures, with additional economic and social consequences.
A summary of the GARM III results that form the basis for this
proposed interim rule is in Table 1 below. Overfishing is occurring on
stocks when the fishing mortality to Fmsy ratio (F/Fmsy) is greater
than 1.0, and a stock is overfished if the biomass level to Bmsy ratio
(B/Bmsy) is equal to or less than 0.5.
Table 1. GARM III Stock Status Determination Criteria and 2007 Status
--------------------------------------------------------------------------------------------------------------------------------------------------------
2007 Fishing Mortality 2007 Biomass (2007 B/
Species Stock Fmsy Bmsy (2007 F/ Fmsy) Bmsy)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Cod GB 0.2466 148,084 1.2 0.12
----------------------------------------------------------------------------------------------------------------------
GOM 0.237 58,248 1.9 0.58
--------------------------------------------------------------------------------------------------------------------------------------------------------
Haddock GB 0.350 158,873 0.49 2.05
----------------------------------------------------------------------------------------------------------------------
GOM 0.430 5,900 0.8. 0.99
--------------------------------------------------------------------------------------------------------------------------------------------------------
Yellowtail flounder GB 0.254 43,200 1.1 0.22
----------------------------------------------------------------------------------------------------------------------
SNE/MA 0.254 27,400 1.6 0.13
----------------------------------------------------------------------------------------------------------------------
CC/GOM 0.239 7,790 1.7 0.25
--------------------------------------------------------------------------------------------------------------------------------------------------------
American plaice .................... 0.190 21,940 0.5 0.51
--------------------------------------------------------------------------------------------------------------------------------------------------------
Witch flounder .................... 0.200 11,447 1.5 0.30
--------------------------------------------------------------------------------------------------------------------------------------------------------
Winter flounder GB 0.260 16,000 1.1 0.31
----------------------------------------------------------------------------------------------------------------------
GOM 0.283 3,792 1.5 0.29
----------------------------------------------------------------------------------------------------------------------
SNE/MA 0.248 38,761 2.6 0.09
--------------------------------------------------------------------------------------------------------------------------------------------------------
Redfish .................... 0.038 271,000 0.1 0.64
--------------------------------------------------------------------------------------------------------------------------------------------------------
White hake .................... 0.125 56,254 1.2 0.35
--------------------------------------------------------------------------------------------------------------------------------------------------------
Pollock .................... 5.660 2.0 * 1.2 * 0.71
--------------------------------------------------------------------------------------------------------------------------------------------------------
Windowpane North 0.500 1.4 * 3.9 * 0.38
----------------------------------------------------------------------------------------------------------------------
South 1.470 0.34 * 1.3 * 0.62
--------------------------------------------------------------------------------------------------------------------------------------------------------
Ocean pout .................... 0.760 4.94 0.5 0.10
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 2962]]
Atlantic halibut .................... 0.073 49,000 0.9 0.03
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Pollock and windowpane flounder information was revised subsequent to GARM III in order to utilize 3 yr averages. Pollock is approaching an overfished
condition.
Because GARM III revised the biological reference points and the
2007 stock status determination, and the current status of stocks is
different from the understanding of stock status based on GARM I and
II, it is necessary to utilize new fishing mortality targets that are
appropriate to the revised stock status. Therefore, this interim action
would utilize the GARM III revised stock status determination as the
basis for developing fishing mortality targets in order to be
consistent with National Standard 2, which requires that conservation
and management measures shall be based upon the best scientific
information available.
New rebuilding plans for those stocks recently determined to be
overfished or approaching an overfished condition, based on results
from GARM III (windowpane flounder (northern stock), GOM and GB winter
flounder, witch flounder, and pollock), are not proposed in this
interim action, but rather are being considered by the Council in
Amendment 16. For these five stocks, the fishing mortality target of
the interim action is proposed to be Fmsy, although, as explained later
in this preamble, the proposed measures would not achieve this
objective for windowpane north.
For those stocks that are either rebuilt (GB haddock) or for stocks
where Fmsy would rebuild the stock (GOM haddock, GOM cod, American
plaice, redfish), the fishing mortality target for the interim action
would be Fmsy. For these stocks, which are currently in rebuilding
programs, Fmsy is the appropriate target fishing mortality rate because
Fmsy is lower than Frebuild, and the stocks are projected to rebuild to
Bmsy within their rebuilding periods.
For stocks currently under rebuilding programs and for which the
fishing mortality rate required to rebuild the stock (Frebuild) is less
than Fmsy (GB cod, GB yellowtail, SNE yellowtail, CC yellowtail, SNE
winter flounder, white hake), the fishing mortality target under this
interim action would be Frebuild, with one exception (noted below).
For GB cod, fishing mortality under this interim action would be
reduced to a level less than Fmsy, but would not achieve Frebuild. The
two recent stock assessments that pertain to GB cod (GARM III for the
entire stock; Transboundary Resource Assessment Committee 2008 for the
eastern portion of the stock) were unable to be reconciled with each
other, with the assessment of the size of the overall stock relatively
low and the assessment of the size of the eastern portion of the stock
relatively high. Given the scientific uncertainty, the fact that the
fishing mortality of the eastern portion of the stock is strictly
controlled through a hard total allowable catch (TAC), and the limited
scope of this action, Fmsy is being proposed as the fishing mortality
rate target for this stock. However, the fishing mortality rate that
would be achieved by the proposed interim action is estimated to be
between Fsmy and Frebuild.
GARM III provided example estimates of Frebuild for overfished
stocks, making assumptions about the rebuild period end-dates and the
starting conditions at the beginning of the rebuilding periods. In
doing so, GARM III assumed that the catch in FY 2008 will equal the
catch in FY 2007. In contrast, for this interim action, an estimated
catch in FY 2008 was used to recalculate the starting conditions in FY
2008, and the Frebuilds. For Amendment 16, the Plan Development Team
(PDT) estimated catch for the entire FY 2008 year based upon an
extrapolation of landings data for calendar year 2008 through June
2008. This interim action relies on the PDT's estimated landings for FY
2008 and a derived estimate of fishing mortality for Calendar Year (CY)
2008 and the recalculated Frebuilds. The probabilities associated with
the Frebuilds and rebuilding end dates are consistent with the current
FMP. Stocks would rebuild with a 50-percent probability, with the
exception of GB yellowtail flounder, which has a 75-percent probability
of rebuilding by the end of the rebuilding period. The end of the
rebuilding period for all stocks with rebuilding plans is 2014, with
the exception of GB cod (2026), CC/GOM yellowtail flounder (2023), and
redfish (2051). Because the measures to be implemented by this action
would begin 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.
In a similar manner, in order to calculate the amount of reduction
in fishing mortality required for pertinent stocks, the estimated
fishing mortality in CY 2008 was considered as the starting condition.
For example, in order to calculate the required fishing mortality
reduction for the CC/GOM stock of yellowtail flounder, Frebuild (0.238)
was compared to F 2008 (0.289). An 18-percent reduction in fishing
mortality is required to reduce F from 0.289 in CY 2008 to achieve an
Frebuild of 0.238 in CY 2009. Table 2 below summarizes information on
the CY 2008 fishing mortality, the fishing mortality goal of the
interim action, and the percentage fishing reduction objective to
reduce fishing mortality from the starting conditions (F 2008) to the
fishing mortality rate goal.
Table 2. Fishing Mortality Reduction Objectives for the Proposed Interim Action
--------------------------------------------------------------------------------------------------------------------------------------------------------
Value Associated with
Species Stock 2008 F Fishing Mortality Rate Fishing Mortality Rate Fishing Mortality Rate
Goal Goal Reduction Objective
--------------------------------------------------------------------------------------------------------------------------------------------------------
Cod GB 0.410 Fmsy 0.2466 - 40 %
-----------------------------------------------------------------------------------------------------------------------
GOM 0.300 Fmsy 0.237 - 21 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 2963]]
Haddock GB 0.083 Fmsy 0.350 322 %
-----------------------------------------------------------------------------------------------------------------------
GOM 0.250 Fmsy 0.430 72 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
Yellowtail flounder GB 0.130 Frebuild 0.109 - 16 %
-----------------------------------------------------------------------------------------------------------------------
SNE/MA 0.120 Frebuild 0.075 -386%
-----------------------------------------------------------------------------------------------------------------------
CC/GOM 0.289 Frebuild 0.238 - 18 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
American plaice ................... 0.099 Fmsy 0.190 92 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
Witch flounder ................... 0.296 Fmsy 0.200 - 32 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
Winter flounder GB 0.131 Fmsy 0.260 98 %
-----------------------------------------------------------------------------------------------------------------------
GOM 0.317 Fmsy 0.283 - 11 %
-----------------------------------------------------------------------------------------------------------------------
SNE/MA 0.265 Frebuild 0.000 - 100 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
Redfish ................... 0.008 Fmsy 0.038 375 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
White hake ................... 0.065 Frebuild 0.084 29 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
Pollock ................... NA Fmsy 5.66 - 48 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
Windowpane ................... NA Fmsy 0.50 - 74 %
-----------------------------------------------------------------------------------------------------------------------
................... NA Fmsy 1.47 - 21 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
Ocean pout ................... NA Fmsy 0.760 NA
--------------------------------------------------------------------------------------------------------------------------------------------------------
Atlantic halibut ................... 0.060 Frebuild 0.044 - 27 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
NA - not available
Proposed Management Measures
All measures in effect prior to May 1, 2009, including the default
measures relating to DAS reductions scheduled to go into place and not
amended by this proposed interim rule, would remain in effect on and
after May 1, 2009. This proposed interim action would implement
management measures to reduce fishing mortality on the commercial and
recreational fisheries, without compromising rebuilding objectives, as
well as revise various management programs in order to mitigate the
negative economic and social impacts of the FMP to ensure consistency
with National Standards and required provisions of the Magnuson-Stevens
Act and to enhance the likelihood of compliance with the measures.
Routine specification of TAC and annual specifications for the U.S./
Canada Management Area are also proposed. As is more fully discussed
later in this document, these measures would result in both
quantifiable and non-quantifiable reductions in fishing mortality for
virtually all of the NE multispecies stocks managed under the FMP.
The proposed interim measures are designed to work in conjunction
with the current FMP to achieve the fishing mortality requirements of
the FMP. The analysis of this action presumes that the proposed
measures would be in effect throughout FY 2009, and that a subsequent
management action (Amendment 16) will be implemented on May 1, 2010.
The current FMP management measures include a FY 2009 default measure
that will change the allocation ratio of Category A:B DAS from 60:40 to
55:45. This measure, therefore, is not discussed specifically in the
description of the proposed interim measures that follows. NMFS
anticipates that, if approved and implemented, this interim action may
be renewed upon expiration for an additional 185 days, given that the
Council does not anticipate the implementation of Amendment 16 until
May 2010. The Council also recommended to NMFS that any interim action
should be in effect for all of FY 2009. The following measures are
proposed to be implemented on May 1, 2009, to reduce overfishing.
Commercial Measures
1. Differential DAS Counting
Under this proposed interim action, the existing differential DAS
areas in the GOM and SNE would no longer apply, and a single, larger
differential DAS area would be implemented in the entire GOM and in the
northern portion of GB, north of 41o 30'N. lat. For the revised Interim
Differential DAS Area, the DAS accrual rate would be 2:1. In other
words, under this action, if a vessel declares into the Interim
Differential DAS Area for 10 hr, the vessel's DAS balance would be
debited 20 hr. A vessel would not be charged at the differential DAS
rate if it declared and transited to another area outside of the
Interim Differential DAS Area. For example, if a vessel steams through
the Interim Differential DAS Area on its way to and from the fishing
grounds in the southern portion of the U.S./Canada Management Area,
where DAS are not counted differentially, it would not be charged at
the 2:1 rate for part of the trip spend steaming through the Interim
Differential DAS Area. If a vessel declared and fished both inside the
Interim Differential DAS Area and
[[Page 2964]]
outside that area on the same trip, it would be charged differential
DAS (2:1) for all the DAS accrued on that trip.
The interaction of current groundfish and non-groundfish regulatory
programs and the different DAS counting rules would remain unchanged
under this action (e.g., the cod running clock, Day Gillnet Category
rules, the application of per DAS possession limits, 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,
vessels fishing in the Interim Differential DAS Area and the Eastern
U.S./Canada Management Area (exclusively) would be charged at the
differential DAS rate of 2:1, but would not be charged steaming time to
or from the area. For vessels fishing in multiple geographic areas
where different rules apply to each area (such as differential DAS 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, would still apply.
As under the current regulations, vessels would be required to
declare, prior to leaving port, their intent to fish in the Interim
Differential DAS Area, via Vessel Monitoring System (VMS). The VMS
declaration screens would be modified slightly to accommodate the fact
that the southern border of the Interim Differential DAS Area divides
the U.S./Canada Management Area into two portions. For example, a
vessel intending to fish in the Eastern U.S./Canada Area would also
have to specify whether it would also fish in the Interim Differential
DAS Area.
The Interim Differential DAS Area is proposed as a means to reduce
fishing mortality on multiple stocks instead of further reductions in
DAS allocations in order to provide flexibility for vessel owners.
2. SNE Closure Area
The area in SNE between 40[deg] 30' and 41[deg] 30' N. lat., and
west of 68[deg] 30' W. long. to the shore, including Nantucket Sound
(30-minute square blocks of 97-107 and 80-90) would be closed to
federally permitted groundfish vessels (both open access and limited
access) when fishing on groundfish, with the exception of NE
multispecies vessels using hook gear, provided such vessels do not
retain winter flounder, and provided the vessels have only hook gear on
board. This interim rule proposes that groundfish vessels using only
hook gear on a particular trip may fish in the SNE Closure Area because
the catch rate of winter flounder is likely to be very low. Non-
groundfish commercial trips fishing in exempted fisheries (e.g., summer
flounder, scallop, and skate exemptions), or using exempted gear, could
also fish in the SNE Closure Area. NE multispecies vessels not fishing
in the SNE Closure Area would be allowed to transit through the area,
provided all fishing gear is properly stowed. The SNE Closure Area is
proposed as a means to reduce fishing mortality on SNE winter flounder
primarily, but would also reduce fishing mortality on other stocks such
as SNE/MA yellowtail flounder.
3. Modified Trip Limits
Under this interim rule, the current white hake possession limit of
1,000 lb (454 kg) per DAS would be increased to 2,000 lb (907 kg) per
DAS, with the same maximum of 10,000 lb (4,536 kg) per trip, and the
trip limit for GB winter flounder, currently 5,000 lb (2.268 kg) per
trip, would be removed. No retention of any fish would be allowed for
SNE winter flounder, northern windowpane flounder, or ocean pout.
Vessels fishing for winter flounder or windowpane flounder in multiple
stock areas would be 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 would be subject to the prohibition on
retention for that trip. Lastly, as explained further under item 7
(``Annual Specifications for U.S./Canada Management Area''), a limit of
5,000 lb (2,268 kg) of GB yellowtail flounder per trip would be
specified. Modifications to trip limits are proposed as a means to
reduce fishing mortality or increase yield because they are a
management tool that can effectively target particular stocks and are
an important component of the current FMP.
4. Specification of Target TACs
Target TACs are utilized in the FMP as one method of evaluating the
success 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
basis of calculating the incidental catch TACs for the Special
Management Programs. Table 3 lists the target TACs for FY 2009, based
upon GARM III data and estimated CY 2008 fishing mortalities.
Table 3. Target TACs (mt) for FY 2009
------------------------------------------------------------------------
Species Stock Target TAC
------------------------------------------------------------------------
Cod GB 3,506
------------------------------------------------------------------------
Cod GOM 10,327
------------------------------------------------------------------------
Haddock GB 86,520
------------------------------------------------------------------------
Haddock GOM 1,564
------------------------------------------------------------------------
Yellowtail flounder GB 1,617
------------------------------------------------------------------------
Yellowtail flounder SNE/MA 389
------------------------------------------------------------------------
Yellowtail flounder CC/GOM 860
------------------------------------------------------------------------
Plaice ................ 3,214
------------------------------------------------------------------------
Witch flounder ................ 928
------------------------------------------------------------------------
Winter flounder GB 2,004
------------------------------------------------------------------------
Winter flounder GOM 379
------------------------------------------------------------------------
Redfish ................ 8,614
------------------------------------------------------------------------
White hake ................ 2,376
------------------------------------------------------------------------
Pollock ................ 6,486
------------------------------------------------------------------------
Windowpane flounder N. ................ 299
------------------------------------------------------------------------
Windowpane flounder S. ................ 338
------------------------------------------------------------------------
Halibut ................ 68
------------------------------------------------------------------------
* A hard TAC, set through a separate process described in item 6.
5. Revisions to Incidental Catch TACs and Allocations to Special
Management Programs
This proposed interim action would revise the specification of
incidental catch TACs applicable to the Special Management Programs of
the FMP 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.
[[Page 2965]]
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 would be adopted under this action, an
incidental catch TAC would no longer be appropriate for American
plaice, because it would no longer be considered a stock of concern.
Further, new incidental catch TACs would be required for GOM winter
flounder and pollock, because they would now be considered stocks of
concern. The percentages that the TACs are currently based on would
remain unchanged, with the exception of witch flounder, which would be
reduced from 5-percent to 2-percent, due to its new proposed status and
the fact that the fishing mortality rate and total catch need to be
reduced. The incidental catch TACs for GOM winter flounder would be 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 proposed management measures are likely to achieve
more than the required reduction in fishing mortality, 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
would be 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 would increase from the current number (8),
to 10. Due to the severe fishing mortality reduction necessary for the
SNE/MA stock of winter flounder, no retention of this stock would be
allowed under this alternative, and there would be no incidental catch
TAC specified (see additional discussion under item 10, 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
----------------------------------------------------------------------------------------------------------------
Stock Percentage of Total TAC Initial TAC Incidental TAC
----------------------------------------------------------------------------------------------------------------
GB cod 2 3,506 70.1
----------------------------------------------------------------------------------------------------------------
GOM cod 1 10,327 103.3
----------------------------------------------------------------------------------------------------------------
GB yellowtail 2 1,617 32.3
----------------------------------------------------------------------------------------------------------------
CC/GOM yellowtail 1 860 8.6
----------------------------------------------------------------------------------------------------------------
SNE/MA yellowtail 1 389 3.9
----------------------------------------------------------------------------------------------------------------
Pollock 5 6,486 324.3
----------------------------------------------------------------------------------------------------------------
Witch flounder 2 928 18.6
----------------------------------------------------------------------------------------------------------------
GB winter flounder 2 2,004 40.1
----------------------------------------------------------------------------------------------------------------
White hake 2 2,376 47.5
----------------------------------------------------------------------------------------------------------------
GOM winter 5 379 19.0
----------------------------------------------------------------------------------------------------------------
This proposed rule would also modify the allocation of the
incidental catch TACs to the various Special Management Programs due to
the change in status of stocks, as well as 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 would be reduced
for GB cod, GB yellowtail, and GB winter flounder, and the percent
allocation to the Regular B DAS Program would be increased due to
higher participation in that program historically. Secondly, this rule
would provide the Administrator, Northeast Region, NMFS (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 rate of catch of stocks of concern in the various
programs is highly variable. The proposed 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 Haddock SAP Closed Area I Hook Gear 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 %
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 2966]]
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./Canada Closed Area I Hook Gear
Stock Regular B DAS Program Haddock SAP Haddock SAP
----------------------------------------------------------------------------------------------------------------
GB Cod 49.1 9.8 11.2
----------------------------------------------------------------------------------------------------------------
GOM Cod 103.3 na na
----------------------------------------------------------------------------------------------------------------
GB Yellowtail flounder 25.9 6.5 na
----------------------------------------------------------------------------------------------------------------
CC/GOM Yellowtail flounder 8.6 na na
----------------------------------------------------------------------------------------------------------------
SNE/MA Yellowtail flounder 3.9 na na
----------------------------------------------------------------------------------------------------------------
Pollock 291.9 16.2 16.2
----------------------------------------------------------------------------------------------------------------
Witch flounder 18.6 na na
----------------------------------------------------------------------------------------------------------------
GB Winter flounder 32.1 8.0 na
----------------------------------------------------------------------------------------------------------------
White hake 47.5 na na
----------------------------------------------------------------------------------------------------------------
GOM Winter flounder 19.0 na na
----------------------------------------------------------------------------------------------------------------
6. 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 will also be
proposing management measures for the entire fishery to reduce fishing
mortality as described above and expects to implement measures for the
entire FY 2009, NMFS is including the specification of the TACs and
other measures for the U.S./Canada Management Area in this proposed
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. The regulations governing the annual development of
TACs were implemented by Amendment 13 to the FMP in order to be
consistent with the U.S./Canada Resource Sharing Understanding
(Understanding), which is an informal (i.e., non-binding) understanding
between the Northeast Region of NMFS and the Maritimes Region of the
Department of Fisheries and Ocean of Canada (DFO) that outlines a
process for the management of the shared GB groundfish resources. The
Understanding specifies an allocation of TAC for these three stocks for
each country, based on a formula that considers historical catch
percentages and current resource distribution.
Annual TACs are determined through a process involving the Council,
the Transboundary Management Guidance Committee (TMGC), and the U.S./
Canada Transboundary Resources Steering Committee. In September 2008,
the TMGC approved the 2008 Guidance Document for Eastern GB cod,
Eastern GB haddock, and GB yellowtail flounder, which included
recommended U.S. TACs for these stocks. The recommended FY 2008 TACs
were based upon the most recent stock assessments TRAC Status Reports
for 2008), and the fishing mortality strategy shared by both NMFS and
DFO. The strategy is to maintain a low to neutral (less than 50-
percent) risk of exceeding the fishing mortality limit reference (Fref
= 0.18, 0.26, and 0.25 for cod, haddock, and yellowtail flounder,
respectively). When stock conditions are poor, fishing mortality rates
should be further reduced to promote rebuilding.
[[Page 2967]]
The TMGC concluded that the most appropriate combined U.S./Canada
TAC for Eastern GB cod for FY 2009 is 1,700 mt. This corresponds to a
low risk (less than 25- percent) of exceeding the Fref of 0.18 (i.e.,
Fmsy) in 2009. However, due to poor recruitment, there is a high risk
(greater than 75-percent) that stock biomass will not increase from CY
2009 to CY 2010. The annual allocation shares between countries for FY
2009 are based on a combination of historical catches (15-percent
weighting) and resource distribution based on trawl surveys (85-percent
weighting). Combining these factors entitles the United States to 31-
percent of the shared TAC and Canada to 69- percent, resulting in a
national quota of 527 mt for the United States and 1,173 mt for Canada.
For Eastern GB haddock, the TMGC concluded that the most
appropriate combined U.S./Canada TAC for FY 2009 fishing year is 30,000
mt. This represents a low to neutral risk (greater than 25-percent but
less than 50-percent) of exceeding the Fref of 0.26. Adult biomass is
projected to peak at 158,000 mt in CY 2008 (reflecting the recruitment
and growth of the exceptional 2003 year class), and decline to 131,000
mt in 2010. The annual allocation shares between countries for FY 2009
are based on a combination of historical catches (15-percent weighting)
and resource distribution based on trawl surveys (85-percent
weighting). Combining these factors entitles the United States to 37-
percent of the shared TAC and Canada to 63-percent, resulting in a
national quota of 11,100 mt for the United States and 18,900 mt for
Canada.
For GB yellowtail flounder, the TMGC concluded that the most
appropriate combined U.S./Canada TAC for the 2009 fishing year is 2,100
mt. This corresponds to an F of 0.11, lower than the Fref of 0.25, and
is consistent with the fishing mortality required to rebuild GB
yellowtail flounder by 2014. With a catch of 2,100 mt in 2009, the age
3+ biomass is expected to increase by about 21-percent. The annual
allocation shares between countries for 2008 are based on a combination
of historical catches (15-percent weighting) and resource distribution
based on trawl surveys (85-percent weighting). Combining these factors
entitles the U.S. to 77-percent of the shared TAC and Canada to 23-
percent, resulting in a national quota of 1,617 mt for the U.S. and 483
mt for Canada.
On October 8, 2009, the Council approved, consistent with the 2008
Guidance Document, the following U.S./TACs recommended by the TMGC: 527
mt of Eastern GB cod; 11,100 mt of Eastern GB haddock; and 1,617 mt of
GB yellowtail flounder. The proposed 2009 fishing year TACs for the
U.S./Canada Management Area represent a decrease for cod and yellowtail
flounder, and an increase for haddock compared with those specified for
the 2008 fishing year (Tables 7 and 8).
Table 7. 2009 U.S./Canada TACs (mt) and Percentage Shares (in parentheses)
----------------------------------------------------------------------------------------------------------------
GB Cod GB Haddock GB Yellowtail Flounder
----------------------------------------------------------------------------------------------------------------
Total Shared TAC 1,700 30,000 2,100
U.S. TAC 527 (31%) 11,100 (37%) 1,617 (77%)
Canada TAC 1,173 (69%) 18,900 (63%) 483 (23%)
----------------------------------------------------------------------------------------------------------------
Table 8. 2008 U.S./Canada TACs (mt) and Percentage Shares (in parentheses)
----------------------------------------------------------------------------------------------------------------
GB Cod GB Haddock GB Yellowtail 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 2007 TAC
The 2009 TACs are based upon stock assessments conducted in June
2008 by the TRAC. The proposed TACs are consistent with the results of
the TRAC and the TMGC's harvest strategy, as well as the GB yellowtail
flounder rebuilding plan implemented by FW 42. 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 would 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 proposing, 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 proposing this same measure for FY 2009. Thus, the
FY 2009 opening of the Eastern U.S./Canada Area for trawl vessels would
be postponed from May 1, 2009, until August 1, 2009, while allowing
more selective longline gear access during May through July. Such
vessels would be limited to a cod catch of 5-percent of the cod TAC, or
26.4 mt of cod. The objective of the proposed 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 proposing implementation of
a possession limit of 5,000 lb (2,268 kg) per trip for GB yellowtail
flo