Fisheries of the Northeastern United States; Summer Flounder, Scup, and Black Sea Bass Fisheries; 2007 Summer Flounder, Scup, and Black Sea Bass Specifications; 2007 Research Set-Aside Projects, 62972-62984 [06-8932]
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Federal Register / Vol. 71, No. 208 / Friday, October 27, 2006 / Proposed Rules
• E-mail: FSB2007@noaa.gov. Include
in the subject line the following
National Oceanic and Atmospheric
identifier: ‘‘Comments on 2007 Summer
Administration
Flounder, Scup, and Black Sea Bass
Specifications.’’
50 CFR Part 648
• Federal e-Rulemaking portal: https://
www.regulations.gov.
RIN 0648–AT60
• Mail and hand delivery: Patricia A.
[Docket No. 061020273–6273–01; I.D.
Kurkul, Regional Administrator, NMFS,
101606A]
Northeast Regional Office, One
Blackburn Drive, Gloucester, MA 01930.
Fisheries of the Northeastern United
Mark the outside of the envelope:
States; Summer Flounder, Scup, and
‘‘Comments on 2007 Summer Flounder,
Black Sea Bass Fisheries; 2007
Scup, and Black Sea Bass
Summer Flounder, Scup, and Black
Specifications.’’
Sea Bass Specifications; 2007
• Fax: (978) 281–9135.
Research Set-Aside Projects
Copies of the specifications
document, including the Environmental
AGENCY: National Marine Fisheries
Assessment, Regulatory Impact Review,
Service (NMFS), National Oceanic and
and Initial Regulatory Flexibility
Atmospheric Administration (NOAA),
Analysis (EA/RIR/IRFA) and other
Commerce.
ACTION: Proposed specifications; request supporting documents for the
specifications are available from Daniel
for comments.
Furlong, Executive Director, MidSUMMARY: NMFS proposes specifications Atlantic Fishery Management Council,
for the 2007 summer flounder, scup,
Room 2115, Federal Building, 300 South
and black sea bass fisheries. The
Street, Dover, DE 19901–6790. Copies of
implementing regulations for the
the supplemental economic analysis are
Summer Flounder, Scup, and Black Sea available from Patricia A. Kurkul,
Bass Fishery Management Plan (FMP)
Regional Administrator, Northeast
require NMFS to publish specifications
Region, National Marine Fisheries
for the upcoming fishing year for each
Service, One Blackburn Drive,
of the species and to provide an
Gloucester, MA 01930–2298. These
opportunity for public comment. The
documents are also accessible via the
intent of this action is to establish
Internet at https://www.nero.noaa.gov.
harvest levels that assure that the target
FOR FURTHER INFORMATION CONTACT:
fishing mortality rates (F) or
Sarah McLaughlin, Fishery Policy
exploitation rates specified for these
Analyst, (978) 281–9279.
species in the FMP are not exceeded
SUPPLEMENTARY INFORMATION:
and to allow for rebuilding of the stocks
Background
in accordance with the MagnusonStevens Fishery Conservation and
The summer flounder, scup, and
Management Act (Magnuson-Stevens
black sea bass fisheries are managed
Act). NMFS has conditionally approved cooperatively by the Council and the
four research projects for the harvest of
Atlantic States Marine Fisheries
the portion of the quota that has been
Commission (Commission), in
recommended by the Mid-Atlantic
consultation with the New England and
Fishery Management Council (Council)
South Atlantic Fishery Management
to be set aside for research purposes. In
Councils. The management units
anticipation of receiving applications
specified in the FMP include summer
for Experimental Fishing Permits (EFPs) flounder (Paralichthys dentatus) in U.S.
to conduct this research, the Assistant
waters of the Atlantic Ocean from the
Regional Administrator for Sustainable
southern border of North Carolina (NC)
Fisheries, Northeast Region, NMFS
northward to the U.S./Canada border,
(Assistant Regional Administrator), has
and scup (Stenotomus chrysops) and
made a preliminary determination that
black sea bass (Centropristis striata) in
the activities authorized under the EFPs U.S. waters of the Atlantic Ocean from
issued in response to the approved
35°13.3′ N. lat. (the latitude of Cape
Research Set-Aside (RSA) projects
Hatteras Lighthouse, Buxton, NC)
would be consistent with the goals and
northward to the U.S./Canada border.
objectives of the FMP. However, further Implementing regulations for these
review and consultation may be
fisheries are found at 50 CFR part 648,
necessary before a final determination is subpart A (General Provisions), subpart
made to issue any EFP.
G (summer flounder), subpart H (scup),
DATES: Comments must be received on
and subpart I (black sea bass).
or before November 17, 2006.
The regulations outline the process
for specifying the annual commercial
ADDRESSES: You may submit comments
quotas and recreational harvest limits
by any of the following methods:
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DEPARTMENT OF COMMERCE
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for the summer flounder, scup, and
black sea bass fisheries, as well as other
management measures (e.g., mesh
requirements, minimum fish sizes, gear
restrictions, possession restrictions, and
area restrictions) for these fisheries. The
measures are intended to achieve the
annual targets set forth for each species
in the FMP, specified either as an F or
an exploitation rate (the proportion of
fish available at the beginning of the
year that are removed by fishing during
the year). Once the catch limits are
established, they are divided into quotas
based on formulas contained in the
FMP.
As required by the FMP, a Monitoring
Committee for each species, made up of
members from NMFS, the Commission,
and both the Mid-Atlantic and New
England Fishery Management Councils,
reviews the best available scientific
information and recommends catch
limits and other management measures
that will achieve the target F or
exploitation rate for each fishery.
Consistent with the implementation of
Framework Adjustment 5 to the FMP
(69 FR 62818, October 28, 2004), each
Monitoring Committee meets annually
to recommend the Total Allowable
Landings (TAL), unless the TAL has
already been established for the
upcoming calendar year as part of a
multiple-year specification process,
provided that new information does not
require a modification to the multipleyear quotas. Further, the TALs may be
specified in any given year for the
following 1, 2, or 3 years. The Council
is not obligated to specify multi-year
TALs, but is able to do so, depending on
the information available and the status
of the fisheries.
The Council’s Demersal Species
Committee and the Commission’s
Summer Flounder, Scup, and Black Sea
Bass Management Board (Board)
consider the Monitoring Committees’
recommendations and any public
comment and make their own
recommendations. While the Board
action is final, the Council’s
recommendations must be reviewed by
NMFS to assure that they comply with
FMP objectives. The Council and Board
made their recommendations, with the
exception of Board recommendations
for the 2007 summer flounder fishery, at
a joint meeting held August 1–3, 2006.
The Board delayed its action regarding
a summer flounder TAL
recommendation until its October 22–
26, 2006, meeting.
Explanation of RSA
In 2001, regulations were
implemented under Framework
Adjustment 1 to the FMP to allow up to
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3 percent of the TAL for each species to
be set aside each year for scientific
research purposes. For the 2007 fishing
year, a Request for Proposals was
published to solicit research proposals
based upon the research priorities that
were identified by the Council (70 FR
76253, December 23, 2005). Four
applicants were notified in August 2005
that their research proposals had
received favorable preliminary review.
For informational purposes, these
proposed specifications include a
statement indicating the amount of
quota that has been preliminarily set
aside for research purposes (3 percent of
the TAL for each fishery, as
recommended by the Council and
Board), and a brief description of the
RSA projects, and the amount of RSA
requested for each project. The RSA
amounts may be adjusted, following
consultation with RSA applicants, in
the final rule establishing the 2007
specifications for the summer flounder,
scup, and black sea bass fisheries. If the
total amount of RSA is not awarded,
NMFS will publish a document in the
Federal Register to restore the unused
amount to the applicable TAL.
For 2007, four RSA projects have been
conditionally approved by NMFS and
are currently awaiting a notice of award.
These projects collectively may be
awarded the following amounts of RSA
(3 percent of the proposed TALs):
389,490 lb (177 mt) of summer flounder;
360,000 lb (163 mt) of scup; and 150,000
lb (68 mt) of black sea bass. The projects
collectively also may be awarded up to
1,124,356 lb (510 mt) of Loligo squid
and 363,677 lb (165 mt) of bluefish.
The University of Rhode Island
submitted a proposal to conduct a
fourth year of work in a fisheryindependent scup survey that would
utilize unvented fish traps fished on
hard bottom areas in southern New
England waters to characterize the size
composition of the scup population.
Survey activities would be conducted
from May 1 through November 30, 2007,
at 10 rocky bottom study sites located
offshore, where there is a minimal scup
pot fishery and no active trawl fishery,
and at 2 scup spawning ground sites. Up
to two vessels would conduct the
survey. Sampling would occur off the
coasts of Rhode Island and southern
Massachusetts. Up to three vessels
would harvest the RSA during the
period January 1 through December 31,
2007. The preliminary RSA requested
for this project is 2,000 lb (907 kg) of
summer flounder; 40,000 lb (18 mt) of
scup; and 30,000 lb (14 mt) of black sea
bass.
The National Fisheries Institute (NFI)
and Rutgers University submitted a
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proposal to conduct a fifth year of work
on a commercial vessel-based trawl
survey program in the Mid-Atlantic
region that would track the migratory
behavior of selected recreationally and
commercially important species.
Information gathered during this project
would supplement the NMFS finfish
survey databases and improve methods
to evaluate how seasonal migration of
fish in the Mid-Atlantic influences stock
abundance estimates. Up to two vessels
would conduct survey work in the MidAtlantic during January, March, May,
and November 2007, along up to eight
offshore transects. The transects would
include six fixed offshore transects, one
each near Alvin, Hudson, Baltimore,
Poor Man’s, Washington, and Norfolk
Canyons, and two to three adaptive
transects positioned within the MidAtlantic area selected during a precruise meeting with NFI, Rutgers
University, and the NMFS Northeast
Fisheries Science Center (Center). Up to
15 1–nautical mile tows would be
conducted along each transect at depths
from 40 to 250 fathoms (73 to 457 m).
Up to 25 vessels would harvest the RSA
during the period January 1 through
December 31, 2007. The preliminary
RSA requested for the project is 223,140
lb (101 kg) of summer flounder; 221,581
lb (101 mt) of scup; 61,500 lb (28 mt) of
black sea bass; 281,059 lb (127 mt) of
Loligo squid; and 363,677 lb (165 mt) of
bluefish.
The Cornell Cooperative Extension of
Suffolk County submitted a proposal to
evaluate summer flounder discard
mortality in the bottom trawl fishery.
The project is intended to improve and
enhance fishery information relative to
discard mortality of summer flounder in
the bottom trawl fishery. Trawl-caught
summer flounder, both legal and sublegal size, would be measured, tagged,
and kept in a live holding pen (net pen)
for mortality monitoring. Mortality
would be monitored on a weekly basis
and fish would be released with tags
after 2 weeks. Extended mortality and
migration information would be
collected upon recapture of tagged fish.
One inshore day trip would be made
every 14 to 17 days from May to
September for a total of 10 day trips.
Overall, with 120 fish taken on each
trip, a total of 1,200 fish would be
collected from commercial vessels
during the project. The research trips
would be made aboard 15 commercial
vessels (vessels of opportunity) engaged
in the mixed trawl fishery, and would
be conducted inshore along the coast of
southern Long Island from Jones Inlet to
Montauk Point, reaching depths of 240
ft (73 m). Areas sampled would include
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NMFS statistical areas 611, 612, 613,
and 539. Vessels would be compensated
to make three specific tows for summer
flounder to assess trawl mortality.
Duration of these tows would be 1, 2,
and 3 hours. An additional 25 vessels
would harvest the RSA amounts
allocated to the project over the course
of the fishing year. The preliminary RSA
requested for the project is 178,000 lbs
(81 mt) of summer flounder.
The National Fisheries Institute (NFI)
and Rutgers University submitted a
proposal to conduct studies on bycatch
reduction and gear development in the
Mid-Atlantic through evaluation of
optimal codend mesh size in the Loligo
squid fishery. The project would
evaluate the performance of
intermediate codend mesh sizes above
the present legal size of 1.875 inches
(4.8 cm) and below 2.5 inches (6.35 cm),
e.g. mesh sizes of 2.125 inches (5.4 cm)
and 2.25 inches (5.7 cm). The
researchers would also attempt to
determine the influence of these
intermediate mesh sizes on the catch of
other species such as butterfish, silver
hake, and accompanying bycatch
species as well as Loligo squid
measuring below market size (4 inches
(10.2 cm)). The project would use two
similar vessels in the 75- to 100–ft (23to 30–m) range to test different mesh
sizes in squid nets under commercial
use. The exact number of tows would
depend on the duration of each tow,
which would be determined by the
vessel captain during fishing. The
research would involve a total of 108 to
144 tows, each lasting approximately 2–
3 hours, and would take place in
February and/or March 2007 near the
Hudson Canyon. Approximately 25
vessels would harvest the RSA amounts
allocated to the project over the course
of the fishing year. The preliminary RSA
requested for the project is 163,633 lb
(74 mt) of summer flounder; 269,305 lb
(122 mt) of scup; 40,358 lb (18 mt) of
black sea bass; and 331,000 lb (150 mt)
of Loligo squid.
Regulations under the MagnusonStevens Act require publication of this
notification to provide interested parties
the opportunity to comment on
applications for proposed EFPs.
Explanation of Quota Adjustments Due
to Quota Overages
This action proposes commercial
quotas based on the proposed TALs and
Total Allowable Catches (TACs) and the
formulas for allocation contained in the
FMP. In 2002, NMFS published final
regulations to implement a regulatory
amendment (67 FR 6877, February 14,
2002) that revised the way in which the
commercial quotas for summer
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flounder, scup, and black sea bass are
adjusted if landings in any fishing year
exceed the quota allocated (thus
resulting in a quota overage). If NMFS
approves a different TAL or TAC at the
final specifications stage, the
commercial quotas will be recalculated
based on the formulas in the FMP.
Likewise, if new information indicates
that overages have occurred and
deductions are necessary, NMFS will
publish notice of the adjusted quotas in
the Federal Register. NMFS anticipates
that the information necessary to
determine whether overage deductions
are necessary will be available by the
time the final specifications are
published. The commercial quotas
contained in these proposed
specifications for summer flounder,
scup, and black sea bass do not reflect
any deductions for overages. The final
specifications, however, will contain
quotas that have been adjusted
consistent with the procedures
described above.
Summer Flounder
The Center’s Southern Demersal
Working Group met in May 2005 to
address the terms of reference for Stock
Assessment Workshop (SAW) 41. The
Stock Assessment Review Committee
(SARC) accepted the 2005 stock
assessment update as the basis for
management advice, and also accepted
the Demersal Working Group’s
recommended updated biological
reference point values as follows:
Fmsy=Fmax=0.276; MSY=42 million lb
(22,000 mt), and Bmsy=204 million lb
(92,532 mt). Fmsy is the fishing mortality
rate that, if applied constantly, would
result in maximum sustainable yield
(MSY). Fmax is the level of fishing
mortality that produces maximum yield
per recruit. When F > Fmax, overfishing
is considered to be occurring, and when
B<1⁄2 Bmsy, the stock is considered
overfished.
The Southern Demersal Working
Group met on June 20, 2006, to update
the summer flounder assessment
through 2005/2006 based on the latest
research survey and fisheries catch data
available. This was a routine annual
update, as called for by the FMP, and
was based on the same population
model as used in recent years. Key
results of the update were as follows:
Overfishing is occurring (i.e., F > Fmax).
Almost all of the full-age structure state
and Federal survey indices used to
update the assessment have dropped
since 2003. Mean fish weight has
decreased, and this has contributed to
increased fishing mortality, as more fish
are taken by weight for a given catch
level. The 2005 F was estimated to have
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been 0.53, a significant decline from the
1.32 estimated for 1994, but well above
the threshold F of 0.276. The stock was
not determined to be overfished and
was estimated to be just above the
biomass threshold. Total stock biomass
(TSB) increased substantially during the
1990s and through 2004, but decreased
slightly since 2004, and was estimated
to be 105 million lb (47,627 mt) on
January 1, 2006, just over the biomass
threshold (1⁄2Bmsy) of 102 million lb
(46,266 mt)). Spawning stock biomass
(SSB) also increased during the 1990s
through 2004 (to 72 million lb (32,659
mt) in 2004), before decreasing to 67
million lb (30,391 mt) in 2005.
Recruitment since 1988 was estimated
to have improved, generally, although
the 2003 and 2005 year classes were
estimated to have been well below the
median (33 million fish) at 24.5 million
fish and 14.5 million fish, respectively.
It has been recognized since 1995 that
the summer flounder stock assessment
model tends to underestimate F and
overestimate stock biomass and
recruitment in the most recent years of
the analysis (typically for the previous
5 years), until those estimates stabilize
as new data are added to the analysis.
For example, the 2006 stock assessment
update showed that the estimate for
F2004 had increased from last year’s
estimate of 0.4 to 0.46; and that the
estimate for F2005 was 0.53. This pattern
is likely the result of an underestimation
of the true catch, due to discards and/
or unreported landings. The impact for
management, given these persistent
retrospective patterns, is that, although
the summer flounder stock continues to
increase, it is increasing at a lower rate
than, and is currently at a smaller size
than, previously forecast. Because the
Magnuson-Stevens Act requires stocks
to be rebuilt to a level that produces
MSY, it was clear from the 2006 stock
assessment update that additional
rebuilding of these species is still
required. For summer flounder, the
rebuilding period ends December 31,
2009.
The regulations state that the Council
shall recommend, and NMFS shall
implement, measures (including the
TAL) necessary to ensure, with at least
a 50–percent probability of success, that
the applicable specified F will not be
exceeded. This requirement is also
consistent with a 2000 Federal Court
Order (Natural Resources Defense
Council v. Daley, Civil No. 1:99 CV
00221 (JLG)) regarding the setting of the
summer flounder TAL. Through the
course of the rebuilding period, NMFS
has set TALs estimated to have at least
a 50–percent probability of not
exceeding Fmax.
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For 2007, the Council’s Summer
Flounder Monitoring Committee
considered that a TAL of 19.9 million lb
(9,026 mt) would meet the 50–percent
probability of success standard (based
on the Southern Demersal Working
Group 2006 update), but recommended
a TAL (13.88 million lb (6,296 mt))
associated with an F of 0.185, i.e., a 33–
percent reduction of the Fmax (0.276), in
order to account for the retrospective
pattern of F underestimation. In August
2006, the Council and the Board
discussed at length the Southern
Demersal Working Group 2006 update,
the TAL for 2007, and potential TALs
for the remainder of the rebuilding
period. The Council considered the
following TAL options: (1) a 2007 TAL
of 19.9 million lb (9,026 mt); (2) the
Summer Flounder Monitoring
Committee’s recommendation of 13.88
million lb (6,296 mt) for 2007; (3) a 2007
TAL projected to result in rebuilding of
the summer flounder stock by 2010
(7.69 million lb (3,489 mt)); (4) a 2007
TAL that would both allow for
rebuilding by 2010 and account for the
retrospective F pattern (5.22 million lb
(2,368 mt)); (5) a constant TAL for 2007
through 2009 that would allow for
rebuilding by 2010 (10.04 million lb
(4,554 mt)); and (6) a constant TAL for
2007 through 2009 that would allow for
rebuilding by 2010 and that corrects for
the retrospective pattern of F
underestimation (6.72 million lb (3,048
mt)). The Council focused discussion on
a 2007 TAL of 19.9 million lb (9,026
mt).
During the August 2006 Council
discussion of the feasibility of achieving
the biomass target, given recent
recruitment levels, NMFS offered to reexamine the biological reference point
values based on the use of the most
recent scientific information available
and on use of a subset (rather than the
full range) of recruitment input data.
Projections were to be re-run based on
the revised reference points, the current
growth potential of the population, and
the recent history of reproductive effort
(recruitment), and the results were to be
peer-reviewed. NMFS encouraged the
Council to recommend a TAL for 2007,
and indicated that any new information
resulting from the stock assessment reexamination and the peer review
thereof, if appropriate, would be
reflected in the proposed specifications.
In the end, the Council adopted a 2007
TAL of 19.9 million lb (9,026 mt), with
3 percent of the TAL set aside for
research. This TAL would represent a
16–percent decrease for 2007 from the
2006 TAL of 23.59 million lb (10,700
mt). After deducting the RSA, the TAL
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would be divided into a commercial
quota (60 percent) and a recreational
harvest limit (40 percent). The Board
delayed its vote until its October 22–26,
2006, meeting, to consider the updated
analyses.
NMFS’s re-examination of the
biological reference points, the peer
review of this work, and subsequent
analysis stemming from the peer review
was completed in September 2006 and
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that F must be substantially lowered for
2007 through 2009 to allow for
rebuilding by 2010. The stock continues
to be considered not overfished, but is
still just slightly above the biomass
threshold. Table 1 summarizes and
compares findings from the Southern
Demersal Working Group 2006 Update
and the recent peer reviewed
assessment and biological reference
point update.
is documented in ‘‘Summer Flounder
Assessment and Biological Reference
Point Update for 2006.’’ This update is
available at https://www.nefsc.noaa.gov/
nefsc/saw/2006FlukeReview/.
The Peer Review Panel’s (Panel’s)
review did not result in any change in
the current stock status determinations
of the summer flounder stock. It
confirmed that overfishing occurred
throughout the rebuilding period, and
TABLE 1. COMPARISON OF THE FINDINGS OF THE SOUTHERN DEMERSAL WORKING GROUP 2006 UPDATE) AND THE PEER
REVIEWED SUMMER FLOUNDER ASSESSMENT AND BIOLOGICAL REFERENCE POINT UPDATE)
Factor
2006 Assessment (June 2006)
Update (September 2006)
Fmax
0.276
0.280
Frebuild
0.099
0.15
F2005
0.528
0.407
Overfishing
Yes
Yes
R
33.11 million fish (median)
37 million fish (mean)
Bmsyproxy
TSB=204 million lb (92,645 mt)
TSB (age 1 + fish) = 215 million lb (97,430 mt)
SSB=197 million lb (89,411 mt)*
Biomass threshold
12
12
SSB2005
67 million lb (30,600 mt)
105 million lb (47,498 mt)
TSB2005
105 million lb (47,800 mt) (age 0+ fish)
113 million lb (51,317 mt) (age 1+ fish)
Overfished
No (52% of Bmsy)
No (53% of Bmsy)
MSY
42 million lb (19,072 mt)
47 million lb (21,444 mt)
⁄ TSB=102 million lb (46,323 mt)
⁄ SSB=98.5 million lb (44,706 mt)
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* Panel suggested use of SSB as Bmsy proxy in the future, but provided TSB information for comparison.
The Panel recommended several
adjustments in the assessment. The
most important of these are that the
stock condition be assessed using SSB
rather than TSB, and several changes in
how the weight of fish not yet Age 1 is
used in the stock assessment model.
With respect to the Southern Demersal
Working Group 2006 Update, the
recently updated analysis (which
incorporated the Panel
recommendations) lowered the best
estimate of Bmsy, raised Fmax slightly,
raised MSY, and raised the SSB
estimates and lowered the F estimates
for 2000–2005. The annual F projected
to allow for rebuilding to SSBmax by
2010 (Frebuild) is currently estimated to
be 0.15. Should an F of 0.15 in the 2007
fishing year prove to be inconsistent
with allowing the stock to rebuild by
2010, based on the results of the annual
summer flounder stock assessment
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update in June 2007, NMFS would
adjust the target F for 2008. Similar
adjustment for the 2009 target F would
occur based on the June 2008 stock
assessment update, if necessary. Fishing
at F=0.15 starting in 2007 is also
anticipated to rebuild the stock to
within 1 percent of the Bmsy proxy
currently in the FMP (a TSB of 204
million lb (92,645 mt)) by 2010. The
Panel acknowledged the retrospective
pattern of F underestimation (by 34
percent), biomass overestimation (by 12
percent), and recruitment
overestimation (by 4 percent). The Panel
made no recommendation on how to
adjust the analysis for this pattern, but
noted that it should be taken into
account when setting management
targets.
At the October 10–12, 2006, Council
meeting, following a presentation of the
Panel’s findings, the Council voted to
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include a provision to amend the
summer flounder biomass target, based
on the updated, best available scientific
information, in Amendment 14 to the
FMP, which is currently under Council
development.
Projections indicate that fishing at a
constant Fmax level of 0.28 would result
in not achieving the biomass target until
after 2022. As indicated above,
commensurate with the objectives of the
FMP, reduced TALs will be needed for
2007 through 2009 to achieve the
biomass target by the end of the 10-year
rebuilding period for summer flounder.
The best available scientific information
indicates that a TAL of 14.156 million
lb (6,421 mt) is expected to have at least
a 50–percent probability of achieving an
F of 0.15 in 2007, if the TAL and
assumed discard level in 2006 are not
exceeded. It also will also ensure, with
a much greater than 50–percent
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probability of success, that Fmax will not
be exceeded. The setting of an annual
TAL greater than this amount would be
contrary to the rebuilding requirements
of the Magnuson-Stevens Act and
objectives of the FMP.
In consideration of the Panel’s
recommendation to take the
retrospective pattern of F
underestimation into account when
setting management targets, and the
requirement to rebuild the stock by the
end of 2009, NMFS proposes a TAL that
is associated with a 75–percent
probability of achieving the F that is
projected to allow the stock to rebuild
to an SSB of 197 million lb (89,411 mt)
and further assure to an even greater
extent that Fmax will not be exceeded.
The best available scientific information
indicates that a TAL of 12.983 million
lb (5,889 mt) is expected to have at least
a 75–percent probability of achieving an
F of 0.15 in 2007, if the TAL and
assumed discard level in 2006 are not
exceeded, and is expected to allow for
rebuilding of the stock to the target
biomass by the end of 2009.
For these reasons, NMFS proposes a
summer flounder TAL of 12.983 million
lb (5,889 mt) for 2007. This TAL would
represent a 45–percent decrease for
2007 from the 2006 TAL of 23.59
million lb (10,700 mt). The initial TAL
would be allocated 60 percent
(7,789,800 lb (3,533 mt)) to the
commercial sector and 40 percent
(5,193,200 lb (2,356 mt)) to the
recreational sector, as specified in the
FMP. For 2007, the Council and Board
agreed to set aside 3 percent of the
summer flounder TAL for research
activities. After deducting the RSA
(389,490 lb (177 mt)) from the TAL
proportionally for the commercial and
recreational sectors, as specified in the
FMP, i.e., 60 percent and 40 percent,
respectively, the commercial quota
would be 7,556,106 lb (3,427 mt) and
the recreational harvest limit would be
5,037,404 lb (2,285 mt). The commercial
quota then would be allocated to the
coastal states based upon percentage
shares specified in the FMP.
In addition, the Commission is
expected to maintain the voluntary
measures currently in place to reduce
regulatory discards that occur as a result
of landing limits established by the
states. The Commission established a
system whereby 15 percent of each
state’s quota would be voluntarily set
aside each year to enable vessels to land
an incidental catch allowance after the
directed fishery has been closed. The
intent of the incidental catch set-aside is
to reduce discards by allowing
fishermen to land summer flounder
caught incidentally in other fisheries
during the year, while also ensuring that
the state’s overall quota is not exceeded.
These Commission set-asides are not
included in these proposed
specifications because these measures
are not authorized by the FMP and
NMFS does not have authority to
implement them.
Table 2 presents the proposed
allocations by state, with and without
the commercial portion of the RSA
deduction. These state quota allocations
are preliminary and are subject to
reductions if there are overages of states
quotas carried over from a previous
fishing year (using the landings
information and procedures described
earlier). Any commercial quota
adjustments to account for overages will
be included in the final rule
implementing these specifications.
TABLE 2. 2007 PROPOSED INITIAL SUMMER FLOUNDER STATE COMMERCIAL QUOTAS.
Commercial Quota less RSA1
Commercial Quota
State
Percent Share
kg2
lb
kg2
lb
ME
0.04756
3,705
1,681
3,594
1,630
NH
0.00046
36
16
35
16
MA
6.82046
531,300
240,998
515,361
233,768
RI
15.68298
1,221,673
554,151
1,185,023
537,526
CT
2.25708
175,822
79,753
170,547
77,360
NY
7.64699
595,685
270,203
577,815
262,097
NJ
16.72499
1,302,843
590,970
1,263,758
573,241
DE
0.01779
1,386
629
1,344
610
MD
2.03910
158,842
72,051
154,077
69,889
VA
21.31676
1,660,533
753,218
1,610,717
730,621
NC
27.44584
2,137,976
969,786
2,073,837
940,692
100.00001
7,789,801
3,553,456
7,556,108
3,427,450
TOTAL3
1
2
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3
Preliminary Research Set-Aside: 3 percent of the commercial quota, i.e., 233,694 lb (106 mt).
Kilograms are as converted from pounds and do not sum to the converted total due to rounding.
Rounding of quotas results in totals exceeding 100 percent.
Scup
For scup, the stock is considered
overfished when the 3-year average of
scup SSB is less than the biomass
threshold (2.77 kg/tow; the maximum
Center spring survey 3-year average of
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13:23 Oct 26, 2006
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SSB). Scup was last formally assessed in
June 2002 at the 35th Northeast Regional
Stock Assessment Workshop (SAW). At
that time, SARC 35 indicated that the
species was no longer overfished, but
that stock status with respect to
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overfishing could not be evaluated. An
anomalously large spring SSB index
value for 2002 resulted in the 3-year
SSB average exceeding the biomass
threshold for 2001 through 2003.
However, more recent information
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indicates that the scup SSB has
decreased, and the 3-year SSB average
values for 2004 (0.69 kg/tow) and 2005
(1.32 kg/tow) were under one-quarter
and one-half of the SSB threshold,
respectively. Therefore, the stock is
considered overfished.
The proposed scup specifications for
2007 are based on an exploitation rate
(21 percent) in the rebuilding schedule
that was approved when scup was
added to the FMP in 1996, prior to
passage of the Sustainable Fisheries Act
(SFA). Subsequently, to comply with
the SFA amendments to the MagnusonStevens Act, the Council prepared
Amendment 12 to the FMP, which
proposed to maintain the existing
rebuilding schedule for scup established
by Amendment 8 to the FMP. On April
28, 1999, NMFS disapproved the
proposed rebuilding plan for scup
because the rebuilding schedule did not
appear to be sufficiently risk-averse.
Later, however, NMFS advised the
Council that use of the exploitation rate
as a proxy for F would be acceptable
and sufficiently risk-averse. NMFS
considers the risks associated with the
disapproved rebuilding plan as not
applicable to the proposed
specifications because they apply only
for 1 fishing year and will be reviewed,
and modified as appropriate, by the
Council and NMFS annually.
Furthermore, setting the scup
specifications using an exploitation rate
of 21 percent is a more risk-averse
approach to managing the resource than
not setting any specifications until the
Council submits, and NMFS approves, a
revised rebuilding plan that complies
with all Magnuson-Stevens Act
requirements. The Council is currently
addressing this deficiency through
Amendment 14 to the FMP, which is
under development.
Given the uncertainty associated with
the spring survey, the Council and
Board agreed with the Scup Monitoring
Committee recommendation to set a
TAC and TAL for 1 year only. A
recommendation on the TAC for 2007 is
complicated by the lack of information
on discards and mortality estimates for
fully recruited fish. In recent years,
Council staff has used the 3-year SSB
index average, the relative exploitation
index (based on total landings and the
spring survey SSB index), and
assumptions about F to develop a TAL
recommendation. That approach would
indicate that a TAL of 31.12 million lb
(14,116 mt; nearly double that for 2006)
would achieve the target exploitation
rate of 21 percent in 2007. Council staff
cautioned against use of the SSB index
to derive a TAC for 2007, given the
current overfished status for scup, poor
2004 and 2005 year classes, and the
uncertainty associated with the survey
indices, and instead suggested a TAL of
12 million lb (5,443 mt). This value,
which is 26–percent lower than the
2006 TAL, falls within the range of
yields expected at about 1⁄2Bmsy (11–16.5
million lb (4,990–7,484 mt)) based on
the long-term potential catch, and
would constrain harvest to the level of
actual landings in 2005. The Scup
Monitoring Committee agreed with the
Council staff recommendation.
Estimated discards of 1.97 million lb
(894 mt) were added to the TAL to
derive a TAC of 17.97 million lb (8,151
mt).
Reasoning that the scup winter trip
limits have been effective in reducing
scup discards and that the commercial
fishery has not met its quota in the last
few years, and concerned about
potential shift in effort from summer
flounder to scup, the Council and Board
rejected the Monitoring Committee
recommendation and instead
recommended a TAL of 16 million lb
(7,258 mt), an amount at the high end
of the range of yields expected at 1⁄2Bmsy,
and representing a less than 2–percent
decrease from 2006, with 3 percent of
the TAL set aside for research.
NMFS is concerned about
implementing the scup TAL
recommended by the Council and Board
for the reasons identified by the Scup
Monitoring Committee and because the
spring survey index values have fallen
below the biomass threshold, upon
which long-term potential catch
projections are based. Following
NMFS’s notification to the Council in
August 2005 that the scup stock had
been designated as overfished, the
Council initiated development of
Amendment 14 to implement a plan to
rebuild the scup fishery. Although the
amendment is not scheduled to be
effective until 2007 (affecting TAL
specification for 2008 and beyond), the
setting of a more conservative 2007 TAL
would contribute to the rebuilding
efforts for this overfished stock.
For these reasons, NMFS proposes to
implement a scup TAL of 12 million lb
(5,443 mt) for 2007. This TAL would
represent a 26–percent decrease for
2007 from the 2006 TAL of 16.27
million lb (7,380 mt). The FMP specifies
that the TAC associated with a given
exploitation rate be allocated 78 percent
to the commercial sector and 22 percent
to the recreational sector. Scup discard
estimates are deducted from both
sectors’ TACs to establish TALs for each
sector, i.e., TAC minus discards equals
TAL. The commercial TAC, discards,
and TAL (commercial quota) are then
allocated on a percentage basis to three
quota periods, as specified in the FMP:
Winter I (January-April)--45.11 percent;
Summer (May-October)--38.95 percent;
and Winter II (November-December)-15.94 percent. The commercial TAC
would be 10,900,000 lb (4,943 mt) and
the recreational TAC would be
3,070,000 lb (1,394 mt). After deducting
estimated discards (1.72 million lb (780
mt) for the commercial sector and
250,000 lb (113 mt) for the recreational
sector), the initial commercial quota
would be 9,176,600 lb (4,163 mt) and
the recreational harvest limit would be
2,823,400 lb (1,281 mt). The Council
and Board agreed to set aside 3 percent
of the TAL for research activities.
Deducting this RSA (360,000 lb (163
mt)) would result in a commercial quota
of 8,895,800 lb (4,035 mt) and a
recreational harvest limit of 2,744,200 lb
(1,245 mt).
The proposed specifications would
maintain the base scup possession
limits, i.e., 30,000 lb (13,608 mt) for
Winter I, to be reduced to 1,000 lb (454
kg) when 80 percent of the quota is
projected to be reached, and 2,000 lb
(907 kg) for Winter II), as implemented
for 2006.
Table 3 presents the 2007 commercial
allocation recommended by the Council,
with and without the preliminary
280,800–lb (127–mt) RSA deduction.
These 2007 allocations are preliminary
and may be subject to downward
adjustment due to 2005 overages in the
final rule implementing these
specifications, based on the procedures
for calculating overages described
earlier.
TABLE 3. 2007 PROPOSED INITIAL TAC, COMMERCIAL SCUP QUOTA, AND POSSESSION LIMITS.
Period
Winter I
VerDate Aug<31>2005
Percent
TAC in lb (mt)
45.11
13:23 Oct 26, 2006
Discards in lb (mt)
4,915,456
(2,230)
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Commercial Quota
in lb (mt)
775,892
(352)
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Commercial Quota
less RSA in lb (mt)
4,139,564
(1878)
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4,012,895
(1820)
27OCP1
Possession Limits
in lb (kg)
30,0001
(13,608)
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TABLE 3. 2007 PROPOSED INITIAL TAC, COMMERCIAL SCUP QUOTA, AND POSSESSION LIMITS.—Continued
Period
Percent
TAC in lb (mt)
Discards in lb (mt)
Commercial Quota
in lb (mt)
Commercial Quota
less RSA in lb (mt)
Possession Limits
in lb (kg)
Summer
38.95
4,244,226
(1,925)
669,940
(304)
3,574,286
(1,621)
3,464,914
(1,572)
n/a
Winter II
15.94
1,736,918
(788)
274,168
(124)
1,462,750
(664)
1,417,991
(643)
2,000
(907)
100.00
10,896,600
(4,943)
1,720,000
(780)
9,176,600
(4,163)
8,895,800
(4,035)
Total2
1The
Winter I landing limit would drop to 1,000 lb (454 kg) upon attainment of 80 percent of the seasonal allocation.
subject to rounding error.
n/a-Not applicable
2Totals
The final rule to implement
Framework 3 to the FMP (68 FR 62250,
November 3, 2003) implemented a
process, for years in which the full
Winter I commercial scup quota is not
harvested, to allow unused quota from
the Winter I period to be rolled over to
the quota for the Winter II period. As
shown in Table 4, the proposed
specifications would maintain the
Winter II possession limit-to-rollover
amount ratios (1,500 lb (680 kg) per
500,000 lb (227 mt) of unused Winter I
period quota), as implemented for 2006.
TABLE 4. POTENTIAL INCREASE IN WINTER II POSSESSION LIMITS BASED ON THE AMOUNT OF SCUP ROLLED OVER FROM
WINTER I TO WINTER II PERIOD.
Initial Winter II Possession
Limit
Rollover from Winter I to Winter II
lb
mt
lb
kg
2,000
907
0–499,999
0–227
2,000
907
500,000–999,999
2,000
907
2,000
2,000
kg
lb
kg
0
0
2,000
907
227–454
1,500
680
3,500
1,588
1,000,000–1,499,999
454–680
3,000
1,361
5,000
2,268
907
1,500,000–1,999,999
680–907
4,500
2,041
6,500
2,948
907
2,000,000–2,500,000
907–1,134
6,000
2,722
8,000
3,629
Amendment 12 to the FMP indicated
that the black sea bass stock, which was
determined by SARC 27 to be overfished
in 1998, could be rebuilt to the target
biomass within a 10-year period, i.e., by
2010. The current target exploitation
rate is based on the current estimate of
Fmax, or 0.33 (25.6 percent). The
northern stock of black sea bass was last
assessed at the 43rd SAW in June 2006.
The SARC 27 Panel did not consider the
stock assessment to provide an adequate
basis to evaluate stock status against the
biological reference points, but did not
recommend any other reference points
to replace them.
The most recent Center spring survey
results indicate that the exploitable
biomass of black sea bass decreased in
2005. The 2005 biomass index, i.e., the
3-year average exploitable biomass for
2004 through 2006, is estimated to be
0.804 kg/tow, below the threshold
biomass value of 0.976 kg/tow. Based on
these results, if the biological reference
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Final Winter II Possession Limit
after Rollover from Winter I to Winter II
lb
Black Sea Bass
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points in the FMP are applied, black sea
bass once again would be determined to
be overfished.
The best available information on
stock status indicates that stock size has
increased in recent years. In addition,
the 2005 year class may be above
average. If protected, this year class
should allow for additional stock
rebuilding in 2006 and beyond. Given
the lack of stock projections, it is
difficult to predict what the actual
biomass will be in 2007. Because the
estimate of exploitable biomass is based
on a 3-year average, the actual estimate
for 2007 will not be derived until the
spring 2008 survey results are available;
if it is 0.328 (equal to the average for
2004–2006), and assuming an
exploitation rate of 21 percent in 2003,
the TAL associated with the target
exploitation rate would be 4.68 million
lb (2,123 mt). However, if the 2007
estimate is 0.396 (equal to the average
for 2003–2005), the TAL associated with
the target exploitation rate would be
5.650 million lb (2,563 mt). Given the
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uncertainty in the survey estimates and
the potential underestimation of the
2003 exploitation rate (21 percent), the
Monitoring Committee agreed with the
Council staff recommendation to set a 1year TAL (for 2007) of 5 million lb
(2,270 mt), noting that it would
constrain the 2007 landings to the 2005
and 2006 levels.
Reasoning that the TAL should be set
at a level higher than 2005 landings (to
avoid discards and highgrading, to
accommodate a potential shift in effort
from the summer flounder fishery, and
assuming that black sea bass availability
may improve in 2007), but recognizing
the need for a more conservative TAL
than implemented for 2006, the Council
and Board rejected the Monitoring
Committee recommendation, and
recommended instead a 6.5–million-lb
(2,948–mt) TAL for 2007, with 3 percent
of the TAL set aside for research. This
TAL would represent a 19–percent
decrease from 2006.
NMFS has concerns regarding the
Council and Board-recommended black
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sea bass TAL, which is well above the
range of TALs considered by the
Monitoring Committee, for the reasons
specified above. More conservative
black sea bass TALs will likely need to
be implemented during the remainder of
the rebuilding period to allow for
growth of exploitable biomass (reflected
by the spring survey index). NMFS has
encouraged the Council to manage this
stock with caution and to initiate a
process to develop replacement stock
status determination criteria that are
scientifically supportable and that can
be relied on to measure the progress of
rebuilding.
For the reasons described above,
NMFS proposes to implement a black
sea bass TAL of 5 million lb (2,270 mt)
for 2007. This TAL would represent a
37.5–percent decrease from the 2006
TAL of 8 million lb (3,629 mt). The FMP
specifies that the TAL associated with a
given exploitation rate be allocated 49
percent to the commercial sector and 51
percent to the recreational sector;
therefore, the initial TAL would be
allocated 2.45 million lb (1,111 mt) to
the commercial sector and 2.55 million
lb (1,157 mt) to the recreational sector.
The Council and Board also agreed to
set aside 3 percent of the black sea bass
TAL for research activities. After
deducting the RSA (150,000 lb (68 mt)),
the TAL would be divided into a
commercial quota commercial quota of
2,376,500 lb (1,078 mt) and a
recreational harvest limit of 2,473,500 lb
(1,122 mt), as specified in the FMP.
Classification
These proposed specifications are
exempt from review under Executive
Order 12866.
An IRFA was prepared, as required by
section 603 of the Regulatory Flexibility
Act (RFA). The IRFA describes the
economic impact these proposed
specifications, 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. A copy of this analysis
is available from NMFS (see
ADDRESSES). A summary of the
economic analysis follows.
The economic analysis assessed the
impacts of the various management
alternatives. The no action alternative is
defined as follows: (1) No proposed
specifications for the 2007 summer
flounder, scup, and black sea bass
fisheries would be published; (2) the
indefinite management measures
(minimum mesh sizes, minimum sizes,
possession limits, permit and reporting
requirements, etc.) would remain
unchanged; (3) there would be no quota
set-aside allocated to research in 2007;
(4) the existing gear restrictive areas
would remain in place for 2007; and (5)
there would be no specific cap on the
allowable annual landings in these
fisheries (i.e., there would be no quotas).
Implementation of the no action
alternative would be inconsistent with
the goals and objectives of the FMP, its
implementing regulations, and the
Magnuson-Stevens Act. In addition, the
no action alternative would
substantially complicate the approved
management program for these fisheries,
and would very likely result in
overfishing of the resources. Therefore,
the no action alternative is not
62979
considered to be a reasonable alternative
to the preferred action.
The Council prepared economic
analyses for Alternatives 1 through 3.
Alternative 1 consists of the harvest
limits proposed by the Council for
summer flounder, and the Council and
Board for scup and black sea bass.
Alternative 2 consists of the most
restrictive quotas (i.e., lowest landings)
considered by the Council and the
Board for all of the species. Alternative
3 consists of the status quo quotas,
which were the least restrictive quotas
(i.e., highest landings) considered by the
Council and Board for all three species.
NMFS prepared a supplemental
economic analysis for Alternatives 4
through 6. Although NMFS defined
Alternative 4 as the no action
alternative, no analysis was undertaken
for the reasons described above, i.e.,
because it would likely result in
overfishing of the resources. Alternative
5 consists of a summer flounder TAL of
14.156 million lb (6,421 mt, associated
with a 50–percent probability of not
exceeding the F target) and the most
restrictive quotas for scup and black sea
bass. Alternative 6 consists of a summer
flounder TAL of 12.983 million lb
(5,889 mt, associated with a 75–percent
probability of not exceeding the F target)
and the most restrictive quotas for scup
and black sea bass. For clarity, these
proposed specifications are described in
Alternative 6.
Table 5 presents the 2007 initial
TALs, RSA, commercial quotas adjusted
for RSA, and preliminary recreational
harvests for the fisheries under these
three quota alternatives.
TABLE 5. COMPARISON, IN LB (MT), OF THE ALTERNATIVES OF QUOTA COMBINATIONS REVIEWED.
Initial TAL
RSA
Preliminary Adjusted Commercial Quota1
Preliminary Recreational Harvest Limit
19.9 million
(9,026)
567,0922
(257)
11.60 million
(5,261)
7.73 million
(3,506)
Scup
16 million
(7,257)
480,000
(218)
11.93 million
(5,411)
3.59 million
(1,628)
Black Sea Bass
6.5 million
(2,948)
132,0002
(60)
3.12 million
(1,415)
3.25 million
(1,474)
5.22 million
(2,368)
156,600
(71)
3.04 million
(1,379)
2.03 million
(921)
Scup
12 million
(5,442)
360,000
(163)
8.9 million
(4,037)
2.74 million
(1,243)
Black Sea Bass
5 million
(2,268)
132,0002
(60)
2.39 million
(1,084)
2.48 million
(1,125)
Quota Alternative 1 (Council’s Preferred)
Summer Flounder
Quota Alternative 2 (Most Restrictive)
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TABLE 5. COMPARISON, IN LB (MT), OF THE ALTERNATIVES OF QUOTA COMBINATIONS REVIEWED.—Continued
RSA
Initial TAL
Preliminary Adjusted Commercial Quota1
Preliminary Recreational Harvest Limit
Quota Alternative 3 (Status Quo-Least Restrictive)
Summer Flounder
23.59 million
(10,700)
567,0622
(257)
13.81 million
(6,264)
9.21 million
(4,178)
Scup
16.27 million
(7,380)
488,100
(221)
12.13 million
(5,502)
3.65 million
(1,656)
8 million
(3,629)
132,0002
(60)
3.86 million
(1,751)
4.01 million
(1,819)
14.156 million
(6,421)
424,680
(193)
8.24 million
(3,738)
5.49 million
(2,490)
Scup
12 million
(5,443)
360,000
(163)
8.9 million
(4,037)
2.74 million
(1,243)
Black Sea Bass
5 million
(2,268)
150,000
(68)
2.38 million
(1,078)
2.47 million
(1,122)
12.983
(5,889)
389,490
(177)
7.56 million
(3,429)
5.04 million
(2,286)
Scup
12 million
(5,443)
360,000
(163)
8.9 million
()
2.74 million
(1,243)
Black Sea Bass
5 million
(2,268)
150,000
(68)
2.38 million
(1,078)
2.47 million
(1,122)
Black Sea Bass
Quota Alternative 4 (No Action - not analyzed)
Quota Alternative 5 (NMFS analysis)
Summer Flounder
Quota Alternative 6 (NMFS analysis - Proposed Action)
Summer Flounder
1
2
3
Note that preliminary quotas are provisional and may change to account for overages of the 2006 quotas.
Actual RSA amount analyzed by Council staff (rather than 3 percent of TAL)
Metric tons are as converted from pounds and are subject to rounding error
Table 6 presents the percent change
associated with each of these
commercial quota alternatives (adjusted
for RSA) compared to the final adjusted
quotas for 2006.
TABLE 6. PERCENT CHANGE ASSOCIATED WITH 2007 ADJUSTED COMMERCIAL QUOTA ALTERNATIVES COMPARED TO 2006
COMMERCIAL ADJUSTED QUOTAS.
Total Changes Including Overages and RSA
Quota Alternative 1
(Council Preferred)
Quota Alternative 2
(Most Restrictive)
Quota Alternative 3*
(Least Restrictive)
Quota Alternative 5
Quota Alternative 6
-16%
-78%
+ less than 1%
-41%
-46%
no change
-25%
+ less than 2%
-25%
-25%
-19%
-38%
+ less than 1%
-38%
-38%
Summer Flounder
Aggregate Change
Scup
Aggregate Change
Black Sea Bass
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Aggregate Change
*Denotes
status quo management measures.
All vessels that would be impacted by
this proposed rulemaking are
considered to be small entities;
therefore, there would be no
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13:23 Oct 26, 2006
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disproportionate impacts between large
and small entities. The categories of
small entities likely to be affected by
this action include commercial and
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charter/party vessel owners holding an
active Federal permit for summer
flounder, scup, or black sea bass, as well
as owners of vessels that fish for any of
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these species in state waters. The
Council estimates that the proposed
2007 quotas could affect 2,242 vessels
that held a Federal summer flounder,
scup, and/or black sea bass permit in
2005. However, the more immediate
impact of this rule will likely be felt by
the 906 vessels that actively participated
in these fisheries (i.e., landed these
species) in 2005.
The Council estimated the total
revenues derived from all species
landed by each vessel during calendar
year 2005 to determine a vessel’s
dependence and revenue derived from a
particular species. This estimate
provided the base from which to
compare the effects of the proposed
quota changes from 2006 to 2007.
The analysis of the harvest limits in
Alternative 1 (the Council’s preferred
alternative) indicated that these harvest
levels would result in revenue losses of
less than 5 percent for 34 vessels and
greater than or equal to 5 percent for 859
vessels. More specifically, vessels are
projected to incur revenue reductions as
follows: No change, 13 vessels; 5–9
percent, 104 vessels; 10–19 percent, 755
vessels; 20 percent or greater, 0 vessels.
Most commercial vessels showing
revenue reduction of greater than 5
percent are concentrated in MA, RI, NY,
NJ, and NC. The Council also examined
the level of ex-vessel revenues for the
impacted vessel to assess further
impacts. While the analysis presented
above indicates that in relative terms a
large number of vessels (859) are likely
to experience revenue reductions of
more than 5 percent, dealer data show
that a large proportion of those vessels
(296 vessels, or 34 percent) had small
gross sales (less than $1,000), thus
indicating that the dependence on
fishing is likely very small.
The Council also analyzed changes in
total gross revenue that would occur as
a result of the quota alternatives.
Alternative 1 would decrease total
summer flounder and black sea bass
revenues by approximately $3.72
million and $1.80 million, respectively,
relative to expected revenues earned
from the 2006 quotas. No changes in
scup revenues are expected in 2007
relative to 2006 since the proposed scup
quota under Alternative 1 is identical to
quota in place in 2006.
The overall reduction in ex-vessel
gross revenue associated with the
potential changes in quotas in 2007
versus 2006 is approximately $5.52
million (in 2005 dollars) under
Alternative 1. Assuming that the
decrease in total ex-vessel gross revenue
associated with the proposed rule for
each fishery is distributed equally
among the vessels that landed those
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Jkt 211001
species in 2005 (the last full year of data
availability), the average decrease in
gross revenue per vessel associated with
the preferred quota would be $4,960 for
summer flounder and $3,197 for black
sea bass. The total average gross revenue
reduction for vessels that land both
summer flounder and black sea bass
would then be $8,157. No revenue
reductions are expected for scup. The
number of vessels landing summer
flounder, scup, and black sea bass in
2005 was 750, 439, and 563,
respectively.
The predicted changes in ex-vessel
gross revenues associated with the
potential changes in quotas in 2007
versus 2006 assumed static 2005 prices
(summer flounder--$1.70/lb; scup-$0.75/lb; and black sea bass--$2.54/lb).
However, if prices for these species
change as a consequence of changes in
landings, then the associated revenue
changes could be different than those
estimated above, and could mitigate
some of the revenue reductions
associated with lower quantities of
quota available under this alternative.
The analysis of the harvest limits of
Alternative 2 (i.e., the most restrictive
harvest limits) indicated that all 906
vessels would incur revenue losses
equal to or greater than 5 percent. More
specifically, vessels are projected to
incur revenue reductions as follows: 5–
9 percent, 0 vessels; 10–19 percent, 0
vessels; 20–29 percent, 24 vessels; 30–
39 percent, 180 vessels; 40–49 percent,
31 vessels; and greater or equal to 50
percent, 671 vessels. The majority of the
revenue losses of 50 percent or higher
are attributed to quota reductions
associated with the summer flounder
fishery. Further examination shows that
311 of the impacted vessels (34 percent)
had gross sales of $1,000 or less and 491
of the impacted vessels (54 percent) had
gross sales of $10,000 or less, thus likely
indicating that the dependence on these
fisheries for some of these vessels is
very small. As in Alternative 1, most
commercial vessels showing revenue
reduction are concentrated in MA, RI,
NY, NJ, and NC.
Alternative 2 was estimated to
decrease total summer flounder, scup,
and black sea bass revenues by
approximately $18.28 million, $2.27
million and $3.64 million respectively,
relative to expected revenues earned
from the 2006 quotas. The overall
reduction in ex-vessel gross revenue
associated with the potential changes in
quotas in 2007 versus 2006 is
approximately $24.19 million (in 2005
dollars) under Alternative 2. Assuming
that the decrease in total ex-vessel gross
revenue associated with the proposed
rule for each fishery is distributed
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62981
equally among the vessels that landed
those species in 2005 (the last full year
of data availability), the average
decrease in gross revenue per vessel
associated with the Alternative 2 quota
would be $24,373 for summer flounder,
$5,170 for scup and $6,465 for black sea
bass. The total average gross revenue
reduction for vessels that land summer
flounder, scup and black sea bass would
then be $36,008. The number of vessels
landing summer flounder, scup, and
black sea bass in 2005 was 750, 439, and
563, respectively.
The predicted changes in ex-vessel
gross revenues associated with the
potential changes in quotas in 2007
versus 2006 assumed static 2005 prices
(summer flounder--$1.70/lb; scup-$0.75/lb; and black sea bass--$2.54/lb).
However, if prices for these species
change as a consequence of changes in
landings, then the associated revenue
changes could be different than those
estimated above, and could mitigate
some of the revenue reductions
associated with lower quantities of
quota available under this alternative.
The analysis of the harvest limits in
Alternative 3 (i.e., the least restrictive
harvest limits) indicated that these
harvest levels would result in revenue
increases for 488 vessels and losses of
less than 5 percent for 418 vessels. As
in the analysis for Alternative 1, it is
likely that a large proportion of the
impacted vessels are likely to have
small gross sales (less than $1,000), thus
indicating that the dependence on these
fisheries is likely very small.
Alternative 3 was estimated to
increase total summer flounder, scup
and black sea bass revenues by
approximately $0.03 million, $0.15
million and $0.08 million respectively,
relative to expected revenues earned
from the 2006 quotas (assuming the
entire quotas are landed).
The overall increase in ex-vessel gross
revenue associated with the potential
changes in quotas in 2007 versus 2006
is approximately $0.26 million (in 2005
dollars) under Alternative 3. Assuming
that the increase in total ex-vessel gross
revenue associated with the proposed
rule for each fishery is distributed
equally among the vessels that landed
those species in 2005 (the last full year
of data availability), the average increase
in gross revenue per vessel associated
with the Alternative 3 quota would be
$40 for summer flounder, $342 for scup
and $142 for black sea bass. The total
average gross revenue reduction for
vessels that land all three species would
then be $524. The number of vessels
landing summer flounder, scup, and
black sea bass in 2005 was 750, 439, and
563, respectively.
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The predicted changes in ex-vessel
gross revenues associated with the
potential changes in quotas in 2007
versus 2006 assumed static 2005 prices
(summer flounder--$1.70/lb; scup-$0.75/lb; and black sea bass--$2.54/lb).
However, if prices for these species
change as a consequence of changes in
landings, then the associated revenue
changes could be different than those
estimated above, and could mitigate
some of the revenue reductions
associated with lower quantities of
quota available under this alternative.
The NMFS analysis of the harvest
limits in Alternative 5 indicate that
these harvest levels would result in
revenue losses of less than 5 percent for
548 vessels and greater than or equal to
5 percent for 369 vessels (with a total of
917 active vessels for 2005). More
specifically, vessels are projected to
incur revenue reductions as follows: 5–
9 percent, 86 vessels; 10–19 percent,
149 vessels; 20–29 percent, 70 vessels;
and 30–39 percent, 64 vessels. As in
Alternative 1, most commercial vessels
showing revenue reduction are
concentrated in MA, RI, NY, NJ, and
NC.
The overall decrease in gross revenue
associated with the reduced quotas in
2007 compared to expected landings
levels in 2006 is approximately
$11,414,200 (in 2006 dollars) under
Alternative 5. By species, Alternative 5
would decrease total summer flounder,
scup and black sea bass revenues by
$9.68 million, $0.51 million and $1.22
million, respectively. If the decreases
are assumed to be distributed equally
among the vessels that landed those
species in 2005 (the last full year of data
availability), the average decrease in
gross revenue per vessel associated with
Alternative 5 would be $12,810 for
summer flounder, $1,145 for scup and
$2,125 for black sea bass. The averages
are additive so for vessels that land all
three species the average gross revenue
reduction is estimated at $16,080. The
number of vessels landing summer
flounder, scup, and black sea bass in
2005 was determined by NMFS to be
756, 448, and 574, respectively.
In the NMFS analysis, a pricequantity equation was used to predict
how reductions in summer flounder
landings affect ex-vessel prices. The
average nominal ex-vessel price per
pound for summer flounder was
estimated to be $1.79 in 2006 (assuming
the entire TAL will be landed) and was
estimated to increase to $1.91 in 2007
under Alternative 5 in response to
reduced landings levels. To compare
projected summer flounder revenues
under Alternative 5 to 2006 levels, the
2007 average ex-vessel price per pound
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($1.91) was converted to its 2006
inflation adjusted value of $1.86. For
scup and black sea bass, it was assumed
that the price-quantity relationships will
remain constant under Alternative 5.
Although to account for the effect of
rising seafood prices, inflation adjusted
2006 average ex-vessel prices per pound
were calculated for both scup ($0.77)
and black sea bass ($2.60) in the
analysis.
The NMFS analysis of the harvest
limits in Alternative 6 indicated that
these harvest levels would result in
revenue losses of less than 5 percent for
542 vessels and greater than or equal to
5 percent for 375 vessels (with a total of
917 active vessels for 2005). More
specifically, vessels are projected to
incur revenue reductions as follows: 5–
9 percent, 83 vessels; 10–19 percent,
145 vessels; 20–29 percent, 64 vessels;
30–39 percent, 52 vessels; and 40–49
percent, 31 vessels. As in Alternative 1,
most commercial vessels showing
revenue reduction are concentrated in
MA, RI, NY, NJ, and NC.
The overall decrease in gross revenue
associated with the reduced quotas in
2007 compared to expected landings
levels in 2006 is approximately
$12,533,500 (in 2006 dollars) under
Alternative 6. By species, Alternative 6
would decrease total summer flounder,
scup and black sea bass revenues by
$10.8 million, $0.51 million and $1.22
million, respectively. If the decreases
are assumed to be distributed equally
among the vessels that landed those
species in 2005 (the last full year of data
availability), the average decrease in
gross revenue per vessel associated with
Alternative 6 would be $14,290 for
summer flounder, $1,145 for scup and
$2,125 for black sea bass. The averages
are additive so for vessels that land all
three species the average gross revenue
reduction is estimated at $17,560. The
number of vessels landing summer
flounder, scup, and black sea bass in
2005 was determined by NMFS to be
756, 448, and 574, respectively.
In the NMFS analysis, a pricequantity equation was used to predict
how reductions in summer flounder
landings affect ex-vessel prices. The
average nominal ex-vessel price per
pound for summer flounder was
estimated to be $1.79 in 2006 (assuming
the entire TAL will be landed) and was
estimated to increase to $1.93 in 2007
under Alternative 6 in response to
reduced landings levels. To compare
projected summer flounder revenues
under Alternative 6 to 2006 levels, the
2007 average ex-vessel price per pound
($1.93) was converted to its 2006
inflation adjusted value of $1.88. For
scup and black sea bass, it was assumed
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that the price-quantity relationships will
remain constant under Alternative 6.
Although to account for the effect of
rising seafood prices, inflation adjusted
2006 average ex-vessel prices per pound
were calculated for both scup ($0.77)
and black sea bass ($2.60) in the
analysis.
For the analysis of the alternative
recreational harvest limits, the 2007
recreational harvest limits were
compared with previous years through
2005, the most recent year with
complete recreational data. Landings
statistics from the last several years
show that recreational summer flounder
landings have generally exceeded the
recreational harvest limits, ranging from
a 5–percent overage in 1993 to a 122–
percent overage in 2000. In 2003,
recreational landings were 11.64 million
lb (5,280 mt), 25 percent above the
recreational harvest limit of 9.28 million
lb (4,209 mt). In 2004, recreational
landings were 10.8 million lb (4,899
mt), 4 percent below the recreational
harvest limit of 11.21 million lb (5,085
mt). In 2005, recreational landings were
10.02 million lb (4,545 mt), 2 percent
below the recreational harvest limit of
11.98 million lb (5,085 mt).
The Alternative 1 summer flounder
2007 recreational harvest limit (adjusted
for RSA) of 7.73 million lb (3,506 mt),
would be a 17–percent decrease from
the 2006 recreational harvest limit of
9.29 million lb (4,214 mt), and would
represent a 23–percent decrease from
2005 landings. The 2007 summer
flounder Alternative 2 recreational
harvest limit of 2.03 million lb (921 mt)
would be 78 percent lower than the
2006 recreational harvest limit, and
would represent an 80–percent decrease
from 2005 recreational landings. The
2007 summer flounder Alternative 3
(status quo) recreational harvest limit of
9.21 million lb (4,178 mt) would be a
less than 1–percent decrease from the
2006 recreational harvest limit (due to
the preliminary summer flounder RSA
for 2005) and would represent an 8–
percent decrease from 2005 recreational
landings. The 2007 summer flounder
Alternative 5 recreational harvest limit
of 5.49 million lb (2,490 mt) would be
41 percent lower than the 2006
recreational harvest limit, and would
represent a 45–percent decrease from
2005 recreational landings. The 2007
summer flounder Alternative 6
recreational harvest limit of 5.04 million
lb (2,286 mt) would be 46 percent lower
than the 2006 recreational harvest limit,
and would represent a 50–percent
decrease from 2005 recreational
landings.
Scup recreational landings declined
over 89 percent for the period 1991 to
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1998, then increased by 517 percent
from 1998 to 2000. The number of
fishing trips also declined over 73
percent from 1991 to 1998, and then
increased by 127 percent from 1998 to
2000. The decrease in the recreational
fishery in the 1990s occurred both with
and without any recreational harvest
limits, and it is perhaps a result of the
stock being over-exploited and at a low
biomass level during that period. In
addition, it is possible that party/charter
boats may have targeted other species
that were relatively more abundant than
scup (e.g., striped bass), thus accounting
for the decrease in the number of fishing
trips in this fishery in the 1990s. In
2003, recreational landings were 8.43
million lb (3,824 mt), 110 percent above
the recreational harvest limit of 4.01
million lb (1,819 mt) and the highest for
the 1991 through 2005 period. In 2004
and 2005, recreational landings were
4.41 million lb (2,000 mt) and 2.38
million lb (1,080 mt), 10 percent above,
and 40 percent below, respectively, the
recreational harvest limit of 4.01 million
lb (1,819 mt) for 2004 and 3.96 million
lb (1,796 mt) for 2005.
Under Alternative 1, the scup
recreational harvest limit for 2007
would be 3.59 million lb (1,628 mt)),
13.5 percent below the 2006 recreational
harvest limit of 4.15 million lb (1,882
mt), and 51 percent above the 2005
recreational landings. The scup
recreational harvest limit of 2.74 million
lb (1,243 mt) for 2007 under
Alternatives 2, 5, and 6 would be 34
percent less than the 2006 recreational
harvest limit, and 15 above 2005
recreational landings. The Alternative 3
scup recreational harvest limit of 3.65
million lb (1,656 mt) for 2007 would be
a 12–percent decrease from the 2006
recreational harvest limit and would
represent a 53–percent increase over
2005 recreational landings.
Black sea bass recreational landings
have shown a slight upward trend from
1991 through 1997, and increased
substantially in 2002 to 4.35 million lb
(1,973 mt). In 2003, 2004, and 2005,
recreational landings were 3.29 million
lb (1,492 mt), 1.67 million lb (757 mt),
and 1.77 million lb (802 mt),
respectively.
Under Alternative 1, the black sea
bass recreational harvest limit for 2007
would be 3.25 million lb (1,474 mt)), 19
percent below the 2006 recreational
harvest limit of 3.99 million lb (1,810
mt), and 82 percent above the 2005
recreational landings. The black sea bass
recreational harvest limit of 2.48 million
lb (1,125 mt) for 2007 under
Alternatives 2, 5, and 6 would be 38
percent less than the 2006 recreational
harvest limit, and 40 percent above 2005
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Jkt 211001
recreational landings. The Alternative 3
black sea bass recreational harvest limit
of 4.01 million lb (1,819 mt) for 2007
would be a less than 1–percent increase
from the 2006 recreational harvest limit
and would represent a 127–percent
increase over 2005 recreational
landings.
If Alternative 1, 2, 5, or 6 is
implemented, more restrictive summer
flounder management measures (i.e.,
lower possession limits, larger
minimum size limits, and/or shorter
open seasons) may be required to
prevent anglers from exceeding the 2007
recreational harvest limit. If 2007 scup
and black sea bass landings are similar
to those for 2006, more restrictive limits
(i.e., lower possession limits, greater
minimum size limits, and/or shorter
seasons) may not be necessary to
prevent anglers from exceeding this
recreational harvest limit under any of
the alternatives.
While it is likely that proposed
management measures under
Alternative 6 would restrict the
recreational fishery for 2007, and that
these measures may cause some
decrease in recreational satisfaction,
there is neither behavioral or demand
data available to estimate how sensitive
party/charter boat anglers might be to
proposed fishing regulations. Currently,
the market demand for this sector is
relatively stable. Summer flounder
recreational trips averaged 5.1 million
for the 1991 to 2005 period, ranging
from 3.8 million in 1992 to 6.1 million
in 2001. For 2002 through 2005,
summer flounder recreational fishing
trips were estimated at 4.6 million, 5.6
million, 5.1 million, and 5.8 million per
year, respectively. Scup recreational
trips have shown a slight upward trend
from the early 1990s to the early 2000s,
ranging from approximately 199,000
trips in 1997 to 972,000 trips in 2003,
with an average of approximately
454,000 trips per year for the 1991
through 2005 period. For 2004 and
2005, scup recreational fishing trips
were estimated at approximately
568,000 and 458,000, respectively.
Black sea bass recreational fishing trips
have averaged approximately 247,000
per year for the 1991 through 2005
period, ranging from approximately
136,000 trips in 1999, to 311,000 trips
in 1997. In 2005, recreational trips for
black sea bass numbered approximately
166,000, the third lowest value in the
1991 through 2005 time series.
It is unlikely that these measures
would result in any substantive
decreases in the demand for party/
charter boat trips. It is likely that party/
charter anglers would target other
species when faced with potential
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62983
reductions in the amount of summer
flounder, scup, and black sea bass that
they are allowed to catch. The Council
intends to recommend specific
measures to attain the 2007 summer
flounder recreational harvest limit in
December 2006, and will provide
additional analysis of the measures
upon submission of its
recommendations in early 2007.
In summary, the proposed
specifications represent substantially
lower 2007 TALs for summer flounder,
scup, and black sea bass. The proposed
specifications were chosen because they
allow for the maximum level of
commercial and recreational landings,
while allowing the NMFS to meet its
legal requirements under the MagnusonStevens Act and while achieving the
objectives of the FMP. The summer
flounder TAL was chosen to allow for
rebuilding of the stock by 2010 and to
acknowledge the pattern of fishing
mortality rate underestimation. Due to
the level of uncertainty in the scup and
black sea bass stock assessments and to
the recent stock indices, the scup and
black sea bass TALs were selected as
risk-averse management alternatives
intended to constrain 2007 landings to
recent (2005) levels. The proposed 2007
adjusted commercial quotas for summer
flounder, scup, and black sea bass for
the year 2007 are 46 percent, 34 percent,
and 38 percent lower, respectively,
relative to the adjusted quotas for year
2006. The proposed recreational harvest
limits (adjusted for RSA) would be 45, 25-, and 38–percent lower than the
adjusted recreational harvest limits for
year 2006.
The proposed commercial scup
possession limits for Winter I (30,000 lb
(13.6 mt) per trip, to be reduced to 1,000
lb (454 kg) upon attainment of 80
percent of the Winter I quota) and
Winter II (2,000 lb (907 kg) per trip) and
the Winter II possession limit-torollover amount ratio were chosen as an
appropriate balance between the
economic concerns of the industry (i.e.,
landing enough scup to make the trip
economically viable) and the need to
ensure the equitable distribution of the
quota over each period. The proposed
Winter I possession limit specifically
coordinates with the 30,000–lb (13.6–
mt) landing limits per 2-week period
recommended by the Commission
(beginning in 2005) to be implemented
by most states, while satisfying concerns
about enforcement of possession limits.
Continuation of these possession limits
and ratios is not expected to result in
changes to the economic or social
aspects of the fishery relative to 2006.
The commercial portion of the
summer flounder RSA preliminary
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allocation in the proposed
specifications, if made available to the
commercial fishery, could be worth as
much as $397,280 dockside, based on a
2005 ex-vessel price of $1.70/lb (or
$439,344 based on NMFS’ inflation
adjusted summer flounder price
estimate of $1.88/lb). Assuming an
equal reduction in fishing opportunity
among all active vessels (i.e., the 750
vessels that landed summer flounder in
2005), this could result in a per-vessel
potential revenue loss of approximately
$530 (or $581 based on NMFS’ 2006
summer flounder price and 2005 active
vessel estimate). Changes in the summer
flounder recreational harvest limit as a
result of the RSA are not expected to be
significant as the deduction of RSA from
the TAL would result in a relatively
marginal decrease in the recreational
harvest limit from 5.2 million lb (2,359
mt) to 5.0 million lb (2,268 mt). Because
this is a marginal change, it is unlikely
that the recreational possession, size, or
seasonal limits would change as the
result of the RSA allocation.
The commercial scup RSA allocation,
if made available to the commercial
fishery, could be worth as much as
$210,600 dockside, based on a 2005 exvessel price of $0.75/lb (or $216,216
based on NMFS’ inflation adjusted scup
price estimate of $0.77/lb). Assuming an
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Jkt 211001
equal reduction in fishing opportunity
for all active commercial vessels (i.e.,
the 439 vessels that landed scup in
2005), this could result in a loss of
potential revenue of approximately $480
per vessel (or $482 based on NMFS’
2006 scup price and 2005 active vessel
estimate). The deduction of RSA from
the TAL results in a relatively marginal
decrease in the recreational harvest
limit from 2.64 million lb (1,197 mt) to
2.56 million lb (1,162 mt). It is unlikely
that scup recreational possession, size,
or seasonal limits would change as the
result of the RSA allocation.
The commercial portion of the black
sea bass RSA, if made available to the
commercial fishery, could be worth as
much as $186,690 dockside, based on a
2005 ex-vessel price of $2.54/lb (or
$191,100 based on NMFS’ inflation
adjusted scup price estimate of $2.60/
lb). Assuming an equal reduction in
fishing opportunity for all active
commercial vessels (i.e., the 563 vessels
that caught black sea bass in 2005), this
could result in a loss of approximately
$332 per vessel (or $333 based on
NMFS’ 2006 black sea bass price and
2005 active vessel estimate). The
deduction of RSA from the TAL would
result in a relatively marginal decrease
in recreational harvest from black sea
bass recreational harvest limit from 2.55
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million lb (1,157 mt) to 2.48 million lb
(1,122 mt). It is unlikely that the black
sea bass possession, size, or seasonal
limits would change as the result of this
RSA allocation.
Overall, long-term benefits are
expected as a result of the RSA program.
The results of these projects will
provide needed information on highpriority fisheries management issues
related to Mid-Atlantic fisheries
management. If the total amount of
quota set-aside is not awarded for any
of the three fisheries, the unused setaside amount will be restored to the
appropriate fishery’s TAL. It should also
be noted that fish harvested under the
RSAs would be sold, and the profits
would be used to offset the costs of
research. As such, total gross revenue to
the industry would not decrease if the
RSAs are utilized.
There are no new reporting or
recordkeeping requirements contained
in any of the alternatives considered for
this action.
Dated: October 23, 2006.
Samuel D. Rauch III,
Deputy Assistant Administrator for
RegulatoryPrograms, National Marine
Fisheries Service.
[FR Doc. 06–8932 Filed 10–24–06; 11:07 am]
BILLING CODE 3510–22–S
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Agencies
[Federal Register Volume 71, Number 208 (Friday, October 27, 2006)]
[Proposed Rules]
[Pages 62972-62984]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 06-8932]
[[Page 62972]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 648
RIN 0648-AT60
[Docket No. 061020273-6273-01; I.D. 101606A]
Fisheries of the Northeastern United States; Summer Flounder,
Scup, and Black Sea Bass Fisheries; 2007 Summer Flounder, Scup, and
Black Sea Bass Specifications; 2007 Research Set-Aside Projects
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Proposed specifications; request for comments.
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SUMMARY: NMFS proposes specifications for the 2007 summer flounder,
scup, and black sea bass fisheries. The implementing regulations for
the Summer Flounder, Scup, and Black Sea Bass Fishery Management Plan
(FMP) require NMFS to publish specifications for the upcoming fishing
year for each of the species and to provide an opportunity for public
comment. The intent of this action is to establish harvest levels that
assure that the target fishing mortality rates (F) or exploitation
rates specified for these species in the FMP are not exceeded and to
allow for rebuilding of the stocks in accordance with the Magnuson-
Stevens Fishery Conservation and Management Act (Magnuson-Stevens Act).
NMFS has conditionally approved four research projects for the harvest
of the portion of the quota that has been recommended by the Mid-
Atlantic Fishery Management Council (Council) to be set aside for
research purposes. In anticipation of receiving applications for
Experimental Fishing Permits (EFPs) to conduct this research, the
Assistant Regional Administrator for Sustainable Fisheries, Northeast
Region, NMFS (Assistant Regional Administrator), has made a preliminary
determination that the activities authorized under the EFPs issued in
response to the approved Research Set-Aside (RSA) projects would be
consistent with the goals and objectives of the FMP. However, further
review and consultation may be necessary before a final determination
is made to issue any EFP.
DATES: Comments must be received on or before November 17, 2006.
ADDRESSES: You may submit comments by any of the following methods:
E-mail: FSB2007@noaa.gov. Include in the subject line the
following identifier: ``Comments on 2007 Summer Flounder, Scup, and
Black Sea Bass Specifications.''
Federal e-Rulemaking portal: https://www.regulations.gov.
Mail and hand delivery: Patricia A. Kurkul, Regional
Administrator, NMFS, Northeast Regional Office, One Blackburn Drive,
Gloucester, MA 01930. Mark the outside of the envelope: ``Comments on
2007 Summer Flounder, Scup, and Black Sea Bass Specifications.''
Fax: (978) 281-9135.
Copies of the specifications document, including the Environmental
Assessment, Regulatory Impact Review, and Initial Regulatory
Flexibility Analysis (EA/RIR/IRFA) and other supporting documents for
the specifications are available from Daniel Furlong, Executive
Director, Mid-Atlantic Fishery Management Council, Room 2115, Federal
Building, 300 South Street, Dover, DE 19901-6790. Copies of the
supplemental economic analysis are available from Patricia A. Kurkul,
Regional Administrator, Northeast Region, National Marine Fisheries
Service, One Blackburn Drive, Gloucester, MA 01930-2298. These
documents are also accessible via the Internet at https://www.nero.noaa.gov.
FOR FURTHER INFORMATION CONTACT: Sarah McLaughlin, Fishery Policy
Analyst, (978) 281-9279.
SUPPLEMENTARY INFORMATION:
Background
The summer flounder, scup, and black sea bass fisheries are managed
cooperatively by the Council and the Atlantic States Marine Fisheries
Commission (Commission), in consultation with the New England and South
Atlantic Fishery Management Councils. The management units specified in
the FMP include summer flounder (Paralichthys dentatus) in U.S. waters
of the Atlantic Ocean from the southern border of North Carolina (NC)
northward to the U.S./Canada border, and scup (Stenotomus chrysops) and
black sea bass (Centropristis striata) in U.S. waters of the Atlantic
Ocean from 35[deg]13.3' N. lat. (the latitude of Cape Hatteras
Lighthouse, Buxton, NC) northward to the U.S./Canada border.
Implementing regulations for these fisheries are found at 50 CFR part
648, subpart A (General Provisions), subpart G (summer flounder),
subpart H (scup), and subpart I (black sea bass).
The regulations outline the process for specifying the annual
commercial quotas and recreational harvest limits for the summer
flounder, scup, and black sea bass fisheries, as well as other
management measures (e.g., mesh requirements, minimum fish sizes, gear
restrictions, possession restrictions, and area restrictions) for these
fisheries. The measures are intended to achieve the annual targets set
forth for each species in the FMP, specified either as an F or an
exploitation rate (the proportion of fish available at the beginning of
the year that are removed by fishing during the year). Once the catch
limits are established, they are divided into quotas based on formulas
contained in the FMP.
As required by the FMP, a Monitoring Committee for each species,
made up of members from NMFS, the Commission, and both the Mid-Atlantic
and New England Fishery Management Councils, reviews the best available
scientific information and recommends catch limits and other management
measures that will achieve the target F or exploitation rate for each
fishery. Consistent with the implementation of Framework Adjustment 5
to the FMP (69 FR 62818, October 28, 2004), each Monitoring Committee
meets annually to recommend the Total Allowable Landings (TAL), unless
the TAL has already been established for the upcoming calendar year as
part of a multiple-year specification process, provided that new
information does not require a modification to the multiple-year
quotas. Further, the TALs may be specified in any given year for the
following 1, 2, or 3 years. The Council is not obligated to specify
multi-year TALs, but is able to do so, depending on the information
available and the status of the fisheries.
The Council's Demersal Species Committee and the Commission's
Summer Flounder, Scup, and Black Sea Bass Management Board (Board)
consider the Monitoring Committees' recommendations and any public
comment and make their own recommendations. While the Board action is
final, the Council's recommendations must be reviewed by NMFS to assure
that they comply with FMP objectives. The Council and Board made their
recommendations, with the exception of Board recommendations for the
2007 summer flounder fishery, at a joint meeting held August 1-3, 2006.
The Board delayed its action regarding a summer flounder TAL
recommendation until its October 22-26, 2006, meeting.
Explanation of RSA
In 2001, regulations were implemented under Framework Adjustment 1
to the FMP to allow up to
[[Page 62973]]
3 percent of the TAL for each species to be set aside each year for
scientific research purposes. For the 2007 fishing year, a Request for
Proposals was published to solicit research proposals based upon the
research priorities that were identified by the Council (70 FR 76253,
December 23, 2005). Four applicants were notified in August 2005 that
their research proposals had received favorable preliminary review. For
informational purposes, these proposed specifications include a
statement indicating the amount of quota that has been preliminarily
set aside for research purposes (3 percent of the TAL for each fishery,
as recommended by the Council and Board), and a brief description of
the RSA projects, and the amount of RSA requested for each project. The
RSA amounts may be adjusted, following consultation with RSA
applicants, in the final rule establishing the 2007 specifications for
the summer flounder, scup, and black sea bass fisheries. If the total
amount of RSA is not awarded, NMFS will publish a document in the
Federal Register to restore the unused amount to the applicable TAL.
For 2007, four RSA projects have been conditionally approved by
NMFS and are currently awaiting a notice of award. These projects
collectively may be awarded the following amounts of RSA (3 percent of
the proposed TALs): 389,490 lb (177 mt) of summer flounder; 360,000 lb
(163 mt) of scup; and 150,000 lb (68 mt) of black sea bass. The
projects collectively also may be awarded up to 1,124,356 lb (510 mt)
of Loligo squid and 363,677 lb (165 mt) of bluefish.
The University of Rhode Island submitted a proposal to conduct a
fourth year of work in a fishery-independent scup survey that would
utilize unvented fish traps fished on hard bottom areas in southern New
England waters to characterize the size composition of the scup
population. Survey activities would be conducted from May 1 through
November 30, 2007, at 10 rocky bottom study sites located offshore,
where there is a minimal scup pot fishery and no active trawl fishery,
and at 2 scup spawning ground sites. Up to two vessels would conduct
the survey. Sampling would occur off the coasts of Rhode Island and
southern Massachusetts. Up to three vessels would harvest the RSA
during the period January 1 through December 31, 2007. The preliminary
RSA requested for this project is 2,000 lb (907 kg) of summer flounder;
40,000 lb (18 mt) of scup; and 30,000 lb (14 mt) of black sea bass.
The National Fisheries Institute (NFI) and Rutgers University
submitted a proposal to conduct a fifth year of work on a commercial
vessel-based trawl survey program in the Mid-Atlantic region that would
track the migratory behavior of selected recreationally and
commercially important species. Information gathered during this
project would supplement the NMFS finfish survey databases and improve
methods to evaluate how seasonal migration of fish in the Mid-Atlantic
influences stock abundance estimates. Up to two vessels would conduct
survey work in the Mid-Atlantic during January, March, May, and
November 2007, along up to eight offshore transects. The transects
would include six fixed offshore transects, one each near Alvin,
Hudson, Baltimore, Poor Man's, Washington, and Norfolk Canyons, and two
to three adaptive transects positioned within the Mid-Atlantic area
selected during a pre-cruise meeting with NFI, Rutgers University, and
the NMFS Northeast Fisheries Science Center (Center). Up to 15 1-
nautical mile tows would be conducted along each transect at depths
from 40 to 250 fathoms (73 to 457 m). Up to 25 vessels would harvest
the RSA during the period January 1 through December 31, 2007. The
preliminary RSA requested for the project is 223,140 lb (101 kg) of
summer flounder; 221,581 lb (101 mt) of scup; 61,500 lb (28 mt) of
black sea bass; 281,059 lb (127 mt) of Loligo squid; and 363,677 lb
(165 mt) of bluefish.
The Cornell Cooperative Extension of Suffolk County submitted a
proposal to evaluate summer flounder discard mortality in the bottom
trawl fishery. The project is intended to improve and enhance fishery
information relative to discard mortality of summer flounder in the
bottom trawl fishery. Trawl-caught summer flounder, both legal and sub-
legal size, would be measured, tagged, and kept in a live holding pen
(net pen) for mortality monitoring. Mortality would be monitored on a
weekly basis and fish would be released with tags after 2 weeks.
Extended mortality and migration information would be collected upon
recapture of tagged fish. One inshore day trip would be made every 14
to 17 days from May to September for a total of 10 day trips. Overall,
with 120 fish taken on each trip, a total of 1,200 fish would be
collected from commercial vessels during the project. The research
trips would be made aboard 15 commercial vessels (vessels of
opportunity) engaged in the mixed trawl fishery, and would be conducted
inshore along the coast of southern Long Island from Jones Inlet to
Montauk Point, reaching depths of 240 ft (73 m). Areas sampled would
include NMFS statistical areas 611, 612, 613, and 539. Vessels would be
compensated to make three specific tows for summer flounder to assess
trawl mortality. Duration of these tows would be 1, 2, and 3 hours. An
additional 25 vessels would harvest the RSA amounts allocated to the
project over the course of the fishing year. The preliminary RSA
requested for the project is 178,000 lbs (81 mt) of summer flounder.
The National Fisheries Institute (NFI) and Rutgers University
submitted a proposal to conduct studies on bycatch reduction and gear
development in the Mid-Atlantic through evaluation of optimal codend
mesh size in the Loligo squid fishery. The project would evaluate the
performance of intermediate codend mesh sizes above the present legal
size of 1.875 inches (4.8 cm) and below 2.5 inches (6.35 cm), e.g. mesh
sizes of 2.125 inches (5.4 cm) and 2.25 inches (5.7 cm). The
researchers would also attempt to determine the influence of these
intermediate mesh sizes on the catch of other species such as
butterfish, silver hake, and accompanying bycatch species as well as
Loligo squid measuring below market size (4 inches (10.2 cm)). The
project would use two similar vessels in the 75- to 100-ft (23- to 30-
m) range to test different mesh sizes in squid nets under commercial
use. The exact number of tows would depend on the duration of each tow,
which would be determined by the vessel captain during fishing. The
research would involve a total of 108 to 144 tows, each lasting
approximately 2-3 hours, and would take place in February and/or March
2007 near the Hudson Canyon. Approximately 25 vessels would harvest the
RSA amounts allocated to the project over the course of the fishing
year. The preliminary RSA requested for the project is 163,633 lb (74
mt) of summer flounder; 269,305 lb (122 mt) of scup; 40,358 lb (18 mt)
of black sea bass; and 331,000 lb (150 mt) of Loligo squid.
Regulations under the Magnuson-Stevens Act require publication of
this notification to provide interested parties the opportunity to
comment on applications for proposed EFPs.
Explanation of Quota Adjustments Due to Quota Overages
This action proposes commercial quotas based on the proposed TALs
and Total Allowable Catches (TACs) and the formulas for allocation
contained in the FMP. In 2002, NMFS published final regulations to
implement a regulatory amendment (67 FR 6877, February 14, 2002) that
revised the way in which the commercial quotas for summer
[[Page 62974]]
flounder, scup, and black sea bass are adjusted if landings in any
fishing year exceed the quota allocated (thus resulting in a quota
overage). If NMFS approves a different TAL or TAC at the final
specifications stage, the commercial quotas will be recalculated based
on the formulas in the FMP. Likewise, if new information indicates that
overages have occurred and deductions are necessary, NMFS will publish
notice of the adjusted quotas in the Federal Register. NMFS anticipates
that the information necessary to determine whether overage deductions
are necessary will be available by the time the final specifications
are published. The commercial quotas contained in these proposed
specifications for summer flounder, scup, and black sea bass do not
reflect any deductions for overages. The final specifications, however,
will contain quotas that have been adjusted consistent with the
procedures described above.
Summer Flounder
The Center's Southern Demersal Working Group met in May 2005 to
address the terms of reference for Stock Assessment Workshop (SAW) 41.
The Stock Assessment Review Committee (SARC) accepted the 2005 stock
assessment update as the basis for management advice, and also accepted
the Demersal Working Group's recommended updated biological reference
point values as follows: Fmsy=Fmax=0.276; MSY=42
million lb (22,000 mt), and Bmsy=204 million lb (92,532 mt).
Fmsy is the fishing mortality rate that, if applied
constantly, would result in maximum sustainable yield (MSY). Fmax
is the level of fishing mortality that produces maximum yield per
recruit. When F > Fmax, overfishing is considered to be
occurring, and when B<\1/2\ Bmsy, the stock is considered
overfished.
The Southern Demersal Working Group met on June 20, 2006, to update
the summer flounder assessment through 2005/2006 based on the latest
research survey and fisheries catch data available. This was a routine
annual update, as called for by the FMP, and was based on the same
population model as used in recent years. Key results of the update
were as follows: Overfishing is occurring (i.e., F > Fmax).
Almost all of the full-age structure state and Federal survey indices
used to update the assessment have dropped since 2003. Mean fish weight
has decreased, and this has contributed to increased fishing mortality,
as more fish are taken by weight for a given catch level. The 2005 F
was estimated to have been 0.53, a significant decline from the 1.32
estimated for 1994, but well above the threshold F of 0.276. The stock
was not determined to be overfished and was estimated to be just above
the biomass threshold. Total stock biomass (TSB) increased
substantially during the 1990s and through 2004, but decreased slightly
since 2004, and was estimated to be 105 million lb (47,627 mt) on
January 1, 2006, just over the biomass threshold (\1/2\Bmsy)
of 102 million lb (46,266 mt)). Spawning stock biomass (SSB) also
increased during the 1990s through 2004 (to 72 million lb (32,659 mt)
in 2004), before decreasing to 67 million lb (30,391 mt) in 2005.
Recruitment since 1988 was estimated to have improved, generally,
although the 2003 and 2005 year classes were estimated to have been
well below the median (33 million fish) at 24.5 million fish and 14.5
million fish, respectively.
It has been recognized since 1995 that the summer flounder stock
assessment model tends to underestimate F and overestimate stock
biomass and recruitment in the most recent years of the analysis
(typically for the previous 5 years), until those estimates stabilize
as new data are added to the analysis. For example, the 2006 stock
assessment update showed that the estimate for F2004 had
increased from last year's estimate of 0.4 to 0.46; and that the
estimate for F2005 was 0.53. This pattern is likely the
result of an underestimation of the true catch, due to discards and/or
unreported landings. The impact for management, given these persistent
retrospective patterns, is that, although the summer flounder stock
continues to increase, it is increasing at a lower rate than, and is
currently at a smaller size than, previously forecast. Because the
Magnuson-Stevens Act requires stocks to be rebuilt to a level that
produces MSY, it was clear from the 2006 stock assessment update that
additional rebuilding of these species is still required. For summer
flounder, the rebuilding period ends December 31, 2009.
The regulations state that the Council shall recommend, and NMFS
shall implement, measures (including the TAL) necessary to ensure, with
at least a 50-percent probability of success, that the applicable
specified F will not be exceeded. This requirement is also consistent
with a 2000 Federal Court Order (Natural Resources Defense Council v.
Daley, Civil No. 1:99 CV 00221 (JLG)) regarding the setting of the
summer flounder TAL. Through the course of the rebuilding period, NMFS
has set TALs estimated to have at least a 50-percent probability of not
exceeding Fmax.
For 2007, the Council's Summer Flounder Monitoring Committee
considered that a TAL of 19.9 million lb (9,026 mt) would meet the 50-
percent probability of success standard (based on the Southern Demersal
Working Group 2006 update), but recommended a TAL (13.88 million lb
(6,296 mt)) associated with an F of 0.185, i.e., a 33-percent reduction
of the Fmax (0.276), in order to account for the
retrospective pattern of F underestimation. In August 2006, the Council
and the Board discussed at length the Southern Demersal Working Group
2006 update, the TAL for 2007, and potential TALs for the remainder of
the rebuilding period. The Council considered the following TAL
options: (1) a 2007 TAL of 19.9 million lb (9,026 mt); (2) the Summer
Flounder Monitoring Committee's recommendation of 13.88 million lb
(6,296 mt) for 2007; (3) a 2007 TAL projected to result in rebuilding
of the summer flounder stock by 2010 (7.69 million lb (3,489 mt)); (4)
a 2007 TAL that would both allow for rebuilding by 2010 and account for
the retrospective F pattern (5.22 million lb (2,368 mt)); (5) a
constant TAL for 2007 through 2009 that would allow for rebuilding by
2010 (10.04 million lb (4,554 mt)); and (6) a constant TAL for 2007
through 2009 that would allow for rebuilding by 2010 and that corrects
for the retrospective pattern of F underestimation (6.72 million lb
(3,048 mt)). The Council focused discussion on a 2007 TAL of 19.9
million lb (9,026 mt).
During the August 2006 Council discussion of the feasibility of
achieving the biomass target, given recent recruitment levels, NMFS
offered to re-examine the biological reference point values based on
the use of the most recent scientific information available and on use
of a subset (rather than the full range) of recruitment input data.
Projections were to be re-run based on the revised reference points,
the current growth potential of the population, and the recent history
of reproductive effort (recruitment), and the results were to be peer-
reviewed. NMFS encouraged the Council to recommend a TAL for 2007, and
indicated that any new information resulting from the stock assessment
re-examination and the peer review thereof, if appropriate, would be
reflected in the proposed specifications. In the end, the Council
adopted a 2007 TAL of 19.9 million lb (9,026 mt), with 3 percent of the
TAL set aside for research. This TAL would represent a 16-percent
decrease for 2007 from the 2006 TAL of 23.59 million lb (10,700 mt).
After deducting the RSA, the TAL
[[Page 62975]]
would be divided into a commercial quota (60 percent) and a
recreational harvest limit (40 percent). The Board delayed its vote
until its October 22-26, 2006, meeting, to consider the updated
analyses.
NMFS's re-examination of the biological reference points, the peer
review of this work, and subsequent analysis stemming from the peer
review was completed in September 2006 and is documented in ``Summer
Flounder Assessment and Biological Reference Point Update for 2006.''
This update is available at https://www.nefsc.noaa.gov/nefsc/saw/2006FlukeReview/.
The Peer Review Panel's (Panel's) review did not result in any
change in the current stock status determinations of the summer
flounder stock. It confirmed that overfishing occurred throughout the
rebuilding period, and that F must be substantially lowered for 2007
through 2009 to allow for rebuilding by 2010. The stock continues to be
considered not overfished, but is still just slightly above the biomass
threshold. Table 1 summarizes and compares findings from the Southern
Demersal Working Group 2006 Update and the recent peer reviewed
assessment and biological reference point update.
Table 1. Comparison of the findings of the Southern Demersal Working Group 2006 Update) and the Peer Reviewed
Summer Flounder assessment and Biological Reference Point Update)
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Factor 2006 Assessment (June 2006) Update (September 2006)
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Fmax 0.276 0.280
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Frebuild 0.099 0.15
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F2005 0.528 0.407
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Overfishing Yes Yes
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.................................. ..................................
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R 33.11 million fish (median) 37 million fish (mean)
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.................................. ..................................
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Bmsyproxy TSB=204 million lb (92,645 mt) TSB (age 1 + fish) = 215 million
lb (97,430 mt)
SSB=197 million lb (89,411 mt)*
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Biomass threshold \1/2\TSB=102 million lb (46,323 \1/2\SSB=98.5 million lb (44,706
mt) mt)
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SSB2005 67 million lb (30,600 mt) 105 million lb (47,498 mt)
----------------------------------------------------------------------------------------------------------------
TSB2005 105 million lb (47,800 mt) (age 0+ 113 million lb (51,317 mt) (age 1+
fish) fish)
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Overfished No (52% of Bmsy) No (53% of Bmsy)
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.................................. ..................................
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MSY 42 million lb (19,072 mt) 47 million lb (21,444 mt)
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* Panel suggested use of SSB as Bmsy proxy in the future, but provided TSB information for comparison.
The Panel recommended several adjustments in the assessment. The
most important of these are that the stock condition be assessed using
SSB rather than TSB, and several changes in how the weight of fish not
yet Age 1 is used in the stock assessment model. With respect to the
Southern Demersal Working Group 2006 Update, the recently updated
analysis (which incorporated the Panel recommendations) lowered the
best estimate of Bmsy, raised Fmax slightly,
raised MSY, and raised the SSB estimates and lowered the F estimates
for 2000-2005. The annual F projected to allow for rebuilding to
SSBmax by 2010 (Frebuild) is currently estimated
to be 0.15. Should an F of 0.15 in the 2007 fishing year prove to be
inconsistent with allowing the stock to rebuild by 2010, based on the
results of the annual summer flounder stock assessment update in June
2007, NMFS would adjust the target F for 2008. Similar adjustment for
the 2009 target F would occur based on the June 2008 stock assessment
update, if necessary. Fishing at F=0.15 starting in 2007 is also
anticipated to rebuild the stock to within 1 percent of the Bmsy
proxy currently in the FMP (a TSB of 204 million lb (92,645 mt)) by
2010. The Panel acknowledged the retrospective pattern of F
underestimation (by 34 percent), biomass overestimation (by 12
percent), and recruitment overestimation (by 4 percent). The Panel made
no recommendation on how to adjust the analysis for this pattern, but
noted that it should be taken into account when setting management
targets.
At the October 10-12, 2006, Council meeting, following a
presentation of the Panel's findings, the Council voted to include a
provision to amend the summer flounder biomass target, based on the
updated, best available scientific information, in Amendment 14 to the
FMP, which is currently under Council development.
Projections indicate that fishing at a constant Fmax
level of 0.28 would result in not achieving the biomass target until
after 2022. As indicated above, commensurate with the objectives of the
FMP, reduced TALs will be needed for 2007 through 2009 to achieve the
biomass target by the end of the 10-year rebuilding period for summer
flounder. The best available scientific information indicates that a
TAL of 14.156 million lb (6,421 mt) is expected to have at least a 50-
percent probability of achieving an F of 0.15 in 2007, if the TAL and
assumed discard level in 2006 are not exceeded. It also will also
ensure, with a much greater than 50-percent
[[Page 62976]]
probability of success, that Fmax will not be exceeded. The
setting of an annual TAL greater than this amount would be contrary to
the rebuilding requirements of the Magnuson-Stevens Act and objectives
of the FMP.
In consideration of the Panel's recommendation to take the
retrospective pattern of F underestimation into account when setting
management targets, and the requirement to rebuild the stock by the end
of 2009, NMFS proposes a TAL that is associated with a 75-percent
probability of achieving the F that is projected to allow the stock to
rebuild to an SSB of 197 million lb (89,411 mt) and further assure to
an even greater extent that Fmax will not be exceeded. The
best available scientific information indicates that a TAL of 12.983
million lb (5,889 mt) is expected to have at least a 75-percent
probability of achieving an F of 0.15 in 2007, if the TAL and assumed
discard level in 2006 are not exceeded, and is expected to allow for
rebuilding of the stock to the target biomass by the end of 2009.
For these reasons, NMFS proposes a summer flounder TAL of 12.983
million lb (5,889 mt) for 2007. This TAL would represent a 45-percent
decrease for 2007 from the 2006 TAL of 23.59 million lb (10,700 mt).
The initial TAL would be allocated 60 percent (7,789,800 lb (3,533 mt))
to the commercial sector and 40 percent (5,193,200 lb (2,356 mt)) to
the recreational sector, as specified in the FMP. For 2007, the Council
and Board agreed to set aside 3 percent of the summer flounder TAL for
research activities. After deducting the RSA (389,490 lb (177 mt)) from
the TAL proportionally for the commercial and recreational sectors, as
specified in the FMP, i.e., 60 percent and 40 percent, respectively,
the commercial quota would be 7,556,106 lb (3,427 mt) and the
recreational harvest limit would be 5,037,404 lb (2,285 mt). The
commercial quota then would be allocated to the coastal states based
upon percentage shares specified in the FMP.
In addition, the Commission is expected to maintain the voluntary
measures currently in place to reduce regulatory discards that occur as
a result of landing limits established by the states. The Commission
established a system whereby 15 percent of each state's quota would be
voluntarily set aside each year to enable vessels to land an incidental
catch allowance after the directed fishery has been closed. The intent
of the incidental catch set-aside is to reduce discards by allowing
fishermen to land summer flounder caught incidentally in other
fisheries during the year, while also ensuring that the state's overall
quota is not exceeded. These Commission set-asides are not included in
these proposed specifications because these measures are not authorized
by the FMP and NMFS does not have authority to implement them.
Table 2 presents the proposed allocations by state, with and
without the commercial portion of the RSA deduction. These state quota
allocations are preliminary and are subject to reductions if there are
overages of states quotas carried over from a previous fishing year
(using the landings information and procedures described earlier). Any
commercial quota adjustments to account for overages will be included
in the final rule implementing these specifications.
Table 2. 2007 Proposed Initial Summer Flounder State Commercial Quotas.
----------------------------------------------------------------------------------------------------------------
Commercial Quota Commercial Quota less RSA\1\
State Percent Share -----------------------------------------------------------
lb kg\2\ lb kg\2\
----------------------------------------------------------------------------------------------------------------
ME 0.04756 3,705 1,681 3,594 1,630
----------------------------------------------------------------------------------------------------------------
NH 0.00046 36 16 35 16
----------------------------------------------------------------------------------------------------------------
MA 6.82046 531,300 240,998 515,361 233,768
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RI 15.68298 1,221,673 554,151 1,185,023 537,526
----------------------------------------------------------------------------------------------------------------
CT 2.25708 175,822 79,753 170,547 77,360
----------------------------------------------------------------------------------------------------------------
NY 7.64699 595,685 270,203 577,815 262,097
----------------------------------------------------------------------------------------------------------------
NJ 16.72499 1,302,843 590,970 1,263,758 573,241
----------------------------------------------------------------------------------------------------------------
DE 0.01779 1,386 629 1,344 610
----------------------------------------------------------------------------------------------------------------
MD 2.03910 158,842 72,051 154,077 69,889
----------------------------------------------------------------------------------------------------------------
VA 21.31676 1,660,533 753,218 1,610,717 730,621
----------------------------------------------------------------------------------------------------------------
NC 27.44584 2,137,976 969,786 2,073,837 940,692
----------------------------------------------------------------------------------------------------------------
TOTAL\3\ 100.00001 7,789,801 3,553,456 7,556,108 3,427,450
----------------------------------------------------------------------------------------------------------------
\1\ Preliminary Research Set-Aside: 3 percent of the commercial quota, i.e., 233,694 lb (106 mt).
\2\ Kilograms are as converted from pounds and do not sum to the converted total due to rounding.
\3\ Rounding of quotas results in totals exceeding 100 percent.
Scup
For scup, the stock is considered overfished when the 3-year
average of scup SSB is less than the biomass threshold (2.77 kg/tow;
the maximum Center spring survey 3-year average of SSB). Scup was last
formally assessed in June 2002 at the 35\th\ Northeast Regional Stock
Assessment Workshop (SAW). At that time, SARC 35 indicated that the
species was no longer overfished, but that stock status with respect to
overfishing could not be evaluated. An anomalously large spring SSB
index value for 2002 resulted in the 3-year SSB average exceeding the
biomass threshold for 2001 through 2003. However, more recent
information
[[Page 62977]]
indicates that the scup SSB has decreased, and the 3-year SSB average
values for 2004 (0.69 kg/tow) and 2005 (1.32 kg/tow) were under one-
quarter and one-half of the SSB threshold, respectively. Therefore, the
stock is considered overfished.
The proposed scup specifications for 2007 are based on an
exploitation rate (21 percent) in the rebuilding schedule that was
approved when scup was added to the FMP in 1996, prior to passage of
the Sustainable Fisheries Act (SFA). Subsequently, to comply with the
SFA amendments to the Magnuson-Stevens Act, the Council prepared
Amendment 12 to the FMP, which proposed to maintain the existing
rebuilding schedule for scup established by Amendment 8 to the FMP. On
April 28, 1999, NMFS disapproved the proposed rebuilding plan for scup
because the rebuilding schedule did not appear to be sufficiently risk-
averse. Later, however, NMFS advised the Council that use of the
exploitation rate as a proxy for F would be acceptable and sufficiently
risk-averse. NMFS considers the risks associated with the disapproved
rebuilding plan as not applicable to the proposed specifications
because they apply only for 1 fishing year and will be reviewed, and
modified as appropriate, by the Council and NMFS annually. Furthermore,
setting the scup specifications using an exploitation rate of 21
percent is a more risk-averse approach to managing the resource than
not setting any specifications until the Council submits, and NMFS
approves, a revised rebuilding plan that complies with all Magnuson-
Stevens Act requirements. The Council is currently addressing this
deficiency through Amendment 14 to the FMP, which is under development.
Given the uncertainty associated with the spring survey, the
Council and Board agreed with the Scup Monitoring Committee
recommendation to set a TAC and TAL for 1 year only. A recommendation
on the TAC for 2007 is complicated by the lack of information on
discards and mortality estimates for fully recruited fish. In recent
years, Council staff has used the 3-year SSB index average, the
relative exploitation index (based on total landings and the spring
survey SSB index), and assumptions about F to develop a TAL
recommendation. That approach would indicate that a TAL of 31.12
million lb (14,116 mt; nearly double that for 2006) would achieve the
target exploitation rate of 21 percent in 2007. Council staff cautioned
against use of the SSB index to derive a TAC for 2007, given the
current overfished status for scup, poor 2004 and 2005 year classes,
and the uncertainty associated with the survey indices, and instead
suggested a TAL of 12 million lb (5,443 mt). This value, which is 26-
percent lower than the 2006 TAL, falls within the range of yields
expected at about \1/2\Bmsy (11-16.5 million lb (4,990-7,484
mt)) based on the long-term potential catch, and would constrain
harvest to the level of actual landings in 2005. The Scup Monitoring
Committee agreed with the Council staff recommendation. Estimated
discards of 1.97 million lb (894 mt) were added to the TAL to derive a
TAC of 17.97 million lb (8,151 mt).
Reasoning that the scup winter trip limits have been effective in
reducing scup discards and that the commercial fishery has not met its
quota in the last few years, and concerned about potential shift in
effort from summer flounder to scup, the Council and Board rejected the
Monitoring Committee recommendation and instead recommended a TAL of 16
million lb (7,258 mt), an amount at the high end of the range of yields
expected at \1/2\Bmsy, and representing a less than 2-
percent decrease from 2006, with 3 percent of the TAL set aside for
research.
NMFS is concerned about implementing the scup TAL recommended by
the Council and Board for the reasons identified by the Scup Monitoring
Committee and because the spring survey index values have fallen below
the biomass threshold, upon which long-term potential catch projections
are based. Following NMFS's notification to the Council in August 2005
that the scup stock had been designated as overfished, the Council
initiated development of Amendment 14 to implement a plan to rebuild
the scup fishery. Although the amendment is not scheduled to be
effective until 2007 (affecting TAL specification for 2008 and beyond),
the setting of a more conservative 2007 TAL would contribute to the
rebuilding efforts for this overfished stock.
For these reasons, NMFS proposes to implement a scup TAL of 12
million lb (5,443 mt) for 2007. This TAL would represent a 26-percent
decrease for 2007 from the 2006 TAL of 16.27 million lb (7,380 mt). The
FMP specifies that the TAC associated with a given exploitation rate be
allocated 78 percent to the commercial sector and 22 percent to the
recreational sector. Scup discard estimates are deducted from both
sectors' TACs to establish TALs for each sector, i.e., TAC minus
discards equals TAL. The commercial TAC, discards, and TAL (commercial
quota) are then allocated on a percentage basis to three quota periods,
as specified in the FMP: Winter I (January-April)--45.11 percent;
Summer (May-October)--38.95 percent; and Winter II (November-December)-
-15.94 percent. The commercial TAC would be 10,900,000 lb (4,943 mt)
and the recreational TAC would be 3,070,000 lb (1,394 mt). After
deducting estimated discards (1.72 million lb (780 mt) for the
commercial sector and 250,000 lb (113 mt) for the recreational sector),
the initial commercial quota would be 9,176,600 lb (4,163 mt) and the
recreational harvest limit would be 2,823,400 lb (1,281 mt). The
Council and Board agreed to set aside 3 percent of the TAL for research
activities. Deducting this RSA (360,000 lb (163 mt)) would result in a
commercial quota of 8,895,800 lb (4,035 mt) and a recreational harvest
limit of 2,744,200 lb (1,245 mt).
The proposed specifications would maintain the base scup possession
limits, i.e., 30,000 lb (13,608 mt) for Winter I, to be reduced to
1,000 lb (454 kg) when 80 percent of the quota is projected to be
reached, and 2,000 lb (907 kg) for Winter II), as implemented for 2006.
Table 3 presents the 2007 commercial allocation recommended by the
Council, with and without the preliminary 280,800-lb (127-mt) RSA
deduction. These 2007 allocations are preliminary and may be subject to
downward adjustment due to 2005 overages in the final rule implementing
these specifications, based on the procedures for calculating overages
described earlier.
Table 3. 2007 Proposed Initial TAC, Commercial Scup Quota, and Possession Limits.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Commercial Quota in Commercial Quota Possession Limits
Period Percent TAC in lb (mt) Discards in lb (mt) lb (mt) less RSA in lb (mt) in lb (kg)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Winter I 45.11 4,915,456 775,892 4,139,564 4,012,895 30,000\1\
(2,230) (352) (1878) (1820) (13,608)
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 62978]]
Summer 38.95 4,244,226 669,940 3,574,286 3,464,914 n/a
(1,925) (304) (1,621) (1,572)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Winter II 15.94 1,736,918 274,168 1,462,750 1,417,991 2,000
(788) (124) (664) (643) (907)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Total\2\ 100.00 10,896,600 1,720,000 9,176,600 8,895,800 ..................
(4,943) (780) (4,163) (4,035)
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\The Winter I landing limit would drop to 1,000 lb (454 kg) upon attainment of 80 percent of the seasonal allocation.
\2\Totals subject to rounding error.
n/a-Not applicable
The final rule to implement Framework 3 to the FMP (68 FR 62250,
November 3, 2003) implemented a process, for years in which the full
Winter I commercial scup quota is not harvested, to allow unused quota
from the Winter I period to be rolled over to the quota for the Winter
II period. As shown in Table 4, the proposed specifications would
maintain the Winter II possession limit-to-rollover amount ratios
(1,500 lb (680 kg) per 500,000 lb (227 mt) of unused Winter I period
quota), as implemented for 2006.
Table 4. Potential Increase in Winter II Possession Limits Based on the Amount of Scup Rolled Over from Winter I
to Winter II Period.
----------------------------------------------------------------------------------------------------------------
Initial Winter II Possession Limit Rollover from Winter I Increase in Initial Final Winter II
------------------------------------------ to Winter II Winter II Possession Possession Limit
------------------------- Limit after Rollover from
----------------------- Winter I to Winter II
lb kg lb mt ----------------------
lb kg lb kg
----------------------------------------------------------------------------------------------------------------
2,000 907 0-499,999 0-227 0 0 2,000 907
----------------------------------------------------------------------------------------------------------------
2,000 907 500,000-999,9 227-454 1,500 680 3,500 1,588
99
----------------------------------------------------------------------------------------------------------------
2,000 907 1,000,000-1,4 454-680 3,000 1,361 5,000 2,268
99,999
----------------------------------------------------------------------------------------------------------------
2,000 907 1,500,000-1,9 680-907 4,500 2,041 6,500 2,948
99,999
----------------------------------------------------------------------------------------------------------------
2,000 907 2,000,000-2,5 907-1,13 6,000 2,722 8,000 3,629
00,000 4
----------------------------------------------------------------------------------------------------------------
Black Sea Bass
Amendment 12 to the FMP indicated that the black sea bass stock,
which was determined by SARC 27 to be overfished in 1998, could be
rebuilt to the target biomass within a 10-year period, i.e., by 2010.
The current target exploitation rate is based on the current estimate
of Fmax, or 0.33 (25.6 percent). The northern stock of black sea bass
was last assessed at the 43rd SAW in June 2006. The SARC 27 Panel did
not consider the stock assessment to provide an adequate basis to
evaluate stock status against the biological reference points, but did
not recommend any other reference points to replace them.
The most recent Center spring survey results indicate that the
exploitable biomass of black sea bass decreased in 2005. The 2005
biomass index, i.e., the 3-year average exploitable biomass for 2004
through 2006, is estimated to be 0.804 kg/tow, below the threshold
biomass value of 0.976 kg/tow. Based on these results, if the
biological reference points in the FMP are applied, black sea bass once
again would be determined to be overfished.
The best available information on stock status indicates that stock
size has increased in recent years. In addition, the 2005 year class
may be above average. If protected, this year class should allow for
additional stock rebuilding in 2006 and beyond. Given the lack of stock
projections, it is difficult to predict what the actual biomass will be
in 2007. Because the estimate of exploitable biomass is based on a 3-
year average, the actual estimate for 2007 will not be derived until
the spring 2008 survey results are available; if it is 0.328 (equal to
the average for 2004-2006), and assuming an exploitation rate of 21
percent in 2003, the TAL associated with the target exploitation rate
would be 4.68 million lb (2,123 mt). However, if the 2007 estimate is
0.396 (equal to the average for 2003-2005), the TAL associated with the
target exploitation rate would be 5.650 million lb (2,563 mt). Given
the uncertainty in the survey estimates and the potential
underestimation of the 2003 exploitation rate (21 percent), the
Monitoring Committee agreed with the Council staff recommendation to
set a 1-year TAL (for 2007) of 5 million lb (2,270 mt), noting that it
would constrain the 2007 landings to the 2005 and 2006 levels.
Reasoning that the TAL should be set at a level higher than 2005
landings (to avoid discards and highgrading, to accommodate a potential
shift in effort from the summer flounder fishery, and assuming that
black sea bass availability may improve in 2007), but recognizing the
need for a more conservative TAL than implemented for 2006, the Council
and Board rejected the Monitoring Committee recommendation, and
recommended instead a 6.5-million-lb (2,948-mt) TAL for 2007, with 3
percent of the TAL set aside for research. This TAL would represent a
19-percent decrease from 2006.
NMFS has concerns regarding the Council and Board-recommended black
[[Page 62979]]
sea bass TAL, which is well above the range of TALs considered by the
Monitoring Committee, for the reasons specified above. More
conservative black sea bass TALs will likely need to be implemented
during the remainder of the rebuilding period to allow for growth of
exploitable biomass (reflected by the spring survey index). NMFS has
encouraged the Council to manage this stock with caution and to
initiate a process to develop replacement stock status determination
criteria that are scientifically supportable and that can be relied on
to measure the progress of rebuilding.
For the reasons described above, NMFS proposes to implement a black
sea bass TAL of 5 million lb (2,270 mt) for 2007. This TAL would
represent a 37.5-percent decrease from the 2006 TAL of 8 million lb
(3,629 mt). The FMP specifies that the TAL associated with a given
exploitation rate be allocated 49 percent to the commercial sector and
51 percent to the recreational sector; therefore, the initial TAL would
be allocated 2.45 million lb (1,111 mt) to the commercial sector and
2.55 million lb (1,157 mt) to the recreational sector. The Council and
Board also agreed to set aside 3 percent of the black sea bass TAL for
research activities. After deducting the RSA (150,000 lb (68 mt)), the
TAL would be divided into a commercial quota commercial quota of
2,376,500 lb (1,078 mt) and a recreational harvest limit of 2,473,500
lb (1,122 mt), as specified in the FMP.
Classification
These proposed specifications are exempt from review under
Executive Order 12866.
An IRFA was prepared, as required by section 603 of the Regulatory
Flexibility Act (RFA). The IRFA describes the economic impact these
proposed specifications, 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. A copy of this analysis is available from NMFS (see ADDRESSES). A
summary of the economic analysis follows.
The economic analysis assessed the impacts of the various
management alternatives. The no action alternative is defined as
follows: (1) No proposed specifications for the 2007 summer flounder,
scup, and black sea bass fisheries would be published; (2) the
indefinite management measures (minimum mesh sizes, minimum sizes,
possession limits, permit and reporting requirements, etc.) would
remain unchanged; (3) there would be no quota set-aside allocated to
research in 2007; (4) the existing gear restrictive areas would remain
in place for 2007; and (5) there would be no specific cap on the
allowable annual landings in these fisheries (i.e., there would be no
quotas). Implementation of the no action alternative would be
inconsistent with the goals and objectives of the FMP, its implementing
regulations, and the Magnuson-Stevens Act. In addition, the no action
alternative would substantially complicate the approved management
program for these fisheries, and would very likely result in
overfishing of the resources. Therefore, the no action alternative is
not considered to be a reasonable alternative to the preferred action.
The Council prepared economic analyses for Alternatives 1 through
3. Alternative 1 consists of the harvest limits proposed by the Council
for summer flounder, and the Council and Board for scup and black sea
bass. Alternative 2 consists of the most restrictive quotas (i.e.,
lowest landings) considered by the Council and the Board for all of the
species. Alternative 3 consists of the status quo quotas, which were
the least restrictive quotas (i.e., highest landings) considered by the
Council and Board for all three species. NMFS prepared a supplemental
economic analysis for Alternatives 4 through 6. Although NMFS defined
Alternative 4 as the no action alternative, no analysis was undertaken
for the reasons described above, i.e., because it would likely result
in overfishing of the resources. Alternative 5 consists of a summer
flounder TAL of 14.156 million lb (6,421 mt, associated with a 50-
percent probability of not exceeding the F target) and the most
restrictive quotas for scup and black sea bass. Alternative 6 consists
of a summer flounder TAL of 12.983 million lb (5,889 mt, associated
with a 75-percent probability of not exceeding the F target) and the
most restrictive quotas for scup and black sea bass. For clarity, these
proposed specifications are described in Alternative 6.
Table 5 presents the 2007 initial TALs, RSA, commercial quotas
adjusted for RSA, and preliminary recreational harvests for the
fisheries under these three quota alternatives.
Table 5. Comparison, in lb (mt), of the alternatives of quota combinations reviewed.
----------------------------------------------------------------------------------------------------------------
Preliminary
Initial TAL RSA Preliminary Adjusted Recreational Harvest
Commercial Quota\1\ Limit
----------------------------------------------------------------------------------------------------------------
Quota Alternative 1 (Council's Preferred)
-----------------------------------
Summer Flounder 19.9 million 567,092\2\ 11.60 million 7.73 million
(9,026) (257) (5,261) (3,506)
----------------------------------------------------------------------------------------------------------------
Scup 16 million 480,000 11.93 million 3.59 million
(7,257) (218) (5,411) (1,628)
----------------------------------------------------------------------------------------------------------------
Black Sea Bass 6.5 million 132,000\2\ 3.12 million 3.25 million
(2,948) (60) (1,415) (1,474)
----------------------------------------------------------------------------------------------------------------
Quota Alternative 2 (Most Restrictive)
----------------------------------- -------------------------------------------------------------
Summer Flounder 5.22 million 156,600 3.04 million 2.03 million
(2,368) (71) (1,379) (921)
----------------------------------------------------------------------------------------------------------------
Scup 12 million 360,000 8.9 million 2.74 million
(5,442) (163) (4,037) (1,243)
----------------------------------------------------------------------------------------------------------------
Black Sea Bass 5 million 132,000\2\ 2.39 million 2.48 million
(2,268) (60) (1,084) (1,125)
----------------------------------------------------------------------------------------------------------------
[[Page 62980]]
Quota Alternative 3 (Status Quo-Least Restrictive)
----------------------------------- -------------------------------------------------------------
Summer Flounder 23.59 million 567,062\2\ 13.81 million 9.21 million
(10,700) (257) (6,264) (4,178)
----------------------------------------------------------------------------------------------------------------
Scup 16.27 million 488,100 12.13 million 3.65 million
(7,380) (221) (5,502) (1,656)
----------------------------------------------------------------------------------------------------------------
Black Sea Bass 8 million 132,000\2\ 3.86 million 4.01 million
(3,629) (60) (1,751) (1,819)
----------------------------------------------------------------------------------------------------------------
Quota Alternative 4 (No Action - not analyzed)
----------------------------------- -------------------------------------------------------------
Quota Alternative 5 (NMFS analysis)
----------------------------------- -------------------------------------------------------------
Summer Flounder 14.156 million 424,680 8.24 million 5.49 million
(6,421) (193) (3,738) (2,490)
----------------------------------------------------------------------------------------------------------------
Scup 12 million 360,000 8.9 million 2.74 million
(5,443) (163) (4,037) (1,243)
----------------------------------------------------------------------------------------------------------------
Black Sea Bass 5 million 150,000 2.38 million 2.47 million
(2,268) (68) (1,078) (1,122)
----------------------------------------------------------------------------------------------------------------
Quota Alternative 6 (NMFS analysis - Proposed Action)
----------------------------------- -------------------------------------------------------------
Summer Flounder 12.983 389,490 7.56 million 5.04 million
(5,889) (177) (3,429) (2,286)
----------------------------------------------------------------------------------------------------------------
Scup 12 million 360,000 8.9 million 2.74 million
(5,443) (163) ( ) (1,243)
----------------------------------------------------------------------------------------------------------------
Black Sea Bass 5 million 150,000 2.38 million 2.47 million
(2,268) (68) (1,078) (1,122)
----------------------------------------------------------------------------------------------------------------
\1\ Note that preliminary quotas are provisional and may change to account for overages of the 2006 quotas.
\2\ Actual RSA amount analyzed by Council staff (rather than 3 percent of TAL)
\3\ Metric tons are as converted from pounds and are subject to rounding error
Table 6 presents the percent change associated with each of these
commercial quota alternatives (adjusted for RSA) compared to the final
adjusted quotas for 2006.
Table 6. Percent change associated with 2007 adjusted commercial quota alternatives compared to 2006 commercial
adjusted quotas.
----------------------------------------------------------------------------------------------------------------