Fisheries of the Northeastern United States; Recreational Management Measures for the Summer Flounder, Scup, and Black Sea Bass Fisheries; Fishing Year 2010, 39170-39178 [2010-16651]
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Federal Register / Vol. 75, No. 130 / Thursday, July 8, 2010 / Rules and Regulations
1. The authority for part 7 continues
to read as follows:
■
Authority: 16 U.S.C. 1, 3, 9a, 462(k); Sec.
7.96 also issued under D.C. Code 10–137
(2001) and D.C. Code 50–2201 (2001).
§ 7.94
■
[Removed and reserved]
2. Remove and reserve § 7.94.
Dated: June 29, 2010.
Will Shafroth,
Acting Assistant Secretary for Fish and
Wildlife and Parks.
[FR Doc. 2010–16600 Filed 7–7–10; 8:45 am]
BILLING CODE 4312–BA–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 0907211158–0265–02]
RIN 0648–AY04
Fisheries of the Northeastern United
States; Recreational Management
Measures for the Summer Flounder,
Scup, and Black Sea Bass Fisheries;
Fishing Year 2010
AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
SUMMARY: NMFS implements
recreational management measures for
the 2010 summer flounder, scup, and
black sea bass fisheries. These actions
are necessary to comply with
regulations implementing the Summer
Flounder, Scup, and Black Sea Bass
Fishery Management Plan (FMP) and to
ensure compliance with the MagnusonStevens Fishery Conservation and
Management Act (Magnuson-Stevens
Act). The intent of these measures is to
prevent overfishing of the summer
flounder, scup, and black sea bass
resources.
Effective August 9, 2010.
Copies of supporting
documents used by the Summer
Flounder, Scup, and Black Sea Bass
Monitoring Committees and of the
Environmental Assessment, Regulatory
Impact Review, and Initial Regulatory
Flexibility Analysis (EA/RIR/IRFA) and
EA/RIR/IRFA Addendum are available
from Daniel Furlong, Executive Director,
Mid-Atlantic Fishery Management
DATES:
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ADDRESSES:
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Council, Room 2115, Federal Building,
800 N. State Street, Suite 201, Dover, DE
19901. The EA/RIR/IRFA is also
accessible via the Internet at https://
www.nero.noaa.gov. The Final
Regulatory Flexibility Analysis (FRFA)
consists of the IRFA, public comments
and responses contained in this final
rule, and the summary of impacts and
alternatives contained in this final rule.
Copies of the small entity compliance
guide and EA/RIR/IRFA document and
addendum are available from Patricia A.
Kurkul, Regional Administrator,
Northeast Region, NMFS, 55 Great
Republic Drive, Gloucester, MA 01930–
2276.
FOR FURTHER INFORMATION CONTACT:
Michael Ruccio, Fishery Policy Analyst,
(978) 281–9104.
SUPPLEMENTARY INFORMATION:
management measures (minimum fish
sizes, possession limits, and fishing
seasons) intended to keep annual
recreational landings from exceeding
the specified harvest limits.
Background
PART 7—SPECIAL REGULATIONS,
AREAS OF THE NATIONAL PARK
SYSTEM
Summer Flounder Management
Measures
The Commission notified the NMFS
Northeast Regional Administrator by
letter dated April 6, 2010, that the 2010
summer flounder recreational fishery
management programs (i.e., minimum
fish size, possession limit, and fishing
seasons) implemented by the states from
Massachusetts to North Carolina have
been reviewed by the Commission’s
Technical Committee and approved by
the Commission’s Summer Flounder
Management Board (SF Board). The
correspondence indicates that the
Commission-approved management
programs are projected to restrict 2010
recreational summer flounder coastwide
landings consistent with the statespecific requirements established by the
Technical Committee and SF Board
through the Commission process.
Based on the recommendation of the
Commission, the NMFS Northeast
Regional Administrator finds that the
recreational summer flounder fishing
measures proposed to be implemented
by the individual states for 2010 are the
conservation equivalent of the season,
minimum size, and possession limit
prescribed in §§ 648.102, 648.103, and
648.105(a), respectively. According to
§ 648.107(a)(1), vessels subject to the
recreational fishing measures of this
part and landing summer flounder in a
state with an approved conservation
equivalency program shall not be
subject to Federal measures, and shall
instead be subject to the recreational
fishing measures implemented by the
state in which they land. Section
648.107(a) has been amended to
recognize state-implemented measures
as conservation equivalent of the
coastwide recreational management
measures for 2010. For clarity, the 2010
The summer flounder, scup, and
black sea bass fisheries are managed
cooperatively by the Atlantic States
Marine Fisheries Commission
(Commission) and the Mid-Atlantic
Fishery Management Council (Council),
in consultation with the New England
and South Atlantic Fishery Management
Councils. The FMP and its
implementing regulations, which are
found at 50 CFR part 648, subparts A
(general provisions), G (summer
flounder), H (scup), and I (black sea
bass), describe the process for specifying
annual recreational management
measures that apply in the Exclusive
Economic Zone (EEZ). The state from
North Carolina to Maine manage these
fisheries within 3 nautical miles of their
coasts, under the Commission’s plan for
summer flounder, scup, and black sea
bass. The Federal regulations govern
fishing activity in the EEZ, as well as
vessels possessing a Federal fisheries
permit, regardless of where they fish.
The 2010 coastwide recreational
harvest limits, after deduction of
research set-aside (RSA), are 8,586,440
lb (3,896 mt) for summer flounder;
3,011,074 lb (1,366 mt) for scup; and
1,830,390 lb (830 mt) for black sea bass.
The final 2010 quota specifications,
inclusive of the recreational harvest
limits, were previously implemented by
NMFS effective January 1, 2010 (74 FR
67978; December 22, 2009), for summer
flounder and scup, and effective
February 2, 2010, for black sea bass (75
FR 6586).
The proposed rule to implement
annual Federal recreational measures
for the 2010 summer flounder, scup,
and black sea bass fisheries was
published on April 27, 2010 (75 FR
22087), along with proposed
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2010 Recreational Management
Measures
Additional discussion on the
development of the recreational
management measures appeared in the
preamble of the proposed rule and is not
repeated here. All minimum fish sizes
discussed below are total length
measurements of the fish, i.e., the
straight-line distance from the tip of the
snout to the end of the tail while the fish
is lying on its side. For black sea bass,
total length measurement does not
include the caudal fin tendril. All
possession limits discussed below are
per person.
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Federal Register / Vol. 75, No. 130 / Thursday, July 8, 2010 / Rules and Regulations
summer flounder management measures
adopted by the individual states vary
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according to the state of landing, as
specified in the following table:
TABLE 1—2010 COMMISSION APPROVED STATE-BY-STATE CONSERVATION EQUIVALENT RECREATIONAL MANAGEMENT
MEASURES FOR SUMMER FLOUNDER
Minimum Fish
Size
State
Possession
Limit
(number of
fish)
Fishing Season
inches
cm
MA
18.5
46.99
5
May 22–September 6
RI
19.5
49.53
6
May 1–December 31
CT
19.5
49.53
3
May 15–August 25
NY
21.0
53.34
2
May 15–September 6
NJ
18.0
45.72
6
May 29–September 6
DE
18.5
46.99
4
January 1–October 13
MD
19.0
48.26
3
April 17 through November 22
VA
18.5
46.99
4
January 1 through December 31
NC1
15.0
38.10
8
January 1 through December 31
1 Pamlico
Sound, NC—No person may possess flounder less than 14.0 in (35.56 cm) total length (TL) taken from internal waters for recreational purposes west of a line beginning at a point on Point of Marsh in Carteret County at 35°04.6166′N lat.-76°27.8000′W long., then running northeasterly to a point at Bluff Point in Hyde County at 35°19.7000′N lat.-76°09.8500′W long. In Core and Clubfoot creeks, the Highway
101 Bridge constitutes the boundary north of which flounder must be at least 14.0 (35.56 cm) in TL.
Albemarle Sound, NC—No person may possess flounder less than 14.0 in (35.56 cm) TL taken from internal waters for recreational purposes
west of a line beginning at a point 35°57.3950′N lat.- 76°00.8166′W long. on Long Shoal Point; running easterly to a point 35°56.7316′N lat.75°59.3000′ W long. near Marker ‘‘5’’ in Alligator River; running northeasterly along the Intracoastal Waterway to a point 36°09.3033′N lat.75°53.4916′W long. near Marker ‘‘171’’ at the mouth of North River; running northwesterly to a point 36°09.9093′N lat.-75°54.6601′W long. on
Camden Point.
Browns Inlet South, NC—No person may possess flounder less than 14.0 in (35.56 cm) TL in internal and Atlantic Ocean fishing waters for
recreational purposes west and south of a line beginning at a point 34°37.0000′N lat.-77°15.000′W long.; running southeasterly to a point
34°32.0000′N lat.-77°10.0000′W long.
Scup Management Measures
This rule implements the measures
contained in the April 27, 2010,
proposed rule: A 10.5–in (26.67–cm)
minimum fish size, a 10–fish per person
possession limit, and an open season of
June 6 through September 26.
TABLE 2—2010 SCUP RECREATIONAL MANAGEMENT MEASURES
Minimum Fish
Size
inches
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Scup
The scup fishery in state waters will
be managed under a regional
conservation equivalency system
developed by the Commission over the
last 8 years. Because the Federal FMP
does not contain provisions for
conservation equivalency, and states
may adopt their own unique measures,
the Federal and state recreational scup
management measures will differ for
2010. In accordance with
§ 648.4(b)(1)(i), when Federal, state, and
local requirements differ, federally
permitted scup vessels are required to
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cm
Possession
Limit
10.5
Fishery
26.674
10 fish
adhere to the most restrictive
requirement regardless of where the
vessel fishes.
Black Sea Bass Management Measures
This rule implements the black sea
bass measures adopted by the
Commission for 2010: A 12.5–in (31.75–
cm) minimum fish size, a 25–fish per
person possession limit and fishing
seasons from May 22–October 11 and
November 1–December 31.
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Fishing Season
June 6 through
September 26
Changes from the Proposed Rule
NMFS had proposed in the April 27,
2010 (75 FR 22087), rule to implement
the Council-preferred measures (12.5–in
(31.75–cm) minimum fish size, 25–fish
possession limit, and fishing seasons of
May 22–August 8 and September 4–
October 4) for the 2010 black sea bass
recreational fishery. NMFS anticipated
additional data that might permit
liberalization of the 2010 measures
would become available in the interim
between publication of the proposed
and final rules. These data, from the
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Marine Recreational Fisheries Statistics
Survey (MRFSS), became available in
late April.
The final MRFSS data indicated that
2009 landings of black sea bass were
2.31 million lb (1,048 mt). Prior to the
release of these data, black sea bass
landing estimates were used for the
months of September and October 2009.
At the time of the proposed rule, the
best available information, which
included estimates for September and
October, indicated that 2009
recreational black sea bass landings
were approximately 3.31 million lb
(1,501 mt). The Council’s originally
preferred measures contained in the
proposed rule would have reduced 2010
landings by 44 percent from 2009 levels,
consistent with the assumption that
2009 landings were 3.31 million lb
(1,501 mt). However, given the final
2009 landings data, a 21–percent
reduction in 2010 landings from 2009
levels is necessary.
Many had expressed concern during
the management measures development
process that actual landings from the 2-
month time period in 2009 would be
significantly different from any
generated estimates, owing in part to the
108-day closure of the black sea bass
recreational fishery in the Federal
waters of the EEZ that was implemented
by NMFS effective October 5, 2009 (74
FR 51092). Because of the timing for
Council and Commission meetings and
the proposed rule 30 day comment
period, NMFS provided a contextual
framework for the likelihood that
additional data would be available for
analysis and solicited specific
comments on alternative management
measures in the proposed rule (75 FR
22087; April 27, 2010).
The Commission had an opportunity
to analyze the final 2009 MRIP landings
data prior to its May 2010 meeting.
During this meeting, the Commission
adopted the measures now implemented
through this final rule. These measures
are projected to reduce landings by 26
percent from 2009 levels. The
Commission adopted measures that
were slightly more precautionary (i.e.,
greater than a 21–percent reduction in
2010 landings from 2009 levels) to allow
for a reasonable conservation buffer to
account for management uncertainty in
the harvest estimates and the
effectiveness of the regulations. The
Council, as well as members of the
public and recreational fishing advocacy
groups, provided written comment fully
supporting implementation of the less
restrictive management measures
adopted by the Commission. NMFS
finds the measures make use of the best
available information in as timely a
fashion as the development, review, and
implementation process will permit. In
addition, NMFS finds that the measures
implemented in this final rule provide
some buffer to offset managementrelated uncertainty and mitigate
foregone recreational opportunity,
thereby reducing adverse socioeconomic impacts. Thus, NMFS is
implementing these measures for the
2010 fishing season, even though they
were not contained in the proposed
rule.
TABLE 3—2010 BLACK SEA BASS RECREATIONAL MANAGEMENT MEASURES
Minimum Fish
Size
inches
Black Sea Bass
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Comments and Responses
Eight comment letters were received
regarding the proposed recreational
management measures. The
Commission’s Black Sea Bass
Management Board provided the revised
2010 black sea bass measures adopted
for state waters as comments on the
proposed rule and recommended
similar measures be adopted for Federal
waters. Five comment letters, including
one from the Council, spoke in support
of the Commission’s revised 2010 black
sea bass measures and urged NMFS to
adopt similar measures for Federal
waters. For clarity, NMFS is
implementing, through this rule, the
identical black sea bass measures
adopted by the Commission and with
the full support of the Council for the
2010 black sea bass recreational fishery
in Federal waters.
One recreational fishery advocacy
group wrote in favor of the summer
flounder conservation equivalency
system being implemented through this
rule.
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cm
Possession
Limit
12.5
Fishery
31.75
25 fish
Comments that require responses are
addressed below. Similar comments
were consolidated for NMFS’s
responses:
Comment 1: One commenter asked
why commercial summer flounder
fishermen can keep fish smaller than
most recreational minimum fish sizes
implemented by states through
conservation equivalency. This
commenter stated that most large
summer flounder are female and the
utilization of high recreational
minimum fish sizes will catch a
disproportionately high number of
female fish and could negatively impact
stock rebuilding efforts.
Response: The issue of different
minimum fish sizes between
commercial and recreational fisheries is
often raised. Minimum fish sizes for
both sectors are implemented by NMFS
based on recommendations received
from the Council. In regards to summer
flounder, the minimum commercial fish
size has been set at 14 in (35.56 cm)
since the late 1990s. The minimum
commercial size was established
following mesh size selectivity studies
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Fishing Season
May 22–October 11 and
November 1–December
31
conducted for implementation of the
original Summer Flounder FMP. These
mesh studies considered the capabilities
of certain mesh sizes to not encounter
fish of certain sizes.
The Council has recommended the
14–in (35.56–cm) minimum commercial
summer flounder size to address
National Standard 9 of the MagnusonStevens Act. National Standard 9
requires that conservation and
management measures shall, to the
extent practicable, minimize bycatch
and, when bycatch cannot be avoided,
minimize the mortality of such bycatch.
Commercial fishing conducted with
bottom tending mobile gear, such as
trawl nets, is less discriminating than
recreational hook-and-line fishing gear.
Thus, commercial fishing operations
tend to capture a wider size range and
higher numbers of summer flounder
than do recreational fishermen. The 14–
in (35.56–cm) size strikes a balance
between converting potential discards to
landings and ensuring summer flounder
have an opportunity to spawn before
becoming legal minimum commercial
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size. The current mesh size required for
most summer flounder trawl gear is 5.5
in (13.97 cm) and is engineered to catch
fish 14 in (35.56 cm) and larger.
Recreational minimum fish size has
been used as a tool to constrain landings
in the recreational fishery.
Recreationally captured summer
flounder have a lower associated
mortality than do those captured by
bottom-tending mobile commercial gear
such as trawl nets and scallop dredges.
Eighty percent of commercially
discarded summer flounder are assumed
to be dead or will die after release. By
contrast, the most recent assessment for
summer flounder used recent research
information that indicated the mortality
rate for recreationally caught and
released summer flounder was 10
percent.
The concept that recreational fisheries
target larger, typically female fish has
been discussed and examined in recent
stock assessments. Additional research
on stock sex ratios, natural and fishing
mortality by sex and size, and
potentially different growth and
maturity rates by sex needs further
examination for definitive conclusions
on potential impacts of the management
strategy that has been employed;
however, current stock projections
indicate that the summer flounder stock
will be rebuilt prior to the January 1,
2013, rebuilding deadline.
Comment 2: One comment suggested
that summer flounder management
measures should be two fish in the 14
to18–in (35.56 to 45.72–cm) size range
and four fish over 18 in (45.72 cm).
Response: The Council-conducted
analysis for the 2010 summer flounder
recreational management measure
coastwide alternatives indicated a 19–in
(48.26–cm) minimum fish size, 2–fish
possession limit, and coastwide season
from May 1 to September 30 was
predicted to constrain 2010 landings to
the 8.85–million-lb (3,896–mt)
recreational harvest limit. The
commenter’s recommended
management measures are substantially
more liberal than this, the most liberal
coastwide measures analyzed and
considered by the Council. Thus, the
commenter’s suggested measures would
likely result in landings well above the
recreational harvest limit. Because such
measures would not adequately
constrain the 2010 recreational summer
flounder fishery and would likely
exceed the established recreational
harvest limit, NMFS finds that such
measures would be inconsistent with
the goals and objectives of the FMP and
the Magnuson-Stevens Act.
NMFS is implementing, through this
final rule, conservation equivalency
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wherein individual state measures
approved through the Commission
process are found to be equivalent to the
coastwide measures. In the conservation
equivalency process, individual states
have the ability to modify the minimum
fish size, possession limits, and fishing
season consistent with Commissionimposed requirements before NMFS
ultimately elects to implement
conservation equivalency or coastwide
measures for the fishery. States have
some ability to adjust management
measures in a manner that best suits the
needs of the anglers and fisheries
prosecuted in the waters adjacent to
their respective state. Some states have
developed and implemented, through
the Commission process, minimum fish
sizes similar to those suggested by the
commenter. NMFS has, in turn, adopted
through this rule, conservation
equivalency for Federal waters.
Comment 3: One recreational fishery
angling group opposed the proposed
scup recreational management measures
stating that (1) the scup stock is rebuilt,
(2) annual catch limits (ACLs) and
accountability measures (AMs) are not
yet a statutory requirement for the scup
fishery, (3) that the 10–fish per person
possession limit will dissuade potential
party/charter anglers from booking trips,
and (4) that there is no conservation or
legal requirement to reduce recreational
scup landings for 2010. The commenter
did not suggest any alternative measures
and did acknowledge that a very small
percentage of annual recreational scup
landings occur in Federally-managed
waters under the jurisdiction of NMFS.
Response: In response, NMFS agrees
that the best available scientific
information does indicate that the scup
stock has been rebuilt, thereby satisfying
the rebuilding requirements for the
previously overfished stock.
NMFS notified the Council on April
22, 2009, that the results of a 2008
externally peer reviewed Data Poor
Stocks Working Group (DPSWG)
assessment of scup had found that the
stock had achieved and exceeded the
required rebuilding biomass target. In
that same correspondence, NMFS
further relayed that the peer-review
panel from the DPSWG indicated that
the assessment contained a high degree
of uncertainty. In its final report, the
peer review panel recommended:
’’...that rapid increases in quota to meet the
revised MSY [Maximum Sustained Yield]
would be unwarranted given uncertainties in
recent [scup] recruitments. A more gradual
increase in quotas is a preferred approach
reflective of the uncertainty in the [scup]
model estimates and stock status.’’
The Council’s SSC has adhered to the
peer review panel’s recommendation in
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setting scup catch levels. For 2010, the
SSC recommended a 10–percent
increase in Total Allowable Catch (TAC)
as the ABC level from the 2009 levels.
The recreational harvest limit is a
derivative of the overall TAC.
While the perception of the scup
stock has changed and is more favorable
than recent years and the statutory
requirements for stock rebuilding have
been satisfied, the catch
recommendations from the Council’s
scientific advisory body, the SSC, has
remained precautionary in light of
uncertainty associated with the revised
stock assessment. NMFS, in turn, has
implemented the Council’s
recommendation for catch levels as
guided by the SSC’s ABC
recommendation. The SSC and
Council’s Scup Monitoring Committee
will review updated stock assessment
information in June 2010 before making
catch level recommendation for the
2011 fishing year.
While the requirement for stocks not
subject to overfishing to have in place
ACLs and AMs, as required by the
Magnuson-Stevens Act, does not take
effect until 2011, the Council has put
into practice the utilization of its SSC
for catch level advice. Utilization of the
SSC in catch level recommendations did
not result in a delayed implementation
phase-in period when the MagnusonStevens Act was reauthorized in 2006.
The SSC has been involved in making
ABC recommendations since 2008 for
the 2009 fishing year.
The SSC brings to bear considerable
scientific expertise in making catch
level recommendations. As such, the
ABC recommended by the SSC sets the
standard for scientifically justifiable
catch levels. For the Council or NMFS
to deviate from the SSC-recommended
ABC would require sufficient
justification to explain why an alternate
catch level was the more appropriate
and a better use of the best available
scientific information. In the case of
scup, the SSC expressed reservations
about the information provided by the
most recent stock assessment and
recommended an ABC that, relative to
the estimated total biomass of scup, is
risk averse.
The Council may further reduce the
ABC recommended by the SSC for
additional considerations, consistent
with the requirements of National
Standard 1 of the Magnuson-Stevens
Act to achieve Optimal Yield (OY) on a
continuing basis. NMFS provided a
detailed response to similar comments
that ACLs and AMs are not yet
requirements and that the 2010 scup
catch level had been set too low to
achieve OY on a continuing basis in the
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2010 specifications final rule (74 FR
67978, December 22, 2009). Those
responses are not repeated here, but are
instead incorporated by reference.
NMFS acknowledges the commenter’s
concern that the scup stock status and
catch level recommendations appear to
be at odds with one another; however,
as explained, the SSC and Council have
taken a precautionary approach in
managing the scup stock, consistent
with assessment-related advice to do so.
This approach continues to be
supported by NMFS.
As part of the regulatory impact
review and general economic impact
analyses performed for the 2010
recreational management measures, the
Council provided an analysis of the
potential impacts of a 10–fish per
person possession limit for scup. The
analysis concluded that up to 2.24
percent of party/charter vessels could be
impacted by the 10–fish possession
limit. While this would suggest that the
impact is low, the analysis indicated
that predicting year-to-year angler
behavior in response to numerous
influential factors, including regulatory
changes, is difficult. The Council
performed an analysis of all potential
combination of summer flounder, scup,
and black sea bass alternatives with a
hypothetical 25- and 50–percent
reduction in fishing trips. The range of
impacts varies considerably from a low
of $399 per vessel in Delaware to up to
$44,000 per vessel in North Carolina.
These are total impacts, inclusive of all
potential changes for summer flounder,
scup, and black sea bass management
measures and up to a 50–percent
reduction in angler trips.
Furthermore, the majority of scup
party/charter landings occur in state
waters and may occur on vessels
without Federal permits. In such
situations, the data necessary to
quantify potential impacts are
unavailable as permit data are utilized
as the basis for impact assessment. See
the Council’s EA/RIR/IRFA document
for additional detail; information on
obtaining a copy of the document is
provided under the ADDRESSES section
of the preamble.
Given the minor magnitude of
recreational scup fishing in Federal
waters, the economic impacts associated
with the implemented measures are
expected to be equally minor relative to
the entire scup recreational fishery.
Under the recreational fishery
management methods utilized by the
Council’s Scup Monitoring Committee
to develop measures designed to
constrain recreational landings to the
recreational harvest limit, the level of
landings in the preceding year are used
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as a basis for calculating the
effectiveness of measures for the
upcoming fishing year relative to the
catch level. More simply stated, when
landings in the previous year exceed the
recreational harvest limit for the current
year, measures are adjusted. The
amount of adjustment necessary is
dependent on the level of recreational
landings that are allowed under the
recreational harvest limit. In years
where the recreational harvest limit
increases from the previous year, it may
not be necessary to adjust measures
even if the previous year recreational
harvest limit had been exceeded if the
amount of the overage is less than the
increase in the limit. This process
occurs regardless of stock status or other
imposed statutory requirements. The
underlying reason for such adjustments
is to constrain the recreational sector
landings within the recreational harvest
limit which, in turn, is part of the total
fishing mortality permitted for the stock
in any given year. As previously
discussed, the annual level of fishing
mortality established for the stock is
established through a Council process
that includes a scientifically-based
recommendation for ABC from the SSC.
The entirety of the catch level process
considers both scientific and
management uncertainty and other
potential issues and is designed to
ensure that the stock is not overfished.
For scup, while the stock status would
suggest that overfishing is unlikely, the
DPSWG peer review panel and SSC
have indicated that sufficient
uncertainty exists within the new
assessment and catch levels should
proceed cautiously rather than be
increased rapidly.
Comment 4: A recreational fishing
advocacy group wrote in support of
extending the black sea bass fishing
season but objected to the Commission’s
approach of providing additional
buffering to account for management
uncertainty. The commenters state that
such buffering is arbitrary and
inconsistent with science-based
management. Furthermore, the
commenter states that there is
insufficient technical information in the
Commission’s decision to explain the
additional buffer.
Response: The additional buffer the
comment refers to is the percent
reduction in 2010 black sea bass
landings from 2009 levels required to
constrain recreational harvest below the
established RHL. Based on the 2009
landings data and the 2010 black sea
bass recreational harvest limit, a
minimum of a 21.4–percent reduction in
landings is required to ensure that
landings do not exceed the established
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limit. However, in selecting measures
for 2010, the Commission elected to
adopt measures (i.e., minimum fish size,
possession limit, and fishing season)
that provide an estimated 26–percent
reduction in landings. In their letter to
NMFS recommending adoption of
identical measures for Federal waters,
the Commission’s Black Sea Bass
Management Board indicated that the
additional 4.6–percent reduction in
landings was
selected to, ‘‘allow for a reasonable
conservation buffer to account for
management uncertainty in the harvest
estimates and the effectiveness of the
regulations.’’
NMFS has determined that this in an
appropriate application of management
uncertainty, consistent with the revised
National Standard 1 Guidance (NS 1
Guidance (74 FR 3178; January 16,
2009)). NMFS is implementing, through
this rule, measures identical to the
Commission-adopted black sea bass
recreational management measures
because the additional offset in landings
provides a greater likelihood of
constraining landings below the
established 2010 recreational harvest
limit. These measures were fully
supported and also recommended by
the Council, which also agreed that
some buffering was advisable given the
uncertainty of harvest estimates and
unknown effectiveness of the
regulations being implemented. NMFS
does not find the application of an
additional 4.6–percent calculated
reduction in landings as arbitrary;
rather, it represents a substantive
attempt by the Commission and Council
to quantify and buffer against issues that
led the 2009 black sea bass fishery to
exceed the established recreational
harvest limit for that year. In the NS 1
Guidance, NMFS recommends that in
situations where both scientific and
management-related uncertainty exist
for a particular fishery, both should be
addressed. While these requirements are
not yet effective for the FMP, the action
taken by the Commission, supported by
the Council, and implemented by NMFS
is consistent with the tenants of the NS
1 Guidance. The additional offset is not,
as the commenter suggests, an offset for
scientific uncertainty. Rather, it is as
previously indicated a buffer to account
for management uncertainty designed to
help ensure that 2010 recreational black
sea bass landings do not exceed the
established recreational harvest limit.
Comment 5: A recreational fishing
advocacy group supported including
January and February in the black sea
bass fishing season in addition to the
May 22–October 11 and November 1–
December 31 season implemented by
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this rule. The comment states that
Fishing Vessel Trip Reports (VTRs)
provided by charter/party vessels would
indicate that black sea bass landings
during these months are minimal and
that closing the season in January and
February provides no contribution to
the calculated reduction in landings.
Response: NMFS disagrees with the
comment that January and February
should be open for the 2010 fishing
season. What is at issue is actually the
2011 fishing year. January and February
2010 have already passed; however, the
rulemaking for 2011 black sea bass
management measures begins with a
Council meeting in December 2010. The
2010 black sea bass management
measures remain effective until
superseded by revised measures. If the
Council were to recommend a 2011
black sea bass fishing season that
included January and February, there
would be insufficient time to implement
such a season through the rulemaking
process.
There is a substantial issue that if
NMFS opened Federal waters in January
and February, effectively opening those
months retroactively for 2010 and for
2011 for the reasons previously
explained, state waters would not be
open unless the Commission
implemented comparable measures. In a
situation such as this wherein Federal
waters are open but state waters are
closed, Federally permitted vessels are
required to adhere to the more
restrictive set of measures. The net
effect of different fishing seasons in this
instance, barring comparable
Commission action, would prohibit
Federally permitted vessels from fishing
in either state or Federal waters.
NMFS has analyzed party/charter
VTR data from 2000–2009. These data
indicate that 58 unique vessels reported
landing or discarding recreationally
captured black sea bass within those
years. Reported landings totaled 260,442
lb (118 mt) and reported discards
totaled 26,073 lb (12 mt) for the time
period, averaging 26,044 landed lb per
year (12 mt). The average annual
landings are less than 1.5 percent of the
2010 black sea bass recreational harvest
limit. The commenters suggest that
landings of this magnitude be
considered de minimis and the fishery
opened. No de minimis provision is
included in the FMP and all mortality
on the stock must be considered when
establishing recreational management
measures. In addition, no
recommendation to open January and
February was forwarded by either the
Council or Commission.
VTRs are wholly self-reported by
party and charter vessel operators and,
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unlike commercial fisheries which have
vessel-by-vessel landing data to validate
the self-reported information,
recreational party/charter vessels have
no independent data validation
mechanism. The For-Hire Survey (FHS)
component of MRFSS does not yield a
vessel-by-vessel independent
assessment that is analogous to
commercial landing weighouts. As a
result, party/charter VTRs are not
utilized in stock assessments or as a
data source for management
decisionmaking. They are informative to
verify that there is indeed a January and
February black sea bass fishery by
Federally permitted vessels and the
magnitude of the fishery would appear
to be small. However, without a means
to independently verify the information
contained in the VTRs, there is no way
to know how representative or accurate
the reported data might be.
The reference to ‘‘no effective
reduction’’ made by the commenter
addresses a sampling deficiency in the
current MRFSS design. Landings in
MRFSS Wave 1 (January-February) are
not monitored on a coastwide basis.
However, pilot projects are underway to
address this deficiency by sampling
within Wave 1 as well as pilot studies
to examine the efficacy of estimation
procedures for when only small sample
sizes can be obtained by the MRFSS
survey. Both of these pilot projects may
lead to additional fishery-independent
information regarding Northeast Region
recreational fishing in January and
February. Because no sampling
currently occurs, when calculating
reduction or liberalization of landings
for an upcoming fishing year is
performed, the disposition of fishing in
January and February contribute no net
effect regardless of if the fishery is open
or closed because of the lack of
estimates for that time period.
Because the FMP does not provide for
a de minimis season and there are
clearly some magnitude of landings that
occur in January and February, NMFS is
disinclined to include those months in
the 2010 black sea bass fishing season.
The result of so doing would effectively
ensure that those months would be open
in 2011. No such recommendation was
forwarded by either the Commission or
Council. There is also the previously
mentioned issue about creating a
different set of measures for state and
Federal waters.
Comment 6: One comment stated that
NMFS uses MRFSS data inconsistently:
Using the data to indicate overages and
impose more restrictive measures, but
dismissing the data when liberalization
of measures can be implemented.
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Response: NMFS has taken a
consistent approach to utilization of
MRFSS data as the best available
information on recreational landings
and effort. Through this rule, NMFS is
implementing liberalized measures for
black sea bass, consistent with the
updated MRFSS data that indicate a
lower percent reduction in 2010
landings are needed relative to 2009.
Classification
The Administrator, Northeast Region,
NMFS, determined that this final rule
implementing the 2010 summer
flounder, scup, and black sea bass
recreational management measures is
necessary for the conservation and
management of the summer flounder,
scup, and black sea bass fisheries, and
that it is consistent with the MagnusonStevens Act and other applicable laws.
This final rule has been determined to
be not significant for purposes of
Executive Order 12866.
Included in this final rule is the FRFA
prepared pursuant to 5 U.S.C. 604(a).
The FRFA incorporates the economic
impacts described in the IRFA, a
summary of the significant issues raised
by the public comments in response to
the IRFA, NMFS’s responses to those
comments, and a summary of the
analyses completed to support the
action. Copies of the EA/RIR/IRFA and
supplement are available from the
Council and NMFS (see ADDRESSES).
Final Regulatory Flexibility Analysis
Statement of Objective and Need
A description of the reasons why this
action is being taken, and the objectives
of and legal basis for this final rule are
explained in the preambles to the
proposed rule and this final rule, and
are not repeated here.
A Summary of the Significant Issues
Raised by the Public Comments in
Response to the IRFA, a Summary of the
Assessment of the Agency of Such
Issues, and a Statement of Any Changes
Made in the Proposed Rule as a Result
of Such Comments
A summary of the comments received
and NMFS’s responses thereto is
contained in the preamble of this rule.
None of those comments addressed
specific information contained in the
IRFA economic analysis or the
economic impacts of the rule more
generally. As outlined in the preamble,
the black sea bass measures
implemented by this rule were changed
from those previously proposed. The
change in measures was a direct result
of comments received from the
Commission, Council, and interested
public.
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Description and Estimate of Number of
Small Entities to Which This Rule Will
Apply
The Council estimated that the
management measures could affect any
of the 948 vessels possessing a Federal
charter/party permit for summer
flounder, scup, and/or black sea bass in
2009, the most recent year for which
complete permit data are available.
However, only 328 vessels reported
active participation in the recreational
summer flounder, scup, and/or black
sea bass fisheries in 2008, the most
recent year for which complete fishing
vessel trip reports (i.e., logbooks) are
available.
Description of Projected Reporting,
Recordkeeping, and Other Compliance
Requirements
No additional reporting,
recordkeeping, or other compliance
requirements are included in this final
rule.
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Description of the Steps Taken to
Minimize Economic Impact on Small
Entities
No-action alternatives. The economic
analysis conducted in support of this
action assessed the impacts of the
various management alternatives. In the
EA, the no action alternative for each
species is defined as the continuation of
the management measures as codified
for the 2009 fishing season. The noaction measures were analyzed in
Alternative 2 for each species in the
Council’s EA/RIR/IRFA.
For summer flounder, the no-action
(coastwide) alternative of a 19.5–inch
(49.53–cm) minimum fish size, a twofish possession limit, and a May 1–
September 30 fishing season would
achieve the mortality objectives
required but would be more restrictive
than necessary for most states.
The no-action alternative for scup, a
10.5–inch (26.67–cm) minimum fish
size, a 15–fish possession limit, and
open seasons of January 1 through
February 28 and October 1 through
October 31, is not expected to reduce
landings from 2009 levels. If scup
Alternative 2 were adopted for 2010,
landings would be expected to be in the
4.0–million-lb (1,814–mt) range, thereby
exceeding the 3.01–million-lb (1,366–
mt) recreational harvest limit. This is
inconsistent with the objectives of the
FMP.
The no-action alternative for black sea
bass (a 12.5–in (31.75–cm) minimum
fish size, a 25–fish possession limit, and
no closed fishing season) would result
landings that exceed the 1.83–million lb
(830–mt) recreational harvest limit for
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2010 and, therefore, cannot be
continued for the 2010 fishing season.
Summer flounder alternatives. In
seeking to minimize the impact of
recreational management measures
(minimum fish size, possession limit,
and fishing season) on small entities
(i.e., Federal party/charter permit
holders), NMFS is constrained to
implementing measures that meet the
conservation objectives of the FMP and
Magnuson-Stevens Act.
The alternatives examined by the
Council and forwarded for
consideration by NMFS consisted of the
preferred alternative of state-by-state
conservation equivalency with a
precautionary default backstop, and the
non-preferred alternative of coastwide
measures. These were alternatives 1 and
2, respectively, in the Council’s EA/RIR/
IRFA. These two alternatives were
determined by the Council analyses to
satisfy the 2010 conservation objectives
for the recreational fishery, i.e., analysis
indicated that implementation of either
would constrain recreational landings
within the 2010 recreational harvest
limit. Therefore, either alternative
recreational management system could
be considered for implementation by
NMFS, as the critical metric of
satisfying the regulatory and statutory
requirements would be met by either.
Next, NMFS considered the
recommendation of both the Council
and Commission. Both groups
recommended implementation of stateby-state conservation equivalency, with
a precautionary default backstop. The
recommendations of both groups were
not unanimous: Some Council and
Commission members objected to the
use of conservation equivalency. In fact,
the State of New York filed litigation
seeking relief from conservation
equivalency implemented for both the
2008 and 2009 recreational summer
flounder fisheries. The litigation for
those cases, State of New York et al. v.
Locke et al. Civil Action Nos. 08–cv–
2503 and 09–cv–3196, remain
unresolved by the U.S. District Court
Eastern District of New York.
For NMFS to disapprove the Council’s
recommendation for conservation
equivalency and substitute coastwide
management measures, NMFS must
reasonably demonstrate that the
recommended measures are either
inconsistent with applicable law or
demonstrate that the conservation
objectives of the FMP will not be
achieved by implementing conservation
equivalency. NMFS does not find the
Council and Commission’s
recommendation to be inconsistent with
the implementing regulations of the
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FMP found at § 648.100 or the
Magnuson-Stevens Act.
The additional metric for
consideration applicable to the FRFA is
examination of the economic impacts of
the alternatives on small entities
consistent with the stated objectives of
applicable statutes. As previously
stated, both conservation equivalency
(alternative 1) and coastwide measures
(alternative 2) are projected to achieve
the conservation objectives in place for
the 2010 summer flounder recreational
fishery. However, the economic impacts
of the two alternatives are not equal:
The economic impacts on small entities
under the coastwide measures
management system would vary in
comparison to the conservation
equivalency system dependent on the
specific state wherein the small entities
operate.
Quantitative analysis of the economic
impacts associated with conservation
equivalency measures are not available.
Because the development of the
individual state measures occurs
concurrent to the NMFS rulemaking
process to ensure timely
implementation of final measures for
the 2010 recreational fishery, the
specific measures implemented by
states are not available for economic
impact analyses. Instead, qualitative
methods are utilized. The Council
analysis concluded, and NMFS agrees,
that conservation equivalency is
expected to minimize impacts on small
entities because individual states can
develop specific summer flounder
management measures that allow the
fishery to operate during each state’s
critical fishing periods while still
achieving conservation goals. To be
clear, there are individual states whose
conservation equivalency measures may
have a more adverse impact to some
small entities, dependent on the
restrictions imposed by the
Commission, than would coastwide
measures. New York stands out as such
a state. However, the one-size-fits-all
approach of coastwide measures would
impact a broader distribution of states
and small entities.
NMFS is implementing the Council
and Commission’s recommended stateby-state conservation equivalency
measures because: (1) NMFS finds no
compelling reason to disapprove the
Council and Commission’s
recommended 2010 management
system, as the management measures
contained in conservation equivalency
are projected to provide the necessary
restriction on recreational landings to
prevent the recreational harvest limit
from being exceeded; and (2) the net
economic impact to small entities on a
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coastwide basis are expected to be
mitigated, to the extent practicable, for
a much larger percentage of small
entities. Data provided by the Council
indicates that 328 federally permitted
party/charter vessels landed some
combination of summer flounder, scup,
and black sea bass in 2008, the most
recent year of available data. Within this
total, 49 vessels, or 15 percent, were
from New York. By inference, 85
percent of the small entities engaged in
recreational fishing would be impacted
less by the implementation of
conservation equivalency, assuming that
the impacts to New York small entities
are indeed greater under conservation
equivalency.
Scup alternatives. The options
available for scup recreational fisheries
management are constrained to a suite
of minimum fish size, possession limit,
and fishing season that achieves the
annual conservation objective expressed
through a recreational harvest limit on
landings. As outlined in the preamble,
the individual states have elected to
implement a state-waters conservation
equivalency system for the 2010 scup
recreational fishery that has no
comparable regulations for use in
Federal waters. The Commissionadopted measures are not expected to
constrain landings to the 2010 scup
recreational harvest limit. Thus, the
conservation objectives and the
recreational harvest limit are likely to be
compromised regardless of action taken
for Federal waters. Very little of the
scup recreational fishery occurs in
Federal waters. Rather than close
Federal waters to scup recreational
fishing, NMFS is implementing the
following measures: A 10.5–inch
(26.67–cm) minimum fish size; a 10–
fish per person possession limit; and an
open season of June 6–September 26.
These measures were not the most
conservative proposed by the Council as
they are projected to reduce 2010
landings by 29 percent from 2009 levels
if comparable measures had been
implemented in state waters.
Implementation of these measures
offers an alternative to outright closure
of Federal waters wherein all scup
encountered would be required to be
discarded. Instead, the limited amount
of scup recreational fishing that occurs
in Federal waters will have some
overlap with the measures implemented
for state waters by the Commission and
fish that would have been discarded
may be landed in limited numbers.
These minor landings are not expected
to add a substantial amount of
recreational fishing mortality to the
stock in 2010, nor is overfishing
expected to occur as a result of either
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the Federal or state measures
implemented for 2010. Estimates from
MRFSS indicate that the amount of scup
recreationally harvested in Federal
waters is typically 5 percent or less of
the total annual take.
The measures of alternative 1 were
also considered by NMFS. This would
have resulted in an 11–inch (27.94–cm)
minimum fish size, a longer season, and
identical possession limit when
compared to alternative 3. These
measures did not synchronize well with
the Commission measures and, while
more conservative--achieving a
projected 35 percent reduction in
landings from 2009 levels if similar
measures had been enacted in state
waters--NMFS found that the minimal
conservation benefit was outweighed by
the lack of consistency with measures
adopted for state waters. The impacts to
charter and party vessels were similar
between alternative 1 and 3 in the
Council’s analysis. Alternative 2 was
not considered for implementation as it
was not expected to effect any reduction
in 2010 scup landing levels.
Black sea bass alternatives. Similar to
both summer flounder and scup, the
options available for black sea bass
recreational management measures are
constrained to selecting a suite of
minimum fish size, possession limit,
and fishing season measures that
achieve the annual conservation
objectives. In this case, this final rule is
implementing measures that differ from
those originally proposed. This rule
implements the measures of alternative
4 (modified) contained in the EA/RIR/
IRFA addendum: A 12.5–inch (31.75–
cm) minimum fish size; a 25–fish
possession limit; and May 22–October
11 and November 1–December 31
fishing seasons. This alternative
provides the lowest associated
economic impacts to small entities.
Alternatives 1, 3, and 4 (unmodified)
were projected to achieve the
conservation objectives for the 2010
black sea bass fishery; however, given
the evolution of increasingly improved
data available during the recreational
management measures development,
these alternatives are now more
conservative than necessary relative to
the conservation objectives and have
higher associated economic impacts
than the measure being implemented
through this rule.
Small Entity Compliance Guide
Section 212 of the Small Business
Regulatory Enforcement Fairness Act of
1996 states that, for each rule or group
of related rules for which an agency is
required to prepare a FRFA, the agency
shall publish one or more guides to
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39177
assist small entities in complying with
the rule, and shall designate such
publications as ‘‘small entity compliance
guides.’’ The agency shall explain the
actions a small entity is required to take
to comply with a rule or group of rules.
As part of this rulemaking process, a
letter to permit holders that also serves
as the small entity compliance guide
was prepared and will be sent to all
holders of Federal party/charter permits
issued for the summer flounder, scup,
and black sea bass fisheries. In addition,
copies of this final rule and the small
entity compliance guide are available
from NMFS (see ADDRESSES) and at the
following website: https://
www.nero.noaa.gov.
List of Subjects in 50 CFR Part 648
Fisheries, Fishing, Reporting and
recordkeeping requirements.
Dated: July 1, 2010
Samuel D. Rauch III,
Deputy Assistant Administrator For
Regulatory Programs, National Marine
Fisheries Service.
For the reasons set out in the
preamble, 50 CFR part 648 is amended
as follows:
■
PART 648—FISHERIES OF THE
NORTHEASTERN UNITED STATES
1. The authority citation for part 648
continues to read as follows:
■
Authority: 16 U.S.C. 1801 et seq.
2. In § 648.103, paragraph (b) is
revised to read as follows:
■
§ 648.103
Minimum fish sizes.
*
*
*
*
*
(b) Unless otherwise specified
pursuant to § 648.107, the minimum
size for summer flounder is 19.5 inch
(49.53 cm) TL for all vessels that do not
qualify for a moratorium permit, and
charter boats holding a moratorium
permit if fishing with more than three
crew members, or party boats holding a
moratorium permit if fishing with
passengers for hire or carrying more
than five crew members.
*
*
*
*
*
■ 3. In § 648.107, paragraph (a)
introductory text and paragraph (b) are
revised to read as follows:
§ 648.107 Conservation equivalent
measures for the summer flounder fishery.
(a) The Regional Administrator has
determined that the recreational fishing
measures proposed to be implemented
by Massachusetts through North
Carolina for 2010 are the conservation
equivalent of the season, minimum fish
size, and possession limit prescribed in
§§ 648.102, 648.103, and 648.105(a),
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respectively. This determination is
based on a recommendation from the
Summer Flounder Board of the Atlantic
States Marine Fisheries Commission.
*
*
*
*
*
(b) Federally permitted vessels subject
to the recreational fishing measures of
this part, and other recreational fishing
vessels subject to the recreational
fishing measures of this part and
registered in states whose fishery
management measures are not
determined by the Regional
Administrator to be the conservation
equivalent of the season, minimum size,
and possession limit prescribed in
§§ 648.102, 648.103(b) and 648.105(a),
respectively, due to the lack of, or the
reversal of, a conservation equivalent
recommendation from the Summer
Flounder Board of the Atlantic States
Marine Fisheries Commission, shall be
subject to the following precautionary
default measures: Season - May 1
through September 30; minimum size 21.5 inches (54.61 cm); and possession
limit - two fish.
■ 4. In § 648.122, paragraph (g) is
revised to read as follows:
§ 648.122
Season and area restrictions.
*
*
*
*
*
(g) Time restrictions. Vessels that are
not eligible for a moratorium permit
under § 648.4(a)(6), and fishermen
subject to the possession limit specified
in § 648.125(a), may not possess scup,
except from June 6 through September
27. This time period may be adjusted
pursuant to the procedures in § 648.120.
■ 5. In § 648.125, the first sentence of
paragraph (a) is revised to read as
follows:
§ 648.122
Possession limit.
(a) No person shall possess more than
10 scup in, or harvested from, the EEZ
unless that person is the owner or
operator of a fishing vessel issued a
scup moratorium permit, or is issued a
scup dealer permit.***
*
*
*
*
*
■ 6. Section 648.142 is revised to read
as follows:
srobinson on DSKHWCL6B1PROD with RULES
§ 648.142
Time restrictions.
Vessels that are not eligible for a
moratorium permit under § 648.4(a)(7),
and fishermen subject to the possession
limit specified in § 648.145(a), may
possess black sea bass from May 22
through October 11 and November 1
through December 31, unless this time
period is adjusted pursuant to the
procedures in § 648.140.
[FR Doc. 2010–16651 Filed 7–7–10; 8:45 am]
BILLING CODE 3510–22–S
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 660
[Docket No. 100617272–0271–02]
RIN 0648–AY94
Magnuson-Stevens Act Provisions;
Fisheries Off West Coast States;
Pacific Coast Groundfish Fishery;
Biennial Specifications and
Management Measures
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule; harvest
specifications; correction.
AGENCY:
SUMMARY: This final rule revises the
optimum yields in the 2010
Specifications for darkblotched rockfish,
cowcod, and yelloweye rockfish. The
U.S. District Court for the Northern
District of California issued an Order on
April 29, 2010, vacating the 2009–2010
specifications for those three species,
and replaced the Specifications with the
most recent optimum yields that were
specified for 2007–2008. This rule
amends the regulatory requirements for
these three species in accordance with
the court’s order. This rule also corrects
a technical error in a table establishing
the 2010 canary rockfish optimum yield.
DATES: Effective July 2, 2010.
FOR FURTHER INFORMATION CONTACT:
Gretchen Hanshew (Northwest Region,
NMFS), phone: 206–526–6147, fax: 206–
526–6736 and e-mail:
gretchen.hanshew@noaa.gov.
SUPPLEMENTARY INFORMATION:
Electronic Access
This final rule is accessible via the
Internet at the Office of the Federal
Register’s Web site at https://
www.gpoaccess.gov/fr/.
Background information and documents
are available at the Pacific Fishery
Management Council’s website at
https://www.pcouncil.org/. Background
information and documents are also
available at the NMFS Northwest Region
Web site at https://www.nwr.noaa.gov/
Groundfish-Halibut/Groundfish-FisheryManagement/index.cfm.
Copies of the final environmental
impact statement (FEIS) for the 2009–
2010 Groundfish Specifications and
Management Measures are available
from Donald McIsaac, Executive
Director, Pacific Fishery Management
Council (Council), 7700 NE.
PO 00000
Frm 00046
Fmt 4700
Sfmt 4700
Ambassador Place, Portland, OR 97220,
phone: 503–820–2280.
Copies of additional reports referred
to in this document may also be
obtained from the Council. Copies of the
Record of Decision (ROD), final
regulatory flexibility analysis (FRFA),
and the Small Entity Compliance Guide
are available from William W. Stelle, Jr.,
Administrator, Northwest Region
(Regional Administrator), NMFS, 7600
Sand Point Way, NE., Seattle, WA
98115–0070.
Background
On December 31, 2008, NMFS
published a proposed rule to implement
the 2009–2010 specifications and
management measures for the Pacific
Coast groundfish fishery (73 FR 80516),
including, among other species,
darkblotched rockfish, cowcod, and
yelloweye rockfish. A final rule was
published on March 6, 2009 (74 FR
9874), which codified the specifications
and management measures in the CFR
(50 CFR part 660, subpart G). That
action set the 2009–2010 harvest
specifications and management
measures for groundfish taken in the
U.S. Exclusive Economic Zone (EEZ) off
the coasts of Washington, Oregon, and
California, and revised rebuilding plans
for four of seven overfished species,
consistent with the Magnuson-Stevens
Fishery Conservation and Management
Act (MSA) and the Pacific Coast
Groundfish Fishery Management Plan
(FMP). The existing and revised
rebuilding plans were consistent with
Amendment 16–4 to the FMP, and were
designed to comply with the rebuilding
requirements of the MSA.
In response to the latest in a series of
complaints filed in Natural Resources
Defense Council v. Locke, Civil Action
No. C 01–0421 JL, challenging the
rebuilding provisions in the FMP, the
U.S. District Court for the Northern
District of California vacated the 2009
and 2010 specifications for
darkblotched rockfish, cowcod, and
yelloweye rockfish. Order on Remedy,
Dkt. No. 342 (April 29, 2010) (Opinion).
The Court held that NMFS violated
National Standard 2 of the MSA by
‘‘failing to use the best scientific
information available on the economic
status of fishing communities in their
2009–2010 Biennial specifications and
Management Measures for the Pacific
Coast Groundfish Fishery (2009–2010
Specifications).’’ Further, the Court held
that NMFS established ‘‘rebuilding plans
for darkblotched rockfish, cowcod, and
yelloweye rockfish in the 2009–2010
Specifications that do not rebuild those
species in time periods that are ‘as short
E:\FR\FM\08JYR1.SGM
08JYR1
Agencies
[Federal Register Volume 75, Number 130 (Thursday, July 8, 2010)]
[Rules and Regulations]
[Pages 39170-39178]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-16651]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 648
[Docket No. 0907211158-0265-02]
RIN 0648-AY04
Fisheries of the Northeastern United States; Recreational
Management Measures for the Summer Flounder, Scup, and Black Sea Bass
Fisheries; Fishing Year 2010
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS implements recreational management measures for the 2010
summer flounder, scup, and black sea bass fisheries. These actions are
necessary to comply with regulations implementing the Summer Flounder,
Scup, and Black Sea Bass Fishery Management Plan (FMP) and to ensure
compliance with the Magnuson-Stevens Fishery Conservation and
Management Act (Magnuson-Stevens Act). The intent of these measures is
to prevent overfishing of the summer flounder, scup, and black sea bass
resources.
DATES: Effective August 9, 2010.
ADDRESSES: Copies of supporting documents used by the Summer Flounder,
Scup, and Black Sea Bass Monitoring Committees and of the Environmental
Assessment, Regulatory Impact Review, and Initial Regulatory
Flexibility Analysis (EA/RIR/IRFA) and EA/RIR/IRFA Addendum are
available from Daniel Furlong, Executive Director, Mid-Atlantic Fishery
Management Council, Room 2115, Federal Building, 800 N. State Street,
Suite 201, Dover, DE 19901. The EA/RIR/IRFA is also accessible via the
Internet at https://www.nero.noaa.gov. The Final Regulatory Flexibility
Analysis (FRFA) consists of the IRFA, public comments and responses
contained in this final rule, and the summary of impacts and
alternatives contained in this final rule. Copies of the small entity
compliance guide and EA/RIR/IRFA document and addendum are available
from Patricia A. Kurkul, Regional Administrator, Northeast Region,
NMFS, 55 Great Republic Drive, Gloucester, MA 01930-2276.
FOR FURTHER INFORMATION CONTACT: Michael Ruccio, Fishery Policy
Analyst, (978) 281-9104.
SUPPLEMENTARY INFORMATION:
Background
The summer flounder, scup, and black sea bass fisheries are managed
cooperatively by the Atlantic States Marine Fisheries Commission
(Commission) and the Mid-Atlantic Fishery Management Council (Council),
in consultation with the New England and South Atlantic Fishery
Management Councils. The FMP and its implementing regulations, which
are found at 50 CFR part 648, subparts A (general provisions), G
(summer flounder), H (scup), and I (black sea bass), describe the
process for specifying annual recreational management measures that
apply in the Exclusive Economic Zone (EEZ). The state from North
Carolina to Maine manage these fisheries within 3 nautical miles of
their coasts, under the Commission's plan for summer flounder, scup,
and black sea bass. The Federal regulations govern fishing activity in
the EEZ, as well as vessels possessing a Federal fisheries permit,
regardless of where they fish.
The 2010 coastwide recreational harvest limits, after deduction of
research set-aside (RSA), are 8,586,440 lb (3,896 mt) for summer
flounder; 3,011,074 lb (1,366 mt) for scup; and 1,830,390 lb (830 mt)
for black sea bass. The final 2010 quota specifications, inclusive of
the recreational harvest limits, were previously implemented by NMFS
effective January 1, 2010 (74 FR 67978; December 22, 2009), for summer
flounder and scup, and effective February 2, 2010, for black sea bass
(75 FR 6586).
The proposed rule to implement annual Federal recreational measures
for the 2010 summer flounder, scup, and black sea bass fisheries was
published on April 27, 2010 (75 FR 22087), along with proposed
management measures (minimum fish sizes, possession limits, and fishing
seasons) intended to keep annual recreational landings from exceeding
the specified harvest limits.
2010 Recreational Management Measures
Additional discussion on the development of the recreational
management measures appeared in the preamble of the proposed rule and
is not repeated here. All minimum fish sizes discussed below are total
length measurements of the fish, i.e., the straight-line distance from
the tip of the snout to the end of the tail while the fish is lying on
its side. For black sea bass, total length measurement does not include
the caudal fin tendril. All possession limits discussed below are per
person.
Summer Flounder Management Measures
The Commission notified the NMFS Northeast Regional Administrator
by letter dated April 6, 2010, that the 2010 summer flounder
recreational fishery management programs (i.e., minimum fish size,
possession limit, and fishing seasons) implemented by the states from
Massachusetts to North Carolina have been reviewed by the Commission's
Technical Committee and approved by the Commission's Summer Flounder
Management Board (SF Board). The correspondence indicates that the
Commission-approved management programs are projected to restrict 2010
recreational summer flounder coastwide landings consistent with the
state-specific requirements established by the Technical Committee and
SF Board through the Commission process.
Based on the recommendation of the Commission, the NMFS Northeast
Regional Administrator finds that the recreational summer flounder
fishing measures proposed to be implemented by the individual states
for 2010 are the conservation equivalent of the season, minimum size,
and possession limit prescribed in Sec. Sec. 648.102, 648.103, and
648.105(a), respectively. According to Sec. 648.107(a)(1), vessels
subject to the recreational fishing measures of this part and landing
summer flounder in a state with an approved conservation equivalency
program shall not be subject to Federal measures, and shall instead be
subject to the recreational fishing measures implemented by the state
in which they land. Section 648.107(a) has been amended to recognize
state-implemented measures as conservation equivalent of the coastwide
recreational management measures for 2010. For clarity, the 2010
[[Page 39171]]
summer flounder management measures adopted by the individual states
vary according to the state of landing, as specified in the following
table:
Table 1--2010 Commission Approved State-by-State Conservation Equivalent Recreational Management Measures for
Summer Flounder
----------------------------------------------------------------------------------------------------------------
Minimum Fish Possession
Size Limit
State ----------------- (number of Fishing Season
inches cm fish)
----------------------------------------------------------------------------------------------------------------
MA 18.5 46.99 5 May 22-September 6
----------------------------------------------------------------------------------------------------------------
RI 19.5 49.53 6 May 1-December 31
----------------------------------------------------------------------------------------------------------------
CT 19.5 49.53 3 May 15-August 25
----------------------------------------------------------------------------------------------------------------
NY 21.0 53.34 2 May 15-September 6
----------------------------------------------------------------------------------------------------------------
NJ 18.0 45.72 6 May 29-September 6
----------------------------------------------------------------------------------------------------------------
DE 18.5 46.99 4 January 1-October 13
----------------------------------------------------------------------------------------------------------------
MD 19.0 48.26 3 April 17 through November 22
----------------------------------------------------------------------------------------------------------------
VA 18.5 46.99 4 January 1 through December 31
----------------------------------------------------------------------------------------------------------------
NC\1\ 15.0 38.10 8 January 1 through December 31
----------------------------------------------------------------------------------------------------------------
\1\ Pamlico Sound, NC--No person may possess flounder less than 14.0 in (35.56 cm) total length (TL) taken from
internal waters for recreational purposes west of a line beginning at a point on Point of Marsh in Carteret
County at 35[deg]04.6166'N lat.-76[deg]27.8000'W long., then running northeasterly to a point at Bluff Point
in Hyde County at 35[deg]19.7000'N lat.-76[deg]09.8500'W long. In Core and Clubfoot creeks, the Highway 101
Bridge constitutes the boundary north of which flounder must be at least 14.0 (35.56 cm) in TL.
Albemarle Sound, NC--No person may possess flounder less than 14.0 in (35.56 cm) TL taken from internal waters
for recreational purposes west of a line beginning at a point 35[deg]57.3950'N lat.- 76[deg]00.8166'W long. on
Long Shoal Point; running easterly to a point 35[deg]56.7316'N lat.-75[deg]59.3000' W long. near Marker ``5''
in Alligator River; running northeasterly along the Intracoastal Waterway to a point 36[deg]09.3033'N lat.-
75[deg]53.4916'W long. near Marker ``171'' at the mouth of North River; running northwesterly to a point
36[deg]09.9093'N lat.-75[deg]54.6601'W long. on Camden Point.
Browns Inlet South, NC--No person may possess flounder less than 14.0 in (35.56 cm) TL in internal and Atlantic
Ocean fishing waters for recreational purposes west and south of a line beginning at a point 34[deg]37.0000'N
lat.-77[deg]15.000'W long.; running southeasterly to a point 34[deg]32.0000'N lat.-77[deg]10.0000'W long.
Scup Management Measures
This rule implements the measures contained in the April 27, 2010,
proposed rule: A 10.5-in (26.67-cm) minimum fish size, a 10-fish per
person possession limit, and an open season of June 6 through September
26.
Table 2--2010 Scup Recreational Management Measures
----------------------------------------------------------------------------------------------------------------
Minimum Fish
Size Possession
Fishery ------------------ Limit Fishing Season
inches cm
----------------------------------------------------------------------------------------------------------------
Scup 10.5 26.674 10 fish June 6 through September
26
----------------------------------------------------------------------------------------------------------------
The scup fishery in state waters will be managed under a regional
conservation equivalency system developed by the Commission over the
last 8 years. Because the Federal FMP does not contain provisions for
conservation equivalency, and states may adopt their own unique
measures, the Federal and state recreational scup management measures
will differ for 2010. In accordance with Sec. 648.4(b)(1)(i), when
Federal, state, and local requirements differ, federally permitted scup
vessels are required to adhere to the most restrictive requirement
regardless of where the vessel fishes.
Black Sea Bass Management Measures
This rule implements the black sea bass measures adopted by the
Commission for 2010: A 12.5-in (31.75-cm) minimum fish size, a 25-fish
per person possession limit and fishing seasons from May 22-October 11
and November 1-December 31.
Changes from the Proposed Rule
NMFS had proposed in the April 27, 2010 (75 FR 22087), rule to
implement the Council-preferred measures (12.5-in (31.75-cm) minimum
fish size, 25-fish possession limit, and fishing seasons of May 22-
August 8 and September 4-October 4) for the 2010 black sea bass
recreational fishery. NMFS anticipated additional data that might
permit liberalization of the 2010 measures would become available in
the interim between publication of the proposed and final rules. These
data, from the
[[Page 39172]]
Marine Recreational Fisheries Statistics Survey (MRFSS), became
available in late April.
The final MRFSS data indicated that 2009 landings of black sea bass
were 2.31 million lb (1,048 mt). Prior to the release of these data,
black sea bass landing estimates were used for the months of September
and October 2009. At the time of the proposed rule, the best available
information, which included estimates for September and October,
indicated that 2009 recreational black sea bass landings were
approximately 3.31 million lb (1,501 mt). The Council's originally
preferred measures contained in the proposed rule would have reduced
2010 landings by 44 percent from 2009 levels, consistent with the
assumption that 2009 landings were 3.31 million lb (1,501 mt). However,
given the final 2009 landings data, a 21-percent reduction in 2010
landings from 2009 levels is necessary.
Many had expressed concern during the management measures
development process that actual landings from the 2-month time period
in 2009 would be significantly different from any generated estimates,
owing in part to the 108-day closure of the black sea bass recreational
fishery in the Federal waters of the EEZ that was implemented by NMFS
effective October 5, 2009 (74 FR 51092). Because of the timing for
Council and Commission meetings and the proposed rule 30 day comment
period, NMFS provided a contextual framework for the likelihood that
additional data would be available for analysis and solicited specific
comments on alternative management measures in the proposed rule (75 FR
22087; April 27, 2010).
The Commission had an opportunity to analyze the final 2009 MRIP
landings data prior to its May 2010 meeting. During this meeting, the
Commission adopted the measures now implemented through this final
rule. These measures are projected to reduce landings by 26 percent
from 2009 levels. The Commission adopted measures that were slightly
more precautionary (i.e., greater than a 21-percent reduction in 2010
landings from 2009 levels) to allow for a reasonable conservation
buffer to account for management uncertainty in the harvest estimates
and the effectiveness of the regulations. The Council, as well as
members of the public and recreational fishing advocacy groups,
provided written comment fully supporting implementation of the less
restrictive management measures adopted by the Commission. NMFS finds
the measures make use of the best available information in as timely a
fashion as the development, review, and implementation process will
permit. In addition, NMFS finds that the measures implemented in this
final rule provide some buffer to offset management-related uncertainty
and mitigate foregone recreational opportunity, thereby reducing
adverse socio-economic impacts. Thus, NMFS is implementing these
measures for the 2010 fishing season, even though they were not
contained in the proposed rule.
Table 3--2010 Black Sea Bass Recreational Management Measures
----------------------------------------------------------------------------------------------------------------
Minimum Fish
Size Possession
Fishery ------------------ Limit Fishing Season
inches cm
----------------------------------------------------------------------------------------------------------------
Black Sea Bass 12.5 31.75 25 fish May 22-October 11 and
November 1-December 31
----------------------------------------------------------------------------------------------------------------
Comments and Responses
Eight comment letters were received regarding the proposed
recreational management measures. The Commission's Black Sea Bass
Management Board provided the revised 2010 black sea bass measures
adopted for state waters as comments on the proposed rule and
recommended similar measures be adopted for Federal waters. Five
comment letters, including one from the Council, spoke in support of
the Commission's revised 2010 black sea bass measures and urged NMFS to
adopt similar measures for Federal waters. For clarity, NMFS is
implementing, through this rule, the identical black sea bass measures
adopted by the Commission and with the full support of the Council for
the 2010 black sea bass recreational fishery in Federal waters.
One recreational fishery advocacy group wrote in favor of the
summer flounder conservation equivalency system being implemented
through this rule.
Comments that require responses are addressed below. Similar
comments were consolidated for NMFS's responses:
Comment 1: One commenter asked why commercial summer flounder
fishermen can keep fish smaller than most recreational minimum fish
sizes implemented by states through conservation equivalency. This
commenter stated that most large summer flounder are female and the
utilization of high recreational minimum fish sizes will catch a
disproportionately high number of female fish and could negatively
impact stock rebuilding efforts.
Response: The issue of different minimum fish sizes between
commercial and recreational fisheries is often raised. Minimum fish
sizes for both sectors are implemented by NMFS based on recommendations
received from the Council. In regards to summer flounder, the minimum
commercial fish size has been set at 14 in (35.56 cm) since the late
1990s. The minimum commercial size was established following mesh size
selectivity studies conducted for implementation of the original Summer
Flounder FMP. These mesh studies considered the capabilities of certain
mesh sizes to not encounter fish of certain sizes.
The Council has recommended the 14-in (35.56-cm) minimum commercial
summer flounder size to address National Standard 9 of the Magnuson-
Stevens Act. National Standard 9 requires that conservation and
management measures shall, to the extent practicable, minimize bycatch
and, when bycatch cannot be avoided, minimize the mortality of such
bycatch. Commercial fishing conducted with bottom tending mobile gear,
such as trawl nets, is less discriminating than recreational hook-and-
line fishing gear. Thus, commercial fishing operations tend to capture
a wider size range and higher numbers of summer flounder than do
recreational fishermen. The 14-in (35.56-cm) size strikes a balance
between converting potential discards to landings and ensuring summer
flounder have an opportunity to spawn before becoming legal minimum
commercial
[[Page 39173]]
size. The current mesh size required for most summer flounder trawl
gear is 5.5 in (13.97 cm) and is engineered to catch fish 14 in (35.56
cm) and larger.
Recreational minimum fish size has been used as a tool to constrain
landings in the recreational fishery. Recreationally captured summer
flounder have a lower associated mortality than do those captured by
bottom-tending mobile commercial gear such as trawl nets and scallop
dredges. Eighty percent of commercially discarded summer flounder are
assumed to be dead or will die after release. By contrast, the most
recent assessment for summer flounder used recent research information
that indicated the mortality rate for recreationally caught and
released summer flounder was 10 percent.
The concept that recreational fisheries target larger, typically
female fish has been discussed and examined in recent stock
assessments. Additional research on stock sex ratios, natural and
fishing mortality by sex and size, and potentially different growth and
maturity rates by sex needs further examination for definitive
conclusions on potential impacts of the management strategy that has
been employed; however, current stock projections indicate that the
summer flounder stock will be rebuilt prior to the January 1, 2013,
rebuilding deadline.
Comment 2: One comment suggested that summer flounder management
measures should be two fish in the 14 to18-in (35.56 to 45.72-cm) size
range and four fish over 18 in (45.72 cm).
Response: The Council-conducted analysis for the 2010 summer
flounder recreational management measure coastwide alternatives
indicated a 19-in (48.26-cm) minimum fish size, 2-fish possession
limit, and coastwide season from May 1 to September 30 was predicted to
constrain 2010 landings to the 8.85-million-lb (3,896-mt) recreational
harvest limit. The commenter's recommended management measures are
substantially more liberal than this, the most liberal coastwide
measures analyzed and considered by the Council. Thus, the commenter's
suggested measures would likely result in landings well above the
recreational harvest limit. Because such measures would not adequately
constrain the 2010 recreational summer flounder fishery and would
likely exceed the established recreational harvest limit, NMFS finds
that such measures would be inconsistent with the goals and objectives
of the FMP and the Magnuson-Stevens Act.
NMFS is implementing, through this final rule, conservation
equivalency wherein individual state measures approved through the
Commission process are found to be equivalent to the coastwide
measures. In the conservation equivalency process, individual states
have the ability to modify the minimum fish size, possession limits,
and fishing season consistent with Commission-imposed requirements
before NMFS ultimately elects to implement conservation equivalency or
coastwide measures for the fishery. States have some ability to adjust
management measures in a manner that best suits the needs of the
anglers and fisheries prosecuted in the waters adjacent to their
respective state. Some states have developed and implemented, through
the Commission process, minimum fish sizes similar to those suggested
by the commenter. NMFS has, in turn, adopted through this rule,
conservation equivalency for Federal waters.
Comment 3: One recreational fishery angling group opposed the
proposed scup recreational management measures stating that (1) the
scup stock is rebuilt, (2) annual catch limits (ACLs) and
accountability measures (AMs) are not yet a statutory requirement for
the scup fishery, (3) that the 10-fish per person possession limit will
dissuade potential party/charter anglers from booking trips, and (4)
that there is no conservation or legal requirement to reduce
recreational scup landings for 2010. The commenter did not suggest any
alternative measures and did acknowledge that a very small percentage
of annual recreational scup landings occur in Federally-managed waters
under the jurisdiction of NMFS.
Response: In response, NMFS agrees that the best available
scientific information does indicate that the scup stock has been
rebuilt, thereby satisfying the rebuilding requirements for the
previously overfished stock.
NMFS notified the Council on April 22, 2009, that the results of a
2008 externally peer reviewed Data Poor Stocks Working Group (DPSWG)
assessment of scup had found that the stock had achieved and exceeded
the required rebuilding biomass target. In that same correspondence,
NMFS further relayed that the peer-review panel from the DPSWG
indicated that the assessment contained a high degree of uncertainty.
In its final report, the peer review panel recommended:
''...that rapid increases in quota to meet the revised MSY
[Maximum Sustained Yield] would be unwarranted given uncertainties
in recent [scup] recruitments. A more gradual increase in quotas is
a preferred approach reflective of the uncertainty in the [scup]
model estimates and stock status.''
The Council's SSC has adhered to the peer review panel's
recommendation in setting scup catch levels. For 2010, the SSC
recommended a 10-percent increase in Total Allowable Catch (TAC) as the
ABC level from the 2009 levels. The recreational harvest limit is a
derivative of the overall TAC.
While the perception of the scup stock has changed and is more
favorable than recent years and the statutory requirements for stock
rebuilding have been satisfied, the catch recommendations from the
Council's scientific advisory body, the SSC, has remained precautionary
in light of uncertainty associated with the revised stock assessment.
NMFS, in turn, has implemented the Council's recommendation for catch
levels as guided by the SSC's ABC recommendation. The SSC and Council's
Scup Monitoring Committee will review updated stock assessment
information in June 2010 before making catch level recommendation for
the 2011 fishing year.
While the requirement for stocks not subject to overfishing to have
in place ACLs and AMs, as required by the Magnuson-Stevens Act, does
not take effect until 2011, the Council has put into practice the
utilization of its SSC for catch level advice. Utilization of the SSC
in catch level recommendations did not result in a delayed
implementation phase-in period when the Magnuson-Stevens Act was
reauthorized in 2006. The SSC has been involved in making ABC
recommendations since 2008 for the 2009 fishing year.
The SSC brings to bear considerable scientific expertise in making
catch level recommendations. As such, the ABC recommended by the SSC
sets the standard for scientifically justifiable catch levels. For the
Council or NMFS to deviate from the SSC-recommended ABC would require
sufficient justification to explain why an alternate catch level was
the more appropriate and a better use of the best available scientific
information. In the case of scup, the SSC expressed reservations about
the information provided by the most recent stock assessment and
recommended an ABC that, relative to the estimated total biomass of
scup, is risk averse.
The Council may further reduce the ABC recommended by the SSC for
additional considerations, consistent with the requirements of National
Standard 1 of the Magnuson-Stevens Act to achieve Optimal Yield (OY) on
a continuing basis. NMFS provided a detailed response to similar
comments that ACLs and AMs are not yet requirements and that the 2010
scup catch level had been set too low to achieve OY on a continuing
basis in the
[[Page 39174]]
2010 specifications final rule (74 FR 67978, December 22, 2009). Those
responses are not repeated here, but are instead incorporated by
reference. NMFS acknowledges the commenter's concern that the scup
stock status and catch level recommendations appear to be at odds with
one another; however, as explained, the SSC and Council have taken a
precautionary approach in managing the scup stock, consistent with
assessment-related advice to do so. This approach continues to be
supported by NMFS.
As part of the regulatory impact review and general economic impact
analyses performed for the 2010 recreational management measures, the
Council provided an analysis of the potential impacts of a 10-fish per
person possession limit for scup. The analysis concluded that up to
2.24 percent of party/charter vessels could be impacted by the 10-fish
possession limit. While this would suggest that the impact is low, the
analysis indicated that predicting year-to-year angler behavior in
response to numerous influential factors, including regulatory changes,
is difficult. The Council performed an analysis of all potential
combination of summer flounder, scup, and black sea bass alternatives
with a hypothetical 25- and 50-percent reduction in fishing trips. The
range of impacts varies considerably from a low of $399 per vessel in
Delaware to up to $44,000 per vessel in North Carolina. These are total
impacts, inclusive of all potential changes for summer flounder, scup,
and black sea bass management measures and up to a 50-percent reduction
in angler trips.
Furthermore, the majority of scup party/charter landings occur in
state waters and may occur on vessels without Federal permits. In such
situations, the data necessary to quantify potential impacts are
unavailable as permit data are utilized as the basis for impact
assessment. See the Council's EA/RIR/IRFA document for additional
detail; information on obtaining a copy of the document is provided
under the ADDRESSES section of the preamble.
Given the minor magnitude of recreational scup fishing in Federal
waters, the economic impacts associated with the implemented measures
are expected to be equally minor relative to the entire scup
recreational fishery.
Under the recreational fishery management methods utilized by the
Council's Scup Monitoring Committee to develop measures designed to
constrain recreational landings to the recreational harvest limit, the
level of landings in the preceding year are used as a basis for
calculating the effectiveness of measures for the upcoming fishing year
relative to the catch level. More simply stated, when landings in the
previous year exceed the recreational harvest limit for the current
year, measures are adjusted. The amount of adjustment necessary is
dependent on the level of recreational landings that are allowed under
the recreational harvest limit. In years where the recreational harvest
limit increases from the previous year, it may not be necessary to
adjust measures even if the previous year recreational harvest limit
had been exceeded if the amount of the overage is less than the
increase in the limit. This process occurs regardless of stock status
or other imposed statutory requirements. The underlying reason for such
adjustments is to constrain the recreational sector landings within the
recreational harvest limit which, in turn, is part of the total fishing
mortality permitted for the stock in any given year. As previously
discussed, the annual level of fishing mortality established for the
stock is established through a Council process that includes a
scientifically-based recommendation for ABC from the SSC. The entirety
of the catch level process considers both scientific and management
uncertainty and other potential issues and is designed to ensure that
the stock is not overfished. For scup, while the stock status would
suggest that overfishing is unlikely, the DPSWG peer review panel and
SSC have indicated that sufficient uncertainty exists within the new
assessment and catch levels should proceed cautiously rather than be
increased rapidly.
Comment 4: A recreational fishing advocacy group wrote in support
of extending the black sea bass fishing season but objected to the
Commission's approach of providing additional buffering to account for
management uncertainty. The commenters state that such buffering is
arbitrary and inconsistent with science-based management. Furthermore,
the commenter states that there is insufficient technical information
in the Commission's decision to explain the additional buffer.
Response: The additional buffer the comment refers to is the
percent reduction in 2010 black sea bass landings from 2009 levels
required to constrain recreational harvest below the established RHL.
Based on the 2009 landings data and the 2010 black sea bass
recreational harvest limit, a minimum of a 21.4-percent reduction in
landings is required to ensure that landings do not exceed the
established limit. However, in selecting measures for 2010, the
Commission elected to adopt measures (i.e., minimum fish size,
possession limit, and fishing season) that provide an estimated 26-
percent reduction in landings. In their letter to NMFS recommending
adoption of identical measures for Federal waters, the Commission's
Black Sea Bass Management Board indicated that the additional 4.6-
percent reduction in landings was
selected to, ``allow for a reasonable conservation buffer to
account for management uncertainty in the harvest estimates and the
effectiveness of the regulations.''
NMFS has determined that this in an appropriate application of
management uncertainty, consistent with the revised National Standard 1
Guidance (NS 1 Guidance (74 FR 3178; January 16, 2009)). NMFS is
implementing, through this rule, measures identical to the Commission-
adopted black sea bass recreational management measures because the
additional offset in landings provides a greater likelihood of
constraining landings below the established 2010 recreational harvest
limit. These measures were fully supported and also recommended by the
Council, which also agreed that some buffering was advisable given the
uncertainty of harvest estimates and unknown effectiveness of the
regulations being implemented. NMFS does not find the application of an
additional 4.6-percent calculated reduction in landings as arbitrary;
rather, it represents a substantive attempt by the Commission and
Council to quantify and buffer against issues that led the 2009 black
sea bass fishery to exceed the established recreational harvest limit
for that year. In the NS 1 Guidance, NMFS recommends that in situations
where both scientific and management-related uncertainty exist for a
particular fishery, both should be addressed. While these requirements
are not yet effective for the FMP, the action taken by the Commission,
supported by the Council, and implemented by NMFS is consistent with
the tenants of the NS 1 Guidance. The additional offset is not, as the
commenter suggests, an offset for scientific uncertainty. Rather, it is
as previously indicated a buffer to account for management uncertainty
designed to help ensure that 2010 recreational black sea bass landings
do not exceed the established recreational harvest limit.
Comment 5: A recreational fishing advocacy group supported
including January and February in the black sea bass fishing season in
addition to the May 22-October 11 and November 1-December 31 season
implemented by
[[Page 39175]]
this rule. The comment states that Fishing Vessel Trip Reports (VTRs)
provided by charter/party vessels would indicate that black sea bass
landings during these months are minimal and that closing the season in
January and February provides no contribution to the calculated
reduction in landings.
Response: NMFS disagrees with the comment that January and February
should be open for the 2010 fishing season. What is at issue is
actually the 2011 fishing year. January and February 2010 have already
passed; however, the rulemaking for 2011 black sea bass management
measures begins with a Council meeting in December 2010. The 2010 black
sea bass management measures remain effective until superseded by
revised measures. If the Council were to recommend a 2011 black sea
bass fishing season that included January and February, there would be
insufficient time to implement such a season through the rulemaking
process.
There is a substantial issue that if NMFS opened Federal waters in
January and February, effectively opening those months retroactively
for 2010 and for 2011 for the reasons previously explained, state
waters would not be open unless the Commission implemented comparable
measures. In a situation such as this wherein Federal waters are open
but state waters are closed, Federally permitted vessels are required
to adhere to the more restrictive set of measures. The net effect of
different fishing seasons in this instance, barring comparable
Commission action, would prohibit Federally permitted vessels from
fishing in either state or Federal waters.
NMFS has analyzed party/charter VTR data from 2000-2009. These data
indicate that 58 unique vessels reported landing or discarding
recreationally captured black sea bass within those years. Reported
landings totaled 260,442 lb (118 mt) and reported discards totaled
26,073 lb (12 mt) for the time period, averaging 26,044 landed lb per
year (12 mt). The average annual landings are less than 1.5 percent of
the 2010 black sea bass recreational harvest limit. The commenters
suggest that landings of this magnitude be considered de minimis and
the fishery opened. No de minimis provision is included in the FMP and
all mortality on the stock must be considered when establishing
recreational management measures. In addition, no recommendation to
open January and February was forwarded by either the Council or
Commission.
VTRs are wholly self-reported by party and charter vessel operators
and, unlike commercial fisheries which have vessel-by-vessel landing
data to validate the self-reported information, recreational party/
charter vessels have no independent data validation mechanism. The For-
Hire Survey (FHS) component of MRFSS does not yield a vessel-by-vessel
independent assessment that is analogous to commercial landing
weighouts. As a result, party/charter VTRs are not utilized in stock
assessments or as a data source for management decisionmaking. They are
informative to verify that there is indeed a January and February black
sea bass fishery by Federally permitted vessels and the magnitude of
the fishery would appear to be small. However, without a means to
independently verify the information contained in the VTRs, there is no
way to know how representative or accurate the reported data might be.
The reference to ``no effective reduction'' made by the commenter
addresses a sampling deficiency in the current MRFSS design. Landings
in MRFSS Wave 1 (January-February) are not monitored on a coastwide
basis. However, pilot projects are underway to address this deficiency
by sampling within Wave 1 as well as pilot studies to examine the
efficacy of estimation procedures for when only small sample sizes can
be obtained by the MRFSS survey. Both of these pilot projects may lead
to additional fishery-independent information regarding Northeast
Region recreational fishing in January and February. Because no
sampling currently occurs, when calculating reduction or liberalization
of landings for an upcoming fishing year is performed, the disposition
of fishing in January and February contribute no net effect regardless
of if the fishery is open or closed because of the lack of estimates
for that time period.
Because the FMP does not provide for a de minimis season and there
are clearly some magnitude of landings that occur in January and
February, NMFS is disinclined to include those months in the 2010 black
sea bass fishing season. The result of so doing would effectively
ensure that those months would be open in 2011. No such recommendation
was forwarded by either the Commission or Council. There is also the
previously mentioned issue about creating a different set of measures
for state and Federal waters.
Comment 6: One comment stated that NMFS uses MRFSS data
inconsistently: Using the data to indicate overages and impose more
restrictive measures, but dismissing the data when liberalization of
measures can be implemented.
Response: NMFS has taken a consistent approach to utilization of
MRFSS data as the best available information on recreational landings
and effort. Through this rule, NMFS is implementing liberalized
measures for black sea bass, consistent with the updated MRFSS data
that indicate a lower percent reduction in 2010 landings are needed
relative to 2009.
Classification
The Administrator, Northeast Region, NMFS, determined that this
final rule implementing the 2010 summer flounder, scup, and black sea
bass recreational management measures is necessary for the conservation
and management of the summer flounder, scup, and black sea bass
fisheries, and that it is consistent with the Magnuson-Stevens Act and
other applicable laws.
This final rule has been determined to be not significant for
purposes of Executive Order 12866.
Included in this final rule is the FRFA prepared pursuant to 5
U.S.C. 604(a). The FRFA incorporates the economic impacts described in
the IRFA, a summary of the significant issues raised by the public
comments in response to the IRFA, NMFS's responses to those comments,
and a summary of the analyses completed to support the action. Copies
of the EA/RIR/IRFA and supplement are available from the Council and
NMFS (see ADDRESSES).
Final Regulatory Flexibility Analysis
Statement of Objective and Need
A description of the reasons why this action is being taken, and
the objectives of and legal basis for this final rule are explained in
the preambles to the proposed rule and this final rule, and are not
repeated here.
A Summary of the Significant Issues Raised by the Public Comments in
Response to the IRFA, a Summary of the Assessment of the Agency of Such
Issues, and a Statement of Any Changes Made in the Proposed Rule as a
Result of Such Comments
A summary of the comments received and NMFS's responses thereto is
contained in the preamble of this rule. None of those comments
addressed specific information contained in the IRFA economic analysis
or the economic impacts of the rule more generally. As outlined in the
preamble, the black sea bass measures implemented by this rule were
changed from those previously proposed. The change in measures was a
direct result of comments received from the Commission, Council, and
interested public.
[[Page 39176]]
Description and Estimate of Number of Small Entities to Which This Rule
Will Apply
The Council estimated that the management measures could affect any
of the 948 vessels possessing a Federal charter/party permit for summer
flounder, scup, and/or black sea bass in 2009, the most recent year for
which complete permit data are available. However, only 328 vessels
reported active participation in the recreational summer flounder,
scup, and/or black sea bass fisheries in 2008, the most recent year for
which complete fishing vessel trip reports (i.e., logbooks) are
available.
Description of Projected Reporting, Recordkeeping, and Other Compliance
Requirements
No additional reporting, recordkeeping, or other compliance
requirements are included in this final rule.
Description of the Steps Taken to Minimize Economic Impact on Small
Entities
No-action alternatives. The economic analysis conducted in support
of this action assessed the impacts of the various management
alternatives. In the EA, the no action alternative for each species is
defined as the continuation of the management measures as codified for
the 2009 fishing season. The no-action measures were analyzed in
Alternative 2 for each species in the Council's EA/RIR/IRFA.
For summer flounder, the no-action (coastwide) alternative of a
19.5-inch (49.53-cm) minimum fish size, a two-fish possession limit,
and a May 1-September 30 fishing season would achieve the mortality
objectives required but would be more restrictive than necessary for
most states.
The no-action alternative for scup, a 10.5-inch (26.67-cm) minimum
fish size, a 15-fish possession limit, and open seasons of January 1
through February 28 and October 1 through October 31, is not expected
to reduce landings from 2009 levels. If scup Alternative 2 were adopted
for 2010, landings would be expected to be in the 4.0-million-lb
(1,814-mt) range, thereby exceeding the 3.01-million-lb (1,366-mt)
recreational harvest limit. This is inconsistent with the objectives of
the FMP.
The no-action alternative for black sea bass (a 12.5-in (31.75-cm)
minimum fish size, a 25-fish possession limit, and no closed fishing
season) would result landings that exceed the 1.83-million lb (830-mt)
recreational harvest limit for 2010 and, therefore, cannot be continued
for the 2010 fishing season.
Summer flounder alternatives. In seeking to minimize the impact of
recreational management measures (minimum fish size, possession limit,
and fishing season) on small entities (i.e., Federal party/charter
permit holders), NMFS is constrained to implementing measures that meet
the conservation objectives of the FMP and Magnuson-Stevens Act.
The alternatives examined by the Council and forwarded for
consideration by NMFS consisted of the preferred alternative of state-
by-state conservation equivalency with a precautionary default
backstop, and the non-preferred alternative of coastwide measures.
These were alternatives 1 and 2, respectively, in the Council's EA/RIR/
IRFA. These two alternatives were determined by the Council analyses to
satisfy the 2010 conservation objectives for the recreational fishery,
i.e., analysis indicated that implementation of either would constrain
recreational landings within the 2010 recreational harvest limit.
Therefore, either alternative recreational management system could be
considered for implementation by NMFS, as the critical metric of
satisfying the regulatory and statutory requirements would be met by
either.
Next, NMFS considered the recommendation of both the Council and
Commission. Both groups recommended implementation of state-by-state
conservation equivalency, with a precautionary default backstop. The
recommendations of both groups were not unanimous: Some Council and
Commission members objected to the use of conservation equivalency. In
fact, the State of New York filed litigation seeking relief from
conservation equivalency implemented for both the 2008 and 2009
recreational summer flounder fisheries. The litigation for those cases,
State of New York et al. v. Locke et al. Civil Action Nos. 08-cv-2503
and 09-cv-3196, remain unresolved by the U.S. District Court Eastern
District of New York.
For NMFS to disapprove the Council's recommendation for
conservation equivalency and substitute coastwide management measures,
NMFS must reasonably demonstrate that the recommended measures are
either inconsistent with applicable law or demonstrate that the
conservation objectives of the FMP will not be achieved by implementing
conservation equivalency. NMFS does not find the Council and
Commission's recommendation to be inconsistent with the implementing
regulations of the FMP found at Sec. 648.100 or the Magnuson-Stevens
Act.
The additional metric for consideration applicable to the FRFA is
examination of the economic impacts of the alternatives on small
entities consistent with the stated objectives of applicable statutes.
As previously stated, both conservation equivalency (alternative 1) and
coastwide measures (alternative 2) are projected to achieve the
conservation objectives in place for the 2010 summer flounder
recreational fishery. However, the economic impacts of the two
alternatives are not equal: The economic impacts on small entities
under the coastwide measures management system would vary in comparison
to the conservation equivalency system dependent on the specific state
wherein the small entities operate.
Quantitative analysis of the economic impacts associated with
conservation equivalency measures are not available. Because the
development of the individual state measures occurs concurrent to the
NMFS rulemaking process to ensure timely implementation of final
measures for the 2010 recreational fishery, the specific measures
implemented by states are not available for economic impact analyses.
Instead, qualitative methods are utilized. The Council analysis
concluded, and NMFS agrees, that conservation equivalency is expected
to minimize impacts on small entities because individual states can
develop specific summer flounder management measures that allow the
fishery to operate during each state's critical fishing periods while
still achieving conservation goals. To be clear, there are individual
states whose conservation equivalency measures may have a more adverse
impact to some small entities, dependent on the restrictions imposed by
the Commission, than would coastwide measures. New York stands out as
such a state. However, the one-size-fits-all approach of coastwide
measures would impact a broader distribution of states and small
entities.
NMFS is implementing the Council and Commission's recommended
state-by-state conservation equivalency measures because: (1) NMFS
finds no compelling reason to disapprove the Council and Commission's
recommended 2010 management system, as the management measures
contained in conservation equivalency are projected to provide the
necessary restriction on recreational landings to prevent the
recreational harvest limit from being exceeded; and (2) the net
economic impact to small entities on a
[[Page 39177]]
coastwide basis are expected to be mitigated, to the extent
practicable, for a much larger percentage of small entities. Data
provided by the Council indicates that 328 federally permitted party/
charter vessels landed some combination of summer flounder, scup, and
black sea bass in 2008, the most recent year of available data. Within
this total, 49 vessels, or 15 percent, were from New York. By
inference, 85 percent of the small entities engaged in recreational
fishing would be impacted less by the implementation of conservation
equivalency, assuming that the impacts to New York small entities are
indeed greater under conservation equivalency.
Scup alternatives. The options available for scup recreational
fisheries management are constrained to a suite of minimum fish size,
possession limit, and fishing season that achieves the annual
conservation objective expressed through a recreational harvest limit
on landings. As outlined in the preamble, the individual states have
elected to implement a state-waters conservation equivalency system for
the 2010 scup recreational fishery that has no comparable regulations
for use in Federal waters. The Commission-adopted measures are not
expected to constrain landings to the 2010 scup recreational harvest
limit. Thus, the conservation objectives and the recreational harvest
limit are likely to be compromised regardless of action taken for
Federal waters. Very little of the scup recreational fishery occurs in
Federal waters. Rather than close Federal waters to scup recreational
fishing, NMFS is implementing the following measures: A 10.5-inch
(26.67-cm) minimum fish size; a 10-fish per person possession limit;
and an open season of June 6-September 26. These measures were not the
most conservative proposed by the Council as they are projected to
reduce 2010 landings by 29 percent from 2009 levels if comparable
measures had been implemented in state waters.
Implementation of these measures offers an alternative to outright
closure of Federal waters wherein all scup encountered would be
required to be discarded. Instead, the limited amount of scup
recreational fishing that occurs in Federal waters will have some
overlap with the measures implemented for state waters by the
Commission and fish that would have been discarded may be landed in
limited numbers. These minor landings are not expected to add a
substantial amount of recreational fishing mortality to the stock in
2010, nor is overfishing expected to occur as a result of either the
Federal or state measures implemented for 2010. Estimates from MRFSS
indicate that the amount of scup recreationally harvested in Federal
waters is typically 5 percent or less of the total annual take.
The measures of alternative 1 were also considered by NMFS. This
would have resulted in an 11-inch (27.94-cm) minimum fish size, a
longer season, and identical possession limit when compared to
alternative 3. These measures did not synchronize well with the
Commission measures and, while more conservative--achieving a projected
35 percent reduction in landings from 2009 levels if similar measures
had been enacted in state waters--NMFS found that the minimal
conservation benefit was outweighed by the lack of consistency with
measures adopted for state waters. The impacts to charter and party
vessels were similar between alternative 1 and 3 in the Council's
analysis. Alternative 2 was not considered for implementation as it was
not expected to effect any reduction in 2010 scup landing levels.
Black sea bass alternatives. Similar to both summer flounder and
scup, the options available for black sea bass recreational management
measures are constrained to selecting a suite of minimum fish size,
possession limit, and fishing season measures that achieve the annual
conservation objectives. In this case, this final rule is implementing
measures that differ from those originally proposed. This rule
implements the measures of alternative 4 (modified) contained in the
EA/RIR/IRFA addendum: A 12.5-inch (31.75-cm) minimum fish size; a 25-
fish possession limit; and May 22-October 11 and November 1-December 31
fishing seasons. This alternative provides the lowest associated
economic impacts to small entities. Alternatives 1, 3, and 4
(unmodified) were projected to achieve the conservation objectives for
the 2010 black sea bass fishery; however, given the evolution of
increasingly improved data available during the recreational management
measures development, these alternatives are now more conservative than
necessary relative to the conservation objectives and have higher
associated economic impacts than the measure being implemented through
this rule.
Small Entity Compliance Guide
Section 212 of the Small Business Regulatory Enforcement Fairness
Act of 1996 states that, for each rule or group of related rules for
which an agency is required to prepare a FRFA, the agency shall publish
one or more guides to assist small entities in complying with the rule,
and shall designate such publications as ``small entity compliance
guides.'' The agency shall explain the actions a small entity is
required to take to comply with a rule or group of rules. As part of
this rulemaking process, a letter to permit holders that also serves as
the small entity compliance guide was prepared and will be sent to all
holders of Federal party/charter permits issued for the summer
flounder, scup, and black sea bass fisheries. In addition, copies of
this final rule and the small entity compliance guide are available
from NMFS (see ADDRESSES) and at the following website: https://www.nero.noaa.gov.
List of Subjects in 50 CFR Part 648
Fisheries, Fishing, Reporting and recordkeeping requirements.
Dated: July 1, 2010
Samuel D. Rauch III,
Deputy Assistant Administrator For Regulatory Programs, National Marine
Fisheries Service.
0
For the reasons set out in the preamble, 50 CFR part 648 is amended as
follows:
PART 648--FISHERIES OF THE NORTHEASTERN UNITED STATES
0
1. The authority citation for part 648 continues to read as follows:
Authority: 16 U.S.C. 1801 et seq.
0
2. In Sec. 648.103, paragraph (b) is revised to read as follows:
Sec. 648.103 Minimum fish sizes.
* * * * *
(b) Unless otherwise specified pursuant to Sec. 648.107, the
minimum size for summer flounder is 19.5 inch (49.53 cm) TL for all
vessels that do not qualify for a moratorium permit, and charter boats
holding a moratorium permit if fishing with more than three crew
members, or party boats holding a moratorium permit if fishing with
passengers for hire or carrying more than five crew members.
* * * * *
0
3. In Sec. 648.107, paragraph (a) introductory text and paragraph (b)
are revised to read as follows:
Sec. 648.107 Conservation equivalent measures for the summer flounder
fishery.
(a) The Regional Administrator has determined that the recreational
fishing measures proposed to be implemented by Massachusetts through
North Carolina for 2010 are the conservation equivalent of the season,
minimum fish size, and possession limit prescribed in Sec. Sec.
648.102, 648.103, and 648.105(a),
[[Page 39178]]
respectively. This determination is based on a recommendation from the
Summer Flounder Board of the Atlantic States Marine Fisheries
Commission.
* * * * *
(b) Federally permitted vessels subject to the recreational fishing
measures of this part, and other recreational fishing vessels subject
to the recreational fishing measures of this part and registered in
states whose fishery management measures are not determined by the
Regional Administrator to be the conservation equivalent of the season,
minimum size, and possession limit prescribed in Sec. Sec. 648.102,
648.103(b) and 648.105(a), respectively, due to the lack of, or the
reversal of, a conservation equivalent recommendation from the Summer
Flounder Board of the Atlantic States Marine Fisheries Commission,
shall be subject to the following precautionary default measures:
Season - May 1 through September 30; minimum size - 21.5 inches (54.61
cm); and possession limit - two fish.
0
4. In Sec. 648.122, paragraph (g) is revised to read as follows:
Sec. 648.122 Season and area restrictions.
* * * * *
(g) Time restrictions. Vessels that are not eligible for a
moratorium permit under Sec. 648.4(a)(6), and fishermen subject to the
possession limit specified in Sec. 648.125(a), may not possess scup,
except from June 6 through September 27. This time period may be
adjusted pursuant to the procedures in Sec. 648.120.
0
5. In Sec. 648.125, the first sentence of paragraph (a) is revised to
read as follows:
Sec. 648.122 Possession limit.
(a) No person shall possess more than 10 scup in, or harvested
from, the EEZ unless that person is the owner or operator of a fishing
vessel issued a scup moratorium permit, or is issued a scup dealer
permit.***
* * * * *
0
6. Section 648.142 is revised to read as follows:
Sec. 648.142 Time restrictions.
Vessels that are not eligible for a moratorium permit under Sec.
648.4(a)(7), and fishermen subject to the possession limit specified in
Sec. 648.145(a), may possess black sea bass from May 22 through
October 11 and November 1 through December 31, unless this time period
is adjusted pursuant to the procedures in Sec. 648.140.
[FR Doc. 2010-16651 Filed 7-7-10; 8:45 am]
BILLING CODE 3510-22-S