Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic; Snapper-Grouper Fishery Off the Southern Atlantic States; Amendment 17B, 82280-82295 [2010-32831]
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Federal Register / Vol. 75, No. 250 / Thursday, December 30, 2010 / Rules and Regulations
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 622
[Docket No. 0907271173–0629–03]
RIN 0648–AY11
Fisheries of the Caribbean, Gulf of
Mexico, and South Atlantic; SnapperGrouper Fishery Off the Southern
Atlantic States; Amendment 17B
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
NMFS issues this final rule to
implement Amendment 17B to the
Fishery Management Plan for the
Snapper-Grouper Fishery of the South
Atlantic Region (FMP), as prepared and
submitted by the South Atlantic Fishery
Management Council (Council). This
final rule establishes annual catch limits
(ACLs) and accountability measures
(AMs) for eight snapper-grouper species
in the FMP that are undergoing
overfishing, and for black grouper,
which was recently assessed and
determined to not be undergoing
overfishing or overfished; modifies
management measures to limit total
mortality of those species to the ACL;
and adds ACLs, annual catch targets
(ACTs), and AMs to the list of
management measures that may be
amended via the framework process.
The intent of this final rule is to address
overfishing of eight snapper-grouper
species while maintaining catch levels
consistent with achieving optimum
yield.
DATES: This rule is effective January 31,
2011.
ADDRESSES: Copies of the Final
Regulatory Flexibility Analysis (FRFA)
and the record of decision may be
obtained from Kate Michie, Southeast
Regional Office, NMFS, 263 13th
Avenue, South, St. Petersburg, FL
33701.
FOR FURTHER INFORMATION CONTACT: Kate
Michie, telephone: 727–824–5305.
SUPPLEMENTARY INFORMATION: The
snapper-grouper fishery off the southern
Atlantic States is managed under the
FMP. The FMP was prepared by the
Council and is implemented under the
authority of the Magnuson-Stevens
Fishery Conservation and Management
Act (Magnuson-Stevens Act) by
regulations at 50 CFR part 622.
On September 22, 2010, NMFS
published a notice of availability of
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SUMMARY:
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Amendment 17B and requested public
comment (75 FR 57734). On October 10,
2010, NMFS published a proposed rule
for Amendment 17B and requested
public comment (75 FR 62488). NMFS
approved Amendment 17B on December
21, 2010. This final rule for Amendment
17B implements ACLs and AMs for
eight snapper-grouper species
undergoing overfishing. The rationale
for the measures contained in
Amendment 17B is provided in the
amendment and in the preamble to the
proposed rule and is not repeated here.
Comments and Responses
A total of 175 comments were
received on Amendment 17B and the
proposed rule, including comments
from individuals, State and Federal
agencies, environmental organizations,
and fishing associations. NMFS received
25 comments of general support and 48
individual comments in general
opposition of Amendment 17B, 31 of
which specifically oppose the
deepwater closure for six deepwater
snapper-grouper species. Included in
the letters of opposition was a minority
report submitted by the five members of
the Council who voted against the final
approval of Amendment 17B. NMFS
also received 85 identical postcards
opposing implementation of
Amendment 17B, and 8 comments that
did not support or oppose Amendment
17B but contained remarks on specific
actions contained in the amendment.
Additionally, 5 comments were received
from environmental organizations, one
of which was endorsed by two of the
organizations, and one which was
endorsed by 30,794 individuals. One
State and one Federal agency submitted
comments on Amendment 17B, and 2
comments were unrelated to actions
contained in Amendment 17B. Of the
175 comments received, 22 contained
remarks on the potential economic
impacts of Amendment 17B. Specific
comments related to the actions
contained in the amendment and the
rule as well as NMFS’S respective
responses, are summarized below.
Comment 1: Several commenters
suggested the prohibition on harvest
and possession of six deepwater
snapper-grouper species beyond 240
feet (73 m) is not necessary, and
reductions in incidental harvest of
speckled hind and warsaw grouper
could be achieved through: (1) A
temporary prohibition on commercial
harvest and sale of speckled hind and
warsaw grouper; (2) responsible fishing
methods such as venting fish; (3) a
temporary deepwater closure; or (4)
seasonal closures.
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Response: Commercial sale of
speckled hind and warsaw grouper is
currently prohibited. NMFS previously
considered a Council-approved measure
to use venting tools for snapper-grouper
species to reduce bycatch mortality
caused by barotrauma (injuries
sustained in response to the sudden
pressure change when brought to the
surface from depth), in Amendment 16
to the FMP. The measure requiring the
use of venting tools was disapproved
based on data indicating the benefits of
venting are not clear for all species, and
venting could potentially cause harm in
some cases if excluded unnecessarily or
improperly. NMFS determined that
additional guidance is needed to
identify species that would benefit from
venting to ensure the maximum benefit
is provided to these species. If future
research on the use of venting tools,
and/or any other barotrauma mitigation
methods, indicate speckled hind or
warsaw grouper would benefit from the
required use of such tools or techniques,
the Council has the option to consider
the issue again in a future amendment.
Implementing the deepwater snappergrouper closure for any period of time
less than year-round could result in
incidental harvest and bycatch mortality
of speckled hind and warsaw grouper,
and could negatively impact efforts to
protect South Atlantic speckled hind
and warsaw grouper. At its December
2010 meeting, the Council requested a
regulatory amendment be prepared to
examine new information related to the
prohibition on harvest and possession of
the six deepwater snapper-grouper
species beyond 240 ft (73 m). The
regulatory amendment would reevaluate the deepwater snapper-grouper
closure and the new information, and
determine if there are more effective
measures to reduce bycatch mortality of
speckled hind and warsaw grouper.
Additionally, a new benchmark stock
assessment for speckled hind and
warsaw grouper is scheduled to be
conducted in 2013. If the results of this
new stock assessment indicate some
modification to the management
measures implemented through
Amendment 17B is needed, the Council
would make such adjustments as
appropriate.
Comment 2: Several commenters
stated the prohibition on all bottom
fishing beyond 240 ft (73 m) is
draconian in nature, and too expansive
to protect only two rarely captured
snapper-grouper species.
Response: The deepwater snappergrouper closure proposed in
Amendment 17B would not prohibit all
bottom fishing beyond 240 ft (73 m).
The closure would prohibit the harvest
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and possession of six snapper-grouper
species that co-occur with specked hind
and warsaw grouper including, snowy
grouper, blueline tilefish, yellowedge
grouper, misty grouper, queen snapper,
and silk snapper.
Both speckled hind and warsaw
grouper are undergoing overfishing, and
the extent to which they are overfished
is unknown. These species are
extremely vulnerable to overfishing
because they are slow growing, longlived, and change sex from female to
male with increasing size and age.
These species are not often targeted due
to the current bag limits (one of each per
vessel per trip), but when they are
caught they are likely to suffer release
mortality. The incidental catch of
speckled hind and warsaw grouper,
particularly in deep water where release
mortality is high, may be responsible for
the continued overfishing of these
species. Therefore, the Council
determined that a prohibition on the
harvest and possession of speckled hind
and warsaw grouper, along with their
co-occurring species caught in 240 ft (73
m) and greater, was an appropriate
action to reduce bycatch mortality of
speckled hind and warsaw grouper in
depths where depth-related release
mortality is very high. Like gag,
speckled hind and warsaw grouper are
slow growing, long lived, and have
similar life histories. Therefore,
speckled hind and warsaw grouper may
be expected to have similar depthrelated bycatch mortality rates to gag. If
depth-related mortality of speckled hind
and warsaw grouper is similar to gag,
release mortality at depths of 240 ft (73
m) would be expected to be greater than
70 percent. The deepwater closure is
expected to provide protection to the
largest, most fecund fish and help
ensure a natural sex ratio into the
future. According to the Amendment
17B biological impacts analysis,
prohibiting all harvest of deepwater
snapper-grouper species beyond 240 ft
(73 m) would also protect spawning
aggregations.
Comment 3: One commenter stated
that NMFS should concentrate efforts on
managing other overexploited species
such as mutton snapper and yellowtail
snapper.
Response: Mutton snapper and
yellowtail snapper are among the 73
species in this FMP. Recent assessments
indicate that mutton snapper and
yellowtail snapper are not overfished
and are not experiencing overfishing.
The Reauthorized Magnuson-Stevens
Act requires that ACLs and AMs be
specified for all species undergoing
overfishing in 2010 and species not
undergoing overfishing in 2011.
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Speckled hind and warsaw grouper are
both undergoing overfishing according
to the 2009 Report to Congress on the
Status of U.S. Fisheries (and in all
previous such Reports to Congress).
Therefore, NMFS is required to establish
ACLs at levels to end and prevent
overfishing of speckled hind and
warsaw grouper, along with
management measures to limit harvest
levels to the ACL. In the case of
speckled hind and warsaw grouper, the
ACL is zero, and the deep water closure
is intended to reduce depth-related
bycatch mortality to reduce the
probability that overfishing will occur.
The Council is currently developing a
Comprehensive ACL Amendment,
which would specify ACLs and AMs for
mutton snapper and yellowtail snapper.
Comment 4: One commenter stated
the cumulative impact of the recent
regulations approved through
Amendment 17A to the FMP and the
regulations contained in this final rule
are overly complex for commercial and
for-hire fishermen to abide by.
Response: The Magnuson-Stevens
Act, as reauthorized in 2006, mandates
the Council and NMFS establish ACLs
and AMs for species undergoing
overfishing by 2010. Section 303(a)(15)
of the Magnuson-Stevens Act states, in
relevant part, that any FMP which is
prepared by any Council ‘‘shall establish
a mechanism for specifying annual
catch limits in the plan * * *
implementing regulations, or annual
specifications, at a level such that
overfishing does not occur in the
fishery, including measures to ensure
accountability.’’ Therefore, in order to
meet these mandates, several recent
regulatory changes have been made in
the snapper-grouper fishery. NMFS
strives to minimize complexity in its
regulations, but must meet statutory
mandates such as the requirements for
ACLs and AMs.
Comment 5: Several commenters
stated the data upon which the
prohibition on the harvest and
possession of the six deepwater
snapper-grouper species beyond 240 ft
(73 m) is based is out of date,
insufficient, and/or incorrect, and is not
the best available science. One
commenter inquired if the data used to
inform the deepwater closure action was
subject to an independent review.
Additionally, two commenters cite the
recently published Federal Register
notice that denies a petition to list
warsaw grouper as threatened or
endangered under the Endangered
Species Act (ESA) as based on a lack of
substantial scientific or commercial
information, and implied that the
speckled hind and warsaw grouper
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management measures in Amendment
17B are not based on adequate scientific
information.
Response: The intent of the action to
prohibit the harvest of six deepwater
species is to reduce bycatch mortality of
speckled hind and warsaw grouper.
Speckled hind and warsaw grouper are
undergoing overfishing, and therefore,
action must be taken to ensure
overfishing is ended and does not occur.
The Southeast Fisheries Science Center
(SEFSC) certified, in a memorandum
dated May 19, 2010, that Amendment
17B is based upon the best available
scientific information. At its December
2010 meeting, the Council requested
that a regulatory amendment be
prepared to examine new information
related to the prohibition on the harvest
and possession of the six deepwater
snapper-grouper species. The regulatory
amendment would evaluate the new
information and the deepwater snappergrouper closure and determine if there
are more effective measures to reduce
bycatch mortality of speckled hind and
warsaw grouper.
The petition to list speckled hind and
warsaw grouper as endangered or
threatened was denied by NMFS under
the ESA because ‘‘the petition does not
present substantial scientific or
commercial information indicating the
petition action may be warranted’’ (75
FR 59690, September 28, 2010). This
means that warsaw grouper was not
determined to be endangered (i.e., is in
danger of extinction throughout all or a
significant portion of its range) or
threatened (i.e., is likely to become
endangered within the foreseeable
future throughout all or a significant
portion of its range). The negative
finding on the ESA petition does not
necessarily mean that inadequate
scientific information was used in
Amendment 17B. Under the MagnusonStevens Act, NMFS must use the best
scientific information available when
establishing management measures,
including ACLs and AMs.
Comment 6: Several commenters are
concerned that the prohibition on
harvest and possession of six deepwater
snapper-grouper species beyond a depth
of 240 ft (73 m) will lead to increased
incidences of release mortality.
Response: Prohibiting the harvest and
possession of species that are most often
caught with speckled hind and warsaw
grouper in deeper waters would reduce
the incentive to target those cooccurring species. As a result, a
reduction in depth-related bycatch
mortality of speckled hind and warsaw
grouper is expected.
Comment 7: Several commenters feel
the deepwater closure in Amendment
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17B should only apply to the
commercial sector.
Response: In the northern portion of
the Council’s area of jurisdiction,
fisheries and fishery components in
depths greater than 240 ft (73 m) are
primarily prosecuted by the commercial
sector. However, the Council chose to
include the recreational sector in the
prohibition on harvest and possession of
snowy grouper, blueline tilefish,
yellowedge grouper, misty grouper,
queen snapper, and silk snapper beyond
240 ft (73 m) because recreational
fishing in deeper waters is common in
the southern area of the Council’s
jurisdiction i.e., southeast Florida and
the Florida Keys, the 240-ft (73-m)
depth contour is close to shore. Because
deep water is much more accessible to
recreational fishermen off southern
Florida, recreational fishermen are more
likely to incidentally capture speckled
hind and warsaw grouper in depths
where these fish are more likely to die
as a result of barotrauma-related
injuries.
Comment 8: One commenter stated
the lack of warsaw grouper landings
data was due to fishermen
misidentifying warsaw grouper as
snowy grouper.
Response: It is unlikely warsaw
grouper landings are significantly
underreported due to misidentification
with snowy grouper. Snowy grouper
and warsaw grouper do share some
common physical characteristics,
however, these species also have several
distinguishing characteristics that make
it possible to easily identify both
species. When fishermen submit species
landings information to NMFS,
identification accuracy is not expected
to be 100 percent, and this is taken into
consideration when conducting stock
assessments.
Comment 9: One commenter asked
how NMFS will determine when the
speckled hind and warsaw grouper
stocks are rebuilt, if fishing for them is
prohibited.
Response: The overfished status of
speckled hind and warsaw grouper is
unknown. Therefore, a rebuilding plan
is not required. The deepwater closure
is intended to reduce depth-related
bycatch mortality to help end
overfishing of speckled hind and
warsaw grouper. Prohibiting harvest of
one or more species in a certain area
does not prevent the collection of
scientific information on those species.
The SEFSC conducts fisheryindependent studies and surveys to
measure the overall abundance of fish
stocks in the South Atlantic. In
Amendment 17A to the FMP, the
Council required implementation of a
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fishery-independent monitoring
program. This program would continue
the long-term data set that already exists
for snapper-grouper species from
sampling programs such as the
Southeast Monitoring Assessment and
Prediction program, and the Marine
Resources Monitoring Assessment and
Prediction program in the South
Atlantic, which monitor fish stocks in
depths shallower and deeper than 240 ft
(73 m), and these programs should
continue to provide information on
warsaw grouper and speckled hind.
Fishery-dependent data may also be
collected during a period when certain
species may not be landed. These data
may be collected through the
Cooperative Research Program (CRP),
which is a competitive Federal
assistance program that funds projects
seeking to increase and improve the
working relationship between
researchers from NMFS, State fishery
agencies, universities, and fishermen.
The intent of the CRP in the Southeast
Region is to utilize the collective
experience of fishermen and scientists
to advise fishery managers of best
fishery management practices based on
fishing experience and sound scientific
research procedures. Other fisherydependent data collection sources
include the Marine Recreational
Fisheries Statistical Survey (MRFSS)
(now part of the Marine Recreational
Information Program (MRIP)),
commercial logbooks, headboat
logbooks, observer data, the Trip
Interview Program, and dealer reported
landings.
Comment 10: After the Council voted
to approve Amendment 17B for
Secretarial review, the five members of
the Council who voted against the final
approval of Amendment 17B submitted
a minority report to NMFS, dated March
23, 2010. This report is endorsed by one
fishing organization and one State
agency. The minority report outlines the
dissenting Council members’ opposition
to the deepwater closure for the six cooccurring snapper-grouper species.
Specifically, these Council members
oppose the inclusion of blueline tilefish
in the list of snapper-grouper species
prohibited beyond 240 ft (73 m). The
report states the deepwater closure was
based on inadequate assessments, does
not include rebuilding plans for
speckled hind and warsaw grouper, and
does not consider and properly analyze
the impacts of the prohibition on the
sale of bag limit-caught snappergrouper. The report also notes a lack of
data on the range where speckled hind
and warsaw grouper are found,
particularly off the coast of North
Carolina. The report mentions that the
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species most commonly caught with
speckled hind are vermilion snapper,
red grouper, and scamp, which are not
deepwater species. The minority report
suggests that other alternatives besides
the deep water closure should have
been considered by the Council,
including allowing fishing for species
other than speckled hind and warsaw
grouper on various well-known ship
wrecks or other potential sites and
closing only a percentage of the most
productive bottom habitat. The minority
report also lists fish stocks that have
been successfully rebuilt or are
currently rebuilding without the
utilization of large area closures for
fishery management, namely Atlantic
king and Spanish mackerel, greater
amberjack, and golden tilefish.
Response: Speckled hind and warsaw
grouper have not undergone a recent
stock assessment. However, the 2009
Report to Congress on the Status of U.S.
Fisheries states that both speckled hind
and warsaw grouper are undergoing
overfishing and their overfished status
is unknown. The stock status
determination for these two species
included in the Report to Congress is
the best scientific information available
for speckled hind and warsaw grouper.
Therefore, NMFS is required to establish
ACLs for these species at levels that can
end, as well as prevent, overfishing and
implement management measures to
limit harvest levels of these species to
the ACL. Since the overfished status of
speckled hind and warsaw grouper is
currently unknown, rebuilding plans are
not required at this time. To address
overfishing of speckled hind and
warsaw grouper, the Council’s Scientific
and Statistical Committee (SSC)
recommended an Acceptable Biological
Catch (ABC) of zero for both species
based on landed catch, rather than total
removals. Subsequent to the SSC ABC
recommendation, the Council specified
an ACL of zero for speckled hind and
warsaw grouper.
Speckled hind and warsaw grouper
are extremely vulnerable to overfishing
because they are slow growing, longlived, change sex from female to male
with increasing size and age, and occur
in deep water where release mortality is
very high. The prohibition on the
harvest and possession of six deepwater
snapper-grouper species, including
blueline tilefish, that co-occur with
speckled hind and warsaw grouper is
expected to reduce the incidental take of
speckled hind and warsaw grouper in
water depths where survival of released
fish is low. Of the six species for which
harvest and possession would be
prohibited beyond 240 ft (73 m),
commercial and recreational landings
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are highest for blueline tilefish and
snowy grouper, which are often caught
together in the same location and during
the same trip. Speckled hind and
warsaw grouper can be incidentally
caught while blueline tilefish and other
deepwater species are being targeted.
This incidental catch, if allowed to
continue, may contribute to the
continued overfishing of speckled hind
and warsaw grouper. Furthermore,
recent snowy grouper regulations
resulted in effort shifts from snowy
grouper to blueline tilefish, which could
increase the probability of snowy
grouper bycatch after the 100-lb (45-kg)
trip limit or quota for snowy grouper is
met, in addition to a potential for
increased bycatch of speckled hind and
warsaw grouper. If blueline tilefish were
eliminated from the list of prohibited
deepwater species, incidental take of
speckled hind and warsaw grouper
could persist in that portion of the
snapper-grouper fishery; therefore, the
Council determined it would be prudent
to retain blueline tilefish in the list of
prohibited species beyond a depth of
240 ft (73 m).
The minority report includes an
examination of trip ticket information
from vessels fishing for blueline tilefish
north of Cape Hatteras, North Carolina,
which suggests blueline tilefish can be
captured without resultant incidental
catch of speckled hind and warsaw
grouper. At its December 2010 meeting,
the Council considered this new
information, and voted to request the
preparation of a regulatory amendment
to examine the new information and to
determine if there are more effective
management measures that could be
implemented to reduce the depthrelated bycatch mortality of speckled
hind and warsaw grouper.
The Magnuson-Stevens Act requires
the establishment of ACLs and AMs. In
the comments and responses section of
the final rule implementing the National
Standard 1 Guidelines, NMFS states,
‘‘ACLs must be implemented using the
best data and information available
* * * NMFS believes that Councils
must implement the best ACLs possible
with the existing data’’ (74 FR 3178,
January 16, 2009). As required by the
Magnuson-Stevens Act, the Council has
developed ACLs and AMs for speckled
hind and warsaw grouper using the best
scientific information available during
the amendment development process.
The minority report points out that
the species most commonly caught with
speckled hind are vermilion snapper,
red grouper, and scamp, none of which
are deepwater species. Juvenile
speckled hind and warsaw grouper are
found in depths less than 240 ft (73 m)
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and are often caught with species such
as vermilion snapper, red grouper,
scamp, and others. However, the
Council chose not to prohibit catch in
shallower water because it is likely that
some portion of released speckled hind
and warsaw grouper would survive the
trauma of capture. Like gag, speckled
hind and warsaw grouper are slow
growing, long lived, and have similar
life histories. Therefore, they may be
expected to have similar bycatch
mortality rates to gag. If release
mortality rates of speckled hind and
warsaw grouper are similar to those
published for gag, release mortality at
depths greater than 240 ft (73 m) would
be expected to be greater than 70
percent. Based on this assumption, the
Council determined the most effective
method of reducing the incidence of
bycatch related mortality in deepwater
was to prohibit the harvest and
possession of the species that co-occur
with speckled hind and warsaw grouper
beyond 240 ft (73 m).
During the development process for
Amendment 17B, alternatives such as
allowing fishing for species other than
speckled hind and warsaw grouper on
various well-known ship wrecks or
other potential sites, and closing only a
percentage of the most productive
bottom habitat, were not proposed by
Council members and thus were not
included in the document for analysis.
The approval and implementation of the
prohibition on harvest and possession of
six deepwater snapper-grouper species
beyond 240 ft (73 m) does not preclude
the Council from proposing future
action to modify this prohibition if
scientific information indicates it is
appropriate to do so. Re-addressing the
deepwater closure will be accomplished
through a regulatory amendment
proposed by the Council at its December
2010 meeting.
The minority report states the impact
of the prohibition on bag-limit sales of
snapper-grouper implemented through
Amendment 15B to the FMP was not
properly analyzed in Amendment 17B
because the impact of sales from only
snapper-grouper fishermen with Federal
permits was not determined. The
impacts of the bag limit sale prohibition
were analyzed and documented by
NMFS in the supporting documentation
for Amendment 15B, including the
National Environmental Policy Act
document, the Regulatory Impact
Review, and the Regulatory Flexibility
Analysis. The analysis conducted for
Amendment 15B to the FMP used State
trip ticket data because at the time the
analysis was conducted, fishermen that
did not possess a Federal permit for
snapper-grouper could still sell their bag
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limit caught fish. The analysis
conducted for Amendment 17B,
however, did not use trip ticket data and
used only Federal logbook data, because
at that time the prohibition on bag limit
sales had been implemented. As such,
the relevant economic analysis does not
include bag limit sales information and
was conducted correctly.
Different actions are needed to end
overfishing of species depending on
their life history and habitat
requirements. Snapper-grouper species
such as speckled hind and warsaw
grouper are long-lived and slow growing
and require more stringent management
measures, such as area closures, to end
overfishing. King mackerel and Spanish
mackerel are not as long lived nor do
they suffer the high release mortality
rates of speckled hind and warsaw
grouper. Therefore, management
measures that would be needed to end
overfishing of mackerel species may not
be as onerous as those that would be
needed for long-lived species found in
deep water.
Golden tilefish has never been
determined to be overfished and it will
not be known if actions taken to end
overfishing of golden tilefish were
successful until the stock is assessed
again in 2011. Greater amberjack have
never been determined to be overfished
or experienced overfishing.
Comment 11: One commenter
questioned why co-occurring species
deeper than 240 ft (73 m) would be
prohibited to protect speckled hind and
warsaw grouper when these species are
not frequently caught in these depths.
The species most commonly caught
along with speckled hind are vermilion
snapper, red grouper, and scamp, none
of which are considered by the Council
to be deepwater species. Since speckled
hind predominately live inshore of 40
fathoms and warsaw grouper are
common inside of 100 ft (31 m), at least
off the Florida coast, NMFS should
consider closing the entire EEZ.
Response: The Council is aware that
speckled hind and warsaw grouper are
currently not commonly caught by
fishermen and that the inshore shelf
edge in 160 ft (49 m) is the area where
juveniles are most abundant. However,
adults of these species do occur in deep
water where release mortality is
extremely high and are incidentally
captured when fishermen target cooccurring species. Therefore, the
Council determined that prohibiting the
harvest of species that co-occur with
warsaw grouper and speckled hind in
water deeper than 240 ft (73 m) could
help reduce bycatch mortality,
particularly as population biomass
increases and more adults occur in
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deeper water. Speckled hind and
warsaw grouper occur in shallower
water as juveniles with vermilion
snapper and others. This is their zone of
greatest abundance where some level of
survival of released fish would be
expected to occur. Therefore, the
Council did not feel it was necessary to
close the harvest of co-occurring species
in depths less than 240 ft (73 m). As
noted previously, speckled hind and
warsaw grouper share similar biological
characteristics to gag. Therefore, if
depth related bycatch is similar to gag,
in depths greater than 240 ft (73 m),
release mortality would be expected to
be greater than 70 percent. By
prohibiting the harvest and possession
of co-occurring species, in addition to
prohibiting all harvest and possession of
speckled hind and warsaw grouper,
fishing mortality of speckled hind and
warsaw grouper is expected to decrease
and protection would be provided to
adult fish with the greatest spawning
potential.
Comment 12: One commenter feels
the deepwater closure will result in an
effort shift to the black sea bass, gray
triggerfish, and vermilion snapper
components of the snapper-grouper
fishery, and lead to more out-of-state
fishing by southern vessels in waters off
North Carolina.
Response: Effort shifts resulting from
the deepwater closure are difficult to
predict. Negative biological impacts of
effort shifts may be mitigated by ACLs
and AMs in Amendment 17B and the
Comprehensive ACL Amendment,
which are designed to prevent the ACL
from being exceeded or correct for ACL
overages should they occur. However,
negative social and economic effects
could result from ACLs being met more
quickly due to effort shifts.
The commercial sector for vermilion
snapper is currently managed under a
quota split into two seasons, and this
amendment will specify the same split
season for commercial ACLs, as well as
specify a recreational ACL.
Additionally, trip limits for vermilion
snapper are being considered by the
Council in Regulatory Amendment 9 to
the FMP. Therefore, effort shift into the
vermilion snapper portion of the fishery
is unlikely to have negative biological
impacts on vermilion snapper because
the commercial harvest and sale of
vermilion snapper would be prohibited
when the ACLs are projected to be met.
The Council is developing
Amendment 18A to the FMP, which
includes actions to: Limit the number of
black sea bass pots allowed per vessel;
limit the number of participants in the
black sea bass component of the
snapper-grouper fishery; and require
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that pots be returned to port at the
completion of a fishing trip. If approved,
these controls should limit effort shift
into the black sea bass component of the
snapper-grouper fishery, minimizing the
occurrence of black sea bass pot ‘‘ghost
fishing’’ on snapper-grouper species, as
well as interactions with protected
species.
Gray triggerfish are included within
the 20 snapper-grouper aggregate bag
limit for the recreational sector, and
there is a 12-inch (30.5-cm) total length
size limit in Federal waters off the east
coast of Florida for the commercial and
recreational sectors. The Comprehensive
ACL Amendment, currently under
development, would establish an ACL
for gray triggerfish. This ACL would be
associated with an AM intended to
maintain harvest at or below the
specified ACL. Therefore, if the
Comprehensive ACL Amendment is
implemented, a mechanism for
controlling harvest of gray triggerfish
would be established and could mitigate
effort shifts that may result from actions
contained in Amendment 17B. The
deepwater closure could result in some
amount of permanent and/or temporary
effort shifting, however, the number of
vessels that may or may not shift effort
to other fisheries in response to the
deepwater area closure cannot be
predicted.
Comment 13: One commenter states
the Council discussion concerning
warsaw grouper and speckled hind was
inadequate considering the scope of the
deepwater closure being implemented
through Amendment 17B.
Response: The Council discussed
management measures for speckled
hind and warsaw grouper beginning in
June 2008. Since that time, the Council
has met seven times and discussed
actions in Amendment 17B before
taking final action to approve the
amendment. At its December 2010
meeting, the Council requested a
regulatory amendment be prepared to
examine new information related to the
prohibition on harvest and possession of
the six deepwater snapper-grouper
species and evaluate the new
information to determine if the
deepwater closure in certain areas of the
South Atlantic is still necessary.
Comment 14: One commenter states
that the Amendment 17B cumulative
impacts assessment of the role of the
marine protected areas (MPAs)
implemented through Amendment 14 to
the FMP is inaccurate, and the ancillary
impacts of the Oculina Experimental
Closed Area for speckled hind and
warsaw grouper were not mentioned in
Amendment 17B.
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Response: The effective date of the
eight MPAs implemented through
Amendment 14 to the FMP was
February 13, 2009. Because these MPAs
have been in place for a short period of
time, little is known about their
potential to positively impact snappergrouper species beyond the basic
protections afforded to habitats in these
MPAs, and subsequent benefits realized
by local fish populations. It is expected
that the MPAs may help, to some extent,
to protect a portion of the population
(including spawning aggregations) and
habitat of long-lived, slow growing,
deepwater snapper-grouper species
(speckled hind, snowy grouper, warsaw
grouper, yellowedge grouper, misty
grouper, golden tilefish, and blueline
tilefish) from directed fishing pressure
to achieve a more natural sex ratio, age,
and size structure within the MPAs.
Because the snapper-grouper species
most affected by the MPAs and the
Oculina closed area are long-lived,
quantifiable biological benefits may not
be measureable in the short-term.
However, future studies are expected to
analyze the affects of the MPAs and the
Oculina closure on snapper-grouper
species. Over time, continued research
will provide further insight on the
ecological benefits of conservation
areas.
Comment 15: One commenter states
that snowy grouper is the main driver
for deepwater snapper-grouper fishing
and past regulations to reduce snowy
grouper harvest have not been
considered in Amendment 17B as they
relate to effort-reduction in the
deepwater portion of the snappergrouper fishery.
Response: Effort reductions resulting
from previously implemented snowy
grouper regulations were taken into
account when analyzing the biological
and socioeconomic impacts of the
deepwater closure. As required under
NEPA, Amendment 17B analyzes the
impacts of the status quo alternative for
each action, including the action to
prohibit the harvest and possession of
six deepwater species beyond 240 ft (73
m). The baseline condition used in the
status quo (no action) analysis for the
action to prohibit the harvest and
possession of six deepwater species
beyond 240 ft (73 m) included the
snowy grouper harvest restrictions
implemented through Amendment 13C
to the FMP. These restrictions included
a recreational bag limit for snowy
grouper of one per person per day, a
commercial trip limit of 100 lb (45 kg)
gutted weight, and a reduced
commercial quota of 84,000 lb (38,102
kg) gutted weight. Amendment 15A to
the FMP specified an ABC for snowy
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grouper that is consistent with the
rebuilding plan for the species.
Comment 16: One commenter is
opposed to reducing the recreational
ACL for snowy grouper to 523 fish, and
favors allowing existing regulations to
rebuild the stock.
Response: The Magnuson-Stevens Act
requires that ACLs and AMs be
specified in 2010 for species undergoing
overfishing. The Council chose to base
the ACL for snowy grouper on the
current total allowable catch (TAC). The
Council also chose to specify sector
ACLs for snowy grouper rather than one
ACL for the commercial and
recreational sectors. The Council
determined the recreational sector ACL
to be 523 fish, based on landings data
from 2005–2008. Because this ACL is
quite small, and recreational landings
data is associated with a high degree of
uncertainty, the AM will compare a 3year running average of recreational
landings to the recreational ACL. The
AMs established for snowy grouper are
intended to maintain harvest levels at or
below the specified ACLs.
Comment 17: One commenter
recommended additional inshore
seasonal closures in the Florida Keys
area to help rebuild overfished stocks.
Response: The Florida Keys area has
an extensive network of marine
sanctuaries, where fishing is limited or
prohibited, and there is the offshore East
Hump MPA, which was established in
Amendment 14 to the FMP. The Council
has not requested consideration of
inshore area closures in the Florida
Keys to address overfishing of the
species addressed in Amendment 17B.
Comment 18: Several commenters
state that aggregating the gag, black
grouper, and red grouper ACLs, and the
associated AMs is not an appropriate
method for managing these stocks. One
commenter emphasizes the fact that
black grouper is no longer considered to
be undergoing overfishing or overfished,
further justifying not including it in the
aggregate ACL. One commenter
recommended developing a catch share
program for these species in order to
ensure all commercial sector
participants are given the opportunity to
harvest them.
Response: Amendment 16 established
a commercial AM for red grouper and
black grouper through a prohibition on
the harvest of all shallow-water
snapper-grouper species that would be
effective when the commercial ACL for
gag (a biologically similar species) is
projected to be met each year. Because
black grouper and red grouper had not
been recently assessed at the time
Amendment 17B was developed, and
the Council was aware that a new stock
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assessment for both species was
forthcoming, the Council chose to
establish an aggregate ACL that includes
gag, red grouper, and black grouper,
based on expected catch resulting from
management measures implemented
through Amendment 16 to the FMP.
The red grouper and black grouper
Southeast Data, Assessment, and
Review (SEDAR) stock assessment
(SEDAR 19) was completed in 2010,
after Amendment 17B had been
submitted to NMFS for Secretarial
review. The assessment indicated black
grouper is not overfished and is not
undergoing overfishing, and red grouper
is overfished and undergoing
overfishing. Therefore, a new FMP
amendment is currently under
development to establish a rebuilding
plan and assign an individual ACL and
AM for red grouper. The black grouper
stock assessment was not completed
until after Amendment 17B was
submitted to the Secretary for review.
Black grouper ACLs and AMs have been
retained in Amendment 17B, however,
the Council will immediately consider
whether adjustments to ACLs and AMs
are needed in light of the new
assessment. The Comprehensive ACL
Amendment, which is also under
development by the Council, would
consider a new ACL and AM for black
grouper, as well as species groups for
many different snapper-grouper species
that could include gag, red grouper, and
black grouper.
Comment 19: Several commenters
state they have witnessed the
progressive decline in deepwater
snapper-grouper species over many
years, and support measures to end
overfishing and rebuild deepwater
snapper-grouper stocks.
Response: NMFS agrees that effective
management strategies must be utilized
to rebuild stocks that are overfished to
sustainable levels and prevent future
overfishing from occurring. Actions
have been taken through previous
amendments to address overfishing of
black sea bass, vermilion snapper, gag,
red grouper, black grouper, snowy
grouper, speckled hind, warsaw
grouper, red snapper, and golden
tilefish. It is the intent of the Council
and NMFS to employ a system of ACLs
and AMs to achieve these goals.
Comment 20: One commenter feels
the restrictions on vermilion snapper
are too restrictive and have fostered a
derby fishery, and suggests a trip limit
be implemented for vermilion snapper.
Another commenter recommended the
implementation of a system of trip
limits, also known as the ‘‘Fisherman’s
Plan,’’ as a means of maintaining harvest
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levels of vermilion snapper below the
specified ACLs.
Response: Regulatory Amendment 9
to the FMP includes an action to specify
trip limits for vermilion snapper. It is
the Council’s intent to alleviate the
derby nature of the vermilion snapper
component of the snapper-grouper
fishery by implementing a trip limit as
soon as possible. Additionally,
Amendment 21 to the FMP, which is in
the early stages of the development
process, includes an action to establish
a catch share program for vermilion
snapper. Establishing a catch share
program would eliminate the derbystyle fishery, and would promote safety
at sea.
Comment 21: One commenter feels
Amendment 17B would not reduce
harvest enough to end overfishing of the
subject stocks, and recommends
reducing all the ACLs contained in
Amendment 17B by 66 percent.
Response: The best scientific
information available supports the
recently implemented harvest
reductions in previous amendments and
the ACLs contained in Amendment 17B.
Actions have been taken in previous
amendments to address overfishing of
most species addressed in Amendment
17B. A reduction of the current ACLs by
66 percent is not supported by the best
available scientific information, and
could result in unnecessary adverse
socioeconomic impacts on the fishing
community. Therefore additional
harvest restrictions beyond those in
Amendment 17B are not necessary to
end overfishing of the species addressed
in Amendment 17B as required by the
Magnuson-Stevens Act. Amendment
17B specifies ACLs and AMs for
speckled hind, warsaw grouper, snowy
grouper, black sea bass, vermilion
snapper, black grouper, red grouper,
gag, and golden tilefish to end
overfishing and help ensure that
overfishing does not occur in the future.
Comment 22: One commenter stated
the impacts of anthropogenic pollutants
such as sunscreens, pharmaceuticals,
and cruise ships could have an effect on
snapper-grouper reproductive fitness.
Response: The direct impacts of
anthropogenic toxins introduced into
the marine environment have been
studied in recent years, but their
impacts on snapper-grouper species are
not quantifiable at this time. Ongoing
research in the field is likely to continue
as human impacts on the environment
increase. Several studies show a
correlation between pharmaceutical
waste and subsequent lowered
reproductive fitness in marine
organisms. The extent to which
chemical waste impacts snapper-
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grouper species in the South Atlantic is
unknown, and may be more difficult to
measure in deepwater species, which do
not spend the majority of their live
cycles in close proximity to known
pollution sources.
The Environmental Protection Agency
(EPA) has participated in several
surveys to assess the impacts of cruise
ship discharge of food waste, gray water,
bilge water, and ballast water on the
marine environment, including a survey
conducted in August 2001 to estimate
the dilution of cruise ship discharges
into receiving waters. Another survey,
conducted in Skagway Harbor, Alaska,
in July 2008, estimated the near-field
dilution of treated sewage/gray water
discharges from docked cruise ships.
The EPA also prepared a Cruise Ship
Discharge Assessment Report
(Assessment Report), which examines
waste streams generated by cruise ships.
The report is available at: https://water.
epa.gov/polwaste/vwd/cruise_ship_
disch_assess_report.cfm. Despite these
and other ongoing studies, the direct
impact of cruise ship waste discharge on
snapper-grouper species in the South
Atlantic is not known at this time.
Comment 23: One commenter
suggests requiring permits and logbooks
on all vessels in all sectors of the
snapper-grouper fishery.
Response: Logbooks and snappergrouper permits are required for
participants in the commercial snappergrouper fishery. Permits are also
required for all participants in the forhire sector of the snapper-grouper
fishery, and logbooks are required on
headboats if selected by NMFS.
Amendment 15B, which became
effective in December 2009, requires any
vessel fishing for snapper-grouper in the
South Atlantic EEZ, if selected by
NMFS, to maintain and submit fishing
records; and requires any vessel that
fishes in the EEZ, if selected by NMFS,
to carry an observer and install an
electronic logbook (ELB) and/or video
monitoring equipment provided by
NMFS. The reporting and recordkeeping requirements contained in
Amendment 15B only include selected
vessels because these requirements are
cost prohibitive if applied to every
fisher in the South Atlantic at this time.
Comment 24: One commenter stated
that a prohibition on all longline fishing
would end overfishing of golden
tilefish.
Response: Golden tilefish are
primarily harvested using bottom
longline gear. Actions were taken in
Amendment 13C to end the overfishing
of golden tilefish, which included a
reduction in the quota to 295,000 lb
(133,810 kg) gutted weight. Therefore,
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eliminating the longline harvest for
golden tilefish could have unnecessary
negative economic and social effects.
The effectiveness of management
measures in ending overfishing for
golden tilefish will be determined in an
assessment scheduled for 2011.
Amendment 17B established ACLs and
AMs to help ensure golden tilefish
overfishing does not occur.
Currently, for the snapper-grouper
fishery, the use of bottom longline
fishing gear is limited by species and
area. A vessel that has on board a valid
Federal commercial permit for South
Atlantic snapper-grouper, excluding
wreckfish, that fishes in the EEZ on a
trip with a longline on board, may
possess only snowy grouper, warsaw
grouper, yellowedge grouper, misty
grouper, golden tilefish, blueline
tilefish, and sand tilefish. Additionally,
under the FMP, a longline may not be
used to fish in the EEZ for South
Atlantic snapper-grouper south of
27°10′ N. latitude (due east of the
entrance to St. Lucie Inlet, FL); or north
of 27°10′ N. latitude where the charted
depth is less than 50 fathoms (91.4 m),
as shown on the latest edition of the
largest scale NOAA chart of the
location. Under the FMP, a person
aboard a vessel with a longline on board
that fishes on a trip in the South
Atlantic EEZ south of 27°10′ N. latitude,
or north of 27°10′ N. latitude where the
charted depth is less than 50 fathoms
(91.4 m), is limited on that trip to the
bag limit for South Atlantic snappergrouper for which a bag limit is
specified, and to zero for all other South
Atlantic snapper-grouper.
Additionally, Amendment 18A to the
FMP is addressing potential effort
control mechanisms for the golden
tilefish component of the snappergrouper fishery, including an
endorsement for hook-and-line and
longline gear. Therefore, Amendment
18A may mitigate, to some extent, any
effort shift into the golden tilefish
component of the snapper-grouper
fishery.
Comment 25: Three commenters felt
the golden tilefish allocation of 97percent commercial and 3-percent
recreational is unfair and allocates too
much of the total ACL to the
commercial sector.
Response: The sector allocations for
golden tilefish were chosen based on
long-term and short-term landings
histories. The preferred allocation of 97
percent for the commercial sector and 3
percent for the recreational sector is
representative of past and current
harvest levels for both sectors and thus
would cause the least disruption to the
economic and social environments. The
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Council considered an alternative that
would allocate half of the ACL to the
commercial sector and half to the
recreational sector, but rejected this
alternative because it would result in
the largest deviation from the short and
long-term landings trend for the two
sectors. It was concluded that the
preferred allocation is fair and equitable
based on the best scientific information
available.
Comment 26: Two commenters
suggested that the Federal government
buy out those fishermen who are ready
to leave the fishery because of overly
burdensome regulations. One
commenter suggested the U.S.
Department of Commerce develop a
fisheries disaster assistance program for
commercial and for-hire fishermen
affected by recently implemented
regulations.
Response: The Council discussed the
establishment of a buy-out program for
commercial snapper-grouper fishermen
in Georgia during the development
process for Amendment 17A to the
FMP, which was drafted concurrently
with Amendment 17B. A buy-out
program for the commercial sector
would require a great deal of planning,
time, funds, and acceptance from
fishery participants. Because of these
limiting factors and the need to end
overfishing immediately as required by
the Magnuson-Stevens Act, a buy-out
program was not pursued by the
Council or NMFS during the
development of Amendment 17B.
The Magnuson-Stevens Act states the
Secretary may establish a regional
economic transition program to provide
immediate disaster relief assistance
upon the request and concurrence with
the Governors of the affected States.
Neither the Secretary nor NMFS has
received a request from any of the four
affected States’ governors for disaster
relief. Therefore, a disaster relief
program for the snapper-grouper fishery
has not been considered.
Comment 27: Several commenters feel
the economic impact analysis for
actions contained in Amendment 17B is
either absent or inadequately represents
the true impacts expected from the
implementation of Amendment 17B.
Response: Amendment 17B contains a
complete economic impact analysis of
all actions and alternatives considered
by the Council in Amendment 17B.
Additionally, Amendment 17B contains
a social impact analysis of all the
alternatives considered by the Council.
Furthermore, in compliance with
Magnuson-Stevens Act, Amendment
17B contains a Regulatory Impact
Review, an initial Regulatory Flexibility
Analysis, a Fishery Impact Statement,
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and a Social Impact Assessment. These
economic and social analyses utilize
recent landings, trip ticket, logbook,
permit, and financial data for the
commercial and recreational sectors. As
such, the subject analyses have been
determined to represent an accurate and
complete economic picture of potential
impacts that may result from the
implementation of Amendment 17B.
Comment 28: Three commenters feel
Amendment 17B contained several
deficiencies, including: the absence of
overfishing limits (OFLs) for six species,
the absence of ABCs for five species, the
lack of an ABC control rule, failing to
account for management uncertainty in
the ACLs, and failing to include discard
mortality in the ACLs (most notably for
speckled hind and warsaw grouper).
One commenter states that Amendment
17B establishes ACLs and management
measures that are unlikely to end
overfishing for golden tilefish, black sea
bass, and snowy grouper. Additionally,
one commenter states that Amendment
17B should include an ACL
performance standard, and re-evaluation
of the ACLs and AMs that would be
triggered if the catch exceeds the ACL
more often than once in a given period
of time.
Response:
OFL: The Magnuson-Stevens Act
National Standard 1 Guidelines give the
Councils flexibility to use either the
maximum fishing mortality threshold
(MFMT) or the overfishing limit (OFL)
to determine if overfishing is occurring.
The National Standard 1 Guidelines
state, ‘‘The OFL is an annual level of
catch that corresponds directly to the
MFMT, and is the best estimate of the
catch level above which overfishing is
occurring.’’ Furthermore, in June 2008,
the SSC stated that for species assessed
through SEDAR, OFL is equal to the
yield at MFMT. Golden tilefish, snowy
grouper, black sea bass, vermilion
snapper, red grouper, and black grouper
have been assessed through SEDAR and,
therefore, have estimates of MFMT. The
numerical estimates of MFMT for black
grouper and red grouper will be
provided in the Comprehensive ACL
Amendment and Amendment 24,
respectively.
The SSC was unable to provide
recommendations of the OFL for
speckled hind and warsaw grouper at its
June 2008 meeting, based on current
data, and, therefore, specified OFL as
‘‘unknown.’’ The SSC encountered
similar problems when attempting to
specify OFLs for species at its April
2010 meeting. Discussion at the April
2010 meeting focused on what the SSC
was responsible for providing to the
Council under National Standard 1
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Guidelines. To explain its reasoning and
judgment, the April 2010 SSC report
states, ‘‘It became clear that
recommending an ABC was the main
goal, and providing this recommended
value without an estimate of OFL was
acceptable in situations where only
catch series data were available.’’
ABC: At its December 2008 meeting,
the SSC considered the guidance given
in the proposed Magnuson-Stevens Act
National Standard 1 Guidelines and
rescinded all estimates of ABC from its
June 2008 meeting (except for an ABC
of zero for speckled hind and warsaw
grouper based on landed catch). At its
December 2008 meeting, the SSC also
recommended that the ABC levels for
snowy grouper, black sea bass, and red
snapper be set consistent with the
rebuilding plans for those species until
they can be further amended using more
updated scientific information. The SSC
reaffirmed, at its April 2010 meeting,
that ‘‘For overfished stocks and stock
complexes, a rebuilding ABC must be
set to reflect the annual catch that is
consistent with the schedule of fishing
mortality rates in the rebuilding plan.’’
At its June 2009 meeting, the SSC
recommended ABCs for gag and
vermilion snapper based on a P*
analysis, which is being used as the
Council’s preferred ABC control rule for
assessed species that are not
experiencing overfishing in the
Comprehensive ACL Amendment.
The SSC did not provide an ABC
value for golden tilefish because of the
age of the assessment and because of the
lack of a current estimate of abundance.
Golden tilefish will be assessed by
SEDAR in 2011. The ABC control rule
being used in the Comprehensive ACL
Amendment will be applied to golden
tilefish to obtain an ABC value when the
assessment and amendment are
completed in 2011. The SSC did not
provide an ABC value for black grouper
and red grouper because assessments
were ongoing for those species when
Amendment 17B was being developed
by the Council, and since the SEDAR
assessments have now been completed,
OFLs, ABCs, and ACLs will be specified
in the Comprehensive ACL Amendment
and Amendment 24 for black grouper
and red grouper, respectively.
ABC Control Rule: For overfished
stocks and stock complexes, the SSC has
indicated that the ABC must be set to
reflect the annual catch that is
consistent with the schedule of fishing
mortality rates in the rebuilding plan.
Amendment 17B did not specify ABC
control rules for assessed species that
were not overfished or for data poor
species because these control rules were
under development by the SSC. The
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SSC met in March and June of 2009 to
determine ABC control rules for data
rich species, and met in April and
August of 2010 to identify the protocol
for determining the ABC for data poor
species. A final version of the SSC’s
recommendation of an ABC control rule
for assessed species was provided to the
Council at its March 2010 meeting, after
the Council had voted to submit
Amendment 17B for Secretarial review.
The SSC has not completed its
recommendations for ABC control rules
for non-assessed species. ABC control
rules for assessed and data poor species
will be included in the Comprehensive
ACL Amendment.
The SSC recommended and the
Council chose an ACL of zero for
speckled hind and warsaw grouper
based on landings only. Choosing an
ACL based on total mortality rather than
landed catch would require the SEFSC
to monitor discarded speckled hind and
warsaw grouper in the commercial and
recreational sectors. The Council’s SSC
expressed concerns about monitoring
discards when discussing ACLs for
speckled hind and warsaw grouper at its
March 2009 meeting. The SSC was not
only concerned about the accuracy of
discard data as currently collected from
the recreational and commercial sector
but also the possibility that some
members of the fishing community
might under-report discarded fish if
they believed further restrictions might
be imposed if levels of dead discards
became elevated. Therefore, due to
concern about monitoring discards, the
SSC recommended an acceptable
biological catch equal to zero for
speckled hind and warsaw grouper
based on landed catch only.
Management Measures: Action is
being taken in Amendment 17B to
reduce discards of speckled hind and
warsaw grouper by prohibiting the take
of co-occurring species in depths greater
than 240 ft (73 m). Rather than retain
and monitor speckled hind and warsaw
grouper discards, the intent of the area
closure is to reduce bycatch in an area
where release mortality is expected to
be very high. The relationship between
depth and mortality has not been
specified for speckled hind and warsaw
grouper. However, as previously
discussed, speckled hind and warsaw
grouper share similar biological
characteristics to gag; therefore, if depth
related release mortality of speckled
hind and warsaw grouper is similar to
gag, release mortality would be expected
to be approximately 70 percent in
depths of 240 ft (73 m).
Actions were taken to end overfishing
of golden tilefish, snowy grouper, and
black sea bass in Amendment 13C to the
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FMP. It will not be known if the
measures were successful in ending
overfishing until new assessments are
conducted for these species. New
benchmark assessments will be
conducted for golden tilefish and black
sea bass in 2011, and snowy grouper
will be assessed in 2013. Amendment
17B specifies ACLs and AMs for
speckled hind, warsaw grouper, snowy
grouper, gag, vermilion snapper, black
sea bass, golden tilefish, black grouper,
and red grouper, to ensure overfishing
of these species does not occur.
The National Standard 1 Guidelines
states that ‘‘if catch exceeds the ACL for
a given stock or stock complex more
than once in the last 4 years, the system
of ACLs and AMs should be reevaluated, and modified if necessary, to
improve its performance and
effectiveness.’’ Amendment 17B follows
this guidance for performance measures
with an action to update the framework
procedure to allow for adjustments to
OFL, ABC, and ACL based on SEDAR
reports or other new information. Under
the updated framework procedure, the
SSC would examine the social and
economic impact analyses for a specific
allocation, ACL, ACT, AM, quota, bag
limit, or other fishing restriction. If it is
determined by the Council and its SSC
that the management measures in place
are not constraining catch to a target
level, adjustments could be made
through a future regulatory amendment.
Comment 29: One commenter stated
Amendment 17B does not adequately
demonstrate that speckled hind and
warsaw grouper are undergoing
overfishing.
Response: According to the most
recent Report to Congress on the Status
of U.S. Fisheries, warsaw grouper and
speckled hind are undergoing
overfishing and have been identified as
experiencing overfishing every year
since the Report was initiated in 1997.
Status determinations in the Report to
Congress on the Status of U.S. Stocks
are generally made during a formal
review of a scientific stock assessment
using the best available scientific
information and status determination
criteria specified in a fishery
management plan. However, many
resources can be used to make status
determinations, including final peerreviewed documents such as Stock
Assessment Review Committee reports
and recommendations of each Council’s
Scientific and Statistical Committee.
The Council and NMFS are mandated to
end overfishing by the Reauthorized
Magnuson-Stevens Act, and to specify
ACLs and AMs for species undergoing
overfishing and to implement
management measures to ensure
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overfishing does not continue to occur.
New SEDAR benchmark assessments for
speckled hind and warsaw grouper are
scheduled for 2012 or 2013.
Comment 30: Three commenters felt
the Finding of No Significant Impact
(FONSI) for Amendment 17B
erroneously concluded that there are no
significant impacts as a result of this
amendment. One commenter requests
that an environmental impact statement
(EIS) be prepared for Amendment 17B.
Response: An environmental
assessment (EA) was conducted for
Amendment 17B, instead of an EIS,
because most of the ACLs and AMs
implemented through this final rule are
based on previously implemented
quotas and allocations, and the
deepwater closure was concluded to
result in a low to moderate level of
socioeconomic impact to the snappergrouper fishery. The deepwater closure
is expected to primarily affect
commercial fishermen who target
blueline tilefish off North Carolina, and
commercial and recreational fishermen
in areas of the Florida Keys where the
240-ft (73-m) depth boundary is close to
shore.
The significance of an action under
NEPA is determined by considering the
action’s context and intensity. In the
case of the deepwater area closure, the
impacts are not considered significant
because select groups of snappergrouper fishery participants are
expected to be impacted, and those
impacts are anticipated to be low to
moderate relative to the entire snappergrouper fishery. For the entire South
Atlantic, the prohibition on harvest and
possession of six deepwater snappergrouper species beyond a depth of 240
ft (73 m) is expected to reduce annual
overall net operating revenues in the
commercial snapper-grouper fishery by
about $292,000, or by 3.3 percent. For
the State of North Carolina alone, the
action is expected to reduce net
operating revenue in the commercial
sector by approximately 7 percent. As
such, the FONSI appropriately
concludes the actions in Amendment
17B are not expected to result in
significant impacts on the human
environment; and therefore, an EIS was
not prepared.
Comment 31: Several commenters
stated that the amendment would have
severe economic impacts on commercial
and recreational fishing opportunities
and operations, including their support
industries and local communities. Many
comments especially singled out the ban
on fishing for, retaining, and possessing
of six deepwater species in waters
beyond 240 ft (73 m) deep as a major
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factor that would put many people out
of work.
Response: The economic analysis of
the actions and alternatives considered
concluded that, with the exception of
the no action alternatives, practically all
management measure alternatives
would result in restricted fishing
opportunities and short-term adverse
economic effects on fishers, support
industries, and associated communities.
However, it is imperative that we take
some action to protect species
undergoing overfishing. The actions
adopted are expected to be those which
best achieve the Council’s objectives
while minimizing, to the extent
practicable, the adverse economic and
social effects on fishing participants and
associated communities.
Comment 32: One commenter stated
that no consideration was made of
potential differences in economic
impacts based on differences in fishing
practices and economic activities along
the coast.
Response: The economic analysis
evaluated the effects of the various
measures in Amendment 17B on vessels
by gear type used and geographic area
in the South Atlantic. Thus, the analysis
addressed, to the extent possible using
available data, the differential economic
effects of the alternatives based on gear
type and geographic location.
Comment 33: One commenter stated
that once the Council and NMFS
decided what the economic impacts are,
public comments would not count at all.
Response: The Council and NMFS
have taken multiple steps to solicit
comments from the public through
meetings, public hearings, and
dissemination of written materials on
the various issues considered in the
amendment. The law, as well as the
policies of the Council and NMFS,
requires consideration of public
comments as an integral part of the
regulatory process even after the
economic analysis is completed.
However, economic impacts are not the
only factor the Council and NMFS must
take into account.
Comment 34: Two commenters noted
that the 97 percent commercial and 3
percent recreational allocation of golden
tilefish neglects the contribution of the
recreational sector into the local
economy.
Response: The commercial/
recreational allocation for golden
tilefish took into account the past and
present landing records of both the
commercial and recreational sectors.
The economic effects of the various
allocation measures were evaluated
independently and in conjunction with
the other alternatives in the amendment.
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The economic analysis concluded that
the allocation ratio was not expected to
introduce severe dislocations of
commercial and recreational fishing
activities.
Comment 35: One commenter
mentioned the lack of analysis of the
cumulative economic impacts of the
amendment.
Response: The economic analysis
evaluated the cumulative effects of past
and present regulatory measures
affecting the snapper-grouper
recreational and commercial sectors.
Both quantitative and qualitative
discussions of cumulative economic
effects were presented.
Comment 36: One commenter
remarked that serious attention to
socioeconomic aspects of fisheries
management is grossly overlooked as
real science.
Response: NMFS has always
recognized the important role of social
science in fisheries management, as
specifically required by the MagnusonStevens Act, Regulatory Flexibility Act,
and Executive Order 12866. Although
the overriding objective of Amendment
17B has been to protect or rebuild the
subject snapper-grouper species, the
socioeconomic effects of the various
alternatives were evaluated and
considered in the choice of preferred
alternatives.
Classification
The Regional Administrator,
Southeast Region, NMFS has
determined that Amendment 17B is
necessary for the conservation and
management of South Atlantic snappergrouper and 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.
NMFS prepared a FRFA, as required
by section 604 of the Regulatory
Flexibility Act. The FRFA describes the
economic impact this final rule is
expected to have on small entities. A
description of the action, why it is being
considered, and the objectives of, and
legal basis for, this action are contained
at the beginning of this section in the
preamble and in the SUMMARY section of
the preamble. A copy of this analysis is
available from the NMFS (see
ADDRESSES). The FRFA follows.
No public comments specific to the
IRFA were received. However, 22 of the
175 comments contained statements
regarding the economic effects of the
amendment, and they are addressed in
comments/responses section,
specifically comments/responses
number 31 through 36.
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NMFS agrees with the Council’s
choice of preferred alternatives as those
which would be expected to best
achieve the Council’s objectives while
minimizing, to the extent practicable,
the adverse effects on fishers, support
industries, and associated communities.
No changes to the proposed rule were
made in response to public comments.
The final rule introduces several
changes to the management of the South
Atlantic snapper-grouper fishery. This
rule establishes an ACL of zero for
speckled hind and warsaw grouper, and
this prohibits the harvest and
possession of speckled hind and warsaw
grouper. The rule prohibits fishing for
and possession of snowy grouper,
blueline tilefish, yellowedge grouper,
warsaw grouper, speckled hind, misty
grouper, queen snapper, and silk
snapper beyond a depth of 240 ft (73 m).
This rule establishes a 97-percent
commercial and 3-percent recreational
allocation of golden tilefish. This rule
establishes a commercial ACL (quota)
for golden tilefish of 282,819 lb (128,284
kg) gutted weight and a recreational
ACL of 1,578 fish based on the chosen
allocation for golden tilefish. The
commercial AM for golden tilefish
prohibits the harvest, possession,
purchase, and sale of golden tilefish
after the quota is met or projected to be
met. The recreational AM is specified as
follows: If the ACL is exceeded, the
Regional Administrator (RA) shall
publish a notice to reduce the length of
the following fishing season by the
amount necessary to ensure landings do
not exceed the sector ACL in the
following fishing year. The recreational
ACL would be compared to recreational
landings using only 2010 landings for
2010, an average of 2010 and 2011
landings for 2011, and a 3-year average
of landings for 2012 and beyond.
This rule establishes a recreational
daily bag limit of one snowy grouper per
vessel, with a recreational ACL of 523
fish and a recreational AM specified as
follows: If the ACL is exceeded, the RA
shall publish a notice to reduce the
length of the following fishing season by
the amount necessary to ensure landings
do not exceed the sector ACL in the
following fishing year. The recreational
ACL would be compared to recreational
landings using only 2010 landings for
2010, an average of 2010 and 2011
landings for 2011, and a 3-year average
of landings for 2012 and beyond.
This rule establishes an aggregate ACL
(quota) for gag, black grouper, and red
grouper of 662,403 lb (300,461 kg)
gutted weight (commercial) and 648,663
lb (294,229 kg) gutted weight
(recreational), but retains the
commercial ACL (quota) for gag or
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82289
352,940 lb (160,091 kg) gutted weight
and recreational ACL for gag of 340,060
lb (154,249 kg) gutted weight. This rule
prohibits the commercial possession of
shallow-water groupers (gag, black
grouper, red grouper, scamp, red hind,
yellowmouth grouper, tiger grouper,
yellowfin grouper, graysby, and coney)
when the gag ACL (currently at 352,940
lb (160,091 kg) gutted weight) or the
aggregate gag, black grouper, and red
grouper ACL is met or projected to be
met. This rule implements recreational
AMs for black grouper, black sea bass,
gag, red grouper, and vermilion snapper
as follows: If a species is overfished and
the sector ACL is met or projected to be
met, prohibit the harvest and retention
of the species or species group. If the
ACL is exceeded, independent of stock
status, the RA shall publish a notice to
reduce the sector ACL in the following
fishing season by the amount of the
overage. The recreational ACL would be
compared to recreational landings using
only 2010 landings for 2010, an average
of 2010 and 2011 landings for 2011, and
a 3-year running average of landings for
2012 and beyond.
Finally, this rule updates the
framework procedure for specification
of Total Allowable Catch (TAC) for the
FMP to incorporate ACLs, ACTs, and
AMs. Such modifications are based
upon new scientific information
indicating such modifications are
prudent.
The Magnuson-Stevens Act provides
the statutory basis for the final rule.
No duplicative, overlapping, or
conflicting Federal rules have been
identified. The final rule does not alter
existing reporting, recordkeeping, or
other compliance requirements.
The final rule is expected to directly
affect commercial fishers and for-hire
operators. The SBA has established size
criteria for all major industry sectors in
the U.S. including commercial fish
harvesters and for-hire operations. A
business involved in fish harvesting is
classified as a small business if it is
independently owned and operated, is
not dominant in its field of operation
(including its affiliates), and has
combined annual receipts not in excess
of $4.0 million (NAICS code 114111,
finfish fishing) for all its affiliated
operations worldwide. For for-hire
vessels, the other qualifiers apply and
the annual receipts threshold is $7.0
million (NAICS code 713990,
recreational industries).
From 2003–2007, an average of 944
vessels per year was permitted to
operate in the commercial sector of the
snapper-grouper fishery. Of these
vessels, 749 held transferable permits
and 195 held non-transferable permits.
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As of December 17, 2010, there are 604
vessels with transferable permits and
138 vessels with non-transferable
permits. On average, 890 vessels landed
6.43 million lb (2.92 million kg) of
snapper-grouper species and 1.95
million lb (0.88 million kg) of other
species on snapper-grouper trips. Total
dockside revenues from snappergrouper species stood at $13.81 million
and at $2.30 million from other species.
Considering revenues from both
snapper-grouper and other species, the
revenues per vessel were approximately
$18,101. An average of 27 vessels per
year harvested more than 50,000 lb
(22,680 million kg) of snapper-grouper
species per year, generating dockside
revenues of at least $107,500, at an
average price of $2.15 (2007 dollars) per
pound. Commercial vessels that operate
in the snapper-grouper fishery may also
operate in other fisheries, the revenues
of which cannot be determined with
available data and are not reflected in
these totals.
Although a vessel that possesses a
commercial snapper-grouper permit can
harvest any snapper-grouper species,
not all permitted vessels or vessels that
landed snapper-grouper landed all of
the major species in this amendment.
The following average number of vessels
landed the subject species in 2003–
2007: 292 vessels landed gag, 253
vessels landed vermilion snapper, 32
vessels landed speckled hind, 64 vessels
landed golden tilefish, 160 vessels
landed snowy grouper, 323 vessels
landed black grouper, 237 vessels
landed black sea bass, and 402 vessels
landed red grouper. Combining
revenues from snapper-grouper and
other species on the same trip, the
average revenue per vessel for vessels
landing the subject species were
$20,551 for gag, $28,454 for vermilion
snapper, $6,250 for speckled hind,
$17,266 for golden tilefish, $7,186 for
black grouper, $19,034 for black sea
bass, and $17,164 for red grouper.
Based on revenue information, all
commercial vessels that would be
affected by the final action are
considered to be small entities.
For the period 2003–2007, an average
of 1,635 vessels were permitted to
operate in the snapper-grouper for-hire
sector, of which 82 are estimated to
have operated as headboats and 1,553 as
charter boats. As of December 17, 2010,
there are 1,474 permitted for-hire
vessels. The for-hire fleet is comprised
of charterboats, which charge a fee on a
vessel basis, and headboats, which
charge a fee on an individual angler
(head) basis. Within the total number of
vessels, 227 also possessed a
commercial snapper-grouper permit and
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would be included in the summary
information provided on the
commercial sector. The charterboat
annual average gross revenue is
estimated to range from approximately
$62,000–$84,000 for Florida vessels,
$73,000–$89,000 for North Carolina
vessels, $68,000–$83,000 for Georgia
vessels, and $32,000–$39,000 for South
Carolina vessels. For headboats, the
appropriate estimates are $170,000–
$362,000 for Florida vessels, and
$149,000–$317,000 for vessels in the
other States.
Based on average revenue figures, all
for-hire operations that would be
affected by the final action are
considered to be small entities.
Some fleet activity (i.e., multiple
vessels owned by a single entity) may
exist in both the commercial and forhire snapper-grouper sectors, but the
extent of such is unknown and all
vessels are treated as independent
entities in this analysis.
The measure to establish an ACL of
zero for speckled hind and warsaw
grouper, together with the ban on
fishing for deepwater species cooccurring with these two species
beyond 240 ft (73 m), is expected to
reduce net operating revenues of
commercial vessels by about $292,000.
This measure is also expected to reduce
net operating revenues of for-hire
vessels by less than $102,000.
Establishing a 97 percent commercial
and 3 percent recreational allocation of
golden tilefish would maintain the longterm and short-term proportional
landings history of the commercial and
recreational sectors, with possible small
short-term changes (depending on the
ACL) in net operating revenues of both
commercial and for-hire vessels. At this
allocation ratio, the corresponding
commercial ACL (quota) would be
282,819 lb (128,284 kg) gutted weight
and the recreational allocation would be
1,578 fish (8,747 lb (3,968 kg) gutted
weight). The golden tilefish commercial
quota in combination with the AM of
closing the fishery after the quota is met
is expected to reduce net operating
revenues of vessels with snappergrouper commercial permits by about
$8,000. The recreational allocation is
expected to result in net revenue
reductions of for-hire snapper-grouper
vessels by about $7,000. It is worth
noting, however, that the reduction in
net operating revenues of for-hire
vessels is not immediate because the
recreational AM would shorten only the
subsequent year’s fishing season and
only when recreational landings over a
number of years (except for 2010)
exceed the ACL.
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Establishing a daily bag limit of one
snowy grouper per vessel is expected to
reduce net operating revenues of forhire snapper-grouper vessels by about
$7,000. This reduction in net operating
revenues would not be immediate
because the recreational AM would
shorten only the subsequent year’s
fishing season and only when
recreational landings over a number of
years (except for 2010) exceed the ACL.
The combined measures of retaining
the commercial ACL for gag of 352,940
lb (160,091 kg) gutted weight, to
establish an aggregate commercial ACL
for gag, red grouper, and black grouper
of 662,403 lb (300,461 kg) gutted weight,
and to close the fishery when the gag
ACL or the aggregate ACL is reached is
expected to reduce net operating
revenues of commercial vessels by about
$103,000. For the recreational
component of the snapper-grouper
fishery, the combined measures of
retaining the recreational ACL for gag of
340,060 lb (154,249 kg) gutted weight
and establishing an aggregate
recreational ACL for gag, red grouper,
and black grouper of 648,663 lb
(294,229 kg) gutted weight are not
expected to affect the net operating
revenues of for-hire snapper-grouper
vessels because these are the expected
landings from implementation of
previous amendments, notably
Amendment 16 to the FMP. There is a
possibility that the recreational AM of
prohibiting the harvest and retention of
an overfished species when the sector
ACL is met or projected to be met would
have negative impacts on for-hire
snapper-grouper vessels fishing for
black sea bass. Under this AM, for-hire
snapper-grouper vessels as a whole
could potentially lose about $860,000 in
net revenues. This reduction is likely to
be an overestimate for at least two
reasons. First, the method used in
estimating the economic effects on the
recreational sector likely overestimated
the number of headboat angler trips
affected by the measure. Second, the
trend of recreational black sea bass
landings has been downward due to the
implementation of more restrictive
measures provided in previous
amendments. Therefore, using average
landings over the period 2005–2008
inflated the landings when compared to
the ACL.
Updating the framework procedure
for specification of TAC has no direct
effects on the net operating revenues of
commercial and for-hire snappergrouper vessels.
Five alternatives, including the final
action, were considered for establishing
an ACL for speckled hind and warsaw
grouper. The first alternative to the final
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action, the no action alternative, would
not conform to the requirements of the
Magnuson-Stevens Act, as reauthorized
in 2006, to establish an ACL for the
subject species. The second alternative
to the final action would establish an
ACL of zero for speckled hind and
warsaw grouper but would not close any
areas to fishing for deepwater species
that co-occur with these two species.
Although this alternative would have
smaller negative economic effects on
small entities than the final action, it
would not be sufficient to end
overfishing of speckled hind and
warsaw grouper due to discard mortality
from fishing for other co-occurring
deepwater species. The third alternative
to the final action is the same as the
final action, except that the fishing
prohibition for other co-occurring
deepwater species would apply to all
depths. In this case, this alternative
would result in greater negative
economic effects on small entities than
the final action. The fourth alternative
to the final action is similar to the final
action, except that the prohibition on
fishing for other co-occurring deepwater
species would be beyond 300 ft (92 m).
With smaller closed areas, this
alternative would result in slightly
smaller negative economic effects on
small entities. On the other hand, the
protection this alternative provides for
adult speckled hind and warsaw
grouper would be less than that of the
final action. The possibility of
continued overfishing for the subject
species may still occur under this
alternative.
Four alternatives, including the final
action, were considered for the golden
tilefish allocation. The first alternative
to the final action, the no action
alternative, would not establish a
commercial and recreational allocation
for golden tilefish. Without a defined
sector allocation, it would be difficult to
define sector ACLs and to take
corrective actions should the sector
ACLs or overall ACL be exceeded. This
would weaken the ability of fishery
managers to effectively manage the
stock. The second alternative to the final
action would establish a 96-percent
commercial and 4-percent recreational
allocation. This allocation is very close
to that provided under the final action,
and thus its economic effects would
only minimally differ from those of the
final action. This alternative uses only
the most current landings records
(2006–2008) while the final action uses
both the long-run (1986–2008) and
short-run (2006–2008) landings history.
The third alternative to the final action
would establish a 50-percent
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commercial and 50-percent recreational
allocation. This alternative would create
significant disruptions to the
commercial sector operations, and thus
would impose relatively large costs to
this sector. The recreational sector
would stand to gain from this allocation,
but whether or not the gains to the
recreational sector would outweigh
losses to the commercial sector cannot
be determined. At least in the short-term
and given the current bag limit of one
fish per person per day, benefits to the
recreational sector would be relatively
small and would not compensate for the
losses in the commercial sector. Thus,
the expected net economic effects of this
alternative in the short-term would be
negative.
Five alternatives, including the final
action, were considered for the golden
tilefish ACL and AM. The first
alternative to the final action, the no
action alternative, would retain the
current ACL (quota) for the commercial
sector based on FMSY and would not
establish an ACL for the recreational
sector. The current AM would close all
fishing for golden tilefish once the
commercial quota is reached. This
alternative would not add any more
fishery restrictions and economic losses
to the fishery participants, but it would
be less conservative than the final action
in rebuilding the stock as to potentially
lengthen the recovery of the stock
beyond the specified rebuilding period.
In addition, it would provide less
flexibility in implementing sectorspecific AMs. The second alternative to
the final action would establish a single
commercial and recreational ACL which
would combine the commercial ACL at
the FOY level and the recreational
allowable harvest at the OY level. The
AM would prohibit commercial and
recreational harvest when the ACL is
projected to be met. This alternative
would result in approximately the same
economic losses to the commercial
sector as the final action. There is some
potential for this alternative to result in
smaller economic losses to the
recreational sector than the final action,
especially if only the commercial
landings were effectively monitored
because then the recreational fishing
season would remain open longer. But
to the extent that the AM under this
alternative would be imposed in-season
while that of the final action would
become effective only in subsequent
years, the economic effects of this
alternative over time could very well
exceed those of the final action. The
third alternative to the final action
would establish a recreational AM of
one golden tilefish per vessel per day
PO 00000
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Fmt 4700
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82291
when the single ACL (sum of the
commercial ACL at the FOY level and
recreational harvest at the OY level) is
met or projected to be met. This
alternative offers potential for smaller
economic losses to the recreational
sector than the final action by
maintaining a year-round recreational
fishing season although at a very limited
bag limit. However, because this
alternative requires an in-season
adjustment in lieu of subsequent-year
adjustments, as under the final action,
the resulting economic losses over time
due to this alternative could exceed
those of the final action. The fourth
alternative to the final action would
establish a commercial and recreational
ACL based on the yield at FOY for the
commercial fishery. The AM for both
sectors would be to prohibit harvest,
possession, and retention of golden
tilefish when commercial landings
exceed the ACL. This alternative would
have the same economic effects on the
commercial sector as the final action,
but losses to the recreational sector
would likely exceed those of the final
action.
Four alternatives, including the final
action, were considered for establishing
a snowy grouper ACL and AM. The first
alternative, the no action alternative, to
the final action would retain the
commercial ACL (quota) of 82,900 lb
(37,603 kg) gutted weight as the ACL
based on the current TAC of 87,254 lb
(39,578 kg) gutted weight; would retain
the commercial AM which is to prohibit
harvest, possession, and retention of
snowy grouper when the quota is met or
projected to be met; would maintain the
recreational ACL of 523 fish; and, would
not implement a recreational AM. This
alternative would not add any
restrictions to either the commercial or
recreational sector. The absence of an
AM for the recreational sector would
make it difficult to implement sectorspecific adjustments. The second
alternative to the final action would
establish a single commercial/
recreational ACL based on the current
TAC of 87,254 lb (39,578 kg) gutted
weight, and the AM for both sectors
would be a closure of the fishery when
the ACL is met or projected to be met.
This alternative may result in slightly
better economic effects on the
commercial sector than the final action
or the no action alternative, but this
slight advantage of the commercial
sector would come at the expense of the
recreational sector. In effect, this
alternative would have slightly larger
short-term economic losses on the
recreational sector than the final action.
In addition, this alternative would not
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allow for sector-specific adjustments
should ACL overages occur. The third
alternative to the final action would
establish a recreational AM of one fish
per vessel per day when the commercial
quota is met or projected to be met. The
commercial AM would be a fishery
closure when the quota is met. This
alternative would have similar
economic effects for the commercial
sector as the no action alternative and
slightly lower short-term negative
effects on the recreational sector than
the final action. However, unlike the
final action, this alternative could result
in overages in the recreational sector
without a possible compensating
adjustment in succeeding years, thereby
potentially resulting in less protection
to the stock.
Five alternatives, two of which
comprise the final action, were
considered for the black grouper, black
sea bass, gag, red grouper, and vermilion
snapper ACL, AM, and ACT. The
alternative for establishing commercial
and recreational ACLs consisted of two
sub-alternatives, one of which is the
final action. The ACT alternative for the
recreational sector consisted of three
sub-alternatives, none of which were
selected as the final action. The AM
alternative for the recreational sector
consisted of three sub-alternatives, one
of which is the final action. The first
alternative to the final action, the no
action alternative, would retain the
commercial and recreational ACLs
(quotas) for black sea bass, gag, and
vermilion snapper and would not
establish commercial and recreational
ACLs for black grouper and red grouper.
This alternative would not comply with
the requirements of the MagnusonStevens Act, as reauthorized in 2006.
The second alternative to the final
action for commercial and recreational
ACLs would establish black grouper
commercial and recreational ACLs of
86,886 lb (39,411 kg) gutted weight and
31,863 lb (14,453 kg) gutted weight,
respectively. It would also establish red
grouper commercial and recreational
ACLs of 221,577 lb (100,505 kg) gutted
weight and 276,740 lb (125,527 kg)
gutted weight, respectively. This
alternative would have similar
biological effects as the final action.
However, it could result in slightly
worse economic effects as the final
action because it would allow less
flexibility for small entities in adjusting
their fishing operations with respect to
gag, black grouper, and red grouper. The
third alternative to the final action for
the recreational AM consisted of two
sub-alternatives. The first subalternative would require the RA to
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reduce the length of the following
fishing year if the ACL were exceeded
in the current year. Although this
alternative would provide less negative
effects in the short-term, it would
provide less biological benefits than the
final action, particularly with respect to
overfished species, so as to delay further
the generation of economic benefits
from the fishery. The second subalternative would close the fishery if the
sector ACT were exceeded for an
overfished species or species group and
would require the RA to reduce the
sector ACT the following year. By not
selecting any ACT, this alternative
would not be a viable alternative. If
ACTs were selected, this alternative
would likely result in larger short-term
economic losses than the final
alternative.
Two alternatives, including the final
action, were considered for updating the
framework procedure for specification
of TAC in the FMP to incorporate ACLs,
ACTs, and AMs. The only alternative to
the final action, the no action
alternative, would delay the
implementation or modification of
ACLs, ACTs, and AMs when new
scientific information becomes available
because this would require the FMP
amendment process which would incur
more administrative costs than the final
action.
Deep-water grouper (DWG) means, in
the Gulf, yellowedge grouper, misty
grouper, warsaw grouper, snowy
grouper, and speckled hind. In addition,
for the purposes of the IFQ program for
Gulf groupers and tilefishes in § 622.20,
scamp are also included as DWG as
specified in § 622.20(b)(2)(vi).
Deep-water snapper-grouper (DWSG)
means, in the South Atlantic,
yellowedge grouper, misty grouper,
warsaw grouper, snowy grouper,
speckled hind, blueline tilefish, queen
snapper, and silk snapper.
*
*
*
*
*
Shallow-water grouper (SWG) means,
in the Gulf, gag, red grouper, black
grouper, scamp, yellowfin grouper, rock
hind, red hind, and yellowmouth
grouper. In addition, for the purposes of
the IFQ program for Gulf groupers and
tilefishes in § 622.20, speckled hind and
warsaw grouper are also included as
SWG as specified in § 622.20(b)(2)(v).
*
*
*
*
*
South Atlantic shallow-water grouper
(SASWG) means, in the South Atlantic,
gag, black grouper, red grouper, scamp,
red hind, rock hind, yellowmouth
grouper, tiger grouper, yellowfin
grouper, graysby, and coney.
*
*
*
*
*
■ 3. In § 622.4, the first sentence of
paragraph (a)(2)(vi) is revised to read as
follows:
List of Subjects in 50 CFR Part 622
§ 622.4
Fisheries, Fishing, Puerto Rico,
Reporting and recordkeeping
requirements, Virgin Islands.
(a) * * *
(2) * * *
(vi) * * * For a person aboard a
vessel to be eligible for exemption from
the bag limits for South Atlantic
snapper-grouper in or from the South
Atlantic EEZ, to sell South Atlantic
snapper-grouper in or from the South
Atlantic EEZ, to engage in the directed
fishery for tilefish in the South Atlantic
EEZ, to use a longline to fish for South
Atlantic snapper-grouper in the South
Atlantic EEZ, or to use a sea bass pot in
the South Atlantic EEZ between
35°15.19′ N. lat. (due east of Cape
Hatteras Light, NC) and 28°35.1′ N. lat.
(due east of the NASA Vehicle
Assembly Building, Cape Canaveral,
FL), a commercial vessel permit for
South Atlantic snapper-grouper must
have been issued to the vessel and must
be on board. * * *
*
*
*
*
*
■ 4. In § 622.9, the first sentence of
paragraph (a)(1) is revised to read as
follows:
Dated: December 22, 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 622 is amended
as follows:
■
PART 622—FISHERIES OF THE
CARIBBEAN, GULF, AND SOUTH
ATLANTIC
1. The authority citation for part 622
continues to read as follows:
■
Authority: 16 U.S.C. 1801 et seq.
2. In § 622.2, the definitions of ‘‘Deepwater grouper (DWG)’’ and ‘‘Shallowwater grouper (SWG)’’ are revised and
definitions of ‘‘Deep-water snappergrouper (DWSG)’’ and ‘‘South Atlantic
shallow-water grouper (SASWG)’’ are
added in alphabetical order to read as
follows:
■
§ 622.2
*
PO 00000
*
Definitions and acronyms.
*
Frm 00076
*
Fmt 4700
*
Sfmt 4700
Permits and fees.
§ 622.9 Vessel monitoring systems
(VMSs).
(a) * * *
(1) * * * An owner or operator of a
vessel that has been issued a limited
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access endorsement for South Atlantic
rock shrimp (until January 27, 2010) or
a Commercial Vessel Permit for Rock
Shrimp (South Atlantic EEZ) must
ensure that such vessel has an operating
VMS approved by NMFS for use in the
South Atlantic rock shrimp fishery on
board when on a trip in the South
Atlantic. * * *
*
*
*
*
*
■ 5. In § 622.32, paragraph (c)(3) is
removed and paragraph (b)(3)(vii) is
added to read as follows:
§ 622.32 Prohibited and limited-harvest
species.
*
*
*
*
*
(b) * * *
(3) * * *
(vii) Speckled hind and warsaw
grouper may not be harvested or
possessed in or from the South Atlantic
EEZ. Such fish caught in the South
Atlantic EEZ must be released
immediately with a minimum of harm.
These restrictions also apply in the
South Atlantic on board a vessel for
which a valid Federal commercial or
charter vessel/headboat permit for
South Atlantic snapper-grouper has
been issued, i.e., in State or Federal
waters.
*
*
*
*
*
■ 6. In § 622.35, the first sentence of
paragraph (j) is revised and paragraph
(o) is added to read as follows:
§ 622.35 Atlantic EEZ seasonal and/or area
closures.
*
*
*
*
*
(j) * * * During January through
April each year, no person may fish for,
harvest, or possess in or from the South
Atlantic EEZ any SASWG (gag, black
grouper, red grouper, scamp, red hind,
rock hind, yellowmouth grouper, tiger
grouper, yellowfin grouper, graysby, and
coney). * * *
*
*
*
*
*
(o) Depth closure for deep-water
snapper-grouper (DWSG). No person
may fish for or possess DWSG
(yellowedge grouper, misty grouper,
warsaw grouper, snowy grouper,
speckled hind, blueline tilefish, queen
snapper, and silk snapper) in or from
the South Atlantic EEZ offshore of
rhumb lines connecting, in order, the
following points:
srobinson on DSKHWCL6B1PROD with RULES
Point
A ...............
B ...............
C ...............
D ...............
E ...............
F ................
G ...............
H ...............
VerDate Mar<15>2010
North lat.
36°31′01″
35°57′29″
35°30′49″
34°19′41″
33°13′31″
33°05′13″
32°24′03″
31°39′04″
17:29 Dec 29, 2010
Point
North lat.
I .................
J ................
K ...............
L ................
M ...............
N ...............
O ...............
P ...............
Q ...............
R ...............
S ...............
T ................
U ...............
V ...............
W ..............
X ...............
Y ...............
30°27′33″
29°53′21″
29°24′03″
28°19′29″
27°32′05″
26°52′45″
26°03′36″
25°31′03″
25°13′44″
24°59′09″
24°42′06″
24°33′53″
24°25′20″
24°25′49″
24°21′35″
24°21′29″
24°25′37″
West long.
80°11′39″
80°16′01″
80°16′01″
80°00′27″
79°58′49″
79°58′49″
80°04′33″
80°04′55″
80°09′40″
80°19′51″
80°46′38″
81°10′23″
81°50′25″
82°11′17″
82°22′32″
82°42′33″
83°00′00″
7. In § 622.39, paragraph (d)(1)(ii)(B)
is revised to read as follows:
■
§ 622.39
Bag and possession limits.
*
*
*
*
*
(d) * * *
(1) * * *
(ii) * * *
(B) No more than one fish per vessel
may be a snowy grouper;
*
*
*
*
*
■ 8. In § 622.42, paragraph (e)(1)(ii) is
removed; paragraphs (e)(1), (e)(2), (e)(5),
and (e)(6) are revised; and paragraph
(e)(8) is added to read as follows:
§ 622.42
Quotas.
*
*
*
*
*
(e) * * *
(1) Snowy grouper—82,900 lb (37,603
kg).
(2) Golden tilefish—282,819 lb
(128,284 kg).
*
*
*
*
*
(5) Black sea bass—309,000 lb
(140,160 kg).
(6) Red porgy—190,050 lb (86,205 kg).
*
*
*
*
*
(8) Gag, black grouper, and red
grouper, combined—662,403 lb (300,461
kg).
*
*
*
*
*
■ 9. In § 622.43, the heading for
paragraph (a)(5) and paragraph (a)(5)(iii)
are revised to read as follows:
§ 622.43
Closures.
(a) * * *
(5) South Atlantic gag, black grouper,
red grouper, greater amberjack, snowy
grouper, golden tilefish, vermilion
snapper, black sea bass, and red porgy.
West long.
*
*
*
*
*
74°48′10″
(iii) For gag and for gag, black
74°55′49″ grouper, and red grouper, combined,
74°49′17″ when the appropriate commercial quota
76°00′21″ is reached, the provisions of paragraphs
77°17′50″
(a)(5)(i) and (ii) of this section apply to
77°49′24″
78°57′03″ gag and all other SASWG.
*
*
*
*
79°38′46″ *
Jkt 223001
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Frm 00077
Fmt 4700
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82293
10. In § 622.44, paragraph (c)(3) is
revised to read as follows:
■
§ 622.44
Commercial trip limits.
*
*
*
*
*
(c) * * *
(3) Snowy grouper. Until the quota
specified in § 622.42(e)(1) is reached—
100 lb (45 kg). See § 622.43(a)(5) for the
limitations regarding snowy grouper
after the fishing year quota is reached.
*
*
*
*
*
■ 11. In § 622.48, paragraph (f) is
revised to read as follows:
§ 622.48 Adjustment of management
measures.
*
*
*
*
*
(f) South Atlantic snapper-grouper
and wreckfish. Biomass levels, agestructured analyses, target dates for
rebuilding overfished species, MSY,
ABC, TAC, quotas, annual catch limits
(ACLs), target catch levels,
accountability measures (AMs), trip
limits, bag limits, minimum sizes, gear
restrictions (ranging from regulation to
complete prohibition), seasonal or area
closures, definitions of essential fish
habitat, essential fish habitat, essential
fish habitat HAPCs or Coral HAPCs, and
restrictions on gear and fishing activities
applicable in essential fish habitat and
essential fish habitat HAPCs.
*
*
*
*
*
■ 12. In § 622.49, paragraph (b) is added
to read as follows:
§ 622.49
Accountability measures.
*
*
*
*
*
(b) South Atlantic snapper-grouper.
(1) Golden tilefish—(i) Commercial
fishery. If commercial landings, as
estimated by the SRD, reach or are
projected to reach the quota specified in
§ 622.42(e)(2), the AA will file a
notification with the Office of the
Federal Register to close the commercial
fishery for the remainder of the fishing
year.
(ii) Recreational fishery. If
recreational landings, as estimated by
the SRD, exceed the recreational annual
catch limit (ACL) of 1,578 fish, the AA
will file a notification with the Office of
the Federal Register, at or near the
beginning of the following fishing year,
to reduce the length of the following
recreational fishing season by the
amount necessary to ensure recreational
landings do not exceed the recreational
ACL in the following fishing year.
Recreational landings will be evaluated
relative to the ACL as follows. For 2010,
only 2010 recreational landings will be
compared to the ACL; in 2011, the
average of 2010 and 2011 recreational
landings will be compared to the ACL;
and in 2012 and subsequent fishing
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years, the most recent 3-year running
average recreational landings will be
compared to the ACL.
(2) Snowy grouper—(i) Commercial
fishery. If commercial landings, as
estimated by the SRD, reach or are
projected to reach the quota specified in
§ 622.42(e)(1), the AA will file a
notification with the Office of the
Federal Register to close the commercial
fishery for the remainder of the fishing
year.
(ii) Recreational fishery. If
recreational landings, as estimated by
the SRD, exceed the recreational ACL of
523 fish, the AA will file a notification
with the Office of the Federal Register,
at or near the beginning of the following
fishing year, to reduce the length of the
following recreational fishing season by
the amount necessary to ensure
recreational landings do not exceed the
recreational ACL in the following
fishing year. Recreational landings will
be evaluated relative to the ACL as
follows. For 2010, only 2010
recreational landings will be compared
to the ACL; in 2011, the average of 2010
and 2011 recreational landings will be
compared to the ACL; and in 2012 and
subsequent fishing years, the most
recent 3-year running average
recreational landings will be compared
to the ACL.
(3) Gag—(i) Commercial fishery. If
commercial landings, as estimated by
the SRD, reach or are projected to reach
the quota specified in § 622.42(e)(7), the
AA will file a notification with the
Office of the Federal Register to close
the commercial fishery for gag and all
other SASWG for the remainder of the
fishing year.
(ii) Recreational fishery. (A) If
recreational landings, as estimated by
the SRD, reach or are projected to reach
the recreational ACL of 340,060 lb
(154,249 kg), gutted weight, and gag are
overfished, based on the most recent
Status of U.S. Fisheries Report to
Congress, the AA will file a notification
with the Office of the Federal Register
to close the gag recreational fishery for
the remainder of the fishing year. On
and after the effective date of such
notification, the bag and possession
limit for gag in or from the South
Atlantic EEZ is zero. This bag and
possession limit also applies in the
South Atlantic on board a vessel for
which a valid Federal charter vessel/
headboat permit for South Atlantic
snapper-grouper has been issued,
without regard to where such species
were harvested, i.e., in State or Federal
waters.
(B) Without regard to overfished
status, if gag recreational landings
exceed the ACL, the AA will file a
VerDate Mar<15>2010
17:29 Dec 29, 2010
Jkt 223001
notification with the Office of the
Federal Register, at or near the
beginning of the following fishing year,
to reduce the ACL for that fishing year
by the amount of the overage.
(C) Recreational landings will be
evaluated relative to the ACL as follows.
For 2010, only 2010 recreational
landings will be compared to the ACL;
in 2011, the average of 2010 and 2011
recreational landings will be compared
to the ACL; and in 2012 and subsequent
fishing years, the most recent 3-year
running average recreational landings
will be compared to the ACL.
(4) Gag, black grouper, and red
grouper, combined—(i) Commercial
fishery. If commercial landings, as
estimated by the SRD, reach or are
projected to reach the quota specified in
§ 622.42(e)(8), the AA will file a
notification with the Office of the
Federal Register to close the commercial
fishery for gag, black grouper, red
grouper and all other SASWG for the
remainder of the fishing year.
(ii) Recreational fishery. (A) If
recreational landings, as estimated by
the SRD, reach or are projected to reach
the combined recreational ACL of
648,663 lb (294,229 kg), gutted weight,
and gag, black grouper, or red grouper
are overfished, based on the most recent
Status of U.S. Fisheries Report to
Congress, the AA will file a notification
with the Office of the Federal Register
to close the recreational fishery for gag,
black grouper, and red grouper for the
remainder of the fishing year. On and
after the effective date of such
notification, the bag and possession
limit of gag, black grouper, and red
grouper in or from the South Atlantic
EEZ is zero. This bag and possession
limit also applies in the South Atlantic
on board a vessel for which a valid
Federal charter vessel/headboat permit
for South Atlantic snapper-grouper has
been issued, without regard to where
such species were harvested, i.e., in
State or Federal waters.
(B) Without regard to overfished
status, if gag, black grouper, and red
grouper recreational landings exceed the
combined ACL, the AA will file a
notification with the Office of the
Federal Register, at or near the
beginning of the following fishing year,
to reduce the combined ACL for that
fishing year by the amount of the
overage.
(C) Recreational landings will be
evaluated relative to the ACL as follows.
For 2010, only 2010 recreational
landings will be compared to the ACL;
in 2011, the average of 2010 and 2011
recreational landings will be compared
to the ACL; and in 2012 and subsequent
fishing years, the most recent 3-year
PO 00000
Frm 00078
Fmt 4700
Sfmt 4700
running average recreational landings
will be compared to the ACL.
(5) Black sea bass—(i) Commercial
fishery. If commercial landings, as
estimated by the SRD, reach or are
projected to reach the quota specified in
§ 622.42(e)(5), the AA will file a
notification with the Office of the
Federal Register to close the commercial
fishery for the remainder of the fishing
year.
(ii) Recreational fishery. (A) If
recreational landings, as estimated by
the SRD, reach or are projected to reach
the recreational ACL of 409,000 lb
(185,519 kg), gutted weight, and black
sea bass are overfished, based on the
most recent Status of U.S. Fisheries
Report to Congress, the AA will file a
notification with the Office of the
Federal Register to close the recreational
fishery for black sea bass for the
remainder of the fishing year. On and
after the effective date of such
notification, the bag and possession
limit of black sea bass in or from the
South Atlantic EEZ is zero. This bag and
possession limit also applies in the
South Atlantic on board a vessel for
which a valid Federal charter vessel/
headboat permit for South Atlantic
snapper-grouper has been issued,
without regard to where such species
were harvested, i.e., in State or Federal
waters.
(B) Without regard to overfished
status, if black sea bass recreational
landings exceed the ACL, the AA will
file a notification with the Office of the
Federal Register, at or near the
beginning of the following fishing year,
to reduce the ACL for that fishing year
by the amount of the overage.
(C) Recreational landings will be
evaluated relative to the ACL as follows.
For 2010, only 2010 recreational
landings will be compared to the ACL;
in 2011, the average of 2010 and 2011
recreational landings will be compared
to the ACL; and in 2012 and subsequent
fishing years, the most recent 3-year
running average recreational landings
will be compared to the ACL.
(6) Vermilion snapper—(i)
Commercial fishery. If commercial
landings, as estimated by the SRD, reach
or are projected to reach a quota
specified in § 622.42(e)(4)(i) or (ii), the
AA will file a notification with the
Office of the Federal Register to close
the commercial fishery for that portion
of the fishing year applicable to the
respective quota.
(ii) Recreational fishery. (A) If
recreational landings, as estimated by
the SRD, reach or are projected to reach
the recreational ACL of 307,315 lb
(139,396 kg), gutted weight, and
vermilion snapper are overfished, based
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on the most recent Status of U.S.
Fisheries Report to Congress, the AA
will file a notification with the Office of
the Federal Register to close the
recreational fishery for vermilion
snapper for the remainder of the fishing
year. On and after the effective date of
such notification, the bag and
possession limit of vermilion snapper in
or from the South Atlantic EEZ is zero.
This bag and possession limit also
applies in the South Atlantic on board
a vessel for which a valid Federal
charter vessel/headboat permit for
South Atlantic snapper-grouper has
been issued, without regard to where
such species were harvested, i.e., in
State or Federal waters.
(B) Without regard to overfished
status, if vermilion snapper recreational
landings exceed the ACL, the AA will
file a notification with the Office of the
Federal Register, at or near the
beginning of the following fishing year,
to reduce the ACL for that fishing year
by the amount of the overage.
(C) Recreational landings will be
evaluated relative to the ACL as follows.
For 2010, only 2010 recreational
landings will be compared to the ACL;
in 2011, the average of 2010 and 2011
recreational landings will be compared
to the ACL; and in 2012 and subsequent
fishing years, the most recent 3-year
running average recreational landings
will be compared to the ACL.
[FR Doc. 2010–32831 Filed 12–29–10; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 0908191244–91427–02]
RIN 0648–XA073
Fisheries of the Northeastern United
States; Summer Flounder Fishery;
Quota Transfer
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Temporary rule; quota transfer.
AGENCY:
NMFS announces that the
State of North Carolina is transferring a
portion of its 2010 commercial summer
flounder quota to the Commonwealth of
Virginia. In addition, the State of Maine
is transferring a portion of its 2010
commercial summer flounder quota to
the State of Rhode Island. By this action,
NMFS adjusts the quotas and announces
srobinson on DSKHWCL6B1PROD with RULES
SUMMARY:
VerDate Mar<15>2010
17:29 Dec 29, 2010
Jkt 223001
the revised commercial quota for each
state involved.
DATES: Effective December 27, 2010,
through December 31, 2010.
FOR FURTHER INFORMATION CONTACT:
Sarah Heil, Fishery Management
Specialist, 978–281–9257.
SUPPLEMENTARY INFORMATION:
Regulations governing the summer
flounder fishery are found at 50 CFR
part 648. The regulations require annual
specification of a commercial quota that
is apportioned among the coastal states
from North Carolina through Maine. The
process to set the annual commercial
quota and the percent allocated to each
state are described in § 648.100.
The final rule implementing
Amendment 5 to the Summer Flounder,
Scup, and Black Sea Bass Fishery
Management Plan, which was published
on December 17, 1993 (58 FR 65936),
provided a mechanism for summer
flounder quota to be transferred from
one state to another. Two or more states,
under mutual agreement and with the
concurrence of the Administrator,
Northeast Region, NMFS (Regional
Administrator), can transfer or combine
summer flounder commercial quota
under § 648.100(d). The Regional
Administrator is required to consider
the criteria set forth in § 648.100(d)(3) in
the evaluation of requests for quota
transfers or combinations.
North Carolina has agreed to transfer
11,815 lb (5,359 kg) of its 2010
commercial quota to Virginia. This
transfer was prompted by summer
flounder landings of two North Carolina
vessels that were granted safe harbor in
Virginia due to mechanical problems on
November 19, 2010, and December 6,
2010. In addition, Maine has agreed to
transfer 6,000 lb (2,722 kg) of its 2010
commercial quota to Rhode Island. The
Regional Administrator has determined
that the criteria set forth in
§ 648.100(d)(3) have been met. The
revised summer flounder quotas for
calendar year 2010 are: North Carolina,
3,358,231 lb (1,523,268 kg); Virginia,
2,922,226 lb (1,325,499 kg); Maine, 126
lb (57 kg); and Rhode Island, 2,025,915
lb (918,940 kg).
Classification
This action is taken under 50 CFR
part 648 and is exempt from review
under Executive Order 12866.
Authority: 16 U.S.C. 1801 et seq.
Dated: December 27, 2010.
Emily H. Menashes,
Acting Director, Office of Sustainable
Fisheries, National Marine Fisheries Service.
[FR Doc. 2010–32947 Filed 12–27–10; 4:15 pm]
PO 00000
Frm 00079
Fmt 4700
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 100204079–0199–02]
RIN 0648–XA084
Fisheries of the Northeastern United
States; Atlantic Bluefish Fishery;
Quota Transfer
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Temporary rule; inseason quota
transfer.
AGENCY:
NMFS announces that the
Commonwealth of Virginia is
transferring commercial bluefish quota
to the State of North Carolina from its
2010 quota. By this action, NMFS
adjusts the quotas and announces the
revised commercial quotas for Virginia
and North Carolina.
DATES: Effective December 27, 2010
through December 31, 2010.
FOR FURTHER INFORMATION CONTACT:
Sarah Heil, Fishery Management
Specialist, (978) 281–9257.
SUPPLEMENTARY INFORMATION:
Regulations governing the Atlantic
bluefish fishery are found at 50 CFR part
648. The regulations require annual
specification of a commercial quota that
is apportioned among the coastal States
from Florida through Maine. The
process to set the annual commercial
quota and the percent allocated to each
State is described in § 648.160.
Two or more States, under mutual
agreement and with the concurrence of
the Administrator, Northeast Region,
NMFS (Regional Administrator), can
transfer or combine bluefish commercial
quota under § 648.160(f). The Regional
Administrator is required to consider
the criteria set forth in § 648.160(f)(1) in
the evaluation of requests for quota
transfers or combinations.
Virginia has agreed to transfer 250,000
lb (113,398 kg) of its 2010 commercial
quota to North Carolina. The Regional
Administrator has determined that the
criteria set forth in § 648.160(f)(1) have
been met. The revised bluefish quotas
for calendar year 2010 are: Virginia,
963,280 lb (436,937 kg); and North
Carolina, 3,524,441 lb (1,528,860 kg).
SUMMARY:
Classification
This action is taken under 50 CFR
part 648 and is exempt from review
under Executive Order 12866.
Authority: 16 U.S.C. 1801 et seq.
BILLING CODE 3510–22–P
Sfmt 4700
82295
E:\FR\FM\30DER1.SGM
30DER1
Agencies
[Federal Register Volume 75, Number 250 (Thursday, December 30, 2010)]
[Rules and Regulations]
[Pages 82280-82295]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-32831]
[[Page 82280]]
=======================================================================
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 622
[Docket No. 0907271173-0629-03]
RIN 0648-AY11
Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic;
Snapper-Grouper Fishery Off the Southern Atlantic States; Amendment 17B
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS issues this final rule to implement Amendment 17B to the
Fishery Management Plan for the Snapper-Grouper Fishery of the South
Atlantic Region (FMP), as prepared and submitted by the South Atlantic
Fishery Management Council (Council). This final rule establishes
annual catch limits (ACLs) and accountability measures (AMs) for eight
snapper-grouper species in the FMP that are undergoing overfishing, and
for black grouper, which was recently assessed and determined to not be
undergoing overfishing or overfished; modifies management measures to
limit total mortality of those species to the ACL; and adds ACLs,
annual catch targets (ACTs), and AMs to the list of management measures
that may be amended via the framework process. The intent of this final
rule is to address overfishing of eight snapper-grouper species while
maintaining catch levels consistent with achieving optimum yield.
DATES: This rule is effective January 31, 2011.
ADDRESSES: Copies of the Final Regulatory Flexibility Analysis (FRFA)
and the record of decision may be obtained from Kate Michie, Southeast
Regional Office, NMFS, 263 13th Avenue, South, St. Petersburg, FL
33701.
FOR FURTHER INFORMATION CONTACT: Kate Michie, telephone: 727-824-5305.
SUPPLEMENTARY INFORMATION: The snapper-grouper fishery off the southern
Atlantic States is managed under the FMP. The FMP was prepared by the
Council and is implemented under the authority of the Magnuson-Stevens
Fishery Conservation and Management Act (Magnuson-Stevens Act) by
regulations at 50 CFR part 622.
On September 22, 2010, NMFS published a notice of availability of
Amendment 17B and requested public comment (75 FR 57734). On October
10, 2010, NMFS published a proposed rule for Amendment 17B and
requested public comment (75 FR 62488). NMFS approved Amendment 17B on
December 21, 2010. This final rule for Amendment 17B implements ACLs
and AMs for eight snapper-grouper species undergoing overfishing. The
rationale for the measures contained in Amendment 17B is provided in
the amendment and in the preamble to the proposed rule and is not
repeated here.
Comments and Responses
A total of 175 comments were received on Amendment 17B and the
proposed rule, including comments from individuals, State and Federal
agencies, environmental organizations, and fishing associations. NMFS
received 25 comments of general support and 48 individual comments in
general opposition of Amendment 17B, 31 of which specifically oppose
the deepwater closure for six deepwater snapper-grouper species.
Included in the letters of opposition was a minority report submitted
by the five members of the Council who voted against the final approval
of Amendment 17B. NMFS also received 85 identical postcards opposing
implementation of Amendment 17B, and 8 comments that did not support or
oppose Amendment 17B but contained remarks on specific actions
contained in the amendment. Additionally, 5 comments were received from
environmental organizations, one of which was endorsed by two of the
organizations, and one which was endorsed by 30,794 individuals. One
State and one Federal agency submitted comments on Amendment 17B, and 2
comments were unrelated to actions contained in Amendment 17B. Of the
175 comments received, 22 contained remarks on the potential economic
impacts of Amendment 17B. Specific comments related to the actions
contained in the amendment and the rule as well as NMFS'S respective
responses, are summarized below.
Comment 1: Several commenters suggested the prohibition on harvest
and possession of six deepwater snapper-grouper species beyond 240 feet
(73 m) is not necessary, and reductions in incidental harvest of
speckled hind and warsaw grouper could be achieved through: (1) A
temporary prohibition on commercial harvest and sale of speckled hind
and warsaw grouper; (2) responsible fishing methods such as venting
fish; (3) a temporary deepwater closure; or (4) seasonal closures.
Response: Commercial sale of speckled hind and warsaw grouper is
currently prohibited. NMFS previously considered a Council-approved
measure to use venting tools for snapper-grouper species to reduce
bycatch mortality caused by barotrauma (injuries sustained in response
to the sudden pressure change when brought to the surface from depth),
in Amendment 16 to the FMP. The measure requiring the use of venting
tools was disapproved based on data indicating the benefits of venting
are not clear for all species, and venting could potentially cause harm
in some cases if excluded unnecessarily or improperly. NMFS determined
that additional guidance is needed to identify species that would
benefit from venting to ensure the maximum benefit is provided to these
species. If future research on the use of venting tools, and/or any
other barotrauma mitigation methods, indicate speckled hind or warsaw
grouper would benefit from the required use of such tools or
techniques, the Council has the option to consider the issue again in a
future amendment.
Implementing the deepwater snapper-grouper closure for any period
of time less than year-round could result in incidental harvest and
bycatch mortality of speckled hind and warsaw grouper, and could
negatively impact efforts to protect South Atlantic speckled hind and
warsaw grouper. At its December 2010 meeting, the Council requested a
regulatory amendment be prepared to examine new information related to
the prohibition on harvest and possession of the six deepwater snapper-
grouper species beyond 240 ft (73 m). The regulatory amendment would
re-evaluate the deepwater snapper-grouper closure and the new
information, and determine if there are more effective measures to
reduce bycatch mortality of speckled hind and warsaw grouper.
Additionally, a new benchmark stock assessment for speckled hind and
warsaw grouper is scheduled to be conducted in 2013. If the results of
this new stock assessment indicate some modification to the management
measures implemented through Amendment 17B is needed, the Council would
make such adjustments as appropriate.
Comment 2: Several commenters stated the prohibition on all bottom
fishing beyond 240 ft (73 m) is draconian in nature, and too expansive
to protect only two rarely captured snapper-grouper species.
Response: The deepwater snapper-grouper closure proposed in
Amendment 17B would not prohibit all bottom fishing beyond 240 ft (73
m). The closure would prohibit the harvest
[[Page 82281]]
and possession of six snapper-grouper species that co-occur with
specked hind and warsaw grouper including, snowy grouper, blueline
tilefish, yellowedge grouper, misty grouper, queen snapper, and silk
snapper.
Both speckled hind and warsaw grouper are undergoing overfishing,
and the extent to which they are overfished is unknown. These species
are extremely vulnerable to overfishing because they are slow growing,
long-lived, and change sex from female to male with increasing size and
age. These species are not often targeted due to the current bag limits
(one of each per vessel per trip), but when they are caught they are
likely to suffer release mortality. The incidental catch of speckled
hind and warsaw grouper, particularly in deep water where release
mortality is high, may be responsible for the continued overfishing of
these species. Therefore, the Council determined that a prohibition on
the harvest and possession of speckled hind and warsaw grouper, along
with their co-occurring species caught in 240 ft (73 m) and greater,
was an appropriate action to reduce bycatch mortality of speckled hind
and warsaw grouper in depths where depth-related release mortality is
very high. Like gag, speckled hind and warsaw grouper are slow growing,
long lived, and have similar life histories. Therefore, speckled hind
and warsaw grouper may be expected to have similar depth-related
bycatch mortality rates to gag. If depth-related mortality of speckled
hind and warsaw grouper is similar to gag, release mortality at depths
of 240 ft (73 m) would be expected to be greater than 70 percent. The
deepwater closure is expected to provide protection to the largest,
most fecund fish and help ensure a natural sex ratio into the future.
According to the Amendment 17B biological impacts analysis, prohibiting
all harvest of deepwater snapper-grouper species beyond 240 ft (73 m)
would also protect spawning aggregations.
Comment 3: One commenter stated that NMFS should concentrate
efforts on managing other overexploited species such as mutton snapper
and yellowtail snapper.
Response: Mutton snapper and yellowtail snapper are among the 73
species in this FMP. Recent assessments indicate that mutton snapper
and yellowtail snapper are not overfished and are not experiencing
overfishing. The Reauthorized Magnuson-Stevens Act requires that ACLs
and AMs be specified for all species undergoing overfishing in 2010 and
species not undergoing overfishing in 2011. Speckled hind and warsaw
grouper are both undergoing overfishing according to the 2009 Report to
Congress on the Status of U.S. Fisheries (and in all previous such
Reports to Congress). Therefore, NMFS is required to establish ACLs at
levels to end and prevent overfishing of speckled hind and warsaw
grouper, along with management measures to limit harvest levels to the
ACL. In the case of speckled hind and warsaw grouper, the ACL is zero,
and the deep water closure is intended to reduce depth-related bycatch
mortality to reduce the probability that overfishing will occur. The
Council is currently developing a Comprehensive ACL Amendment, which
would specify ACLs and AMs for mutton snapper and yellowtail snapper.
Comment 4: One commenter stated the cumulative impact of the recent
regulations approved through Amendment 17A to the FMP and the
regulations contained in this final rule are overly complex for
commercial and for-hire fishermen to abide by.
Response: The Magnuson-Stevens Act, as reauthorized in 2006,
mandates the Council and NMFS establish ACLs and AMs for species
undergoing overfishing by 2010. Section 303(a)(15) of the Magnuson-
Stevens Act states, in relevant part, that any FMP which is prepared by
any Council ``shall establish a mechanism for specifying annual catch
limits in the plan * * * implementing regulations, or annual
specifications, at a level such that overfishing does not occur in the
fishery, including measures to ensure accountability.'' Therefore, in
order to meet these mandates, several recent regulatory changes have
been made in the snapper-grouper fishery. NMFS strives to minimize
complexity in its regulations, but must meet statutory mandates such as
the requirements for ACLs and AMs.
Comment 5: Several commenters stated the data upon which the
prohibition on the harvest and possession of the six deepwater snapper-
grouper species beyond 240 ft (73 m) is based is out of date,
insufficient, and/or incorrect, and is not the best available science.
One commenter inquired if the data used to inform the deepwater closure
action was subject to an independent review. Additionally, two
commenters cite the recently published Federal Register notice that
denies a petition to list warsaw grouper as threatened or endangered
under the Endangered Species Act (ESA) as based on a lack of
substantial scientific or commercial information, and implied that the
speckled hind and warsaw grouper management measures in Amendment 17B
are not based on adequate scientific information.
Response: The intent of the action to prohibit the harvest of six
deepwater species is to reduce bycatch mortality of speckled hind and
warsaw grouper. Speckled hind and warsaw grouper are undergoing
overfishing, and therefore, action must be taken to ensure overfishing
is ended and does not occur. The Southeast Fisheries Science Center
(SEFSC) certified, in a memorandum dated May 19, 2010, that Amendment
17B is based upon the best available scientific information. At its
December 2010 meeting, the Council requested that a regulatory
amendment be prepared to examine new information related to the
prohibition on the harvest and possession of the six deepwater snapper-
grouper species. The regulatory amendment would evaluate the new
information and the deepwater snapper-grouper closure and determine if
there are more effective measures to reduce bycatch mortality of
speckled hind and warsaw grouper.
The petition to list speckled hind and warsaw grouper as endangered
or threatened was denied by NMFS under the ESA because ``the petition
does not present substantial scientific or commercial information
indicating the petition action may be warranted'' (75 FR 59690,
September 28, 2010). This means that warsaw grouper was not determined
to be endangered (i.e., is in danger of extinction throughout all or a
significant portion of its range) or threatened (i.e., is likely to
become endangered within the foreseeable future throughout all or a
significant portion of its range). The negative finding on the ESA
petition does not necessarily mean that inadequate scientific
information was used in Amendment 17B. Under the Magnuson-Stevens Act,
NMFS must use the best scientific information available when
establishing management measures, including ACLs and AMs.
Comment 6: Several commenters are concerned that the prohibition on
harvest and possession of six deepwater snapper-grouper species beyond
a depth of 240 ft (73 m) will lead to increased incidences of release
mortality.
Response: Prohibiting the harvest and possession of species that
are most often caught with speckled hind and warsaw grouper in deeper
waters would reduce the incentive to target those co-occurring species.
As a result, a reduction in depth-related bycatch mortality of speckled
hind and warsaw grouper is expected.
Comment 7: Several commenters feel the deepwater closure in
Amendment
[[Page 82282]]
17B should only apply to the commercial sector.
Response: In the northern portion of the Council's area of
jurisdiction, fisheries and fishery components in depths greater than
240 ft (73 m) are primarily prosecuted by the commercial sector.
However, the Council chose to include the recreational sector in the
prohibition on harvest and possession of snowy grouper, blueline
tilefish, yellowedge grouper, misty grouper, queen snapper, and silk
snapper beyond 240 ft (73 m) because recreational fishing in deeper
waters is common in the southern area of the Council's jurisdiction
i.e., southeast Florida and the Florida Keys, the 240-ft (73-m) depth
contour is close to shore. Because deep water is much more accessible
to recreational fishermen off southern Florida, recreational fishermen
are more likely to incidentally capture speckled hind and warsaw
grouper in depths where these fish are more likely to die as a result
of barotrauma-related injuries.
Comment 8: One commenter stated the lack of warsaw grouper landings
data was due to fishermen misidentifying warsaw grouper as snowy
grouper.
Response: It is unlikely warsaw grouper landings are significantly
underreported due to misidentification with snowy grouper. Snowy
grouper and warsaw grouper do share some common physical
characteristics, however, these species also have several
distinguishing characteristics that make it possible to easily identify
both species. When fishermen submit species landings information to
NMFS, identification accuracy is not expected to be 100 percent, and
this is taken into consideration when conducting stock assessments.
Comment 9: One commenter asked how NMFS will determine when the
speckled hind and warsaw grouper stocks are rebuilt, if fishing for
them is prohibited.
Response: The overfished status of speckled hind and warsaw grouper
is unknown. Therefore, a rebuilding plan is not required. The deepwater
closure is intended to reduce depth-related bycatch mortality to help
end overfishing of speckled hind and warsaw grouper. Prohibiting
harvest of one or more species in a certain area does not prevent the
collection of scientific information on those species. The SEFSC
conducts fishery-independent studies and surveys to measure the overall
abundance of fish stocks in the South Atlantic. In Amendment 17A to the
FMP, the Council required implementation of a fishery-independent
monitoring program. This program would continue the long-term data set
that already exists for snapper-grouper species from sampling programs
such as the Southeast Monitoring Assessment and Prediction program, and
the Marine Resources Monitoring Assessment and Prediction program in
the South Atlantic, which monitor fish stocks in depths shallower and
deeper than 240 ft (73 m), and these programs should continue to
provide information on warsaw grouper and speckled hind.
Fishery-dependent data may also be collected during a period when
certain species may not be landed. These data may be collected through
the Cooperative Research Program (CRP), which is a competitive Federal
assistance program that funds projects seeking to increase and improve
the working relationship between researchers from NMFS, State fishery
agencies, universities, and fishermen. The intent of the CRP in the
Southeast Region is to utilize the collective experience of fishermen
and scientists to advise fishery managers of best fishery management
practices based on fishing experience and sound scientific research
procedures. Other fishery-dependent data collection sources include the
Marine Recreational Fisheries Statistical Survey (MRFSS) (now part of
the Marine Recreational Information Program (MRIP)), commercial
logbooks, headboat logbooks, observer data, the Trip Interview Program,
and dealer reported landings.
Comment 10: After the Council voted to approve Amendment 17B for
Secretarial review, the five members of the Council who voted against
the final approval of Amendment 17B submitted a minority report to
NMFS, dated March 23, 2010. This report is endorsed by one fishing
organization and one State agency. The minority report outlines the
dissenting Council members' opposition to the deepwater closure for the
six co-occurring snapper-grouper species. Specifically, these Council
members oppose the inclusion of blueline tilefish in the list of
snapper-grouper species prohibited beyond 240 ft (73 m). The report
states the deepwater closure was based on inadequate assessments, does
not include rebuilding plans for speckled hind and warsaw grouper, and
does not consider and properly analyze the impacts of the prohibition
on the sale of bag limit-caught snapper-grouper. The report also notes
a lack of data on the range where speckled hind and warsaw grouper are
found, particularly off the coast of North Carolina. The report
mentions that the species most commonly caught with speckled hind are
vermilion snapper, red grouper, and scamp, which are not deepwater
species. The minority report suggests that other alternatives besides
the deep water closure should have been considered by the Council,
including allowing fishing for species other than speckled hind and
warsaw grouper on various well-known ship wrecks or other potential
sites and closing only a percentage of the most productive bottom
habitat. The minority report also lists fish stocks that have been
successfully rebuilt or are currently rebuilding without the
utilization of large area closures for fishery management, namely
Atlantic king and Spanish mackerel, greater amberjack, and golden
tilefish.
Response: Speckled hind and warsaw grouper have not undergone a
recent stock assessment. However, the 2009 Report to Congress on the
Status of U.S. Fisheries states that both speckled hind and warsaw
grouper are undergoing overfishing and their overfished status is
unknown. The stock status determination for these two species included
in the Report to Congress is the best scientific information available
for speckled hind and warsaw grouper. Therefore, NMFS is required to
establish ACLs for these species at levels that can end, as well as
prevent, overfishing and implement management measures to limit harvest
levels of these species to the ACL. Since the overfished status of
speckled hind and warsaw grouper is currently unknown, rebuilding plans
are not required at this time. To address overfishing of speckled hind
and warsaw grouper, the Council's Scientific and Statistical Committee
(SSC) recommended an Acceptable Biological Catch (ABC) of zero for both
species based on landed catch, rather than total removals. Subsequent
to the SSC ABC recommendation, the Council specified an ACL of zero for
speckled hind and warsaw grouper.
Speckled hind and warsaw grouper are extremely vulnerable to
overfishing because they are slow growing, long-lived, change sex from
female to male with increasing size and age, and occur in deep water
where release mortality is very high. The prohibition on the harvest
and possession of six deepwater snapper-grouper species, including
blueline tilefish, that co-occur with speckled hind and warsaw grouper
is expected to reduce the incidental take of speckled hind and warsaw
grouper in water depths where survival of released fish is low. Of the
six species for which harvest and possession would be prohibited beyond
240 ft (73 m), commercial and recreational landings
[[Page 82283]]
are highest for blueline tilefish and snowy grouper, which are often
caught together in the same location and during the same trip. Speckled
hind and warsaw grouper can be incidentally caught while blueline
tilefish and other deepwater species are being targeted. This
incidental catch, if allowed to continue, may contribute to the
continued overfishing of speckled hind and warsaw grouper. Furthermore,
recent snowy grouper regulations resulted in effort shifts from snowy
grouper to blueline tilefish, which could increase the probability of
snowy grouper bycatch after the 100-lb (45-kg) trip limit or quota for
snowy grouper is met, in addition to a potential for increased bycatch
of speckled hind and warsaw grouper. If blueline tilefish were
eliminated from the list of prohibited deepwater species, incidental
take of speckled hind and warsaw grouper could persist in that portion
of the snapper-grouper fishery; therefore, the Council determined it
would be prudent to retain blueline tilefish in the list of prohibited
species beyond a depth of 240 ft (73 m).
The minority report includes an examination of trip ticket
information from vessels fishing for blueline tilefish north of Cape
Hatteras, North Carolina, which suggests blueline tilefish can be
captured without resultant incidental catch of speckled hind and warsaw
grouper. At its December 2010 meeting, the Council considered this new
information, and voted to request the preparation of a regulatory
amendment to examine the new information and to determine if there are
more effective management measures that could be implemented to reduce
the depth-related bycatch mortality of speckled hind and warsaw
grouper.
The Magnuson-Stevens Act requires the establishment of ACLs and
AMs. In the comments and responses section of the final rule
implementing the National Standard 1 Guidelines, NMFS states, ``ACLs
must be implemented using the best data and information available * * *
NMFS believes that Councils must implement the best ACLs possible with
the existing data'' (74 FR 3178, January 16, 2009). As required by the
Magnuson-Stevens Act, the Council has developed ACLs and AMs for
speckled hind and warsaw grouper using the best scientific information
available during the amendment development process.
The minority report points out that the species most commonly
caught with speckled hind are vermilion snapper, red grouper, and
scamp, none of which are deepwater species. Juvenile speckled hind and
warsaw grouper are found in depths less than 240 ft (73 m) and are
often caught with species such as vermilion snapper, red grouper,
scamp, and others. However, the Council chose not to prohibit catch in
shallower water because it is likely that some portion of released
speckled hind and warsaw grouper would survive the trauma of capture.
Like gag, speckled hind and warsaw grouper are slow growing, long
lived, and have similar life histories. Therefore, they may be expected
to have similar bycatch mortality rates to gag. If release mortality
rates of speckled hind and warsaw grouper are similar to those
published for gag, release mortality at depths greater than 240 ft (73
m) would be expected to be greater than 70 percent. Based on this
assumption, the Council determined the most effective method of
reducing the incidence of bycatch related mortality in deepwater was to
prohibit the harvest and possession of the species that co-occur with
speckled hind and warsaw grouper beyond 240 ft (73 m).
During the development process for Amendment 17B, alternatives such
as allowing fishing for species other than speckled hind and warsaw
grouper on various well-known ship wrecks or other potential sites, and
closing only a percentage of the most productive bottom habitat, were
not proposed by Council members and thus were not included in the
document for analysis. The approval and implementation of the
prohibition on harvest and possession of six deepwater snapper-grouper
species beyond 240 ft (73 m) does not preclude the Council from
proposing future action to modify this prohibition if scientific
information indicates it is appropriate to do so. Re-addressing the
deepwater closure will be accomplished through a regulatory amendment
proposed by the Council at its December 2010 meeting.
The minority report states the impact of the prohibition on bag-
limit sales of snapper-grouper implemented through Amendment 15B to the
FMP was not properly analyzed in Amendment 17B because the impact of
sales from only snapper-grouper fishermen with Federal permits was not
determined. The impacts of the bag limit sale prohibition were analyzed
and documented by NMFS in the supporting documentation for Amendment
15B, including the National Environmental Policy Act document, the
Regulatory Impact Review, and the Regulatory Flexibility Analysis. The
analysis conducted for Amendment 15B to the FMP used State trip ticket
data because at the time the analysis was conducted, fishermen that did
not possess a Federal permit for snapper-grouper could still sell their
bag limit caught fish. The analysis conducted for Amendment 17B,
however, did not use trip ticket data and used only Federal logbook
data, because at that time the prohibition on bag limit sales had been
implemented. As such, the relevant economic analysis does not include
bag limit sales information and was conducted correctly.
Different actions are needed to end overfishing of species
depending on their life history and habitat requirements. Snapper-
grouper species such as speckled hind and warsaw grouper are long-lived
and slow growing and require more stringent management measures, such
as area closures, to end overfishing. King mackerel and Spanish
mackerel are not as long lived nor do they suffer the high release
mortality rates of speckled hind and warsaw grouper. Therefore,
management measures that would be needed to end overfishing of mackerel
species may not be as onerous as those that would be needed for long-
lived species found in deep water.
Golden tilefish has never been determined to be overfished and it
will not be known if actions taken to end overfishing of golden
tilefish were successful until the stock is assessed again in 2011.
Greater amberjack have never been determined to be overfished or
experienced overfishing.
Comment 11: One commenter questioned why co-occurring species
deeper than 240 ft (73 m) would be prohibited to protect speckled hind
and warsaw grouper when these species are not frequently caught in
these depths. The species most commonly caught along with speckled hind
are vermilion snapper, red grouper, and scamp, none of which are
considered by the Council to be deepwater species. Since speckled hind
predominately live inshore of 40 fathoms and warsaw grouper are common
inside of 100 ft (31 m), at least off the Florida coast, NMFS should
consider closing the entire EEZ.
Response: The Council is aware that speckled hind and warsaw
grouper are currently not commonly caught by fishermen and that the
inshore shelf edge in 160 ft (49 m) is the area where juveniles are
most abundant. However, adults of these species do occur in deep water
where release mortality is extremely high and are incidentally captured
when fishermen target co-occurring species. Therefore, the Council
determined that prohibiting the harvest of species that co-occur with
warsaw grouper and speckled hind in water deeper than 240 ft (73 m)
could help reduce bycatch mortality, particularly as population biomass
increases and more adults occur in
[[Page 82284]]
deeper water. Speckled hind and warsaw grouper occur in shallower water
as juveniles with vermilion snapper and others. This is their zone of
greatest abundance where some level of survival of released fish would
be expected to occur. Therefore, the Council did not feel it was
necessary to close the harvest of co-occurring species in depths less
than 240 ft (73 m). As noted previously, speckled hind and warsaw
grouper share similar biological characteristics to gag. Therefore, if
depth related bycatch is similar to gag, in depths greater than 240 ft
(73 m), release mortality would be expected to be greater than 70
percent. By prohibiting the harvest and possession of co-occurring
species, in addition to prohibiting all harvest and possession of
speckled hind and warsaw grouper, fishing mortality of speckled hind
and warsaw grouper is expected to decrease and protection would be
provided to adult fish with the greatest spawning potential.
Comment 12: One commenter feels the deepwater closure will result
in an effort shift to the black sea bass, gray triggerfish, and
vermilion snapper components of the snapper-grouper fishery, and lead
to more out-of-state fishing by southern vessels in waters off North
Carolina.
Response: Effort shifts resulting from the deepwater closure are
difficult to predict. Negative biological impacts of effort shifts may
be mitigated by ACLs and AMs in Amendment 17B and the Comprehensive ACL
Amendment, which are designed to prevent the ACL from being exceeded or
correct for ACL overages should they occur. However, negative social
and economic effects could result from ACLs being met more quickly due
to effort shifts.
The commercial sector for vermilion snapper is currently managed
under a quota split into two seasons, and this amendment will specify
the same split season for commercial ACLs, as well as specify a
recreational ACL. Additionally, trip limits for vermilion snapper are
being considered by the Council in Regulatory Amendment 9 to the FMP.
Therefore, effort shift into the vermilion snapper portion of the
fishery is unlikely to have negative biological impacts on vermilion
snapper because the commercial harvest and sale of vermilion snapper
would be prohibited when the ACLs are projected to be met.
The Council is developing Amendment 18A to the FMP, which includes
actions to: Limit the number of black sea bass pots allowed per vessel;
limit the number of participants in the black sea bass component of the
snapper-grouper fishery; and require that pots be returned to port at
the completion of a fishing trip. If approved, these controls should
limit effort shift into the black sea bass component of the snapper-
grouper fishery, minimizing the occurrence of black sea bass pot
``ghost fishing'' on snapper-grouper species, as well as interactions
with protected species.
Gray triggerfish are included within the 20 snapper-grouper
aggregate bag limit for the recreational sector, and there is a 12-inch
(30.5-cm) total length size limit in Federal waters off the east coast
of Florida for the commercial and recreational sectors. The
Comprehensive ACL Amendment, currently under development, would
establish an ACL for gray triggerfish. This ACL would be associated
with an AM intended to maintain harvest at or below the specified ACL.
Therefore, if the Comprehensive ACL Amendment is implemented, a
mechanism for controlling harvest of gray triggerfish would be
established and could mitigate effort shifts that may result from
actions contained in Amendment 17B. The deepwater closure could result
in some amount of permanent and/or temporary effort shifting, however,
the number of vessels that may or may not shift effort to other
fisheries in response to the deepwater area closure cannot be
predicted.
Comment 13: One commenter states the Council discussion concerning
warsaw grouper and speckled hind was inadequate considering the scope
of the deepwater closure being implemented through Amendment 17B.
Response: The Council discussed management measures for speckled
hind and warsaw grouper beginning in June 2008. Since that time, the
Council has met seven times and discussed actions in Amendment 17B
before taking final action to approve the amendment. At its December
2010 meeting, the Council requested a regulatory amendment be prepared
to examine new information related to the prohibition on harvest and
possession of the six deepwater snapper-grouper species and evaluate
the new information to determine if the deepwater closure in certain
areas of the South Atlantic is still necessary.
Comment 14: One commenter states that the Amendment 17B cumulative
impacts assessment of the role of the marine protected areas (MPAs)
implemented through Amendment 14 to the FMP is inaccurate, and the
ancillary impacts of the Oculina Experimental Closed Area for speckled
hind and warsaw grouper were not mentioned in Amendment 17B.
Response: The effective date of the eight MPAs implemented through
Amendment 14 to the FMP was February 13, 2009. Because these MPAs have
been in place for a short period of time, little is known about their
potential to positively impact snapper-grouper species beyond the basic
protections afforded to habitats in these MPAs, and subsequent benefits
realized by local fish populations. It is expected that the MPAs may
help, to some extent, to protect a portion of the population (including
spawning aggregations) and habitat of long-lived, slow growing,
deepwater snapper-grouper species (speckled hind, snowy grouper, warsaw
grouper, yellowedge grouper, misty grouper, golden tilefish, and
blueline tilefish) from directed fishing pressure to achieve a more
natural sex ratio, age, and size structure within the MPAs. Because the
snapper-grouper species most affected by the MPAs and the Oculina
closed area are long-lived, quantifiable biological benefits may not be
measureable in the short-term. However, future studies are expected to
analyze the affects of the MPAs and the Oculina closure on snapper-
grouper species. Over time, continued research will provide further
insight on the ecological benefits of conservation areas.
Comment 15: One commenter states that snowy grouper is the main
driver for deepwater snapper-grouper fishing and past regulations to
reduce snowy grouper harvest have not been considered in Amendment 17B
as they relate to effort-reduction in the deepwater portion of the
snapper-grouper fishery.
Response: Effort reductions resulting from previously implemented
snowy grouper regulations were taken into account when analyzing the
biological and socioeconomic impacts of the deepwater closure. As
required under NEPA, Amendment 17B analyzes the impacts of the status
quo alternative for each action, including the action to prohibit the
harvest and possession of six deepwater species beyond 240 ft (73 m).
The baseline condition used in the status quo (no action) analysis for
the action to prohibit the harvest and possession of six deepwater
species beyond 240 ft (73 m) included the snowy grouper harvest
restrictions implemented through Amendment 13C to the FMP. These
restrictions included a recreational bag limit for snowy grouper of one
per person per day, a commercial trip limit of 100 lb (45 kg) gutted
weight, and a reduced commercial quota of 84,000 lb (38,102 kg) gutted
weight. Amendment 15A to the FMP specified an ABC for snowy
[[Page 82285]]
grouper that is consistent with the rebuilding plan for the species.
Comment 16: One commenter is opposed to reducing the recreational
ACL for snowy grouper to 523 fish, and favors allowing existing
regulations to rebuild the stock.
Response: The Magnuson-Stevens Act requires that ACLs and AMs be
specified in 2010 for species undergoing overfishing. The Council chose
to base the ACL for snowy grouper on the current total allowable catch
(TAC). The Council also chose to specify sector ACLs for snowy grouper
rather than one ACL for the commercial and recreational sectors. The
Council determined the recreational sector ACL to be 523 fish, based on
landings data from 2005-2008. Because this ACL is quite small, and
recreational landings data is associated with a high degree of
uncertainty, the AM will compare a 3-year running average of
recreational landings to the recreational ACL. The AMs established for
snowy grouper are intended to maintain harvest levels at or below the
specified ACLs.
Comment 17: One commenter recommended additional inshore seasonal
closures in the Florida Keys area to help rebuild overfished stocks.
Response: The Florida Keys area has an extensive network of marine
sanctuaries, where fishing is limited or prohibited, and there is the
offshore East Hump MPA, which was established in Amendment 14 to the
FMP. The Council has not requested consideration of inshore area
closures in the Florida Keys to address overfishing of the species
addressed in Amendment 17B.
Comment 18: Several commenters state that aggregating the gag,
black grouper, and red grouper ACLs, and the associated AMs is not an
appropriate method for managing these stocks. One commenter emphasizes
the fact that black grouper is no longer considered to be undergoing
overfishing or overfished, further justifying not including it in the
aggregate ACL. One commenter recommended developing a catch share
program for these species in order to ensure all commercial sector
participants are given the opportunity to harvest them.
Response: Amendment 16 established a commercial AM for red grouper
and black grouper through a prohibition on the harvest of all shallow-
water snapper-grouper species that would be effective when the
commercial ACL for gag (a biologically similar species) is projected to
be met each year. Because black grouper and red grouper had not been
recently assessed at the time Amendment 17B was developed, and the
Council was aware that a new stock assessment for both species was
forthcoming, the Council chose to establish an aggregate ACL that
includes gag, red grouper, and black grouper, based on expected catch
resulting from management measures implemented through Amendment 16 to
the FMP.
The red grouper and black grouper Southeast Data, Assessment, and
Review (SEDAR) stock assessment (SEDAR 19) was completed in 2010, after
Amendment 17B had been submitted to NMFS for Secretarial review. The
assessment indicated black grouper is not overfished and is not
undergoing overfishing, and red grouper is overfished and undergoing
overfishing. Therefore, a new FMP amendment is currently under
development to establish a rebuilding plan and assign an individual ACL
and AM for red grouper. The black grouper stock assessment was not
completed until after Amendment 17B was submitted to the Secretary for
review. Black grouper ACLs and AMs have been retained in Amendment 17B,
however, the Council will immediately consider whether adjustments to
ACLs and AMs are needed in light of the new assessment. The
Comprehensive ACL Amendment, which is also under development by the
Council, would consider a new ACL and AM for black grouper, as well as
species groups for many different snapper-grouper species that could
include gag, red grouper, and black grouper.
Comment 19: Several commenters state they have witnessed the
progressive decline in deepwater snapper-grouper species over many
years, and support measures to end overfishing and rebuild deepwater
snapper-grouper stocks.
Response: NMFS agrees that effective management strategies must be
utilized to rebuild stocks that are overfished to sustainable levels
and prevent future overfishing from occurring. Actions have been taken
through previous amendments to address overfishing of black sea bass,
vermilion snapper, gag, red grouper, black grouper, snowy grouper,
speckled hind, warsaw grouper, red snapper, and golden tilefish. It is
the intent of the Council and NMFS to employ a system of ACLs and AMs
to achieve these goals.
Comment 20: One commenter feels the restrictions on vermilion
snapper are too restrictive and have fostered a derby fishery, and
suggests a trip limit be implemented for vermilion snapper. Another
commenter recommended the implementation of a system of trip limits,
also known as the ``Fisherman's Plan,'' as a means of maintaining
harvest levels of vermilion snapper below the specified ACLs.
Response: Regulatory Amendment 9 to the FMP includes an action to
specify trip limits for vermilion snapper. It is the Council's intent
to alleviate the derby nature of the vermilion snapper component of the
snapper-grouper fishery by implementing a trip limit as soon as
possible. Additionally, Amendment 21 to the FMP, which is in the early
stages of the development process, includes an action to establish a
catch share program for vermilion snapper. Establishing a catch share
program would eliminate the derby-style fishery, and would promote
safety at sea.
Comment 21: One commenter feels Amendment 17B would not reduce
harvest enough to end overfishing of the subject stocks, and recommends
reducing all the ACLs contained in Amendment 17B by 66 percent.
Response: The best scientific information available supports the
recently implemented harvest reductions in previous amendments and the
ACLs contained in Amendment 17B. Actions have been taken in previous
amendments to address overfishing of most species addressed in
Amendment 17B. A reduction of the current ACLs by 66 percent is not
supported by the best available scientific information, and could
result in unnecessary adverse socioeconomic impacts on the fishing
community. Therefore additional harvest restrictions beyond those in
Amendment 17B are not necessary to end overfishing of the species
addressed in Amendment 17B as required by the Magnuson-Stevens Act.
Amendment 17B specifies ACLs and AMs for speckled hind, warsaw grouper,
snowy grouper, black sea bass, vermilion snapper, black grouper, red
grouper, gag, and golden tilefish to end overfishing and help ensure
that overfishing does not occur in the future.
Comment 22: One commenter stated the impacts of anthropogenic
pollutants such as sunscreens, pharmaceuticals, and cruise ships could
have an effect on snapper-grouper reproductive fitness.
Response: The direct impacts of anthropogenic toxins introduced
into the marine environment have been studied in recent years, but
their impacts on snapper-grouper species are not quantifiable at this
time. Ongoing research in the field is likely to continue as human
impacts on the environment increase. Several studies show a correlation
between pharmaceutical waste and subsequent lowered reproductive
fitness in marine organisms. The extent to which chemical waste impacts
snapper-
[[Page 82286]]
grouper species in the South Atlantic is unknown, and may be more
difficult to measure in deepwater species, which do not spend the
majority of their live cycles in close proximity to known pollution
sources.
The Environmental Protection Agency (EPA) has participated in
several surveys to assess the impacts of cruise ship discharge of food
waste, gray water, bilge water, and ballast water on the marine
environment, including a survey conducted in August 2001 to estimate
the dilution of cruise ship discharges into receiving waters. Another
survey, conducted in Skagway Harbor, Alaska, in July 2008, estimated
the near-field dilution of treated sewage/gray water discharges from
docked cruise ships. The EPA also prepared a Cruise Ship Discharge
Assessment Report (Assessment Report), which examines waste streams
generated by cruise ships. The report is available at: https://water.epa.gov/polwaste/vwd/cruise_ship_disch_assess_report.cfm.
Despite these and other ongoing studies, the direct impact of cruise
ship waste discharge on snapper-grouper species in the South Atlantic
is not known at this time.
Comment 23: One commenter suggests requiring permits and logbooks
on all vessels in all sectors of the snapper-grouper fishery.
Response: Logbooks and snapper-grouper permits are required for
participants in the commercial snapper-grouper fishery. Permits are
also required for all participants in the for-hire sector of the
snapper-grouper fishery, and logbooks are required on headboats if
selected by NMFS. Amendment 15B, which became effective in December
2009, requires any vessel fishing for snapper-grouper in the South
Atlantic EEZ, if selected by NMFS, to maintain and submit fishing
records; and requires any vessel that fishes in the EEZ, if selected by
NMFS, to carry an observer and install an electronic logbook (ELB) and/
or video monitoring equipment provided by NMFS. The reporting and
record-keeping requirements contained in Amendment 15B only include
selected vessels because these requirements are cost prohibitive if
applied to every fisher in the South Atlantic at this time.
Comment 24: One commenter stated that a prohibition on all longline
fishing would end overfishing of golden tilefish.
Response: Golden tilefish are primarily harvested using bottom
longline gear. Actions were taken in Amendment 13C to end the
overfishing of golden tilefish, which included a reduction in the quota
to 295,000 lb (133,810 kg) gutted weight. Therefore, eliminating the
longline harvest for golden tilefish could have unnecessary negative
economic and social effects. The effectiveness of management measures
in ending overfishing for golden tilefish will be determined in an
assessment scheduled for 2011. Amendment 17B established ACLs and AMs
to help ensure golden tilefish overfishing does not occur.
Currently, for the snapper-grouper fishery, the use of bottom
longline fishing gear is limited by species and area. A vessel that has
on board a valid Federal commercial permit for South Atlantic snapper-
grouper, excluding wreckfish, that fishes in the EEZ on a trip with a
longline on board, may possess only snowy grouper, warsaw grouper,
yellowedge grouper, misty grouper, golden tilefish, blueline tilefish,
and sand tilefish. Additionally, under the FMP, a longline may not be
used to fish in the EEZ for South Atlantic snapper-grouper south of
27[deg]10' N. latitude (due east of the entrance to St. Lucie Inlet,
FL); or north of 27[deg]10' N. latitude where the charted depth is less
than 50 fathoms (91.4 m), as shown on the latest edition of the largest
scale NOAA chart of the location. Under the FMP, a person aboard a
vessel with a longline on board that fishes on a trip in the South
Atlantic EEZ south of 27[deg]10' N. latitude, or north of 27[deg]10' N.
latitude where the charted depth is less than 50 fathoms (91.4 m), is
limited on that trip to the bag limit for South Atlantic snapper-
grouper for which a bag limit is specified, and to zero for all other
South Atlantic snapper-grouper.
Additionally, Amendment 18A to the FMP is addressing potential
effort control mechanisms for the golden tilefish component of the
snapper-grouper fishery, including an endorsement for hook-and-line and
longline gear. Therefore, Amendment 18A may mitigate, to some extent,
any effort shift into the golden tilefish component of the snapper-
grouper fishery.
Comment 25: Three commenters felt the golden tilefish allocation of
97-percent commercial and 3-percent recreational is unfair and
allocates too much of the total ACL to the commercial sector.
Response: The sector allocations for golden tilefish were chosen
based on long-term and short-term landings histories. The preferred
allocation of 97 percent for the commercial sector and 3 percent for
the recreational sector is representative of past and current harvest
levels for both sectors and thus would cause the least disruption to
the economic and social environments. The Council considered an
alternative that would allocate half of the ACL to the commercial
sector and half to the recreational sector, but rejected this
alternative because it would result in the largest deviation from the
short and long-term landings trend for the two sectors. It was
concluded that the preferred allocation is fair and equitable based on
the best scientific information available.
Comment 26: Two commenters suggested that the Federal government
buy out those fishermen who are ready to leave the fishery because of
overly burdensome regulations. One commenter suggested the U.S.
Department of Commerce develop a fisheries disaster assistance program
for commercial and for-hire fishermen affected by recently implemented
regulations.
Response: The Council discussed the establishment of a buy-out
program for commercial snapper-grouper fishermen in Georgia during the
development process for Amendment 17A to the FMP, which was drafted
concurrently with Amendment 17B. A buy-out program for the commercial
sector would require a great deal of planning, time, funds, and
acceptance from fishery participants. Because of these limiting factors
and the need to end overfishing immediately as required by the
Magnuson-Stevens Act, a buy-out program was not pursued by the Council
or NMFS during the development of Amendment 17B.
The Magnuson-Stevens Act states the Secretary may establish a
regional economic transition program to provide immediate disaster
relief assistance upon the request and concurrence with the Governors
of the affected States. Neither the Secretary nor NMFS has received a
request from any of the four affected States' governors for disaster
relief. Therefore, a disaster relief program for the snapper-grouper
fishery has not been considered.
Comment 27: Several commenters feel the economic impact analysis
for actions contained in Amendment 17B is either absent or inadequately
represents the true impacts expected from the implementation of
Amendment 17B.
Response: Amendment 17B contains a complete economic impact
analysis of all actions and alternatives considered by the Council in
Amendment 17B. Additionally, Amendment 17B contains a social impact
analysis of all the alternatives considered by the Council.
Furthermore, in compliance with Magnuson-Stevens Act, Amendment 17B
contains a Regulatory Impact Review, an initial Regulatory Flexibility
Analysis, a Fishery Impact Statement,
[[Page 82287]]
and a Social Impact Assessment. These economic and social analyses
utilize recent landings, trip ticket, logbook, permit, and financial
data for the commercial and recreational sectors. As such, the subject
analyses have been determined to represent an accurate and complete
economic picture of potential impacts that may result from the
implementation of Amendment 17B.
Comment 28: Three commenters feel Amendment 17B contained several
deficiencies, including: the absence of overfishing limits (OFLs) for
six species, the absence of ABCs for five species, the lack of an ABC
control rule, failing to account for management uncertainty in the
ACLs, and failing to include discard mortality in the ACLs (most
notably for speckled hind and warsaw grouper). One commenter states
that Amendment 17B establishes ACLs and management measures that are
unlikely to end overfishing for golden tilefish, black sea bass, and
snowy grouper. Additionally, one commenter states that Amendment 17B
should include an ACL performance standard, and re-evaluation of the
ACLs and AMs that would be triggered if the catch exceeds the ACL more
often than once in a given period of time.
Response:
OFL: The Magnuson-Stevens Act National Standard 1 Guidelines give
the Councils flexibility to use either the maximum fishing mortality
threshold (MFMT) or the overfishing limit (OFL) to determine if
overfishing is occurring. The National Standard 1 Guidelines state,
``The OFL is an annual level of catch that corresponds directly to the
MFMT, and is the best estimate of the catch level above which
overfishing is occurring.'' Furthermore, in June 2008, the SSC stated
that for species assessed through SEDAR, OFL is equal to the yield at
MFMT. Golden tilefish, snowy grouper, black sea bass, vermilion
snapper, red grouper, and black grouper have been assessed through
SEDAR and, therefore, have estimates of MFMT. The numerical estimates
of MFMT for black grouper and red grouper will be provided in the
Comprehensive ACL Amendment and Amendment 24, respectively.
The SSC was unable to provide recommendations of the OFL for
speckled hind and warsaw grouper at its June 2008 meeting, based on
current data, and, therefore, specified OFL as ``unknown.'' The SSC
encountered similar problems when attempting to specify OFLs for
species at its April 2010 meeting. Discussion at the April 2010 meeting
focused on what the SSC was responsible for providing to the Council
under National Standard 1 Guidelines. To explain its reasoning and
judgment, the April 2010 SSC report states, ``It became clear that
recommending an ABC was the main goal, and providing this recommended
value without an estimate of OFL was acceptable in situations where
only catch series data were available.''
ABC: At its December 2008 meeting, the SSC considered the guidance
given in the proposed Magnuson-Stevens Act National Standard 1
Guidelines and rescinded all estimates of ABC from its June 2008
meeting (except for an ABC of zero for speckled hind and warsaw grouper
based on landed catch). At its December 2008 meeting, the SSC also
recommended that the ABC levels for snowy grouper, black sea bass, and
red snapper be set consistent with the rebuilding plans for those
species until they can be further amended using more updated scientific
information. The SSC reaffirmed, at its April 2010 meeting, that ``For
overfished stocks and stock complexes, a rebuilding ABC must be set to
reflect the annual catch that is consistent with the schedule of
fishing mortality rates in the rebuilding plan.'' At its June 2009
meeting, the SSC recommended ABCs for gag and vermilion snapper based
on a P* analysis, which is being used as the Council's preferred ABC
control rule for assessed species that are not experiencing overfishing
in the Comprehensive ACL Amendment.
The SSC did not provide an ABC value for golden tilefish because of
the age of the assessment and because of the lack of a current estimate
of abundance. Golden tilefish will be assessed by SEDAR in 2011. The
ABC control rule being used in the Comprehensive ACL Amendment will be
applied to golden tilefish to obtain an ABC value when the assessment
and amendment are completed in 2011. The SSC did not provide an ABC
value for black grouper and red grouper because assessments were
ongoing for those species when Amendment 17B was being developed by the
Council, and since the SEDAR assessments have now been completed, OFLs,
ABCs, and ACLs will be specified in the Comprehensive ACL Amendment and
Amendment 24 for black grouper and red grouper, respectively.
ABC Control Rule: For overfished stocks and stock complexes, the
SSC has indicated that the ABC must be set to reflect the annual catch
that is consistent with the schedule of fishing mortality rates in the
rebuilding plan. Amendment 17B did not specify ABC control rules for
assessed species that were not overfished or for data poor species
because these control rules were under development by the SSC. The SSC
met in March and June of 2009 to determine ABC control rules for data
rich species, and met in April and August of 2010 to identify the
protocol for determining the ABC for data poor species. A final version
of the SSC's recommendation of an ABC control rule for assessed species
was provided to the Council at its March 2010 meeting, after the
Council had voted to submit Amendment 17B for Secretarial review. The
SSC has not completed its recommendations for ABC control rules for
non-assessed species. ABC control rules for assessed and data poor
species will be included in the Comprehensive ACL Amendment.
The SSC recommended and the Council chose an ACL of zero for
speckled hind and warsaw grouper based on landings only. Choosing an
ACL based on total mortality rather than landed catch would require the
SEFSC to monitor discarded speckled hind and warsaw grouper in the
commercial and recreational sectors. The Council's SSC expressed
concerns about monitoring discards when discussing ACLs for speckled
hind and warsaw grouper at its March 2009 meeting. The SSC was not only
concerned about the accuracy of discard data as currently collected
from the recreational and commercial sector but also the possibility
that some members of the fishing community might under-report discarded
fish if they believed further restrictions might be imposed if levels
of dead discards became elevated. Therefore, due to concern about
monitoring discards, the SSC recommended an acceptable biological catch
equal to zero for speckled hind and warsaw grouper based on landed
catch only.
Management Measures: Action is being taken in Amendment 17B to
reduce discards of speckled hind and warsaw grouper by prohibiting the
take of co-occurring species in depths greater than 240 ft (73 m).
Rather than retain and monitor speckled hind and warsaw grouper
discards, the intent of the area closure is to reduce bycatch in an
area where release mortality is expected to be very high. The
relationship between depth and mortality has not been specified for
speckled hind and warsaw grouper. However, as previously discussed,
speckled hind and warsaw grouper share similar biological
characteristics to gag; therefore, if depth related release mortality
of speckled hind and warsaw grouper is similar to gag, release
mortality would be expected to be approximately 70 percent in depths of
240 ft (73 m).
Actions were taken to end overfishing of golden tilefish, snowy
grouper, and black sea bass in Amendment 13C to the
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FMP. It will not be known if the measures were successful in ending
overfishing until new assessments are conducted for these species. New
benchmark assessments will be conducted for golden tilefish and black
sea bass in 2011, and snowy grouper will be assessed in 2013. Amendment
17B specifies ACLs and AMs for speckled hind, warsaw grouper, snowy
grouper, gag, vermilion snapper, black sea bass, golden tilefish, black
grouper, and red grouper, to ensure overfishing of these species does
not occur.
The National Standard 1 Guidelines states that ``if catch exceeds
the ACL for a given stock or stock complex more than once in the last 4
years, the system of ACLs and AMs should be re-evaluated, and modified
if necessary, to improve its performance and effectiveness.'' Amendment
17B follows this guidance for performance measures with an action to
update the framework procedure to allow for adjustments to OFL, ABC,
and ACL based on SEDAR reports or other new information. Under the
updated framework procedure, the SSC would examine the social and
economic impact analyses for a specific allocation, ACL, ACT, AM,
quota, bag limit, or other fishing restriction. If it is determined by
the Council and its SSC that the management measures in place are not
constraining catch to a target level, adjustments could be made through
a future regulatory amendment.
Comment 29: One commenter stated Amendment 17B does not adequately
demonstrate that speckled hind and warsaw grouper are undergoing
overfishing.
Response: According to the most recent Report to Congress on the
Status of U.S. Fisheries, warsaw grouper and speckled hind are
undergoing overfishing and have been identified as experiencing
overfishing every year since the Report was initiated in 1997. Status
determinations in the Report to Congress on the Status of U.S. Stocks
are generally made during a formal review of a scientific stock
assessment using the best available scientific information and status
determination criteria specified in a fishery management plan. However,
many resources can be used to make status determinations, including
final peer-reviewed documents such as Stock Assessment Review Committee
reports and recommendations of each Council's Scientific and
Statistical Committee. The Council and NMFS are mandated to end
overfishing by the Reauthorized Magnuson-Stevens Act, and to specify
ACLs and AMs for species undergoing overfishing and to implement
management measures to ensure overfishing does not continue to occur.
New SEDAR benchmark assessments for speckled hind and warsaw grouper
are scheduled for 2012 or 2013.
Comment 30: Three commenters felt the Finding of No Significant
Impact (FONSI) for Amendment 17B erroneously concluded that there are
no significant impacts as a result of this amendment. One commenter
requests that an environmental impact statement (EIS) be prepared for
Amendment 17B.
Response: An environmental assessment (EA) was conducted for
Amendment 17B, instead of an EIS, because most of the ACLs and AMs
implemented through this final rule are based on previously implemented
quotas and allocations, and the deepwater closure was concluded to
result in a low to moderate level of socioeconomic impact to the
snapper-grouper fishery. The deepwater closure is expected to primarily
affect commercial fishermen who target blueline tilefish off North
Carolina, and commercial and recreational fishermen in areas of the
Florida Keys where the 240-ft (73-m) depth boundary is close to shore.
The significance of an action under NEPA is determined by
considering the action's context and intensity. In the case of the
deepwater area closure, the impacts are not considered significant
because select groups of snapper-grouper fishery participants are
expected to be impacted, and those impacts are anticipated to be low to
moderate relative to the entire snapper-grouper fishery. For the entire
South Atlantic, the prohibition on harvest and possession of six
deepwater snapper-grouper species beyond a depth of 240 ft (73 m) is
expected to reduce annual overall net operating revenues in the
commercial snapper-grouper fishery by about $292,000, or by 3.3
percent. For the State of North Carolina alone, the action is expected
to reduce net operating revenue in the commercial sector by
approximately 7 percent. As such, the FONSI appropriately concludes the
actions in Amendment 17B are not expected to result in significant
impacts on the human environment; and therefore, an EIS was not
prepared.
Comment 31: Several commenters stated that the amendment would have
severe economic impacts on commercial and recreational fishing
opportunities and operations, inclu