Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic; Amendments to the Queen Conch and Reef Fish Fishery Management Plans of Puerto Rico and the U.S. Virgin Islands, 82404-82412 [2011-33512]
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Federal Register / Vol. 76, No. 251 / Friday, December 30, 2011 / Rules and Regulations
National Oceanic and Atmospheric
Administration
50 CFR Part 622
[Docket No. 100120037–1626–02]
RIN 0648–AY55
Fisheries of the Caribbean, Gulf of
Mexico, and South Atlantic;
Amendments to the Queen Conch and
Reef Fish Fishery Management Plans
of Puerto Rico and the U.S. Virgin
Islands
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
NMFS issues this final rule to
implement Amendment 2 to the Fishery
Management Plan for Queen Conch
Resources of Puerto Rico and the U.S.
Virgin Islands, and Amendment 5 to the
Fishery Management Plan for the Reef
Fish Fishery of Puerto Rico and the U.S.
Virgin Islands (Amendments 2 and 5),
prepared by the Caribbean Fishery
Management Council (Council). This
final rule: Establishes annual catch
limits (ACLs) and accountability
measures (AMs) for queen conch and for
all reef fish units or sub-units that are
classified as undergoing overfishing
(i.e., snapper, grouper and parrotfish);
allocates ACLs among island
management areas; revises the
composition of the snapper and grouper
complexes; prohibits fishing for and
possession of three parrotfish species;
establishes recreational bag limits for
snappers, groupers, and parrotfishes;
and establishes framework procedures
for the queen conch and reef fish fishery
management plans. Amendments 2 and
5 also revise management reference
points and status determination criteria.
The intended effect of the rule is to
prevent overfishing of queen conch and
reef fish species while maintaining
catch levels consistent with achieving
optimum yield (OY).
DATES: This final rule is effective
January 30, 2012.
ADDRESSES: Electronic copies of
Amendments 2 and 5, which include an
Environmental Impact Statement (EIS),
a final regulatory flexibility analysis
(FRFA), a regulatory impact review
(RIR), and a fishery impact statement
may be obtained from the Southeast
Regional Office Web site at https://sero.
nmfs.noaa.gov/sf/pdfs/2010_Caribbean_
ACL_Amendment_FEIS_092011.pdf.
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SUMMARY:
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Bill
Arnold, Southeast Regional Office,
NMFS, telephone: (727) 824–5305,
email: Bill.Arnold@noaa.gov.
SUPPLEMENTARY INFORMATION: In the
exclusive economic zone (EEZ) of the
U.S. Caribbean, the queen conch fishery
is managed under the Fishery
Management Plan for Queen Conch
Resources of Puerto Rico and the U.S.
Virgin Islands (USVI) (Queen Conch
FMP), and the reef fish fishery is
managed under the Reef Fish Fishery
Management Plan of Puerto Rico and
the USVI (Reef Fish FMP). These FMPs
were prepared by the Council and are
implemented through regulations at 50
CFR part 622 under the authority of the
Magnuson-Stevens Fishery
Conservation and Management Act
(Magnuson-Stevens Act).
NMFS’ 2011 Report on the Status of
U.S. Fisheries classifies Caribbean
queen conch, Grouper Units 1 and 4,
Snapper Unit 1, and parrotfishes as
undergoing overfishing.
On September 26, 2011, NMFS
published a notice of availability for
Amendments 2 and 5 and requested
public comment (76 FR 59375). On
October 27, 2011, NMFS published a
proposed rule for Amendments 2 and 5
and requested public comment (76 FR
66675). The proposed rule and
Amendments 2 and 5 outline the
rationale for the actions contained in
this final rule. A summary of the actions
implemented by this final rule are
provided below.
This final rule amends the
composition of stock complexes within
the Reef Fish FMP. Grouper and
snapper unit complexes are being
revised to include two species of
commonly harvested fish that were
previously excluded, remove the creolefish from the Reef Fish FMP since the
Council decided the species is no longer
in need of Federal conservation and
management due to no reported
landings in the EEZ in recent years, and
aggregate species in an ecologically
consistent manner within the Reef Fish
FMP.
This final rule revises and establishes
management reference points for
snapper, grouper, parrotfish and queen
conch in the following manner: (1)
Establishes average catch as a proxy for
calculating the MSY for all units or
complexes; (2) calculates the MSY
proxy for each species or unit using
average catch from commercial landings
data from 1999–2005 for Puerto Rico
and St. Croix, and from 2000–2005 for
St. Thomas/St. John, and recreational
catch data from 2000–2005 for Puerto
Rico only; (3) sets the ABC for queen
FOR FURTHER INFORMATION CONTACT:
DEPARTMENT OF COMMERCE
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conch and parrotfish equal to the fishing
level recommendation specified by the
Council’s Scientific and Statistical
Committee (SSC) for those species; (4)
defines the overfishing threshold of all
species as the OFL, which would equal
the MSY proxy; setting the OY and the
ACL as equal values; (5) sets the OY
equal to the OFL multiplied by a
reduction factor of 0.85 to account for
uncertainty in the scientific and
management process for snapper and
grouper in all three management areas.
The OY of queen conch was not reduced
below the ABC; (6) sets the ACL for
parrotfish as a 0.85 reduction of the
SSC’s ABC recommendation to account
for uncertainty, ecological factors and
other concerns for all three island
groups; and (7) sets the OY/ACL equal
to zero for Nassau grouper, goliath
grouper, rainbow parrotfish, blue
parrotfish, and midnight parrotfish.
This final rule also establishes islandspecific management to enable
application of AMs in response to
harvesting activities on a single island
(Puerto Rico, St. Croix) or island group
(St. Thomas/St. John) without
necessarily affecting fishing activities on
the other islands or island groups. This
final rule establishes geographic
boundaries between islands/island
groups based upon an equidistant
approach that uses a mid-point to divide
the exclusive economic zone (EEZ)
among islands. The three island
management areas are: Puerto Rico, St.
Croix, and St. Thomas/St. John.
This final rule establishes ACLs and
AMs for queen conch and for all
snapper, grouper, and parrotfish units or
complexes in the Caribbean Reef Fish
FMP. The ACLs include reductions in
catch to buffer allocations to account for
scientific and catch-level uncertainty.
Each ACL is sub-divided among the
three islands/island groups, and for
Puerto Rico only, separate sector ACLs
(commercial and recreational) are
established because commercial and
recreational sector landings data are
both available. For the St. Croix and St.
Thomas/St. John island management
areas, only commercial data are
available; therefore, ACLs are
established for the St. Croix and St.
Thomas/St. John management areas
based on commercial landings data
only. The final rule specifies an ACL of
zero for Nassau grouper, goliath
grouper, rainbow parrotfish, blue
parrotfish, and midnight parrotfish.
The AMs are designed to prevent
fishermen from exceeding the ACLs.
The AMs for queen conch are described
in the 2010 regulatory amendment (May
26, 2011, 76 FR 30554) to the Queen
Conch FMP, and state that when the
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USVI closes its territorial waters off St.
Croix to the harvest and possession of
queen conch, NMFS will concurrently
close the EEZ in the area of Lang Bank
until the start of the next territorial
fishing season. For Puerto Rico and St
Thomas/St. John, the applicable ACL
will be set at zero and so the harvest
prohibition will function as the AM in
the EEZ for those areas.
This final rule triggers AMs if an ACL
has been exceeded based on a moving
multi-year average of landings as
described in the FMP. If the ACL is
exceeded, this final rule reduces the
length of the fishing season for the
affected species the year following an
overage by the amount needed to
prevent such an overage from occurring
again. The AM is triggered unless
NMFS’ Southeast Fisheries Science
Center, in consultation with the Council
and its Scientific and Statistical
Committee (SSC), determines the
overage occurred because data
collection and monitoring improved,
rather than because catches actually
increased. In such circumstances NMFS
and the Council would review the
relevant information and take further
action as appropriate.
To maintain the role of parrotfish
with respect to the health and ecological
protection of threatened Acropora coral,
this final rule prohibits the harvest of
the three largest species of parrotfish
that occur on Caribbean coral reefs. The
harvest of blue, midnight, and rainbow
parrotfish will be prohibited.
Additionally, this final rule
establishes an aggregate bag limit for the
recreational harvest of snapper, grouper
and parrotfish. The daily recreational
bag limit for snapper, grouper, and
parrotfish combined will be five fish per
person per day, with no more than two
parrotfish per person within the
aggregate. This rule also establishes a
vessel limit on snapper, grouper, and
parrotfish of 15 fish per day, including
no more than 6 parrotfish per vessel per
day.
To facilitate timely adjustments to
harvest parameters and other
management measures, this final rule
establishes framework procedures for
both the Reef Fish and Queen Conch
FMPs. Management measures to be
adjusted through framework
amendments include but are not limited
to quotas, closures, trip limits, bag
limits, size limits, gear restrictions,
fishing years, and reference points.
Comments and Responses
The following summarizes the
comments NMFS received on
Amendments 2 and 5 and the proposed
rule, and NMFS’ respective responses.
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Nine submissions were received on the
amendments and the proposed rule,
including comments from individuals,
state and Federal agencies,
environmental organizations, and
fishing associations. Several
commenters were generally supportive
of the actions included in Amendments
2 and 5. A Federal agency had no
specific comments and a nongovernmental organization was
supportive and recommended approval.
Comments that pertain to specific
actions addressed in Amendments 2 and
5 or the proposed rule are summarized
and responded to below.
Comment 1: The boundary lines
defining the EEZ subdivisions should
take into account the distribution of
marine biotopes and an additional
(unquantified) buffer be added to the
15 percent uncertainty reduction in the
setting of ACLs.
Response: Although state and Federal
efforts are underway to map and define
biological communities throughout the
U.S. Caribbean, suitable information is
not yet available to support allocation of
subdivisions by biotope. However, input
from fishers with regard to their fishing
locations were taken into consideration
when establishing the boundary lines.
Additionally, those boundary lines do
not prevent fishers from fishing in any
area of the U.S. Caribbean EEZ. Instead,
the boundary lines only become
restrictive when the ACL has been met
for a species or species group within the
EEZ subdivision for a particular island
or island group. Then, AMs will be
applied for that EEZ subdivision.
With respect to the additional buffer
for setting ACLs, the 15-percent
reduction serves as a buffer between the
overfishing level and the ACL, thus
minimizing the likelihood that
overfishing will occur. Other ‘‘buffers,’’
including more stringent ones (i.e.,
buffers that reduce allowable catch to an
even greater degree), were considered by
the Council but not implemented. The
Council determined that these more
stringent buffers were not necessary to
prevent overfishing of snapper, grouper,
and parrotfish. The Council also
determined that the 15 percent
reduction would more effectively
encourage the development of
compatible regulations by territorial and
commonwealth governments and
increase data collection efforts, which
would bring more stability to the
management regime. The Council
further reduced allowable parrotfish
harvest in St. Croix EEZ waters by
15,000 lb (6,804 kg) to address
ecological considerations as described
in Amendments 2 and 5.
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Comment 2: There is a need to reduce
emphasis on fisheries management and
to instead increase emphasis on
restocking, preservation, establishment
of defined shipping lanes, and
deployment of fish attraction devices to
better protect the environment and
improve fishing opportunities.
Response: The amendment and
associated rule are designed to address
the requirements of the MagnusonStevens Act. The Magnuson-Stevens Act
is focused on the Federal management
of fishing activities. While an ecosystem
based approach to fisheries management
is a principle of NMFS’ overall
management strategy, achieving that
goal requires the cooperation by a host
of local, state, and Federal agencies and
the constituencies upon which those
agencies depend. These efforts are
ongoing.
Comment 3: There is no rationale for
the Council’s SSC to establish a specific
parrotfish quota for St. Croix, St.
Thomas/St. John, and Puerto Rico.
Response: The SSC’s rationale for
establishing the ABC levels from which
ACLs were derived for each of the
islands or island groups, was that those
levels are roughly equal to the average
catch during the reference years chosen
by the Council (1999–2005 for Puerto
Rico and St. Croix commercial landings,
2000–2005 for Puerto Rico recreational
and St. Thomas/St. John commercial
landings). Those year sequences were
chosen by the Council based on
outcomes from working group meetings
of the Annual Catch Limit Working
Group (ACLG), Technical Monitoring
and Compliance Team (TMCT), and
Southeast Data Assessment and Review
(SEDAR), whose task was to identify
and analyze available data in the U.S.
Caribbean. The SEDAR findings, along
with those of the ACLG, were presented
to the SSC for development of OFL and
ABC limits. Using those year sequences,
the SSC established ABC values
separately for St. Croix, St. Thomas/St.
John, and Puerto Rico. The Council
chose to reduce by 15 percent from each
ABC when setting the ACL for each
island, with an additional 5.8822
percent reduction (equal to 15,000 lb
whole weight (6,804 kg)) for St. Croix,
due the intense and directed nature of
the parrotfish fishery on that island.
That 15 percent reduction acts to ensure
that the OFL is not exceeded as a result
of both scientific and management
uncertainty.
Comment 4: The prohibition on
harvest of midnight, blue, and rainbow
parrotfish would have little biological
impact because the species are
extremely rare to the point of being
effectively unavailable for harvest by the
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commercial and recreational sectors. It
is necessary to maintain the largestsized individuals among grazing species
and the lack of species-specific
parrotfish landings data would render it
impossible to enforce prohibitions on
the take of midnight, blue, and rainbow
parrotfish.
Response: The Council chose to
prohibit the harvest of these three
parrotfish species because they are so
rare on U.S. Caribbean coral reefs. Given
those very low densities, it is likely that
their recovery will be lengthy as the
populations rebuild to densities
adequate to support consistently
successful reproduction. However,
without this prohibition on harvest, it is
probable that recovery will take much
longer, so the Council and NMFS
consider the harvest prohibition to be an
essential first step in the process of
recovering these parrotfish populations.
Regarding the need to maintain the
largest individuals among grazing
species, this rule prohibits harvesting
the three largest species of parrotfish
(midnight, blue, rainbow) to accomplish
that goal. Finally, regardless of how the
parrotfish species are reported, they are
easily identified, making it relatively
straightforward to enforce the
prohibition on harvest of midnight,
blue, and rainbow parrotfish in
Caribbean EEZ waters.
Comment 5: The parrotfish harvest
reductions, particularly from the waters
surrounding St. Croix, are inadequate to
address overfishing of these species and
do not ensure adequate provision of
critical settlement substrate for
threatened Acroporid corals. Parrotfish
harvest in the U.S. Caribbean is
unsustainable and the proposed
parrotfish harvest reductions are very
unlikely to significantly decrease fishing
pressure on parrotfish. Since the
collapse of long-spined sea urchin
populations, parrotfish are the only
major grazer remaining on U.S.
Caribbean coral reefs.
Response: The NMFS Protected
Resources Division developed a
Biological Opinion (BiOp) in October
2011 regarding the continued
authorization of the reef fish fishery in
the U.S. Caribbean. The BiOp focused
its analyses on impacts to various
species of turtles and on the impacts of
continued parrotfish harvest on the
availability of critical settlement
substrate for Acroporid corals
(specifically Acropora cervicornis and
A. palmata). The BiOp determined that
the continued operation of the U.S.
Caribbean reef fish fishery is not likely
to jeopardize the continued existence of
Acroporid corals and not likely to
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destroy or adversely modify Acropora
critical habitat in the U.S. Caribbean.
This rule reduces all parrotfish
harvest levels in an effort to end
overfishing of all parrotfish species.
These reductions are described in detail
in Amendment 5 to the Reef Fish FMP.
For St. Croix, the ACL established by
this final rule will adjust harvest to a
level roughly 33 percent below the
average of the most recent 2 years (2006
and 2007) of landings available at the
time the Notice of Intent to Prepare an
Environmental Impact Statement for
Amendment 5 was published in April
2009 (April 17, 2009, 74 FR 17818) for.
These are substantial parrotfish harvest
reductions, and both NMFS and the
Council believe that these reductions
will substantially decrease fishing
pressure on these species. NMFS agrees
that parrotfish may be the only major
grazer remaining on U.S. Caribbean
coral reefs after the collapse of longspined sea urchin populations.
Although there are other grazers on
Caribbean coral reefs (e.g., surgeonfish),
NMFS and the Council acknowledge
that parrotfish are an important
component of Caribbean coral reef
ecosystems. The level of reduction was
designed to balance those ecological
considerations with the cultural
importance of parrotfish to U.S.
Caribbean residents, particularly
residents of St. Croix.
Comment 6: The AMs proposed in the
rule are inadequate to prevent
overfishing. The provision that allows
the Council to not apply AMs if it is
determined by the Council’s SSC, in
conjunction with the SEFSC, that
surpassing the ACL resulted from
enhanced reporting of landings, rather
than by an actual increase in harvest,
contradicts the intent of the MagnusonStevens Act with respect to the
application of AMs.
Response: AMs included in both
Amendments 2 and 5 are post-season in
nature to account for the present
reporting characteristics of the U.S.
Caribbean fisheries. The AMs will be
applied automatically unless there is a
determination by the SEFSC (in
consultation with the Council’s SSC)
that the ACL increase is due to
improved reporting rather than due to
an actual increase in landings. Postseason AMs are not always the preferred
method of a management strategy to
respond to an ACL overage, and the
fishers themselves have requested that
in-season monitoring schemes be
developed. Regional efforts are ongoing
in the U.S. Caribbean to develop better
methodologies to submit, compile,
distribute, and analyze landings data.
Progress has already been made,
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particularly in the electronic transmittal
of data from state to Federal agencies.
However, due to delays inherent in the
present reporting process, landings data
are not available within the fishing
season, so only post-season AMs are
presently feasible. Regarding the SSC
and SEFSC review of data to determine
if exceeding an ACL was the result of
better reporting or increased landings,
this provision allows for the best
scientific information available to be
applied to more effectively manage
fishing activity. Thus, both the Council
and NMFS decided this was a necessary
approach if the long-term goal of more
timely and accurate reporting was to be
achieved.
Comment 7: The adverse economic
impacts of the rule on USVI small
businesses are overestimated because it
assumes all of the licensed fisherman
land species that are the subject of the
final rule.
Response: It was assumed in the
initial regulatory flexibility analysis
(IRFA), and is assumed here that each
and every one of the 383 licensed
commercial fishermen of the USVI
represents a small business. Hence, the
final rule potentially impacts 383 small
businesses in the USVI, whether they all
presently fish for these species or not.
The total adverse economic impacts to
St. Croix and St. Thomas/St. John
commercial fishermen are estimated
independently of the number of small
businesses, and instead by estimated
reductions in historical and forecasted
annual landings caused by shortened
fishing seasons. The number of small
businesses is used to estimate the
average adverse economic impact per
small business. If the number of small
businesses adversely affected is lower,
the average adverse economic impact
per small business will be greater, but
the estimates of the total adverse
economic impacts do not change. The
best information available was used to
analyze these economic impacts.
Comment 8: The species of concern in
this amendment should not have been
considered as being ‘‘overfished or
undergoing overfishing’’ in all of the
island areas, as the incidents of
overfishing are localized. As a result of
previous management measures taken
by both the Council and the states to
address these incidents of overfishing
(i.e., the 2005 Sustainable Fisheries Act
Amendment (2005 Caribbean SFA
Amendment); seasonal and permanent
closures; size limits; quotas) along with
the use of available scientific
information, the species groups
classified as overfishing should have
been reclassified. All of these previous
actions should have been considered
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while setting ACLs, and these values in
most cases should have been the same
as for species considered not to be
undergoing overfishing.
Response: The purpose of
Amendments 2 and 5 was not to revise
the status of stocks with respect to their
classification as either undergoing
overfishing or overfished, but to
establish management reference points
and ACLs based upon the previously
determined status of those stocks.
Overfished or undergoing overfishing
designations apply to the fishery as
defined in the FMP, which is Caribbeanwide. Management reference points
were set U.S. Caribbean-wide, then
allocated among the three island groups
(St. Thomas/St. John, St. Croix, Puerto
Rico) according to proportional
contribution by each island group to the
total average landings used to set the
MSY proxy and OFL. Because of the
nature of landings data in the U.S.
Caribbean, where landings are
commonly reported to fishery
management unit (FMU) level rather
than to species level (with the exception
of snapper in Puerto Rico, as described
in Amendment 5 to Reef Fish FMP),
ACL assignments were made at the FMU
level rather than at the level of the
individual species.
The 2005 Caribbean SFA Amendment
was taken into consideration when
devising alternatives included in
Amendments 2 and 5. That amendment
implemented a variety of management
measures for reef fish species in the U.S.
Caribbean, including area closures that
may have affected reported landings. A
primary consideration during the
development of the management
reference point alternatives was the
choice of the year sequence used to
establish the average catch, and from
that, the MSY proxy and overfishing
limit (OFL) were developed. When
evaluating alternatives for year
sequences for average catch, the Council
chose not to use data from any years
more recent than 2005, due to the
potential impact on landings of the
previous management measures listed
in the comment.
The Council chose a 0.85 reduction to
set the ACLs. Before making a decision
on the appropriate reduction, the
Council reviewed public comments and
the recommendation of its Reef Fish
Advisory Panel, which functions as
interface between user groups and the
Council and provides insight from inthe-field observations. Fishers and the
Advisory Panel supported a 0.85
reduction while an environmental
organization supported a 0.75 reduction.
The Council also had several
discussions regarding the issue of
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uncertainty and the value of choosing
an uncertainty factor that would be most
acceptable to the territorial and
commonwealth governments. The
Council determined that the 0.85 scalar
would be most likely to result in the
application of compatible state
regulations and increased data
collection efforts, thereby stabilizing the
management regime.
After Amendments 2 and 5 were
developed, the Council initiated
development of the 2011 Caribbean ACL
Amendment pertaining to those species
not designated as undergoing
overfishing. The Council chose to
reduce by 10 percent for most of the
units included in the 2011 Caribbean
ACL Amendment, rather than by 15
percent as was done for the units
included in Amendment 5 to the Reef
Fish FMP. This 10 percent reduction
was chosen because landings patterns
for the species included in the 2011
Caribbean ACL Amendment were less
variable than for the species included in
Amendment 5 to the Reef Fish FMP. It
was determined by the Council that
those less variable landings required a
smaller reduction to minimize the
likelihood that landings in any year
would exceed the OFL.
Comment 9: The ACLs proposed are
inconsistent with National Standard
(NS) 1, which requires that conservation
and management measures shall prevent
overfishing while achieving the OY
from each fishery. Setting ACLs creates
artificial limitations for the fishermen of
St. Thomas, and management to an
artificial buffer is not necessary because
their fishery has been stable throughout
the past four decades.
Response: The 2006 revisions to the
Magnuson-Stevens Act require that
ACLs be set at a level such that
overfishing does not occur, regardless of
the relative stability of the reported
landings. Available data in the U.S.
Caribbean are not sufficient to support
direct estimation of MSY and other key
parameters. In such cases, the NS 1
guidelines direct regional fishery
management councils to estimate them
using reasonable proxies, like long-term
average catch, and to consider
uncertainty in determining the
appropriateness of alternative proxies.
The NS 1 guidelines suggest that ACLs
and OY should generally be reduced
from the overfishing threshold and
MSY, respectively, to effectively prevent
overfishing. The Council chose to set
OY and ACL as equal values, taking into
consideration the socioeconomic and
ecological components of OY when
determining how far ACLs should be
reduced below the overfishing
threshold. An ‘uncertainty’ factor was
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applied to reduce allowable landings
below the OFL in an effort to account
for uncertainty in the scientific and
management processes. The uncertainty
factor is designed to account for
scientific uncertainty in estimating the
OFL and management uncertainty in
effectively constraining harvest over
time. The reduction (buffer) chosen by
the Council will prevent overfishing by
minimizing the likelihood that annual
landings will exceed the OFL, while
achieving, on a continuing basis, OY.
Comment 10: The establishment of
ACLs is not consistent with National
Standard 2 (NS 2), which requires that
conservation and management measures
be based in the best scientific
information available. ACLs are not
based on the best scientific information
because they were based on unreliable
reported landings data (e.g. not speciesspecific), and that data should be
obtained from port sampling and this
method was not used to formulate the
ACLs.
Response: NMFS and the Council
have considered NS 2 in the
development of ACLs. Although the
reported landings data has areas in need
of improvement, this is the best
scientific information available. Those
landings data are provided by the
fishers on an island-specific basis. The
SEFSC, along with participating state,
Federal, private, and fishing interests
conducted analyses of port sampling
data and determined they were
inadequate with respect to the
requirements for randomness and
temporal consistency which therefore
minimizes the utility of port sampling
for establishing ACLs.
Comment 11: The establishment of
management measures in Amendments
2 and 5 is not consistent with National
Standard 6 (NS 6), which requires that
conservation and management measures
take into account, and allow for
variations among fisheries, fishery
resources, and catches. The variability
in the fishery of St. Thomas/St. John is
low and almost entirely due to normal
year-to-year fluctuations in
environmental variables, and that
variability should be considered in the
establishment of management measures
for the specific island group.
Response: The landings variability for
all island groups was analyzed. The data
used for all islands for establishing
management measures has the same
limitations and were therefore treated in
the same manner to account for both
expected and unpredictable variations.
This was done by applying a buffer to
reduce OY and ACL from the OFL or
ABC. Management reference points
were set for the U.S. Caribbean and then
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allocated among the three island groups
(St. Thomas/St. John, St. Croix, Puerto
Rico) according to the proportional
contribution by each island group to the
total average landings used to set the
MSY proxy and OFL.
Comment 12: The designation of
Puerto Rico and the USVI as fishing
communities under the terms of
National Standard 8 (NS 8) is
questionable. NS 8 requires that
conservation and management measures
take into account the importance of
fishery resources to fishing communities
by using economic and social data to
provide the sustained participation of
the communities and minimize adverse
economic impacts to the community to
the extent practicable. The passage of
recent ACLs in 2010 and 2011 should
have been accompanied by in-depth
analysis of the impacts of those actions
upon the USVI fishing communities,
and no ACLs should be approved until
the analyses are completed and
implications are considered.
Response: NMFS and the Council
recognize the designation of St.
Thomas/St. John, St. Croix, and coastal
areas of Puerto Rico as fishing
communities. However, for Puerto Rico,
the fishing community designation does
not apply to the entire island, but
instead to the northern coastal, southern
coastal, eastern coastal, and western
coastal municipalities combined. The
impacts of the provisions of
Amendments 2 and 5 are included
within the analysis of the social
impacts, which is found in the Social
Impact Assessment (section 9) of the
Final Environmental Impact Statement.
Additionally, the NS 8 guidelines state
that consideration of impacts to
designated fishing communities be
within the context of the conservation
requirements of the Magnuson-Stevens
Act. These requirements were
considered during the development of
Amendments 2 and 5. The impacts to
the fishing communities were analyzed
and minimized to the extent practicable
while still meeting the other MagnusonStevens Act requirements. Deliberations
regarding the importance of fishery
resources to affected fishing
communities, therefore, must not
compromise the achievement of
conservation requirements and goals of
the FMP.
Comment 13: For ACLs and AMs to be
effective, Puerto Rico and the USVI
should achieve compatibility with
Federal regulations, and adequate
funding should be available to collect
and process data, enforce regulations,
and effectively manage the fishery.
There is an importance to ‘‘buy in’’ by
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the fishers with regard to the concept of
a regulated, sustainable resource.
Response: Efforts are underway by the
Council, NMFS, and the states to
establish compatible regulations in both
Puerto Rico and the USVI, but those
regulatory changes must be effectuated
by the state governments rather than by
the Council or NMFS. NMFS recognizes
the advantages to developing and
implementing regulations to ensure the
long-term sustainability of Caribbean
fisheries resources and the ecosystems
upon which they depend.
Comment 14: The cost of the
prohibition on fishing for blue, rainbow
and midnight parrotfish in the EEZ off
the USVI, especially St. Croix, was
overestimated because the species are
rarely, if ever, caught in Federal waters
and the adverse impacts should be
minimal.
Response: Because parrotfish harvest
data is not available at the species level
in the USVI, the expected economic
effects of the regulations associated with
blue, rainbow, and midnight parrotfish
could not be quantitatively assessed at
the species level. As a result, the IRFA
only provided quantitative estimates of
the expected economic effects of the
proposed regulations on all parrotfish
species combined. Because blue,
rainbow, and midnight parrotfish may
not be the primary parrotfish species
harvested, the estimates of the expected
economic impacts on all parrotfish
species may not be representative of the
impacts on these three species and may,
in fact, overestimate actual effects.
However, overestimation of potential
economic effects is not expected to be
a substantive issue because the purpose
of the RFA is to identify alternatives
that achieve the regulatory objective
while reducing or minimizing
significant adverse economic effects on
small entities. If the effects are minimal,
as the comment suggests, then the need
to reduce these effects is diminished.
Comment 15: Fishermen will not be
able to relocate into territorial waters to
mitigate for any losses of parrotfish
landings because the resource is
overexploited in territorial waters. It is
incorrect to assume that USVI fishermen
may be able to mitigate for some, but not
all, of the losses incurred by the
parrotfish prohibition.
Response: The RIR determined and
the IRFA indicated that USVI fishermen
could mitigate for 20 percent of the
potential loss of landings by shifting
effort into territorial waters. In response
to this comment on the proposed rule,
the FRFA includes the possibility that
fishermen cannot mitigate for any losses
of landings of parrotfish, snapper and
grouper in the USVI as a result of new
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ACLs. This new assumption indicates
that the ACLs may be up to 100 percent
effective in reducing ACL overages.
Classification
The Regional Administrator,
Southeast Region, NMFS has
determined that this final rule is
necessary for the conservation and
management of the species within
Amendments 2 and 5 and is consistent
with the Magnuson-Stevens Act, and
other applicable law.
This final rule has been determined to
be not significant for purposes of
Executive Order 12866. However, ACLs
are a controversial issue in the U.S.
Caribbean, which is a region with
populations characterized by large
percents of racial/ethnic minorities,
high poverty rates, and low median
household incomes. Moreover,
commercial fishermen of St. Croix and
St. Thomas/St. John will experience a
substantially greater adverse economic
impact relative to their counterparts in
Puerto Rico.
Pursuant to the Regulatory Flexibility
Act, 5 U.S.C. 601–612, NMFS prepared
a final regulatory flexibility analysis
(FRFA) that includes a statement of
need for, and objectives of, the rule; a
summary and assessment of significant
issues raised by public comments; a
description and estimate of the number
of small entities; a description of the
compliance requirements, including
estimates of the adverse economic
impacts; and a description of steps
taken to minimize significant adverse
economic impact on small entities. The
description of the action, why it is being
considered, and the objectives of this
action are contained in the proposed
rule (76 FR 66675, Oct. 27, 2011), at the
beginning of this section in the
preamble, and in the SUMMARY section of
the preamble. A copy of the full analysis
is available from NMFS (see ADDRESSES).
A summary of the FRFA follows.
The final rule, which consists of
several actions, will establish
recreational bag limits for specified reef
fish species; specify ACLs and AMs for
parrotfish, grouper, snapper, and queen
conch and establish framework
measures to facilitate regulatory
modifications. The rule will not alter
existing reporting or record-keeping
requirements.
The Magnuson Stevens Act provides
the statutory basis for the rule.
There were no significant issues
regarding the IRFA raised by public
comments; however, three comments
were received regarding the estimate of
the adverse economic impacts on USVI
fishermen. The first comment disagreed
with the description of the impact of the
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prohibition on fishing for blue, rainbow
and midnight parrotfish in the EEZ off
the USVI, especially St. Croix. The
comment contends that the cost of the
prohibition on fishing for and
possession of blue, rainbow and
midnight parrotfish in the EEZ,
particularly off St. Croix, was
overestimated because the species are
rarely, if ever, caught in Federal waters
and the adverse impact should be
minimal. Because parrotfish harvest
data is not available at the species level
in the USVI, the expected economic
effects of the regulations associated with
blue, rainbow, and midnight parrotfish
could not be quantitatively assessed at
the species level. As a result, the IRFA
only provided quantitative estimates of
the expected economic effects of the
proposed regulations on all parrotfish
species combined. Because blue,
rainbow, and midnight parrotfish may
not be the primary parrotfish species
harvested, the estimates of the expected
economic impacts on all parrotfish
species may not be representative of the
impacts on these three species and, in
fact, overestimate actual effects.
However, overestimation of potential
economic effects is not expected to be
a substantive issue because the purpose
of the RFA is to identify alternatives
that achieve the regulatory objective
while reducing or minimizing
significant adverse economic effects on
small entities. If the effects are minimal,
as the comment suggests, then the need
to reduce these effects is diminished.
The second comment disagreed with
the assumption that USVI fishermen
may be able to mitigate for some, but not
all, losses by increasing landings of
snapper, grouper, and parrotfish species
taken in the EEZ by relocating into
territorial waters, although it is more
difficult for USVI fishermen to
substitute fishing in territorial waters for
fishing in Federal waters. The comment
contends that fishermen would not be
able to relocate into territorial waters to
mitigate for any losses of parrotfish
landings because the resource is
overexploited in territorial waters.
NMFS, in its RIR, determined and
through the IRFA indicated that USVI
fishermen could mitigate for 20 percent
of the potential loss of landings by
shifting effort into territorial waters. In
response to this comment, the FRFA
includes the possibility that fishermen
cannot mitigate for any losses of
landings of parrotfish, snapper and
grouper in the USVI. That new
assumption results in the ACLs being up
to 100 percent effective in reducing an
overage.
The third comment contended the
estimate of the adverse economic
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impacts to USVI small businesses was
too high because it assumed all of the
licensed fishermen land species that are
the subject of the final rule. NMFS
assumed in the IRFA, and assumes here,
that every one of the 383 licensed
commercial fishermen of the USVI
represents a small business that may
potentially be impacted by this rule,
whether they all presently fish for these
species or not. The total adverse
economic impacts to St. Croix and St.
Thomas/St. John commercial fishermen
are estimated independently of the
number of small businesses and instead
by estimated reductions in historical
and forecasted annual landings. The
number of small businesses is used to
estimate the average adverse economic
impact per small business. If the
number of small businesses adversely
affected is lower, the average adverse
economic impact per small business
will be greater.
This final rule is expected to directly
affect businesses that harvest parrotfish,
snapper and grouper from Federal
waters off Puerto Rico and the USVI and
those that harvest queen conch in
Federal waters off St. Croix. These
businesses are in the finfish fishing
(NAICS 114111), shellfish fishing
(NAICS 114112) and charter fishing
industries (NAICS 487210). A business
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 or number of
employees not in excess of the Small
Business Administration’s (SBA’s) size
standards. The finfish and shellfish
fishing industries have an SBA size
standard of $4.0 million in annual
receipts, and the charter fishing
industry’s size standard is $7.0 million
in annual receipts. NMFS assumes all
commercial (finfish and shellfish) and
charter fishing businesses that operate
in the U.S. Caribbean have annual
receipts less than these size standards
and are small businesses.
In 2008, there were from 868 to 874
active commercial fishermen in Puerto
Rico; 74 percent of these fishermen were
captains and the remaining 26 percent
were crew members. NMFS assumes
each captain represents a small business
in the finfish fishing and shellfish
fishing industries and each member of
the crew an employee of one of those
businesses. Therefore, NMFS concludes
that there are 642 to 644 small
businesses in the finfish fishing and
shellfish fishing industries in Puerto
Rico, and potentially all of these
businesses will be directly affected by
the rule. In 2008, there were 223
licensed commercial fishermen in St.
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82409
Croix and 160 in St. Thomas/St. John.
There is a moratorium on increasing the
number of U.S. Virgin Islands
commercial fishing licenses, so the
FRFA assumes the 223 commercial
fishermen in St. Croix and 160
commercial fishermen in St. Thomas/St.
John represent 383 small businesses in
the finfish fishing and shellfish fishing
industries in the U.S. Virgin Islands
who will be directly affected by the rule.
There are an estimated 9 small
businesses in the charter fishing
industry in Puerto Rico, 12 such
businesses in St. Thomas/St. John and 1
in St. Croix. The final rule will apply to
all of these small businesses.
The final rule will apply to all small
businesses in Puerto Rico, St. Croix and
St. Thomas/St. John within the finfish
fishing, shellfish fishing, and charter
fishing industries. Therefore, the final
rule applies to a substantial number of
small entities in the U.S. Caribbean in
these industries. Charter fishing
operations in Puerto Rico and the U.S.
Virgin Islands target pelagic species and
tend not to target queen conch or reef
fish species in Federal waters.
Consequently, it is expected that small
businesses in the charter fishing
industry in Puerto Rico, St. Croix or St.
Thomas/St. John will experience little to
no adverse economic impact because of
this final rule.
The final rule is expected to result in
one shortened Federal fishing season in
the Puerto Rico EEZ, three shortened
fishing seasons in the St. Croix EEZ, and
three shortened fishing seasons in the
St. Thomas/St. John EEZ. This final rule
is expected to have a substantially
greater adverse economic impact on
small businesses in the finfish fishing
industries in St. Croix and St. Thomas/
St. John than in Puerto Rico because the
projected reductions in harvest of the
different species, as discussed in the
following paragraphs, are substantially
larger in the USVI than in Puerto Rico.
There is expected to be no adverse
economic impact on small businesses in
the shellfish fishing industry.
A comparison of the Puerto Rico
commercial ACLs for parrotfish, grouper
and Snapper Units 1, 3 and 4 to baseline
annual commercial landings suggests
the commercial ACLs for these units
will not require reductions in the
lengths of the Federal commercial
fishing seasons for these units in the
Puerto Rico EEZ. Therefore, NMFS
expects no adverse economic impact on
small businesses in Puerto Rico that
harvest these species.
The Puerto Rico commercial Snapper
Unit 2 ACL is less than the baseline
annual landings, which suggests there
will be an overage of Snapper Unit 2
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landings of 509 lb (231 kg) and a
shortened Snapper Unit 2 fishing season
in the Puerto Rico EEZ. NMFS expects
that Puerto Rico’s small businesses will
mitigate for the potentially shortened
Snapper Unit 2 fishing season in the
Puerto Rico EEZ by moving into
territorial waters to harvest Snapper
Unit 2 species during the time the
Federal season is closed, because
approximately 95 percent of fishable
area off Puerto Rico is in territorial
waters. Hence, NMFS projects that
Puerto Rico small businesses would lose
up to 10 percent of baseline Snapper
Unit 2 landings annually with a value
up to $383. That loss represents less
than a tenth of a percent of annual
Snapper Unit 2 landings and on average,
less than 1 lb (0.45 kg) of Snapper Unit
2 species and less than $1 lost per small
business in Puerto Rico. Another
mitigating behavior would be to target
alternative species in the Puerto Rico
EEZ that have open seasons.
The St. Croix ACLs for parrotfish,
snapper and grouper are less than
baseline average annual landings, which
indicates fishing seasons for these units
will be reduced. St. Croix small
businesses will incur annual losses of
landings of up to 34 percent of
parrotfish landings, 27 percent of
snapper landings, and 6 percent of
grouper landings each year. These
reductions represent losses of ex-vessel
revenue up to approximately $0.83
million annually. The average St. Croix
small business will lose up to $3,706
annually. When estimated losses of
revenues from the 2011 ACLs
Amendment are added, St. Croix small
businesses lose collectively up to $1.19
million annually.
The St. Thomas/St. John ACLs for
parrotfish, snapper and grouper are less
than baseline average annual landings,
which indicates fishing seasons for
these units will be reduced. St. Thomas/
St. John small businesses will lose up to
6 percent of parrotfish, 20 percent of
snapper and 9 percent of grouper
landings each year. These reductions
represent losses of ex-vessel revenue up
to approximately $0.27 million. The
average St. Thomas/St. John small
business will lose up to $1,690
annually. When estimated losses of
revenues from the 2011 ACLs
Amendment are added, St. Thomas/St.
John small businesses lose collectively
up to $0.51 million annually.
The percent of fishable area in the
U.S. Virgin Islands’ territorial waters is
significantly less than the percent of
fishable area in Puerto Rico’s territorial
waters. 38 percent of fishable area off
the U.S. Virgin Islands lies within the
U.S. Caribbean EEZ, and a larger share
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Jkt 226001
of landings in St. Croix and St. Thomas/
St. John derive from fishing in the EEZ
than in Puerto Rico. Therefore, it is
more difficult for U.S. Virgin Islands
fishermen to substitute fishing in
territorial waters for fishing in Federal
waters.
The final rule rejects alternatives that
would have established ACLs and AMs
that would have resulted in larger
reductions in Federal fishing seasons
and greater significant adverse
economic impacts on small businesses,
especially in the USVI.
List of Subjects in 50 CFR Part 622
Fisheries, Fishing, Puerto Rico,
Reporting and recordkeeping
requirements, Virgin Islands.
Dated: December 22, 2011.
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 § 622.32, paragraph (b)(1)(v) is
added to read as follows:
■
§ 622.32 Prohibited and limited-harvest
species.
*
*
*
*
*
(b) * * *
(1) * * *
(v) No person may fish for or possess
midnight parrotfish, blue parrotfish, or
rainbow parrotfish in or from the
Caribbean EEZ. Such fish caught in the
Caribbean EEZ must be released with a
minimum of harm.
*
*
*
*
*
■ 3. In § 622.33, paragraph (d)(1) is
revised to read as follows:
§ 622.33 Caribbean EEZ seasonal and/or
area closures.
*
*
*
*
*
(d) * * *
(1) Pursuant to the procedures and
criteria established in the FMP for
Queen Conch Resources in Puerto Rico
and the U.S. Virgin Islands, when the
ACL, as specified in § 622.49(c)(2)(i)(A),
is reached or projected to be reached,
the Regional Administrator will close
the Caribbean EEZ to the harvest and
possession of queen conch, in the area
east of 64°34′ W. longitude which
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includes Lang Bank, east of St. Croix,
U.S. Virgin Islands, by filing a
notification of closure with the Office of
the Federal Register.
*
*
*
*
*
■ 4. In § 622.39, paragraph (g) is added
to read as follows:
§ 622.39
Bag and possession limits.
*
*
*
*
*
(g) Caribbean reef fish—(1)
Applicability. Paragraph (a)(1) of this
section notwithstanding, the bag limits
of paragraph (g)(2) of this section do not
apply to a person who has a valid
commercial fishing license issued by
Puerto Rico or the U.S. Virgin Islands.
(2) Bag limits. Groupers, snappers,
and parrotfishes combined—5 per
person per day or, if 3 or more persons
are aboard, 15 per vessel per day; but
not to exceed 2 parrotfish per person per
day or 6 parrotfish per vessel per day.
5. In § 622.48, paragraph (b) is revised
and paragraph (m) is added to read as
follows:
■
§ 622.48 Adjustment of management
measures.
*
*
*
*
*
(b) Caribbean reef fish. Fishery
management units (FMUs), quotas, trip
limits, bag limits, size limits, closed
seasons or areas, gear restrictions,
fishing years, MSY, OY, TAC, maximum
fishing mortality threshold (MFMT),
minimum stock size threshold (MSST),
overfishing limit (OFL), acceptable
biological catch (ABC) control rules,
ACLs, AMs, ACTs, and actions to
minimize the interaction of fishing gear
with endangered species or marine
mammals.
*
*
*
*
*
(m) Caribbean queen conch. Quotas,
trip limits, bag limits, size limits, closed
seasons or areas, gear restrictions,
fishing year, MSY, OY, TAC, MFMT,
MSST, OFL, ABC control rules, ACLs,
AMs, ACTs, and actions to minimize the
interaction of fishing gear with
endangered species or marine mammals.
6. In § 622.49, the section heading is
revised and paragraph (c) is added to
read as follows:
■
§ 622.49 Annual catch limits (ACLs) and
accountability measures (AMs).
*
*
*
*
*
(c) Caribbean island management
areas. If landings from a Caribbean
island management area, as specified in
Appendix E to part 622, except for
landings of queen conch (see
§ 622.33(d)), are estimated by the SRD to
have exceeded the applicable ACL, as
specified in paragraph (c)(1) of this
section for Puerto Rico management
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area species or species groups,
paragraph (c)(2) of this section for St.
Croix management area species or
species groups, or paragraph (c)(3) for
St. Thomas/St. John management area
species or species groups, 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 fishing
season for the applicable species or
species groups that year by the amount
necessary to ensure landings do not
exceed the applicable ACL. If NMFS
determines the ACL for a particular
species or species group was exceeded
because of enhanced data collection and
monitoring efforts instead of an increase
in total catch of the species or species
group, NMFS will not reduce the length
of the fishing season for the applicable
species or species group the following
fishing year. Landings will be evaluated
relative to the applicable ACL based on
a moving multi-year average of landings,
as described in the FMP. With the
exceptions of Caribbean queen conch in
Puerto Rico and St. Thomas/St. John
management areas, goliath grouper,
Nassau grouper, midnight parrotfish,
blue parrotfish, and rainbow parrotfish,
ACLs are based on the combined
Caribbean EEZ and territorial landings
for each management area. The ACLs
specified in paragraphs (c)(1), (c)(2), and
(c)(3) of this section are given in round
weight. (See § 622.32 for limitations on
taking prohibited and limited harvest
species. The limitations in § 622.32
apply without regard to whether the
species is harvested by a vessel
operating under a valid commercial
fishing license issued by Puerto Rico or
the U.S. Virgin Islands or by a person
subject to the bag limits.)
(1) Puerto Rico—(i) Commercial ACLs.
The following ACLs apply to
commercial landings of Puerto Rico
management area species or species
groups.
(A) Queen conch—0 lb (0 kg), for the
EEZ only.
(B) Parrotfishes—52,737 lb (23,915
kg).
(C) Snapper Unit 1—284,685 lb
(129,131 kg).
(D) Snapper Unit 2—145,916 lb
(66,186 kg).
(E) Snapper Unit 3—345,775 lb
(156,841 kg).
(F) Snapper Unit 4—373,295 lb
(169,324 kg).
(G) Groupers—177,513 lb (80,519 kg).
(ii) Recreational ACLs. The following
ACLs apply to recreational landings of
Puerto Rico management area species or
species groups.
(A) Queen conch—0 lb (0 kg), for the
EEZ only.
(B) Parrotfishes—15,263 lb (6,921 kg).
(C) Snapper Unit 1—95,526 lb (43,330
kg).
(D) Snapper Unit 2—34,810 lb (15,790
kg).
(E) Snapper Unit 3—83,158 lb (37,720
kg).
(F) Snapper Unit 4—28,509 lb (12,931
kg).
(G) Groupers—77,213 lb (35,023 kg).
(2) St. Croix. (i) ACLs. The following
ACLs apply to landings of St. Croix
management area species or species
groups.
(A) Queen conch—50,000 lb (22,680
kg).
(B) Parrotfishes—240,000 lb (108,863
kg).
(C) Snappers—102,946 lb (46,696 kg).
(D) Groupers—30,435 lb (13,805 kg).
(ii) [Reserved]
(3) St. Thomas/St. John. (i) ACLs. The
following ACLs apply to landings of St.
Thomas/St. John management area
species or species groups.
(A) Queen conch—0 lb (0 kg), for the
EEZ only.
(B) Parrotfishes—42,500 lb (19,278
kg).
(C) Snappers—133,775 lb (60,679 kg).
(D) Groupers—51,849 lb (23,518 kg).
(ii) [Reserved]
7. In table 2 of Appendix A to Part
622, Lutjanidae—Snappers, units 1 and
2 are revised; In Serranidae—Sea basses
and groupers, units 3 and 4 are revised;
■
and In Serranidae—Sea basses and
groupers, unit 5 is added to read as
follows:
Appendix A to Part 622—Species
Tables
*
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*
Unit 1
Black snapper, Apsilus dentatus
Blackfin snapper, Lutjanus buccanella
Silk snapper, Lutjanus vivanus
Vermilion snapper, Rhomboplites
aurorubens
Wenchman, Pristipomoides aquilonaris
Unit 2
Cardinal, Pristipomoides macrophthalmus
Queen snapper, Etelis oculatus
*
*
*
*
Sfmt 4700
*
Serranidae—Sea basses and Groupers
*
*
*
*
*
Unit 3
Coney, Epinephelus fulvus
Graysby, Epinephelus cruentatus
Red hind, Epinephelus guttatus
Rock hind, Epinephelus adscensionis
Unit 4
Black grouper, Mycteroperca bonaci
Red grouper, Epinephelus morio
Tiger grouper, Mycteroperca tigris
Yellowfin grouper, Mycteroperca venenosa
Unit 5
Misty grouper, Epinephelus mystacinus
Yellowedge grouper, Epinephelus
flavolimbatus
*
*
*
*
*
8. Appendix E to part 622 is added to
read as follows:
■
Appendix E to Part 622—Caribbean
Island/Island Group Management
Areas
Table 1 of Appendix E to Part 622—
Coordinates of the Puerto Rico Management
Area.
The Puerto Rico management area is
bounded by rhumb lines connecting, in
order, the following points.
North lat.
Fmt 4701
*
Lutjanidae—Snappers
A (intersects with the International/EEZ boundary) .......................................................................................
B (intersects with the EEZ/Territorial boundary) ............................................................................................
From Point B, proceed southerly along the EEZ/Territorial boundary to Point C
C (intersects with the EEZ/Territorial boundary) ....................................................................................
D ..............................................................................................................................................................
E ..............................................................................................................................................................
F ..............................................................................................................................................................
From Point F, proceed southwesterly, then northerly, then easterly, and finally southerly along the International/EEZ boundary to Point A
A (intersects with the International/EEZ boundary) ................................................................................
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*
Table 2 of Appendix A to Part 622—
Caribbean Reef Fish
Point
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*
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West long.
19°37′29″
18°25′46.3015″
65°20′57″
65°06′31.866″
18°13′59.0606″
18°01′16.9636″
17°30′00.000″
16°02′53.5812″
65°05′33.058″
64°57′38.817″
65°20′00.1716″
65°20′00.1716″
19°37′29″
65°20′57″
30DER3
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Federal Register / Vol. 76, No. 251 / Friday, December 30, 2011 / Rules and Regulations
Table 2 of Appendix E to Part 622—
Coordinates of the St. Croix Management
Area.
The St. Croix management area is bounded
by rhumb lines connecting, in order, the
following points.
Point
North lat.
G .....................................................................................................................................................................
From Point G, proceed easterly, then southerly, then southwesterly along the EEZ/Territorial boundary to
Point F
F ..............................................................................................................................................................
E ..............................................................................................................................................................
D ..............................................................................................................................................................
G .............................................................................................................................................................
Table 3 of Appendix E to Part 622—
Coordinates of the St. Thomas/St. John
Management Area.
18°03′03″
64°38′03″
16°02′53.5812″
17°30′00.000″
18°01′16.9636″
18°03′03″
65°20′00.1716″
65°20′00.1716″
64°57′38.817″
64°38′03″
The St. Thomas/St. John management area
is bounded by rhumb lines connecting, in
order, the following points.
Point
North lat.
A (intersects with the International/EEZ boundary) .......................................................................................
From Point A, proceed southeasterly along the EEZ/Territorial boundary to Point G
G .............................................................................................................................................................
D ..............................................................................................................................................................
C (intersects with the EEZ/Territorial boundary) ....................................................................................
From Point C, proceed northerly along the EEZ/Territorial boundary to Point B
B (intersects with the EEZ/Territorial boundary) ....................................................................................
A (intersects with the International/EEZ boundary) ................................................................................
65°20′57″
18°03′03″
18°01′16.9636″
18°13′59.0606″
64°38′03″
64°57′38.817″
65°05′33.058″
18°25′46.3015″
19°37′29″
65°06′31.866″
65°20′57″
tkelley on DSK3SPTVN1PROD with RULES3
BILLING CODE 3510–22–P
19:54 Dec 29, 2011
Jkt 226001
PO 00000
Frm 00010
Fmt 4701
Sfmt 9990
E:\FR\FM\30DER3.SGM
West long.
19°37′29″
[FR Doc. 2011–33512 Filed 12–29–11; 8:45 am]
VerDate Mar<15>2010
West long.
30DER3
Agencies
[Federal Register Volume 76, Number 251 (Friday, December 30, 2011)]
[Rules and Regulations]
[Pages 82404-82412]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-33512]
[[Page 82403]]
Vol. 76
Friday,
No. 251
December 30, 2011
Part III
Department of Commerce
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National Oceanic and Atmospheric Administration
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50 CFR Part 622
Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic;
Amendments to the Queen Conch and Reef Fish Fishery Management Plans of
Puerto Rico and the U.S. Virgin Islands; Final Rule
Federal Register / Vol. 76, No. 251 / Friday, December 30, 2011 /
Rules and Regulations
[[Page 82404]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 622
[Docket No. 100120037-1626-02]
RIN 0648-AY55
Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic;
Amendments to the Queen Conch and Reef Fish Fishery Management Plans of
Puerto Rico and the U.S. Virgin Islands
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 2 to the
Fishery Management Plan for Queen Conch Resources of Puerto Rico and
the U.S. Virgin Islands, and Amendment 5 to the Fishery Management Plan
for the Reef Fish Fishery of Puerto Rico and the U.S. Virgin Islands
(Amendments 2 and 5), prepared by the Caribbean Fishery Management
Council (Council). This final rule: Establishes annual catch limits
(ACLs) and accountability measures (AMs) for queen conch and for all
reef fish units or sub-units that are classified as undergoing
overfishing (i.e., snapper, grouper and parrotfish); allocates ACLs
among island management areas; revises the composition of the snapper
and grouper complexes; prohibits fishing for and possession of three
parrotfish species; establishes recreational bag limits for snappers,
groupers, and parrotfishes; and establishes framework procedures for
the queen conch and reef fish fishery management plans. Amendments 2
and 5 also revise management reference points and status determination
criteria. The intended effect of the rule is to prevent overfishing of
queen conch and reef fish species while maintaining catch levels
consistent with achieving optimum yield (OY).
DATES: This final rule is effective January 30, 2012.
ADDRESSES: Electronic copies of Amendments 2 and 5, which include an
Environmental Impact Statement (EIS), a final regulatory flexibility
analysis (FRFA), a regulatory impact review (RIR), and a fishery impact
statement may be obtained from the Southeast Regional Office Web site
at https://sero.nmfs.noaa.gov/sf/pdfs/2010_Caribbean_ACL_Amendment_FEIS_092011.pdf.
FOR FURTHER INFORMATION CONTACT: Bill Arnold, Southeast Regional
Office, NMFS, telephone: (727) 824-5305, email: Bill.Arnold@noaa.gov.
SUPPLEMENTARY INFORMATION: In the exclusive economic zone (EEZ) of the
U.S. Caribbean, the queen conch fishery is managed under the Fishery
Management Plan for Queen Conch Resources of Puerto Rico and the U.S.
Virgin Islands (USVI) (Queen Conch FMP), and the reef fish fishery is
managed under the Reef Fish Fishery Management Plan of Puerto Rico and
the USVI (Reef Fish FMP). These FMPs were prepared by the Council and
are implemented through regulations at 50 CFR part 622 under the
authority of the Magnuson-Stevens Fishery Conservation and Management
Act (Magnuson-Stevens Act).
NMFS' 2011 Report on the Status of U.S. Fisheries classifies
Caribbean queen conch, Grouper Units 1 and 4, Snapper Unit 1, and
parrotfishes as undergoing overfishing.
On September 26, 2011, NMFS published a notice of availability for
Amendments 2 and 5 and requested public comment (76 FR 59375). On
October 27, 2011, NMFS published a proposed rule for Amendments 2 and 5
and requested public comment (76 FR 66675). The proposed rule and
Amendments 2 and 5 outline the rationale for the actions contained in
this final rule. A summary of the actions implemented by this final
rule are provided below.
This final rule amends the composition of stock complexes within
the Reef Fish FMP. Grouper and snapper unit complexes are being revised
to include two species of commonly harvested fish that were previously
excluded, remove the creole-fish from the Reef Fish FMP since the
Council decided the species is no longer in need of Federal
conservation and management due to no reported landings in the EEZ in
recent years, and aggregate species in an ecologically consistent
manner within the Reef Fish FMP.
This final rule revises and establishes management reference points
for snapper, grouper, parrotfish and queen conch in the following
manner: (1) Establishes average catch as a proxy for calculating the
MSY for all units or complexes; (2) calculates the MSY proxy for each
species or unit using average catch from commercial landings data from
1999-2005 for Puerto Rico and St. Croix, and from 2000-2005 for St.
Thomas/St. John, and recreational catch data from 2000-2005 for Puerto
Rico only; (3) sets the ABC for queen conch and parrotfish equal to the
fishing level recommendation specified by the Council's Scientific and
Statistical Committee (SSC) for those species; (4) defines the
overfishing threshold of all species as the OFL, which would equal the
MSY proxy; setting the OY and the ACL as equal values; (5) sets the OY
equal to the OFL multiplied by a reduction factor of 0.85 to account
for uncertainty in the scientific and management process for snapper
and grouper in all three management areas. The OY of queen conch was
not reduced below the ABC; (6) sets the ACL for parrotfish as a 0.85
reduction of the SSC's ABC recommendation to account for uncertainty,
ecological factors and other concerns for all three island groups; and
(7) sets the OY/ACL equal to zero for Nassau grouper, goliath grouper,
rainbow parrotfish, blue parrotfish, and midnight parrotfish.
This final rule also establishes island-specific management to
enable application of AMs in response to harvesting activities on a
single island (Puerto Rico, St. Croix) or island group (St. Thomas/St.
John) without necessarily affecting fishing activities on the other
islands or island groups. This final rule establishes geographic
boundaries between islands/island groups based upon an equidistant
approach that uses a mid-point to divide the exclusive economic zone
(EEZ) among islands. The three island management areas are: Puerto
Rico, St. Croix, and St. Thomas/St. John.
This final rule establishes ACLs and AMs for queen conch and for
all snapper, grouper, and parrotfish units or complexes in the
Caribbean Reef Fish FMP. The ACLs include reductions in catch to buffer
allocations to account for scientific and catch-level uncertainty. Each
ACL is sub-divided among the three islands/island groups, and for
Puerto Rico only, separate sector ACLs (commercial and recreational)
are established because commercial and recreational sector landings
data are both available. For the St. Croix and St. Thomas/St. John
island management areas, only commercial data are available; therefore,
ACLs are established for the St. Croix and St. Thomas/St. John
management areas based on commercial landings data only. The final rule
specifies an ACL of zero for Nassau grouper, goliath grouper, rainbow
parrotfish, blue parrotfish, and midnight parrotfish.
The AMs are designed to prevent fishermen from exceeding the ACLs.
The AMs for queen conch are described in the 2010 regulatory amendment
(May 26, 2011, 76 FR 30554) to the Queen Conch FMP, and state that when
the
[[Page 82405]]
USVI closes its territorial waters off St. Croix to the harvest and
possession of queen conch, NMFS will concurrently close the EEZ in the
area of Lang Bank until the start of the next territorial fishing
season. For Puerto Rico and St Thomas/St. John, the applicable ACL will
be set at zero and so the harvest prohibition will function as the AM
in the EEZ for those areas.
This final rule triggers AMs if an ACL has been exceeded based on a
moving multi-year average of landings as described in the FMP. If the
ACL is exceeded, this final rule reduces the length of the fishing
season for the affected species the year following an overage by the
amount needed to prevent such an overage from occurring again. The AM
is triggered unless NMFS' Southeast Fisheries Science Center, in
consultation with the Council and its Scientific and Statistical
Committee (SSC), determines the overage occurred because data
collection and monitoring improved, rather than because catches
actually increased. In such circumstances NMFS and the Council would
review the relevant information and take further action as appropriate.
To maintain the role of parrotfish with respect to the health and
ecological protection of threatened Acropora coral, this final rule
prohibits the harvest of the three largest species of parrotfish that
occur on Caribbean coral reefs. The harvest of blue, midnight, and
rainbow parrotfish will be prohibited.
Additionally, this final rule establishes an aggregate bag limit
for the recreational harvest of snapper, grouper and parrotfish. The
daily recreational bag limit for snapper, grouper, and parrotfish
combined will be five fish per person per day, with no more than two
parrotfish per person within the aggregate. This rule also establishes
a vessel limit on snapper, grouper, and parrotfish of 15 fish per day,
including no more than 6 parrotfish per vessel per day.
To facilitate timely adjustments to harvest parameters and other
management measures, this final rule establishes framework procedures
for both the Reef Fish and Queen Conch FMPs. Management measures to be
adjusted through framework amendments include but are not limited to
quotas, closures, trip limits, bag limits, size limits, gear
restrictions, fishing years, and reference points.
Comments and Responses
The following summarizes the comments NMFS received on Amendments 2
and 5 and the proposed rule, and NMFS' respective responses. Nine
submissions were received on the amendments and the proposed rule,
including comments from individuals, state and Federal agencies,
environmental organizations, and fishing associations. Several
commenters were generally supportive of the actions included in
Amendments 2 and 5. A Federal agency had no specific comments and a
non-governmental organization was supportive and recommended approval.
Comments that pertain to specific actions addressed in Amendments 2 and
5 or the proposed rule are summarized and responded to below.
Comment 1: The boundary lines defining the EEZ subdivisions should
take into account the distribution of marine biotopes and an additional
(unquantified) buffer be added to the 15 percent uncertainty reduction
in the setting of ACLs.
Response: Although state and Federal efforts are underway to map
and define biological communities throughout the U.S. Caribbean,
suitable information is not yet available to support allocation of
subdivisions by biotope. However, input from fishers with regard to
their fishing locations were taken into consideration when establishing
the boundary lines. Additionally, those boundary lines do not prevent
fishers from fishing in any area of the U.S. Caribbean EEZ. Instead,
the boundary lines only become restrictive when the ACL has been met
for a species or species group within the EEZ subdivision for a
particular island or island group. Then, AMs will be applied for that
EEZ subdivision.
With respect to the additional buffer for setting ACLs, the 15-
percent reduction serves as a buffer between the overfishing level and
the ACL, thus minimizing the likelihood that overfishing will occur.
Other ``buffers,'' including more stringent ones (i.e., buffers that
reduce allowable catch to an even greater degree), were considered by
the Council but not implemented. The Council determined that these more
stringent buffers were not necessary to prevent overfishing of snapper,
grouper, and parrotfish. The Council also determined that the 15
percent reduction would more effectively encourage the development of
compatible regulations by territorial and commonwealth governments and
increase data collection efforts, which would bring more stability to
the management regime. The Council further reduced allowable parrotfish
harvest in St. Croix EEZ waters by 15,000 lb (6,804 kg) to address
ecological considerations as described in Amendments 2 and 5.
Comment 2: There is a need to reduce emphasis on fisheries
management and to instead increase emphasis on restocking,
preservation, establishment of defined shipping lanes, and deployment
of fish attraction devices to better protect the environment and
improve fishing opportunities.
Response: The amendment and associated rule are designed to address
the requirements of the Magnuson-Stevens Act. The Magnuson-Stevens Act
is focused on the Federal management of fishing activities. While an
ecosystem based approach to fisheries management is a principle of
NMFS' overall management strategy, achieving that goal requires the
cooperation by a host of local, state, and Federal agencies and the
constituencies upon which those agencies depend. These efforts are
ongoing.
Comment 3: There is no rationale for the Council's SSC to establish
a specific parrotfish quota for St. Croix, St. Thomas/St. John, and
Puerto Rico.
Response: The SSC's rationale for establishing the ABC levels from
which ACLs were derived for each of the islands or island groups, was
that those levels are roughly equal to the average catch during the
reference years chosen by the Council (1999-2005 for Puerto Rico and
St. Croix commercial landings, 2000-2005 for Puerto Rico recreational
and St. Thomas/St. John commercial landings). Those year sequences were
chosen by the Council based on outcomes from working group meetings of
the Annual Catch Limit Working Group (ACLG), Technical Monitoring and
Compliance Team (TMCT), and Southeast Data Assessment and Review
(SEDAR), whose task was to identify and analyze available data in the
U.S. Caribbean. The SEDAR findings, along with those of the ACLG, were
presented to the SSC for development of OFL and ABC limits. Using those
year sequences, the SSC established ABC values separately for St.
Croix, St. Thomas/St. John, and Puerto Rico. The Council chose to
reduce by 15 percent from each ABC when setting the ACL for each
island, with an additional 5.8822 percent reduction (equal to 15,000 lb
whole weight (6,804 kg)) for St. Croix, due the intense and directed
nature of the parrotfish fishery on that island. That 15 percent
reduction acts to ensure that the OFL is not exceeded as a result of
both scientific and management uncertainty.
Comment 4: The prohibition on harvest of midnight, blue, and
rainbow parrotfish would have little biological impact because the
species are extremely rare to the point of being effectively
unavailable for harvest by the
[[Page 82406]]
commercial and recreational sectors. It is necessary to maintain the
largest-sized individuals among grazing species and the lack of
species-specific parrotfish landings data would render it impossible to
enforce prohibitions on the take of midnight, blue, and rainbow
parrotfish.
Response: The Council chose to prohibit the harvest of these three
parrotfish species because they are so rare on U.S. Caribbean coral
reefs. Given those very low densities, it is likely that their recovery
will be lengthy as the populations rebuild to densities adequate to
support consistently successful reproduction. However, without this
prohibition on harvest, it is probable that recovery will take much
longer, so the Council and NMFS consider the harvest prohibition to be
an essential first step in the process of recovering these parrotfish
populations. Regarding the need to maintain the largest individuals
among grazing species, this rule prohibits harvesting the three largest
species of parrotfish (midnight, blue, rainbow) to accomplish that
goal. Finally, regardless of how the parrotfish species are reported,
they are easily identified, making it relatively straightforward to
enforce the prohibition on harvest of midnight, blue, and rainbow
parrotfish in Caribbean EEZ waters.
Comment 5: The parrotfish harvest reductions, particularly from the
waters surrounding St. Croix, are inadequate to address overfishing of
these species and do not ensure adequate provision of critical
settlement substrate for threatened Acroporid corals. Parrotfish
harvest in the U.S. Caribbean is unsustainable and the proposed
parrotfish harvest reductions are very unlikely to significantly
decrease fishing pressure on parrotfish. Since the collapse of long-
spined sea urchin populations, parrotfish are the only major grazer
remaining on U.S. Caribbean coral reefs.
Response: The NMFS Protected Resources Division developed a
Biological Opinion (BiOp) in October 2011 regarding the continued
authorization of the reef fish fishery in the U.S. Caribbean. The BiOp
focused its analyses on impacts to various species of turtles and on
the impacts of continued parrotfish harvest on the availability of
critical settlement substrate for Acroporid corals (specifically
Acropora cervicornis and A. palmata). The BiOp determined that the
continued operation of the U.S. Caribbean reef fish fishery is not
likely to jeopardize the continued existence of Acroporid corals and
not likely to destroy or adversely modify Acropora critical habitat in
the U.S. Caribbean.
This rule reduces all parrotfish harvest levels in an effort to end
overfishing of all parrotfish species. These reductions are described
in detail in Amendment 5 to the Reef Fish FMP. For St. Croix, the ACL
established by this final rule will adjust harvest to a level roughly
33 percent below the average of the most recent 2 years (2006 and 2007)
of landings available at the time the Notice of Intent to Prepare an
Environmental Impact Statement for Amendment 5 was published in April
2009 (April 17, 2009, 74 FR 17818) for. These are substantial
parrotfish harvest reductions, and both NMFS and the Council believe
that these reductions will substantially decrease fishing pressure on
these species. NMFS agrees that parrotfish may be the only major grazer
remaining on U.S. Caribbean coral reefs after the collapse of long-
spined sea urchin populations. Although there are other grazers on
Caribbean coral reefs (e.g., surgeonfish), NMFS and the Council
acknowledge that parrotfish are an important component of Caribbean
coral reef ecosystems. The level of reduction was designed to balance
those ecological considerations with the cultural importance of
parrotfish to U.S. Caribbean residents, particularly residents of St.
Croix.
Comment 6: The AMs proposed in the rule are inadequate to prevent
overfishing. The provision that allows the Council to not apply AMs if
it is determined by the Council's SSC, in conjunction with the SEFSC,
that surpassing the ACL resulted from enhanced reporting of landings,
rather than by an actual increase in harvest, contradicts the intent of
the Magnuson-Stevens Act with respect to the application of AMs.
Response: AMs included in both Amendments 2 and 5 are post-season
in nature to account for the present reporting characteristics of the
U.S. Caribbean fisheries. The AMs will be applied automatically unless
there is a determination by the SEFSC (in consultation with the
Council's SSC) that the ACL increase is due to improved reporting
rather than due to an actual increase in landings. Post-season AMs are
not always the preferred method of a management strategy to respond to
an ACL overage, and the fishers themselves have requested that in-
season monitoring schemes be developed. Regional efforts are ongoing in
the U.S. Caribbean to develop better methodologies to submit, compile,
distribute, and analyze landings data. Progress has already been made,
particularly in the electronic transmittal of data from state to
Federal agencies. However, due to delays inherent in the present
reporting process, landings data are not available within the fishing
season, so only post-season AMs are presently feasible. Regarding the
SSC and SEFSC review of data to determine if exceeding an ACL was the
result of better reporting or increased landings, this provision allows
for the best scientific information available to be applied to more
effectively manage fishing activity. Thus, both the Council and NMFS
decided this was a necessary approach if the long-term goal of more
timely and accurate reporting was to be achieved.
Comment 7: The adverse economic impacts of the rule on USVI small
businesses are overestimated because it assumes all of the licensed
fisherman land species that are the subject of the final rule.
Response: It was assumed in the initial regulatory flexibility
analysis (IRFA), and is assumed here that each and every one of the 383
licensed commercial fishermen of the USVI represents a small business.
Hence, the final rule potentially impacts 383 small businesses in the
USVI, whether they all presently fish for these species or not. The
total adverse economic impacts to St. Croix and St. Thomas/St. John
commercial fishermen are estimated independently of the number of small
businesses, and instead by estimated reductions in historical and
forecasted annual landings caused by shortened fishing seasons. The
number of small businesses is used to estimate the average adverse
economic impact per small business. If the number of small businesses
adversely affected is lower, the average adverse economic impact per
small business will be greater, but the estimates of the total adverse
economic impacts do not change. The best information available was used
to analyze these economic impacts.
Comment 8: The species of concern in this amendment should not have
been considered as being ``overfished or undergoing overfishing'' in
all of the island areas, as the incidents of overfishing are localized.
As a result of previous management measures taken by both the Council
and the states to address these incidents of overfishing (i.e., the
2005 Sustainable Fisheries Act Amendment (2005 Caribbean SFA
Amendment); seasonal and permanent closures; size limits; quotas) along
with the use of available scientific information, the species groups
classified as overfishing should have been reclassified. All of these
previous actions should have been considered
[[Page 82407]]
while setting ACLs, and these values in most cases should have been the
same as for species considered not to be undergoing overfishing.
Response: The purpose of Amendments 2 and 5 was not to revise the
status of stocks with respect to their classification as either
undergoing overfishing or overfished, but to establish management
reference points and ACLs based upon the previously determined status
of those stocks. Overfished or undergoing overfishing designations
apply to the fishery as defined in the FMP, which is Caribbean-wide.
Management reference points were set U.S. Caribbean-wide, then
allocated among the three island groups (St. Thomas/St. John, St.
Croix, Puerto Rico) according to proportional contribution by each
island group to the total average landings used to set the MSY proxy
and OFL. Because of the nature of landings data in the U.S. Caribbean,
where landings are commonly reported to fishery management unit (FMU)
level rather than to species level (with the exception of snapper in
Puerto Rico, as described in Amendment 5 to Reef Fish FMP), ACL
assignments were made at the FMU level rather than at the level of the
individual species.
The 2005 Caribbean SFA Amendment was taken into consideration when
devising alternatives included in Amendments 2 and 5. That amendment
implemented a variety of management measures for reef fish species in
the U.S. Caribbean, including area closures that may have affected
reported landings. A primary consideration during the development of
the management reference point alternatives was the choice of the year
sequence used to establish the average catch, and from that, the MSY
proxy and overfishing limit (OFL) were developed. When evaluating
alternatives for year sequences for average catch, the Council chose
not to use data from any years more recent than 2005, due to the
potential impact on landings of the previous management measures listed
in the comment.
The Council chose a 0.85 reduction to set the ACLs. Before making a
decision on the appropriate reduction, the Council reviewed public
comments and the recommendation of its Reef Fish Advisory Panel, which
functions as interface between user groups and the Council and provides
insight from in-the-field observations. Fishers and the Advisory Panel
supported a 0.85 reduction while an environmental organization
supported a 0.75 reduction. The Council also had several discussions
regarding the issue of uncertainty and the value of choosing an
uncertainty factor that would be most acceptable to the territorial and
commonwealth governments. The Council determined that the 0.85 scalar
would be most likely to result in the application of compatible state
regulations and increased data collection efforts, thereby stabilizing
the management regime.
After Amendments 2 and 5 were developed, the Council initiated
development of the 2011 Caribbean ACL Amendment pertaining to those
species not designated as undergoing overfishing. The Council chose to
reduce by 10 percent for most of the units included in the 2011
Caribbean ACL Amendment, rather than by 15 percent as was done for the
units included in Amendment 5 to the Reef Fish FMP. This 10 percent
reduction was chosen because landings patterns for the species included
in the 2011 Caribbean ACL Amendment were less variable than for the
species included in Amendment 5 to the Reef Fish FMP. It was determined
by the Council that those less variable landings required a smaller
reduction to minimize the likelihood that landings in any year would
exceed the OFL.
Comment 9: The ACLs proposed are inconsistent with National
Standard (NS) 1, which requires that conservation and management
measures shall prevent overfishing while achieving the OY from each
fishery. Setting ACLs creates artificial limitations for the fishermen
of St. Thomas, and management to an artificial buffer is not necessary
because their fishery has been stable throughout the past four decades.
Response: The 2006 revisions to the Magnuson-Stevens Act require
that ACLs be set at a level such that overfishing does not occur,
regardless of the relative stability of the reported landings.
Available data in the U.S. Caribbean are not sufficient to support
direct estimation of MSY and other key parameters. In such cases, the
NS 1 guidelines direct regional fishery management councils to estimate
them using reasonable proxies, like long-term average catch, and to
consider uncertainty in determining the appropriateness of alternative
proxies. The NS 1 guidelines suggest that ACLs and OY should generally
be reduced from the overfishing threshold and MSY, respectively, to
effectively prevent overfishing. The Council chose to set OY and ACL as
equal values, taking into consideration the socioeconomic and
ecological components of OY when determining how far ACLs should be
reduced below the overfishing threshold. An `uncertainty' factor was
applied to reduce allowable landings below the OFL in an effort to
account for uncertainty in the scientific and management processes. The
uncertainty factor is designed to account for scientific uncertainty in
estimating the OFL and management uncertainty in effectively
constraining harvest over time. The reduction (buffer) chosen by the
Council will prevent overfishing by minimizing the likelihood that
annual landings will exceed the OFL, while achieving, on a continuing
basis, OY.
Comment 10: The establishment of ACLs is not consistent with
National Standard 2 (NS 2), which requires that conservation and
management measures be based in the best scientific information
available. ACLs are not based on the best scientific information
because they were based on unreliable reported landings data (e.g. not
species-specific), and that data should be obtained from port sampling
and this method was not used to formulate the ACLs.
Response: NMFS and the Council have considered NS 2 in the
development of ACLs. Although the reported landings data has areas in
need of improvement, this is the best scientific information available.
Those landings data are provided by the fishers on an island-specific
basis. The SEFSC, along with participating state, Federal, private, and
fishing interests conducted analyses of port sampling data and
determined they were inadequate with respect to the requirements for
randomness and temporal consistency which therefore minimizes the
utility of port sampling for establishing ACLs.
Comment 11: The establishment of management measures in Amendments
2 and 5 is not consistent with National Standard 6 (NS 6), which
requires that conservation and management measures take into account,
and allow for variations among fisheries, fishery resources, and
catches. The variability in the fishery of St. Thomas/St. John is low
and almost entirely due to normal year-to-year fluctuations in
environmental variables, and that variability should be considered in
the establishment of management measures for the specific island group.
Response: The landings variability for all island groups was
analyzed. The data used for all islands for establishing management
measures has the same limitations and were therefore treated in the
same manner to account for both expected and unpredictable variations.
This was done by applying a buffer to reduce OY and ACL from the OFL or
ABC. Management reference points were set for the U.S. Caribbean and
then
[[Page 82408]]
allocated among the three island groups (St. Thomas/St. John, St.
Croix, Puerto Rico) according to the proportional contribution by each
island group to the total average landings used to set the MSY proxy
and OFL.
Comment 12: The designation of Puerto Rico and the USVI as fishing
communities under the terms of National Standard 8 (NS 8) is
questionable. NS 8 requires that conservation and management measures
take into account the importance of fishery resources to fishing
communities by using economic and social data to provide the sustained
participation of the communities and minimize adverse economic impacts
to the community to the extent practicable. The passage of recent ACLs
in 2010 and 2011 should have been accompanied by in-depth analysis of
the impacts of those actions upon the USVI fishing communities, and no
ACLs should be approved until the analyses are completed and
implications are considered.
Response: NMFS and the Council recognize the designation of St.
Thomas/St. John, St. Croix, and coastal areas of Puerto Rico as fishing
communities. However, for Puerto Rico, the fishing community
designation does not apply to the entire island, but instead to the
northern coastal, southern coastal, eastern coastal, and western
coastal municipalities combined. The impacts of the provisions of
Amendments 2 and 5 are included within the analysis of the social
impacts, which is found in the Social Impact Assessment (section 9) of
the Final Environmental Impact Statement. Additionally, the NS 8
guidelines state that consideration of impacts to designated fishing
communities be within the context of the conservation requirements of
the Magnuson-Stevens Act. These requirements were considered during the
development of Amendments 2 and 5. The impacts to the fishing
communities were analyzed and minimized to the extent practicable while
still meeting the other Magnuson-Stevens Act requirements.
Deliberations regarding the importance of fishery resources to affected
fishing communities, therefore, must not compromise the achievement of
conservation requirements and goals of the FMP.
Comment 13: For ACLs and AMs to be effective, Puerto Rico and the
USVI should achieve compatibility with Federal regulations, and
adequate funding should be available to collect and process data,
enforce regulations, and effectively manage the fishery. There is an
importance to ``buy in'' by the fishers with regard to the concept of a
regulated, sustainable resource.
Response: Efforts are underway by the Council, NMFS, and the states
to establish compatible regulations in both Puerto Rico and the USVI,
but those regulatory changes must be effectuated by the state
governments rather than by the Council or NMFS. NMFS recognizes the
advantages to developing and implementing regulations to ensure the
long-term sustainability of Caribbean fisheries resources and the
ecosystems upon which they depend.
Comment 14: The cost of the prohibition on fishing for blue,
rainbow and midnight parrotfish in the EEZ off the USVI, especially St.
Croix, was overestimated because the species are rarely, if ever,
caught in Federal waters and the adverse impacts should be minimal.
Response: Because parrotfish harvest data is not available at the
species level in the USVI, the expected economic effects of the
regulations associated with blue, rainbow, and midnight parrotfish
could not be quantitatively assessed at the species level. As a result,
the IRFA only provided quantitative estimates of the expected economic
effects of the proposed regulations on all parrotfish species combined.
Because blue, rainbow, and midnight parrotfish may not be the primary
parrotfish species harvested, the estimates of the expected economic
impacts on all parrotfish species may not be representative of the
impacts on these three species and may, in fact, overestimate actual
effects. However, overestimation of potential economic effects is not
expected to be a substantive issue because the purpose of the RFA is to
identify alternatives that achieve the regulatory objective while
reducing or minimizing significant adverse economic effects on small
entities. If the effects are minimal, as the comment suggests, then the
need to reduce these effects is diminished.
Comment 15: Fishermen will not be able to relocate into territorial
waters to mitigate for any losses of parrotfish landings because the
resource is overexploited in territorial waters. It is incorrect to
assume that USVI fishermen may be able to mitigate for some, but not
all, of the losses incurred by the parrotfish prohibition.
Response: The RIR determined and the IRFA indicated that USVI
fishermen could mitigate for 20 percent of the potential loss of
landings by shifting effort into territorial waters. In response to
this comment on the proposed rule, the FRFA includes the possibility
that fishermen cannot mitigate for any losses of landings of
parrotfish, snapper and grouper in the USVI as a result of new ACLs.
This new assumption indicates that the ACLs may be up to 100 percent
effective in reducing ACL overages.
Classification
The Regional Administrator, Southeast Region, NMFS has determined
that this final rule is necessary for the conservation and management
of the species within Amendments 2 and 5 and is consistent with the
Magnuson-Stevens Act, and other applicable law.
This final rule has been determined to be not significant for
purposes of Executive Order 12866. However, ACLs are a controversial
issue in the U.S. Caribbean, which is a region with populations
characterized by large percents of racial/ethnic minorities, high
poverty rates, and low median household incomes. Moreover, commercial
fishermen of St. Croix and St. Thomas/St. John will experience a
substantially greater adverse economic impact relative to their
counterparts in Puerto Rico.
Pursuant to the Regulatory Flexibility Act, 5 U.S.C. 601-612, NMFS
prepared a final regulatory flexibility analysis (FRFA) that includes a
statement of need for, and objectives of, the rule; a summary and
assessment of significant issues raised by public comments; a
description and estimate of the number of small entities; a description
of the compliance requirements, including estimates of the adverse
economic impacts; and a description of steps taken to minimize
significant adverse economic impact on small entities. The description
of the action, why it is being considered, and the objectives of this
action are contained in the proposed rule (76 FR 66675, Oct. 27, 2011),
at the beginning of this section in the preamble, and in the SUMMARY
section of the preamble. A copy of the full analysis is available from
NMFS (see ADDRESSES). A summary of the FRFA follows.
The final rule, which consists of several actions, will establish
recreational bag limits for specified reef fish species; specify ACLs
and AMs for parrotfish, grouper, snapper, and queen conch and establish
framework measures to facilitate regulatory modifications. The rule
will not alter existing reporting or record-keeping requirements.
The Magnuson Stevens Act provides the statutory basis for the rule.
There were no significant issues regarding the IRFA raised by
public comments; however, three comments were received regarding the
estimate of the adverse economic impacts on USVI fishermen. The first
comment disagreed with the description of the impact of the
[[Page 82409]]
prohibition on fishing for blue, rainbow and midnight parrotfish in the
EEZ off the USVI, especially St. Croix. The comment contends that the
cost of the prohibition on fishing for and possession of blue, rainbow
and midnight parrotfish in the EEZ, particularly off St. Croix, was
overestimated because the species are rarely, if ever, caught in
Federal waters and the adverse impact should be minimal. Because
parrotfish harvest data is not available at the species level in the
USVI, the expected economic effects of the regulations associated with
blue, rainbow, and midnight parrotfish could not be quantitatively
assessed at the species level. As a result, the IRFA only provided
quantitative estimates of the expected economic effects of the proposed
regulations on all parrotfish species combined. Because blue, rainbow,
and midnight parrotfish may not be the primary parrotfish species
harvested, the estimates of the expected economic impacts on all
parrotfish species may not be representative of the impacts on these
three species and, in fact, overestimate actual effects. However,
overestimation of potential economic effects is not expected to be a
substantive issue because the purpose of the RFA is to identify
alternatives that achieve the regulatory objective while reducing or
minimizing significant adverse economic effects on small entities. If
the effects are minimal, as the comment suggests, then the need to
reduce these effects is diminished.
The second comment disagreed with the assumption that USVI
fishermen may be able to mitigate for some, but not all, losses by
increasing landings of snapper, grouper, and parrotfish species taken
in the EEZ by relocating into territorial waters, although it is more
difficult for USVI fishermen to substitute fishing in territorial
waters for fishing in Federal waters. The comment contends that
fishermen would not be able to relocate into territorial waters to
mitigate for any losses of parrotfish landings because the resource is
overexploited in territorial waters. NMFS, in its RIR, determined and
through the IRFA indicated that USVI fishermen could mitigate for 20
percent of the potential loss of landings by shifting effort into
territorial waters. In response to this comment, the FRFA includes the
possibility that fishermen cannot mitigate for any losses of landings
of parrotfish, snapper and grouper in the USVI. That new assumption
results in the ACLs being up to 100 percent effective in reducing an
overage.
The third comment contended the estimate of the adverse economic
impacts to USVI small businesses was too high because it assumed all of
the licensed fishermen land species that are the subject of the final
rule. NMFS assumed in the IRFA, and assumes here, that every one of the
383 licensed commercial fishermen of the USVI represents a small
business that may potentially be impacted by this rule, whether they
all presently fish for these species or not. The total adverse economic
impacts to St. Croix and St. Thomas/St. John commercial fishermen are
estimated independently of the number of small businesses and instead
by estimated reductions in historical and forecasted annual landings.
The number of small businesses is used to estimate the average adverse
economic impact per small business. If the number of small businesses
adversely affected is lower, the average adverse economic impact per
small business will be greater.
This final rule is expected to directly affect businesses that
harvest parrotfish, snapper and grouper from Federal waters off Puerto
Rico and the USVI and those that harvest queen conch in Federal waters
off St. Croix. These businesses are in the finfish fishing (NAICS
114111), shellfish fishing (NAICS 114112) and charter fishing
industries (NAICS 487210). A business 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 or number of employees not in excess of the Small Business
Administration's (SBA's) size standards. The finfish and shellfish
fishing industries have an SBA size standard of $4.0 million in annual
receipts, and the charter fishing industry's size standard is $7.0
million in annual receipts. NMFS assumes all commercial (finfish and
shellfish) and charter fishing businesses that operate in the U.S.
Caribbean have annual receipts less than these size standards and are
small businesses.
In 2008, there were from 868 to 874 active commercial fishermen in
Puerto Rico; 74 percent of these fishermen were captains and the
remaining 26 percent were crew members. NMFS assumes each captain
represents a small business in the finfish fishing and shellfish
fishing industries and each member of the crew an employee of one of
those businesses. Therefore, NMFS concludes that there are 642 to 644
small businesses in the finfish fishing and shellfish fishing
industries in Puerto Rico, and potentially all of these businesses will
be directly affected by the rule. In 2008, there were 223 licensed
commercial fishermen in St. Croix and 160 in St. Thomas/St. John. There
is a moratorium on increasing the number of U.S. Virgin Islands
commercial fishing licenses, so the FRFA assumes the 223 commercial
fishermen in St. Croix and 160 commercial fishermen in St. Thomas/St.
John represent 383 small businesses in the finfish fishing and
shellfish fishing industries in the U.S. Virgin Islands who will be
directly affected by the rule.
There are an estimated 9 small businesses in the charter fishing
industry in Puerto Rico, 12 such businesses in St. Thomas/St. John and
1 in St. Croix. The final rule will apply to all of these small
businesses.
The final rule will apply to all small businesses in Puerto Rico,
St. Croix and St. Thomas/St. John within the finfish fishing, shellfish
fishing, and charter fishing industries. Therefore, the final rule
applies to a substantial number of small entities in the U.S. Caribbean
in these industries. Charter fishing operations in Puerto Rico and the
U.S. Virgin Islands target pelagic species and tend not to target queen
conch or reef fish species in Federal waters. Consequently, it is
expected that small businesses in the charter fishing industry in
Puerto Rico, St. Croix or St. Thomas/St. John will experience little to
no adverse economic impact because of this final rule.
The final rule is expected to result in one shortened Federal
fishing season in the Puerto Rico EEZ, three shortened fishing seasons
in the St. Croix EEZ, and three shortened fishing seasons in the St.
Thomas/St. John EEZ. This final rule is expected to have a
substantially greater adverse economic impact on small businesses in
the finfish fishing industries in St. Croix and St. Thomas/St. John
than in Puerto Rico because the projected reductions in harvest of the
different species, as discussed in the following paragraphs, are
substantially larger in the USVI than in Puerto Rico. There is expected
to be no adverse economic impact on small businesses in the shellfish
fishing industry.
A comparison of the Puerto Rico commercial ACLs for parrotfish,
grouper and Snapper Units 1, 3 and 4 to baseline annual commercial
landings suggests the commercial ACLs for these units will not require
reductions in the lengths of the Federal commercial fishing seasons for
these units in the Puerto Rico EEZ. Therefore, NMFS expects no adverse
economic impact on small businesses in Puerto Rico that harvest these
species.
The Puerto Rico commercial Snapper Unit 2 ACL is less than the
baseline annual landings, which suggests there will be an overage of
Snapper Unit 2
[[Page 82410]]
landings of 509 lb (231 kg) and a shortened Snapper Unit 2 fishing
season in the Puerto Rico EEZ. NMFS expects that Puerto Rico's small
businesses will mitigate for the potentially shortened Snapper Unit 2
fishing season in the Puerto Rico EEZ by moving into territorial waters
to harvest Snapper Unit 2 species during the time the Federal season is
closed, because approximately 95 percent of fishable area off Puerto
Rico is in territorial waters. Hence, NMFS projects that Puerto Rico
small businesses would lose up to 10 percent of baseline Snapper Unit 2
landings annually with a value up to $383. That loss represents less
than a tenth of a percent of annual Snapper Unit 2 landings and on
average, less than 1 lb (0.45 kg) of Snapper Unit 2 species and less
than $1 lost per small business in Puerto Rico. Another mitigating
behavior would be to target alternative species in the Puerto Rico EEZ
that have open seasons.
The St. Croix ACLs for parrotfish, snapper and grouper are less
than baseline average annual landings, which indicates fishing seasons
for these units will be reduced. St. Croix small businesses will incur
annual losses of landings of up to 34 percent of parrotfish landings,
27 percent of snapper landings, and 6 percent of grouper landings each
year. These reductions represent losses of ex-vessel revenue up to
approximately $0.83 million annually. The average St. Croix small
business will lose up to $3,706 annually. When estimated losses of
revenues from the 2011 ACLs Amendment are added, St. Croix small
businesses lose collectively up to $1.19 million annually.
The St. Thomas/St. John ACLs for parrotfish, snapper and grouper
are less than baseline average annual landings, which indicates fishing
seasons for these units will be reduced. St. Thomas/St. John small
businesses will lose up to 6 percent of parrotfish, 20 percent of
snapper and 9 percent of grouper landings each year. These reductions
represent losses of ex-vessel revenue up to approximately $0.27
million. The average St. Thomas/St. John small business will lose up to
$1,690 annually. When estimated losses of revenues from the 2011 ACLs
Amendment are added, St. Thomas/St. John small businesses lose
collectively up to $0.51 million annually.
The percent of fishable area in the U.S. Virgin Islands'
territorial waters is significantly less than the percent of fishable
area in Puerto Rico's territorial waters. 38 percent of fishable area
off the U.S. Virgin Islands lies within the U.S. Caribbean EEZ, and a
larger share of landings in St. Croix and St. Thomas/St. John derive
from fishing in the EEZ than in Puerto Rico. Therefore, it is more
difficult for U.S. Virgin Islands fishermen to substitute fishing in
territorial waters for fishing in Federal waters.
The final rule rejects alternatives that would have established
ACLs and AMs that would have resulted in larger reductions in Federal
fishing seasons and greater significant adverse economic impacts on
small businesses, especially in the USVI.
List of Subjects in 50 CFR Part 622
Fisheries, Fishing, Puerto Rico, Reporting and recordkeeping
requirements, Virgin Islands.
Dated: December 22, 2011.
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
0
1. The authority citation for part 622 continues to read as follows:
Authority: 16 U.S.C. 1801 et seq.
0
2. In Sec. 622.32, paragraph (b)(1)(v) is added to read as follows:
Sec. 622.32 Prohibited and limited-harvest species.
* * * * *
(b) * * *
(1) * * *
(v) No person may fish for or possess midnight parrotfish, blue
parrotfish, or rainbow parrotfish in or from the Caribbean EEZ. Such
fish caught in the Caribbean EEZ must be released with a minimum of
harm.
* * * * *
0
3. In Sec. 622.33, paragraph (d)(1) is revised to read as follows:
Sec. 622.33 Caribbean EEZ seasonal and/or area closures.
* * * * *
(d) * * *
(1) Pursuant to the procedures and criteria established in the FMP
for Queen Conch Resources in Puerto Rico and the U.S. Virgin Islands,
when the ACL, as specified in Sec. 622.49(c)(2)(i)(A), is reached or
projected to be reached, the Regional Administrator will close the
Caribbean EEZ to the harvest and possession of queen conch, in the area
east of 64[deg]34[min] W. longitude which includes Lang Bank, east of
St. Croix, U.S. Virgin Islands, by filing a notification of closure
with the Office of the Federal Register.
* * * * *
0
4. In Sec. 622.39, paragraph (g) is added to read as follows:
Sec. 622.39 Bag and possession limits.
* * * * *
(g) Caribbean reef fish--(1) Applicability. Paragraph (a)(1) of
this section notwithstanding, the bag limits of paragraph (g)(2) of
this section do not apply to a person who has a valid commercial
fishing license issued by Puerto Rico or the U.S. Virgin Islands.
(2) Bag limits. Groupers, snappers, and parrotfishes combined--5
per person per day or, if 3 or more persons are aboard, 15 per vessel
per day; but not to exceed 2 parrotfish per person per day or 6
parrotfish per vessel per day.
0
5. In Sec. 622.48, paragraph (b) is revised and paragraph (m) is added
to read as follows:
Sec. 622.48 Adjustment of management measures.
* * * * *
(b) Caribbean reef fish. Fishery management units (FMUs), quotas,
trip limits, bag limits, size limits, closed seasons or areas, gear
restrictions, fishing years, MSY, OY, TAC, maximum fishing mortality
threshold (MFMT), minimum stock size threshold (MSST), overfishing
limit (OFL), acceptable biological catch (ABC) control rules, ACLs,
AMs, ACTs, and actions to minimize the interaction of fishing gear with
endangered species or marine mammals.
* * * * *
(m) Caribbean queen conch. Quotas, trip limits, bag limits, size
limits, closed seasons or areas, gear restrictions, fishing year, MSY,
OY, TAC, MFMT, MSST, OFL, ABC control rules, ACLs, AMs, ACTs, and
actions to minimize the interaction of fishing gear with endangered
species or marine mammals.
0
6. In Sec. 622.49, the section heading is revised and paragraph (c) is
added to read as follows:
Sec. 622.49 Annual catch limits (ACLs) and accountability measures
(AMs).
* * * * *
(c) Caribbean island management areas. If landings from a Caribbean
island management area, as specified in Appendix E to part 622, except
for landings of queen conch (see Sec. 622.33(d)), are estimated by the
SRD to have exceeded the applicable ACL, as specified in paragraph
(c)(1) of this section for Puerto Rico management
[[Page 82411]]
area species or species groups, paragraph (c)(2) of this section for
St. Croix management area species or species groups, or paragraph
(c)(3) for St. Thomas/St. John management area species or species
groups, 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 fishing season for the applicable species or
species groups that year by the amount necessary to ensure landings do
not exceed the applicable ACL. If NMFS determines the ACL for a
particular species or species group was exceeded because of enhanced
data collection and monitoring efforts instead of an increase in total
catch of the species or species group, NMFS will not reduce the length
of the fishing season for the applicable species or species group the
following fishing year. Landings will be evaluated relative to the
applicable ACL based on a moving multi-year average of landings, as
described in the FMP. With the exceptions of Caribbean queen conch in
Puerto Rico and St. Thomas/St. John management areas, goliath grouper,
Nassau grouper, midnight parrotfish, blue parrotfish, and rainbow
parrotfish, ACLs are based on the combined Caribbean EEZ and
territorial landings for each management area. The ACLs specified in
paragraphs (c)(1), (c)(2), and (c)(3) of this section are given in
round weight. (See Sec. 622.32 for limitations on taking prohibited
and limited harvest species. The limitations in Sec. 622.32 apply
without regard to whether the species is harvested by a vessel
operating under a valid commercial fishing license issued by Puerto
Rico or the U.S. Virgin Islands or by a person subject to the bag
limits.)
(1) Puerto Rico--(i) Commercial ACLs. The following ACLs apply to
commercial landings of Puerto Rico management area species or species
groups.
(A) Queen conch--0 lb (0 kg), for the EEZ only.
(B) Parrotfishes--52,737 lb (23,915 kg).
(C) Snapper Unit 1--284,685 lb (129,131 kg).
(D) Snapper Unit 2--145,916 lb (66,186 kg).
(E) Snapper Unit 3--345,775 lb (156,841 kg).
(F) Snapper Unit 4--373,295 lb (169,324 kg).
(G) Groupers--177,513 lb (80,519 kg).
(ii) Recreational ACLs. The following ACLs apply to recreational
landings of Puerto Rico management area species or species groups.
(A) Queen conch--0 lb (0 kg), for the EEZ only.
(B) Parrotfishes--15,263 lb (6,921 kg).
(C) Snapper Unit 1--95,526 lb (43,330 kg).
(D) Snapper Unit 2--34,810 lb (15,790 kg).
(E) Snapper Unit 3--83,158 lb (37,720 kg).
(F) Snapper Unit 4--28,509 lb (12,931 kg).
(G) Groupers--77,213 lb (35,023 kg).
(2) St. Croix. (i) ACLs. The following ACLs apply to landings of
St. Croix management area species or species groups.
(A) Queen conch--50,000 lb (22,680 kg).
(B) Parrotfishes--240,000 lb (108,863 kg).
(C) Snappers--102,946 lb (46,696 kg).
(D) Groupers--30,435 lb (13,805 kg).
(ii) [Reserved]
(3) St. Thomas/St. John. (i) ACLs. The following ACLs apply to
landings of St. Thomas/St. John management area species or species
groups.
(A) Queen conch--0 lb (0 kg), for the EEZ only.
(B) Parrotfishes--42,500 lb (19,278 kg).
(C) Snappers--133,775 lb (60,679 kg).
(D) Groupers--51,849 lb (23,518 kg).
(ii) [Reserved]
0
7. In table 2 of Appendix A to Part 622, Lutjanidae--Snappers, units 1
and 2 are revised; In Serranidae--Sea basses and groupers, units 3 and
4 are revised; and In Serranidae--Sea basses and groupers, unit 5 is
added to read as follows:
Appendix A to Part 622--Species Tables
* * * * *
Table 2 of Appendix A to Part 622--Caribbean Reef Fish
Lutjanidae--Snappers
Unit 1
Black snapper, Apsilus dentatus
Blackfin snapper, Lutjanus buccanella
Silk snapper, Lutjanus vivanus
Vermilion snapper, Rhomboplites aurorubens
Wenchman, Pristipomoides aquilonaris
Unit 2
Cardinal, Pristipomoides macrophthalmus
Queen snapper, Etelis oculatus
* * * * *
Serranidae--Sea basses and Groupers
* * * * *
Unit 3
Coney, Epinephelus fulvus
Graysby, Epinephelus cruentatus
Red hind, Epinephelus guttatus
Rock hind, Epinephelus adscensionis
Unit 4
Black grouper, Mycteroperca bonaci
Red grouper, Epinephelus morio
Tiger grouper, Mycteroperca tigris
Yellowfin grouper, Mycteroperca venenosa
Unit 5
Misty grouper, Epinephelus mystacinus
Yellowedge grouper, Epinephelus flavolimbatus
* * * * *
0
8. Appendix E to part 622 is added to read as follows:
Appendix E to Part 622--Caribbean Island/Island Group Management Areas
Table 1 of Appendix E to Part 622--Coordinates of the Puerto
Rico Management Area.
The Puerto Rico management area is bounded by rhumb lines
connecting, in order, the following points.
----------------------------------------------------------------------------------------------------------------
Point North lat. West long.
----------------------------------------------------------------------------------------------------------------
A (intersects with the International/EEZ 19[deg]37'29'' 65[deg]20'57''
boundary).
B (intersects with the EEZ/Territorial 18[deg]25'46.3015'' 65[deg]06'31.866''
boundary).
From Point B, proceed southerly along the
EEZ/Territorial boundary to Point C
C (intersects with the EEZ/Territorial 18[deg]13'59.0606'' 65[deg]05'33.058''
boundary).
D..................................... 18[deg]01'16.9636'' 64[deg]57'38.817''
E..................................... 17[deg]30'00.000'' 65[deg]20'00.1716''
F..................................... 16[deg]02'53.5812'' 65[deg]20'00.1716''
From Point F, proceed southwesterly, then
northerly, then easterly, and finally
southerly along the International/EEZ
boundary to Point A
A (intersects with the International/ 19[deg]37'29'' 65[deg]20'57''
EEZ boundary).
----------------------------------------------------------------------------------------------------------------
[[Page 82412]]
Table 2 of Appendix E to Part 622--Coordinates of the St. Croix
Management Area.
The St. Croix management area is bounded by rhumb lines
connecting, in order, the following points.
----------------------------------------------------------------------------------------------------------------
Point North lat. West long.
----------------------------------------------------------------------------------------------------------------
G......................................... 18[deg]03'03'' 64[deg]38'03''
From Point G, proceed easterly, then
southerly, then southwesterly along the
EEZ/Territorial boundary to Point F
F..................................... 16[deg]02'53.5812'' 65[deg]20'00.1716''
E..................................... 17[deg]30'00.000'' 65[deg]20'00.1716''
D..................................... 18[deg]01'16.9636'' 64[deg]57'38.817''
G..................................... 18[deg]03'03'' 64[deg]38'03''
----------------------------------------------------------------------------------------------------------------
Table 3 of Appendix E to Part 622--Coordinates of the St.
Thomas/St. John Management Area.
The St. Thomas/St. John management area is bounded by rhumb
lines connecting, in order, the following points.
----------------------------------------------------------------------------------------------------------------
Point North lat. West long.
----------------------------------------------------------------------------------------------------------------
A (intersects with the International/EEZ 19[deg]37'29'' 65[deg]20'57''
boundary).
From Point A, proceed southeasterly along
the EEZ/Territorial boundary to Point G
G..................................... 18[deg]03'03'' 64[deg]38'03''
D..................................... 18[deg]01'16.9636'' 64[deg]57'38.817''
C (intersects with the EEZ/Territorial 18[deg]13'59.0606'' 65[deg]05'33.058''
boundary).
From Point C, proceed northerly along the
EEZ/Territorial boundary to Point B
B (intersects with the EEZ/Territorial 18[deg]25'46.3015'' 65[deg]06'31.866''
boundary).
A (intersects with the International/ 19[deg]37'29'' 65[deg]20'57''
EEZ boundary).
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[FR Doc. 2011-33512 Filed 12-29-11; 8:45 am]
BILLING CODE 3510-22-P